Skip to main content

Full text of "Journal of ethnobiology."

See other formats


VIC j 
5ILY 


JOURNAL (of) ETHNOBIOLOGY 


Maya knowledge and “science wars” 


— Anderson 


Eastern Sumbanese bird classification 
— Forth 


Knowing, gathering and eating: 
knowledge and attitudes about wild food 
in an Isan village in Northeastern Thailand 


— Somnasang & Moreno-Black 


The jaguars of Altar Q, Copan, Honduras: 
faunal analysis, archaeology, and ecology 
— Ballinger & Stomper 


Perception and management of cassava 
(Manihot esculenta Crantz) diversity 
among Makushi Amerindians of Guyana 


— Elias et al. 


The historical ecology of Southeastern 
longleaf pine and its southernmost 
expression — Walker 


A cladistic approach to comparative 
ethnobotany — Hart & Cox 


Volume 20, Number 2. Winter 2000 


JOURNAL STAFF 
EDITOR: ng sca “ie 1 Oi of Anthropology, Tulane University, New Orleans, LA 70118 


deere penn ‘Spanish Alejandro de Avila B., A. P. 533, Oaxaca, Oaxaca C.P. 68000, MEXICO 


(serbo@antequera 
aici si vk STANT: mei Dudley, Department of Anthropology, Tulane University, New Orleans, LA 
mul abot Dalen br edu) 
BOOK REVIEW Michael K. Steinberg, Department of Geography-Anthropology, University of Southern 


aine Gian ME 04038 (mstein@usm. vate edu) 


SOCIETY OFFICERS 
PRESIDENT: Deborah M. Pearsall, American Archaeology Division, University of Missouri, Columbia, 
ee ae 


PRESIDENT-ELECT: Karen R. Adams, Crow Canyon Archaeological Center, Cortez, CO 
SEC CRETARY/TRE mnie aaa Virginia Popper, UCLA Institute of Archaeology, Box 951519 Fowler A-210, Los Angeles, 


erratic cia ee Mollie S. Toll, Museum of New Mexico, Office of Archaeological Studies, Box 2087, 
Santa Fe, NM 87. 


BOARD OF TRUSTEES 
M. Kat Anderson, University of California, Davis, CA 
Enrique Salmé6n, Fort Lewis College, Durango, CO 
Melinda A. Zeder, Smithsonian Institution, Washington, D.C. 


Ex officio 
Past presidents: Steven A. Weber, Amadeo M. Rea, Elizabeth S. Wing, Paul Minnis, Cecil Brown, Catherine S. 
Fowler, ae seach Panne Permanent board member Steven D. Emslie. The editor, president, 
president-e d conference coordinator. 


at iP 


EDITORIAL BOARD 

Eugene N. Anderson, University of California, Riverside, CA: ethnobotany, China, Maya. 
Scott Atran, CNRS, Paris, FRANCE: vecaanng ag ci cea aa coagi slow science, eal 
Brent Berlin, University of Georgia, Athens, GA: ethnobiological classificat 
Robert A. Bye, Jr., ay Botanico, Universidad Satan Aut6noma de ac Aides, DE. ek ethno- 

otany, Mex 
H. Sorayya Carr, El ann California: zooarchaeology. 
Nina Etkin, University of Hawaii, Honolulu, HI: medical ethnobotany, the Pacific. 
Gayle J. Fritz, Washington University, St. oats MO: eae hae 
Terence E. Hays, Rhode Island College, Providence, RI: ethnobiology, Papua New Guinea. 
Chris Healey, Northern Territory University, Darwin, AUSTRALIA: ethnozoology, Australia and New Gui 
Timothy Johns, Macdonald College of McGill whites Quebec, CANADA: chemical ecology, a East 
Africa 


Harriet V. Kahuilediy, McGill ei Quebec, CANADA: ethno/human nutrition, First Nations cf Canada. 

David L. Lentz, New York Botanical Garden, Bronx, NY: paleoethnobotany, Mesoamerica, Central A 

Brien A. Meilleur, Center for Plant eon game Missouri Botanical Garden, St. Louis, MO: mca plant 
conservation, aR 

Naomi Miller, University of P srl wet Philadelphia, PA: paleobotany, ethnobotany, Near mssrhg Archaeology. 

Gary Nabhan, Arizona Scie Cnet useum, Tucson, AZ: ethnobiology, Sonoran desert cultu 

Darrell A. svi Oxford Centre for the Environment, Ethics, and peo Oxford University, esteae ENGLAND: 

tatural resource management, ethnoecology, tropical cultural ecolo 

Amadeo M. Rea, San Diego, CA: cultural e per zooarchaeology, ieee 

Elizabeth J. Reitz, University of Georgia, Athens, GA: zooarchaeolo 

Mollie S. Toll, Museum of New Mexico, Santa re, NM: prehistoric and historic ethnobiology. 


The Journal of Ethnobiology is published semi- annually. Manuscripts for publication and book review sections should 


sent to the appropriate editors as listed on the inside back cover of this issue. 


© Society of Ethnobiology 
ISSN 0278-0771 


a Drawing of Sumba Hornbill by Chris Healey, Visiting Fellow, North Australia 
esearc 


enna ant cn tery pie 


Journal of 
Ethnobiology 


VOLUME 20, NUMBER 2 WINTER 2000 


Si vners sete. 
pie a 


a 


Aiea 


CONTENTS 


ETHNOBIOTICA iv 


MAYA KNOWLEDGE AND “SCIENCE WARS” 
Anderson 129 


EASTERN SUMBANESE BIRD CLASSIFICATION 
Forth 161 


KNOWING, GATHERING AND EATING: KNOWLEDGE AND ATTITUDES 
ABOUT WILD FOOD IN AN ISAN VILLAGE IN NORTHEASTERN 
THAILAND 

Somnasang & Moreno-Black 197 


THE JAGUARS OF ALTAR Q, COPAN, HONDURAS: FAUNAL ANALYSIS, 
ARCHAEOLOGY, AND ECOLOGY 
Ballinger & Stomper 223 


PERCEPTION AND MANAGEMENT OF CASSAVA (MANIHOT ESCULENTA 
CRANTZ) DIVERSITY AMONG MAKUSHI AMERINDIANS OF GUYANA 
Elias et al. 239 


THE HISTORICAL ECOLOGY OF SOUTHEASTERN LONGLEAF PINE AND 
ITS SOUTHERNMOST EXPRESSION 
Walker 269 


A CLADISTIC APPROACH TO COMPARATIVE ETHNOBOTANY 
Cox 


Hart & 303 


BOOK REVIEWS 159, 193, 217, 237, 266, 300 


ETHNOBIOTICA 


Darrell Addison Posey 
1947-2001 
Darrell Posey, 53, who had a celebrated thnok ist, activ- 


ist, and specialist on Amazonia, died at Oxford, England on March oe 2001 eae inoper- 
able brain tumors that had been diagnosed a few months before. Posey probably will be 
most remembered for his research on Kayap6 Indian resource management and environ- 
mental knowledge together with his notable activism in defending the Kayap6 and other 
peoples against the Xingu Hydroelectric Project of the late 1980s. On both academic and 
darts fronts, Hoey Freres seeds su doet from — loyal colengnes and friends as 
assor nemies. A fi , Posey 
ponies! to thrive at the center of controversy. It must be that his personal drive and many 
friendships weighed more heavily in the end than the = ee —— = ond cal 
saries and his disappointments in life. Other than h 
Posey had attended the second meeting of the Society of Ethnobiology as well as many 
meetings after that and was a member of the Editorial Board of the Journal of Ethnobiology 
since the founding of the journal with volume 1, number 1 in May 1981 until his death. 

Born and raised in Henderson County, Kentucky, Posey never lost the midland accent 
characteristic of that region. He earned the B.S. in entomology at Louisiana State Univer- 
sity in 1970, the M.A. in geography and anthropology at Louisiana State University in 1974, 
and the Ph. we in anEOPEIEY at ahs sis cicn ee of ieaincer in 1979. Posey was an os 
ciplinary scl linary programs in 
research institutes in \ the 1980s and 1990s. He was also z a prolific writer. In terms of his pub- 
lished output to date, dents authored or co-authored Eee books, edited or co-edited four 
books, wrote 154 articles chapters, and produced 22 bool , some of which were 
reprinted in one form or another. He directed two museum exhibits on Kayap6 resource 
ponalaa ec and so eee the catalogs that accompanied them. He was also involved 
in the p tary films and videos, mainly on Kayapé ethnobiology 
and resource management. At the time of his death, Posey had two authored books and 
three edited books in press. 

Among the numerous awards Posey received for his k and activism were the “Chico 
Mendes Award” for Extraordinary Courage in the Defense of Nature, given by the Interna- 
tional Sierra Club in 1989 and the United Nations “Global 500 Award” for Outstanding 
Achievement in Service to the Environment, bestowed on him by the U.N. Environmental 
Programme in 1993. At the time of his death, he was coordinator of ECOS (Ethnoecology: 
The Ecological and Social Dimensions of Well-Being) at the Institute for Social and Cul- 
tural Anthropology of the University of Oxford. He also held other positions at Mansfield 
College, Oxford and the Federal University of Maranhdo, Brazil. He was elected Fellow of 
the prestigious Linnean Society of London in 1999 and he maintained professional affilia- 
tions with Linacre College (Oxford), St. Anthony’s College (Oxford), the Institute of 
Ethnobiology of the Amazon (which he had founded at Belém, Brazil), and the Carnegie 
Museum of Natural History. He held numerous advisory and editorial positions with vari- 
ous organizations, including the Society of Ethnobiology, the International Society of 
Ethnobiology, the Global Environment Facility, and the Indigenous Peoples Media Center. 

Posey rather en eny ae the ethnobiological study of Amazonia and its 
peoples. Already well-known as an } 


on Kayap6 folk entomology (among 
other findings, his research in this area showed that the Kayap6 recognized more species 
of wasps than Western taxonomy in regard to the Kayapé area, and that, indeed, one of the 


species so recognized was new to science) and native resource management, having pub- 
lished his research in numerous peer-reviewed journals, Posey in 1988 found himself at 
the center of a professional and political crisis that would catapult him eventually to glo- 
bal renown. In 1987, while serving as Director of the Ethnobiology Program at the Museu 
Paraense Emilio Goeldi in Belém, Brazil, net was asked by the then Director of mak mu- 
seum, Dr. Guilherme de La Penha, to und tal and social i 
of indi lations in the area of influence of the Xingu Hydroelectric Project, with 
unding for the shaky to be provided by Hietronorte, i a state-run electrical paver company. 
Posey later said he believed he could 
then in the late stages of planning, by working against it from the aide The dam project 
itself, once completed on the lower Xingu River, would flood a large area of indigenous 
lands and reserves, including part of the lands pertaining to the Kayap6o of the village of 
Gorotire, which i is where hidressds nee ceed: out seletie of his ethnobiological research since 
the time of his d 1 many friends. By early 1988, Posey 
realized that his work from within would come to naught; he called it an “aborted effort.” 
Later that year, he traveled with two Kayap6 Indian leaders to Washington, D.C. in order 
to denounce the dam project in the offices of the President of the World Bank, who was 
then intending to disburse half a billion dollars in loans to Brazil in order to finance that 
project. As a result of this visit, and of the negative publicity that attended it, the World 
Bank soon suspended payment of ne funds needed to drive the dam project forward. (In 
spite of Posey’s efforts, the dam f been removed from national energy plans 
in Brazil). 

Upon his return to Brazil, Posey and the K 5 lead ted and finger- 
printed on charges of harming the reputation abroad of Brazil. Soon released and awaiting 
trial on the charges, and also warned by the United States Embassy in Brasilia that his life 
was now in danger, Posey continued with plans to host the First International Congress of 
Ethnobiology, which was held in July, 1988, at Belém, Brazil. The congress included hun- 
dreds of scholars from thirty-five countries and proved to be a resounding success, in spite 
of the presence of undercover federal intelligence agents, who mingled with the crowd. 
The Declaration of Belém, which called for protection of native knowledge, use, and man- 
agement of biological resources as well as human rights of native peoples, was one of the 
results of this congress, largely thanks to Posey’s efforts. While Posey was enjoying wide- 
spread endorsement for his activism by many colleagues in the international arena, the 
charges against him and the two Kayap6 leaders were quietly dropped. 

Posey lived mostly in Germany during 1989-91 as a Humboldt Fellow; he also founded 
INEA (Institute of Ethnobiology of the Amazon), an NGO headquartered in Belém. He 
eventually vacated his research position at the Museu Goeldi and became Senior Associate 
Fellow at Oxford in 1992, where he remained in one capacity or another until his death. 
Having confronted the Brazilian federal machinery over the Xingu Hydroelectric Project 
in 1988 (and it must be said in sacs that some of Posey’s supporters were Brazilian fed- 
eral and state officials who th shared sympathy for his cause), Posey became Spe- 
cial Advisor to the Brazilian Special Secretary on Internal Affairs and Indigenous Peoples 
during 1992. In that same year, he was Convenor and President of the Earth Parliament at 
the Earth Summit in Rio de Janeiro. 

From about that time on, Posey’s work was primarily aimed at promoting the intellec- 
eas proper’) spa (IPR) = ect peoples while ees ef pen ~~ threats to 


ti g from int d other 


J 


een interests. In 1992, Eugene Parker, who had been one : of Posey’s aaicaions. 
published a scathing review of Posey’s work with the Kayap6, calling into question, in 


particular, Posey’s findings with regard to Kayap6 management and fostering of the forest 
islands _ — — hese eure savanna pscveaie tah Posey had claimed in 
Parker argued, 
essentially, that the forest islands were naturally occurring phenomena and that Posey’s 
methods in determining them to be otherwise were flawed and sloppy. The debate over 
the validity of Posey’s data was reminiscent of the Redfield/Lewis and Mead/Freeman 
controversies from earlier generations of anthropology. Posey replied in the American An- 
i = since dbaccad did not conduct his interviews in the Kayapo language, he 
to negate Posey’s conclusions about the efficacy 
of native seers in remaking the jandacupe under question. Parker then supplied a 
rejoinder in the same journal, reiterating what he had asserted to be questionable science 
on Posey’s part. Posey responded, in his defense, one more time to this critique in a chap- 
ter published in W. Balée (ed.), Advances in Historical Ecology (1998). It seems likely that this 
controversy between Parker and Posey will remain unsettled until further, scientifically 
sound archaeological and ethnolinguistic research is carried out to determine the origins 
and development of forest islands in the cerrado country of the Gorotire Kayap6. 
Regardless of this inflammatory exchange in the pages of the American Anthropologist, 
Posey by 1992 was devoting much more of his time to IPR. Indeed, he published three major 
books on that subject in 1996 (D.A. Posey and G. Dutfield, Beyond Intellectual Property; D.A. 
Posey, Traditional Resource Rights; and D.A. Posey and G. Dutfield, Indigenous Peoples and 
SHS te all = — were favorably cciisihaaes a the very end of gs life, peeey s un- 
published I to hi the K 
The two books authored . Posey and still i in press at the time oe his death are entitled 
Ethnobiology of the Kayapo Indians of Brazil and E ete ee ita nee 
A full account of Darrell Posey and the infl ayapo 
studies, native resource t, and activism for native land rights and IPR remains 
to be written. For those who knew him i in life, Darrell Posey will be remembered for his 
courage in the face of danger; his loyalty as a friend and colleague; his charismatic effect 
on researchers, young and old, around the globe; and his folksy, Kentucky wit and humor 
that never seemed to fail him, even in his darkest trials. He will be missed. 


Journal of Ethnobiology 20(2): 129-158 Winter 2000 


MAYA KNOWLEDGE AND “SCIENCE WARS” 


E. N. ANDERSON 
Department of Anthropolo 
University of California, Riverside 
Riverside, CA 92521-0418 


ABSTRACT. e-RnOWIEdge! is sociatly constructed, i ha homanis succeed i ee ‘knowing 
a great deal al t “science” 
involve extreme positions, from claims that all science is arbitrary to claims that 
science is somehow a epriiinged body of truth. : Something may be learned by 
considerin ver witha long record 
of high piiaeton: _ Yucatec Maya cuenchiainay agrees with contemporary 
g y rere tS, almost all of them highly specific, 
1. It differs in ma ts, most of them highly 
inferential and cys Lape One may centatively. conclude that common 
observation of everyday matters is more directly affected by interaction with the 
- Tae | s bead yee pelle | Bed 4 1 4 41 4 nt o. 4 


al 


operate at all levels. 


a1 Lee 1 
ovr 


Key words: Yucatec Maya, science wars, philosophy of science, 


Yucatan Peninsula 


RESUMEN.—E] El conocimiento es una construccién social, pero los humanos 


proponen que “ciencia” es verdad absoluto. Seria posible conocer mucho si 

investiguemos el conocimiento biolégico de una cultura, muy diferente, con una 

ees larga de alta en as snclaes wine etnobioldgico de los Yucatecos 
orme 


en pene Gerivedas de 3 I gases pragmatica. Pero, el es deferente en otros 


recnectons logical. S 


tentativamente que la observacion de fenémenos concretas es mas afectada por la 
interaccién con el medio ambiente que por el razén deductivo, pero que factores 
sociales influyen el pensamiento en todos niveles. 


—La connaissance est construée socialement, mais, aussi, les hommes 
apprendrent beaucoup de leurs environs. En les debats reciens sous la nature de 
“science” il y a positions extremes. Les uns propose que “science” est des chose 
arbitraires; les ities Age are science’ “est la vérité absolue. C’est possible a 
savoir plus de ces logique d’un culture 
different—un culture que tient une hae durée” civilisée. Les Maya yucateque 
possédent un sae biologique que ressemble . — ne la science 

4 s ] o. hI © ch. ‘; rva ati n 
, selon Derrida, “differances”) sont 
des choses ‘aia ou cosmologiques. On peut concluir, tentativement, que la 
observation de phenoménes concrétes est plus afectée par l’interaction avec 
l’environment que le raison logical, mais les influences sociales existent en touts 
niveaux 


gi rt 
ae as Tee Asée. / 


130 ANDERSON Vol. 20, No. 2 


SCIENCE WARS 


Anthropology has recently seen debates concerning the nature and value of 
“science.” These debates are part of a wider challenge to canons of truth, of liter- 
ary quality, and indeed of all those matters that anthropologists regard as part of 
culture. 

As is frequent in academic conflicts, the debate over “science” has quickly 
escalated, with the most famous participants being those who take the most ex- 
treme positions. This has led to the term “science wars” (see the excellent account 
in Hacking 1999). However, there are serious questions under the rhetoric. Lead- 
ing philosophers of science disagree profoundly—though, of course, less 
profoundly than the extremists of the semi-popular media—over the nature and 
practice of science. 

It is obviously impossible to summarize this debate here, even at a superficial 
level; the present article merely makes a small contribution to the knowledge base 
that underlies one aspect of the controversy, the debate on how much of science— 
in this article, more specifically the classification of living things—is social 
construction, and how much is based on a reality out there in the world. 

Loosely arrayed on one side are those such as Imre Lakatos (1976), Thomas 
Kuhn (1962), Ian Hacking (1999), and Paul Feyerabend (1987), who hold various 
positions that give social construction a large role in scientific practice. They are 
not a uniform group. Kuhn sees the social organization of science as structuring 
the quest for truth, but is not ready to write off either the search or the goal as 
hopeless. (In spite of certain claims to the contrary, Kuhn clearly states that he 
regards some paradigms as more correct than others, and he sees progress in sci- 
ence over time.) Hacking, also, explicitly distances himself from those who see 
“science” as the construction of arbitrary nonsense, though he sees social con- 
struction as important and sometimes overriding the truth. Feyerabend seems to 
hold a more radical position, at least for debating purposes; he appears to see 
science as a social belief system, no more believable on the face of it than witch- 
craft or flying-saucer lore. 

There are those who think—following Foucault (e.g. 1971) but going far be- 
yond anything Foucault actually said—that, since we cannot know external truth, 
all of the claims of science must be false, and must be made simply to keep elites in 
power, as “truth” was constructed in Orwell’s 1984 (Orwell 1948). This is the “vul- 
gar Marxist” version of Marx’ claims about religion, expanded to cover the field 
that many people see as the “new religion” of “20 century” people (on these 
matters see Hacking 1999). 

This position depends on an inconsistency: people are seen to be living in a 
completely solipsistic world in relation to the natural environment, yet to havea 
perfect grasp of the realities of interpersonal power. Thus, this position, like other 
radically “culturological” and culture-essentializing positions in anthropology, is 
deeply incoherent. People are hypothesized to have a mystical, virtually perfect 
grasp of their culture, such that insiders participate in a perfect unity that is un- 
fathomable to outsiders—yet somehow this perfect learning does not extend to 
any phenomena other than social or cultural ones, and somehow the visiting eth- 
nographer has no way of contacting that mystic participation. The natural world, 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 131 


in particular, is apprehended only via this mystically absorbed cultural percep- 
tion. The individual humans who are so superbly good at learning from their elders 
are incapable of learning from their observations. 

Arrayed on the other side are a number of philosophers who see science as a 
way of getting at real truth about the environment—an — that can be sub- 
verted or mistaken, but, when done right, gives us pragmatically consistent and 
useful data. Leaders of this general view include Philip Kitcher (1985, 1993), Larry 
Laudan (1996), Alexander Rosenberg (1992), Lewis Wolpert (1993), and many more. 
These too are a diverse lot, but they all agree that science is a search that produces 
ever more accurate data and theories, not just a social game that produces ever 
more complex arbitrary representations. 

However, and notably, all these writers have abandoned the naive positivist 
positions so popular in the early 20 century. No current philosopher of science 
(so far as Iam aware) continues to defend the near-religious regard for “covering 
laws,” “falsification,” and “objectivity” that dominated science, and confined it in 
narrow channels, through much of the Tan Hacking and Philip Kitcher 
provide especially sober and thoughtful critiques of this position (rather unfairly 
blamed on Karl Popper, who advocated such procedures but was not so naive as 
to think they defined all science; see Hacking 1999; Laudan 1996). 

It may be remembered that Francis Bacon, in his original definitions of the 
scientific enterprise, was not only aware of all these problems but was more sensi- 
tive to them than are some modern philosophers. He defined the 
observation-experiment method and warned his readers of the “Four Idols”—the 
biases we would now call “social construction” or “cultural baggage”—that can 
blind the unwary and unaware (Bacon 1901, orig. 16" cent 

As noted above, Hacking, in the most recent salvo in the long and confusing 
“science wars,” concludes that science is somewhat socially constructed, some- 
what factual (1999:99). This seems to me to be rather an evasion. 

The present paper obviously cannot even begin to summarize the literature 
on science wars.” It merely makes a single point: science is 100% socially con- 
structed, but usually an accurate representation of the world in spite of that. 
Evidence is supplied from a comparison of Maya and biological classifications of 
birds. Maya ornithological taxonomy maps fairly well onto biological taxonomy, 
but there are major differences. This disproves both simple realism (the Maya see 
the natural distinctions just as the biologists do) and extreme social construction- 
ism (the Maya system must be totally different from the biologists’, since the 
societies are so different). 

What has been missed, in the “science wars,” is the fact that society does not 
necessarily get things wrong. To say something is socially constructed is not to say 
it is inaccurate. After all, people have to learn their social constructions from each 
other. If they can learn their culture through interaction, why can they (and, thus, 
their culture) not learn about the environment from interaction, and then teach 
each other in further interpersonal interactions? 

Anthropologists have turned their ethnographic gazes onto the actual prac- 
tice of science in dozens of societies. Beginning with traditional small-scale societies, 
they have expanded their gaze to encompass modern laboratories. Particularly 
noteworthy for its impact on the intellectual field is the work of Laura Nader and 


132 ANDERSON Vol. 20, No. 2 


her associates (Nader 1996). Nader has long encouraged research on the movers 
and shapers of contemporary society, including scientists. Her group has thus stud- 
ied modern laboratories and university halls, often comparing them with her 
alternative study area, the highland Zapotec world, which has its own science 
(Gonzalez 1998; Nader 1996). 

Roberto Gonzalez, in particular, has provided some very thoughtful insights 
into Zapotec traditional agricultural science. He sees it as definitely a science (tak- 
ing “science” in sense #1, below). He analyzes it in terms of “assumptions” —folk 
theories—that hold together a body of empirical, pragmatic knowledge. He shows 
that these work like the theories of modern international science: they are basic, 
largely counterintuitive ideas, extracted from experience, and used to generate 
new practices and to explain and justify old ones. Some of them are highly ques- 
tionable, but so are some assumptions of modern science. 

Serious studies of nonwestern science go back to the dawn of anthropology. 
One recalls Frank Cushing’s researches on Zuni agriculture and food, not pub- 
lished in book form until 1920 (Cushing 1920) but carried out in the early 1870s. 
Malinowski also produced classic studies in this area (Malinowski 1935), as did 
his students such as Raymond Firth (1957) and Audrey Richards (1948). A self- 
conscious movement to study “ethnoscience” arose in the late 1940s, largely among 
students of George Murdock at Yale, working in Oceania (Goodenough 1953; 
Conklin 1962; Frake 1980). Many of the earlier ethnoscience studies seem to the 
contemporary anthropologist rather naively positivistic and formalistic, paying 
rather little attention to such ideas as did not fit well into a “Western” scientific 
framework. Ironically, this was not true of Cushing’s (or, to a somewhat lesser 
extent, Malinowski’s) work, which should have served as examples. 

Closer to the area of this paper, Scott Atran (1999) has analyzed Itz4 Maya 
“folkbiology” from a similar point of view, analyzing knowledge and its linguistic 
recognition. 

In any case, this large body of research established “ethnoscience” or “folk 
science” as something to study. Ethnographers came to see traditional knowledge 
as worthy of serious, detailed attention. They were exhorted to understand it in its 
own terms (“emically”), rather than merely comparing it (usually unfavorably) 
with “Western” science. In spite of rearguard action by opposing scholars like 
Marvin Harris (1968), studies of traditional knowledge grew and flourished apace. 
It seems only natural—in fact, surprisingly long in coming—that ethnographers 
should turn their attention on contemporary university laboratories. 


SCIENCE 


This, of course, brings us up against the question of defining “science.” Much 
recent writing conflates several different things under that label. The following 
seem to me to be quite separate phenomena: 


1. Science as search for truth—for accurate data about the world, and for theo- 


ries and hypotheses that model that world in ways that guide further searching 
and understanding. Wolpert (1993) notes that these latter are critical, and that 
science depends on fearlessly generating and testing even the most counter- 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 133 


a 


a 


i 


intuitive of proposals. It is understood that the search for truth often takes 
wrong turns, as in the famous cases of “phlogiston” (see Kuhn 1962) and static 
continents (Oreskes 1999), but that is in the nature of a search. The search is 
seen as resulting in a body of facts, or at least pragmatically useful data, held 
together by a framework of higher-level representations that can be called 
“theories” and “axioms,” or, with Gonzalez (1998), “assumptions.” To extreme 
social constructionists, this framework might be seen as merely “worldview” 
or “cosmovision. 

Science as a repository of True Facts or of Absolute Truth. Although still mili- 
tantly upheld by some champions (e.g. Sokal 1997), this position is no longer 
really tenable. Contemporary scientific practice can get us to the truth about 
many things when ordinary observation will not, but that does not make Sci- 
ence a God-given repository of infallible wisdom. In fact, philosophers of 
science now hold that a genuine search for truth must take wrong turns. Oth- 
erwise it is not a search—merely a repetition of the obvious. Humoral medicine, 
alchemy, phlogiston, and many other theories were good ideas in their time, 
probably the best that could have been done with the data at hand. The 
disproofs of these theories signalled advances in the methods and techniques 
of scientific practice, and, following those, the improvement of theory. Science 
advances not by learning ex cathedra truth but by providing better and better 
theories, as Kuhn (1962) pointed out and as most scientists now agree. Possi- 
bly a subvariant of the old science-as-God’s-truth view is the popular 
conception of “science”: Flashy technology. This is the concept we find in mass 
media and Star Wars. (Wolpert [1993] overmakes the distinction between sci- 
ence and technology, but has some valuable comments on the issue.) 

Science as one specific form—the modern Western form—of the search for 
accurate knowledge. There are two major contenders for the form. First, there 
is the self-conscious “science” that began in perhaps the 14" century and was 
formulated in the 16'" and 17" centuries in the writings and work of Francis 
Bacon, Galileo Galilei, René Descartes, and, later, men like Robert Boyle and 
Isaac Newton. This is a science defined (ultimately) as working from observa- 
tion to inductive and then hypothetico-deductive theories, and testing these 
(and the observations also) by experiment. It contrasts this search with re- 
ceived wisdom, bias, and popular belief. This science did indeed break radically 
with earlier ways of knowing. If it is not the only “science,” it at least deserves 
some sort of terminological marking; Randall Collins’ “rapid discovery sci- 
ence” (Collins 1998) is a good choice. The second is “science” as defined by 
the logical positivists in the mid-20" century, with its formal operations, cov- 
ering laws, emphasis on verification and/or falsification, and formally 
(=mathematically) stated theoretical models. (This is so restrictive that it has 
been abandoned by most current authorities.) This type of definition has the 
nee of cutting off one specific type of truth- search, but it has the disad- 


wag oh t 7 
science aad other knowledge traditions. 
Science as “what scientists do.” This allows us to include the faked data, char- 
latanry, and vendettas that sometimes characterize scientific practice. It also 


134 ANDERSON Vol. 20, No. 2 


directs us to look at scientists as whole people—with their own eating habits, 
daily lives, paranoias, and so forth. 

5. Science as a social institution. This, of course, does not exist in most tradi- 
tional societies—even China, with its unquesti y great scientific tradition, 
did not have a concept of “science” or a “science establishment” (until mod- 
ern times). Traditional societies usually have a term for “knowledge” but not 
one for “science” as opposed to other types of knowledge. Chinese xue, Arabic 
‘ilm, and, of course, Greek/Latin scientia included philosophy, literary stud- 
ies, history, and other humanities. By contrast, in the United States and other 
rich modern countries, “Big Science” now has a life of its own, institutional- 
ized in such organizations as the National Science Foundation. 


Evidently, the first three of these approaches characterize science as a special 
kind of truth-seeking activity. The second pair treat science as a part of social ac- 
tion in general—as a social construction. The third approach above is somewhat 
intermediate, in that it regards science as a social construction—but a superior 
one, one that inevitably leads to truer and better knowledge. 

Champions of science see science as a truth-seeking activity, and see faked 
data, vendettas and the like as “bad science”—alien contamination of the enter- 
prise. The attackers and critics of science see it as a part of social action, and thus 
see it in terms of 4 and 5 above. For many of them, the “bad science” is just as 
scientific as the “good,” and phlogiston is just as real as any other scientific con- 
clusion (presumably including well-demonstrated things like the laws of 
thermodynamics). 

There are thoughtful reasons to see science in all the above ways—so long as 
they are kept analytically distinct. 

If one looks at institutions, modern American “Big Science” is a totally differ- 
ent thing from the tiny and scattered band of experimenters, often working in 
terror of religious persecution, who created European “modern science” in the 
1500s. They are linked by being related to the search for truth and understanding, 
but they are not linked by similarities in institutional or political forms. 

Conversely, if one is looking at the accumulation of accurate data, one can 
reasonably look at Assyrian medicine, Chi gricultural i ts, and Maya 
bird lore along with Nobel Prize experiments. One will not, however, be terribly 
concerned about the personal lives of the Assyrian or Chinese scholars. 

If one sees science in a broader and more sociological sense—science as the 
activities of people who want to know something about the world, beyond what 
intuition and received wisdom tell them—then the personal lives of the Assyrian 
and Maya scholars become more interesting. This is the position of most histori- 
ans of science. It has the major advantage of allowing all human societies into the 
club, rather than defining “science” so as to restrict it to one cultural tradition. 
Given the high prestige of the word “science” in today’s world, there are obvious 
political ramifications to these alternate courses of action. 

Certainly the most reasonable of the restrictive definitions would confine the 
term “science” to post-1600 Baconian-Galilean science. This would reduce to a 
historical footnote the Assyrians, Chinese, Mayas, and indeed well over 99% of 
the human species’ long quest for understanding.! If “science” is limited to the 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 135 


institutionalized rules of methodology that the positivists and scientific philoso- 
phers of the early 17" century (let alone the 20" century) invoked, then by definition 
there was no science before 1600 (or 1900 in the case of the positivists). Moreover, 
much of modern science does not count. Astronomy, astrophysics, paleontology, 
historical geology, most of ecology, and most of behavior biology are basically 
observational sciences, rather thar being based on controlled experiments. Not 
only Maya bird lore, but even 5 | research, rarely conforms 
to the full Popperian or Hempelian canon (see Kitcher 1993 for the best discussion 
of these issues). Above all, and most directly relevant to the present paper, tax- 
onomy is not a hypothesis-and-lab-experiment science, though modern cladistics 
is beginning to change that. 

Much of the rhetoric in the “science wars” of the late 20" century has been 
associated with a disregard for the above distinctions. Sometimes the disregard 
appears to be willful, but often it is simply careless. In any case, what has often 
happened has been an all-out attack on the entire search for knowledge and un- 
derstanding, justified by the failings of some scientists (some do fake their data, 
many are biased in one way or another). Conversely, some champions of science 
have failed to make the necessary distinctions, and have talked as if an attack on 
the current social i tion of science in the United States was an attack 
on all attempts to know anything. Sokal (1997), in particular, seems to be peril- 
ously close to taking such a view. 

Of course, in the real world, it is impossible to have a search for truth that is 
completely disinterested, wholly objective, and uninfluenced by social attitudes 
and institutions. We have known this since at least the day of David Hume. Even 
after half a century of critical theory, C. Wright Mills’ book The Sociological Imagi- 
nation (1950) remains probably the best statement on the subject in social science. 
The best the scientist can hope for is to understand biases, adjust them in a moral 
direction, and compensate for them by seeking verification or disproof of findings 
from other investigators from other schools or laboratories (Bacon 1901; Kitcher 
1993). 

At this point, it may be interesting to turn to a different tradition. If two ut- 
terly different societies, with utterly different scientific traditions, come to similar 
conclusions from similar data, perhaps there is objective truth lurking behind the 
cultural screen. If and when two such societies differ totally in the way they con- 
struct the world, then science may not exist at all, and the social construction of 
knowledge may truly be said to be an arbitrary and solipsistic activity. To some 
extent, the degree of “social construction” in science is an empirical question. 


THE MAYA OF QUINTANA ROO 


For the last ten years, in collaboration with Mexican (including Maya) and 
United States colleagues, I have been carrying out on knowledge of plants 
and animals among the Yucatec Maya of the “Maya Zone” of Quintana Roo. This, 
the central part of the state, is the area that was never truly reconquered after the 
Maya rebellion of 1846-48 known as the “Caste War” (Bricker 1981; Dumond 1998). 
The Maya in the present Yucatan state were crushed in 1848, but in what is now 


136 ANDERSON Vol. 20, No. 2 


Quintana Roo they remained independent until 1901, and in the remote west-cen- 
tral interior they were never really subdued. There was fighting as recently as 
1934 in Dzula, the community next to my own base in Chunhuhub. Current in- 
habitants of Dzula do not admit defeat. Alfonso Villa Rojas, ethnographizing the 
area eastward in the mid-1930s, encountered much hostility and some personal 
danger. The Maya, unsubdued, have continued to preserve a cultural tradition 
that is at least five thousand years old in the area (Redfield & Villa Rojas 1934). 

Like all cultures, Yucatec culture has profoundly changed over time, and is 
rapidly changing today; but Yucatec biological knowledge retains much knowl- 
edge of respectable antiquity. This is shown by archaeology, which discloses five 
millennia of milpa fields and cropping patterns not dissimilar to many one sees 
today (see Sharer 1994). It is also shown by colonial documents, which, from the 
16 century onward (Landa 1937; Alvarez 1997; Arzépalo Marin 1987, 1996; analy- 
ses in Anderson and Medina in prep.), record biological and medical lore close to 
today’s. The Maya, as everyone knows, created one of the greatest, most brilliant, 
most innovative, and most original civilizations the world has ever seen (Sharer 
1994). The modern Yucatec of Quintana Roo are one of the several successor groups 
of the Classic Maya. It is probably safe to assume that much of their biological 
knowledge is derived from a Classic Maya base, given the consistency in usage 
since the very earliest dictionaries (Alvarez 1997; Anderson and Medina in prep.). 
This base has been greatly supplemented in more recent centuries by Spanish (in- 
cluding Moorish) lore and international biological science. The modern Maya are 
not some sort of living fossil, preserving for us the mysteries of the Classic Maya; 
nor are they a tiny isolated group. They are bearers of the elaborate and expert 
science of a long-lived, populous, brilliantly successful, constantly evolving civili- 
zation. 

Maya languages have a written tradition going back 1600 years, at first in 
hieroglyphic and syllabi ipts, later in Spanish letters. Written transmission has 
been a small but significant part of cultural transmission for a very long time. In 
Yucatan, for instance, we have such examples as the Rituals of the Bacabs (orig. ca. 
1600; see Roys 1965, Arzapalo Marin 1987), which records magical and medical 
lore from the earliest part of the Colonial period. 

Such a huge tradition is far from homogeneous or uniform (see e.g. Hervik 
1999), and has its own self-reflexive turn (Sullivan 1989). This article focuses on 
knowledge recorded in and around Chunhuhub, Quintana Roo. 

Chunhuhub is a large farming town of some 5,000 people, occupying an ejido 
(communal landholding) of 14,330 ha. All are Yucatec Maya except for a few ad- 
ministrators and technicians, and a small number of in-migrants from central 
Mexico. Al t is bi 


ilinoial Most m3 sia 4517] 


2x J raise maize, beans, squash, 
chilies, and other crops by slash-and-burn cultivation of tracts ranging from 1 to 4 
ha. Yields reach a ton per hectare or more. Every family has its dooryard garden; 
many of these are large and contain up to 90 species of useful plants. Herbal medi- 
cine is commonly practiced. Some g is still obtained, but hunting in recent 
years has depleted game stocks (Anderson and Medina in prep.). Seventy percent 
of the ejido is covered with forest, all of it in various stages of regrowth from past 
cultivation. Some logging is carried out, but valuable woods were depleted in the 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 137 


early 1990s. Stockrearing and beekeeping are important. The vast majority of the 
population is highly knowledgeable about forests, fields, wild and tame animals, 
medicinal herbs, insects, and indeed all aspects of the environment. Given the 
solidly agricultural nature of the community, this knowledge is of a pragmatic, 
experiential type, fitting well into the wider model of “ecology of practice” devel- 
oped by Nyerges (1997). 

Research in Chunhuhub lasted for six months in 1991 and six more in 1996, 
with almost annual visits during intervening years. I was joined in the field by 
Eugene Hunn during a month in 1991; he introduced me to Felix Medina Tzuc, 
who became my collaborator and field assistant. Dr. Hunn al ded bird voices 
in the field for Maya experts to identify (Hunn 1992) and worked with Don Felix 
and myself on seeing how far Maya could go in identifying birds from pictures in 
Peterson and Chalif’s guide to Mexican birds (Peterson and Chalif 1989). Other- 
wise, research consisted primarily of walking through Chunhuhub and neighboring 
ejido and ranch lands, observing birds in the field and obtaining Maya identifica- 
tions. I also listened to a great deal of Maya conversation about birds and other 
biota, including a great deal of discussion and argument over just what to call a 
particular bird. Since I was studying “referential practice” (Hanks 1990), rather 
than in the psychology of classification, I found it expedient to spend a great deal 
of time in the field listening to actual practice, and made minimal use of formal 
eliciting techniques beyond the frame interviewing described by Frake (1980). Thus, 
the following data refer strictly to name usage in ordinary conversation. I did not 
carry out experiments of the sort done by Atran (1999) and others, since I was 
interested, at this stage of research, in different questions (see Hanks 1990 for dis- 
cussion and justification of the referential-practice approach in studying Maya; 
however, experimentation will be carried out in future research, opportunity per- 


The Maya do noth concept of “science” in the modern international sense. 
They do, however, have a reasonable equivalent. It is based on the core term k’aj 
“to know.” Connected to this is the complex word ool, which means “heart,” and 
by extension “knowledge, will, condition” (and sometimes also “lungs” and other 
internal items near the heart). Uniting these, we get k’ajool, “to know something, 
to recognize,” and thus the verbal noun k’ajoolal “knowledge.” This is as near as 
we can get to “science.” It is not a far reach; k’ajoolal focally signifies practical 
working knowledge. 

This article focuses on classification and uses of birds, with some comparisons 
to bird representation in contemporary international biological science. 


MAYA BIRD CLASSIFICATION 


Classification is often described as “carving nature at the joints.” This, of course, 
assumes that nature has joints. How similar are Maya bird taxa to those of con- 
temporary biological science? 

In ethnoornithology, as in science wars, there is a range from social-construc- 
tionist to realist positions. No one is as extreme as Feyerabend (1987), but Ellen 
(1993), Forth (1996), and to a degree Bulmer (1967) stress social factors, and Ellen 


138 ANDERSON Vol. 20, No. 2 


has been sharply critical of narrowly realist models. Conversely, Boster (1987; Boster, 
Berlin and O’Neill 1986; Boster and d’ Andrade 1988) and Hunn (1977) seem more 
prone to assume people recognize categories that are real in the sense of evolu- 
tionary biology. Atran (1990) and Berlin (1992) take a relatively strong position: 
people are mentally programmed to recognize the multistranded similarities that 
evolutionary relationships provide, and thus do carve nature at the joints. Atran’s 
later position seems considerably more qualified and nuanced, due to his pro- 
longed study (including use of psychological experiments, in collaboration with 
psychologists) of Itzaj Maya classification (Atran 1999). 

e Yucatec Maya data are consistent with the position that the Maya recog- 
nize groupings that are natural in the sense of evolutionary biology. However, use 
and other cultural and social factors enter into and shape the classification system. 
The system can be understood only by taking both culture and nature into ac- 
count. 

Maya bird names are mostly at a level that Brent Berlin (1992) calls “folk ge- 
nerics.”* These are usually one-word names. They contrast with each other; to 
place a bird in one folk generic means it is not in any of the others. They are some- 
times broken down into “folk specifics,” which are normally formed by adding an 
adjective to the generic. Thus ch’om means “vulture”; chak pool ch’om, “red-headed 
vulture,” is the Turkey Vulture (Cathartes aura). Maya, English, and Latin, like most 
languages (Berlin 1992; his usage is followed here, rather than that of Atran 1999, 
more for convenience than because of any deep theoretical reason), use the classic 
pattern in which a folk-generic name is modified by an adjective to produce a 
specific. (The Greco-Latin genus name Cathartes, roughly “one who cleans up,” 
covers one or two other vulture species; aura comes from a Native American name 
for this bird.) Latin terminology has many higher categories—the familiar phyla, 
classes, orders, and families of Linnaean taxonomy. Maya terminology has only 
one: the unique beginner ch’ich’ “bird.” Maya also has very few folk specifics. 
Almost all classifying of animals and plants is done at the folk-generic level. (This 
is true in most Native American systems. 

Of the 89 named terminal taxa (folk genera not broken down, or folk species) 
listed in the Appendix below, 63 have a one-to-one correspondence with the spe- 
cies recognized by international ornithology. Ten are focus-and-extension names: 
a focal species whose name is extended, more or less often, to other birds that are 
seen as distinct but are not named. In 9 cases, a terminal taxon is a Linnaean genus 
(4 cases), part of a genus (2 cases), or a group of closely related genera (5 cases). In 
3 cases, a terminal taxon names a whole family, and in one case a name covers two 
unrelated but very similar families (kusuun: swifts and swallows). One name— 
only one—is a broad, vague category without Linnaean counterpart. 

In two cases, a folk generic is broken down into folk specifics, all of which 
have a one-to-one correspondence with the international ones. One of these folk 
generics corresponds to a Linnaean family, one to a pair of closely related Lin- 
naean genera. 

In addition, I identify 13 groups, loosely named or named by extension of the 
name of one of their species (see below). Of these 13 larger groups (“folk fami- 
lies”), one corresponds to two (Linnaean) orders, two to an order, six to a family, 
two to part of a family, and two to a genus. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 139 


Many small birds are not idered important enough to have names of their 
own. These are lumped into broad, vague categories that may or may not resemble 
international scientific taxa. 

These groupings are of two kinds. First, there are some genuine categories 
that are well-bounded, well-recognized, and correspond loosely to international 
taxonomic units. An example is provided by flycatchers of the Linnaean family 
Tyrannidae. These are divided into three groups in Maya: takay “large yellow- 
bellied flycatchers,” juiiro “large flycatchers that have a loud call that sounds like 
juiiro,” and yaj “small flycatchers.” These groups are seen as related, as is proved 
by the fact that juiiro (a rather exotic term) can be lumped with either takay or 
yaj. It is explicitly recognized that these groups are diverse. Felix Medina Tzuc, 
for instance, pointed out to me the only pair of Piratic Flycatchers that we saw in 
our many months of co-work, and explained: “That takay is taking over the nest 
of those orioles.” It was, indeed, doing that, but not so obviously that Don Felix 
could observe it on the spot; he relied on his knowledge of the bird. The Piratic 
Flycatcher (Legatus leucophaius) is a rare bird in Yucatan, and only a person with a 
great deal of field knowledge would realize that it is a special sort of yellow-bel- 
lied flycatcher that takes over the nests of other birds rather than building its own. 
It does not have a special name in Yucatec Maya, but it is recognized nonetheless. 

To some extent, there is a “focus and extension” semantics here. Takay most 
commonly refers to the Couch’s Kingbird (Tyrannus couchii). Yaj has a definite 
focus: the small Myiarchus flycatchers. These birds have a miserably mournful- 
sounding call, like a child whimpering “yaj!” (“pain!” or “I hurt!”). No other small 
flycatchers call like this, so the name qualifies as an extension. Another type of 
broad category is much vaguer. “Little brown birds” are all vaguely lumped as 
yankotij, a name which properly belongs to the Tropical House Wren. (This is 
clear from its literal translation: “The one under the wall.” Only Tropical House 
Wrens forage and nest in the stonewalls of the Maya house compounds.) “Little 
yellow birds” are all vaguely lumped as chinchinbakal, a name that has no gener- 
ally agreed focal referent. It covers goldfinches, warblers, small yellow-marked 
tanagers, and much more. 

Several other names can be extended ad hoc. The ones that can be extended 
are known and constantly used to label some unknown bird. Other names are 
never extended. Unknown medium-sized red birds, such as migrant red tanagers, 
are lumped as chakts’its’i (“the red bird that says ts’its’i” )—a name that properly 
belongs to the Northern Cardinal (Richmondena cardinalis). By contrast, sojlin “ant- 
tanager” is not normally extended; if it is used for anything but an ant-tanager, the 
extension is regarded as a mistake. Ts’‘apim “saltator” (Saltator spp.) is extended to 
any medium-sized brownish bird of unknown identity. K’ok’ “Clay-colored Robin” 
(Turdus grayi) is extended to cover any robin-like bird, such as wintering thrushes 
from North America. Pich’ “Melodious Blackbird” (Dives dives) is the name used 
for unknown birds that are smallish and black. 

A very different type of extension is the use of one common name to cover a 
natural group. In these cases, the name contrasts at two levels: (1) in its normal or 
proper referential usage, it applies to one species; (2) in its extended usage, it ap- 
plies to that species and the natural group it is in. Acommon case is t’uut, properly 
the White-fronted Parrot (Amazona albifrons—by far the commonest parrot in the 


140 ANDERSON Vol. 20, No. 2 


area). This name is extended to cover all parrots (though not parakeets). In par- 
ticular, the Yucatan Parrot (Amazona xantholora), ek’xikin “black ear” in Maya, looks 
very much like the White-fronted and often travels with it; the two species are 
collectively t’uut to everyone, unless and until the distinctive black earpatch can 
be seen. Similarly, woodpeckers can be collectivized under the term k’olonte’ (or 
sometimes che’hun); quail under bech’; hawks under ii’ or chuy; and a few others 
as noted in the Appendix. 

Hofling and Tesuctin (1997), in their dictionary of Itzaj Maya (which is very 
close to Yucatec), treat these generalized terms as higher-level taxa that might be 
called “folk families.” Thus, they treat ixt’ut (=t’uut) as a general term for parrots, 
with the several folk generics (including t’uut in its more restricted sense) grouped 
under it. Yucatec does exactly the same. The Itzaj use ixpaloomaj (the Spanish 
word paloma, Mayanized) for pigeons and doves; Yucatec has a similar way of 
labeling pigeons by extending the term ukum. Hofling and Tesuctin (1997) also 
introduce a range of gender and environment categories that seem to cross-cut 
rather than structure the Maya general purpose taxonomy. This is problematic for 
the comparative nomenclaturist. In particular, their separation of tame and wild 
birds under totally different headings is certainly not the Yucatec pattern. How- 
ever, in general, Hofling and Tesuctin’s Itzaj classification is very close to Yucatec, 
though their lumping of blackbirds and anis seems definitely not a Yucatec view, 
and their lumping of quails and tinamous ina “covert category” of “ground birds” 
(1997:76-77) seems rather ad hoc. 

Atran’s excellent work on the Itzaj (1999) has gone into a different realm: cat- 
egories psychologically real to his specific consultants, as shown by tests in the 
field. These categories include “fish-eating water birds,...edible fruit-eating ground 
birds,...edible fruit-eating tree birds,...inedible flesh-eating birds,...inedible fruit- 
eating birds,” and “inedible blood-sucking birds [i.e., vampire bats]” (Atran 
1999:172-174). None of these have emerged as categories from any work done by 
me or others in Yucatec. It is notable that the category of “edible fruit-eating ground 
birds” has a very different composition from Hofling and Tesuctin’s similar cat- 
egory, though the same people were talking about the same general set of birds. 
Similarly, “inedible flesh-eating birds” includes groups that Hofling and Tesuctin 
and the Chunhuhub Yucatec both separate into a “hawk” group and an “owl” 
group. The other assemblages found by Atran are even larger and less well de- 
fined, and nothing like them emerges from Hofling and Tesuctin’s data or from 
mine; they appear to be categories arrived at by testing for psychological similar- 
ity, and are certainly not part of a linguistic taxonomy. 

Hunn (1977) treats Tzeltal bird names similarly, recognizing “groups” that 
are, de facto, folk families—natural groupings as recognized by the Tzeltal, but 
not named as formally as the folk genera are. These, again, are similar to Yucatec 
and to Itzaj (Hofling and Tesuctin 1997), but also include several other sets that he 
calls “complexes. Most of these are the same, or much the same, as Yucatec (hawks, 
vultures, doves...). Others include montane Chiapas species outside the knowl- 
edge of Yucatec observers. However, some groupings psychologically real to the 
Tzeltal would seem exceedingly far-fetched to the Yucatec, e.g. the link of squirrel 
cuckoos with quail (Hunn 1977:153-5) or of trogons and motmots (Hunn 1977:169- 
170). Hunn found the wide groups of waterbirds and black birds that Hofling and 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 141 


Tesuctn found and that seem nonexistent for the Yucatec (except in so far as the 
latter use the general descriptive term ch’ich’ ha’, “water bird”—without any im- 
plication of real relationship). 

Such groups blend into the “covert categories” of Berlin and his students. I am 
very loath to invoke covert categories without proof that the people in question 
really do think that a group is a real category. I think that wider-than-generic cat- 
egories are clearly shown by extension of terms, if reliable and predictable—not 
purely ad hoc like the extensions of ts’apim and chakts’its’i. But one must work 
constantly in the field, with consultants, to make these distinctions, and even then 
they could be challenged. I have done it in the appended table, but I have done it 
with great care—only when a group is explicitly and reliably named by an ex- 
tended term, and I have independent interview data suggesting that the group is 
seen as a natural one. The extension of terms like t’uut and k’olonte’ does most 
certainly show that the Maya recognize the parrots and the woodpeckers as natu- 
ral categories. The extensions are thus of considerable interest. 

All this reveals a pattern (the Yucatec one is very similar to the Itzaj one de- 
scribed by Atran 1999). Big, obvious, or useful birds have their own names, which, 
though “folk generics,” correspond with the species of Latin taxonomy. Small, 
rare, or unobtrusive birds are referred to by names that are also “folk generics,” 
but that do really correspond to genera or even families. Very small, insignificant 
birds are simply lumped with the most convenient and well-known small bird of 
the same color. 

Consider the guild of woodpeckers and teank foragers: : 

The area’s five common species f d t, obtrusive, noisy, 
confiding, and impossible to miss. They are . parceled out under three names (two 
almost identical species being lumped as kolonte’, and two as che’hun; either is 
sometimes extended to cover woodpeckers in general). 

Woodcreepers, though equally diverse in the area, are much less common, 
less easy to observe, and dull in color. They have only one name, tatak’ che’, cor- 
responding exactly with the Linnaean family Dendrocolaptidae. 

Small trunk-foraging birds (such as the Plain Xenops, Xenops minutus) are rare 
and obscure. They have no names at all, but, when noticed, are lumped under the 
garbage-can category created by extension of yankotij. 

Similarly, all game birds have their own names, but various non-eaten birds of 
equal size and obviousness are lumped into broad categories. Hawks are lumped 
into form-classes: each group with a distinctive flight profile, or appearance in 
flight, has its own name. This causes some interesting debates about e.g. the posi- 
tion of the White-tailed Kite (Elanus leucurus), which has pointed wings like a falcon 
and thus could be a k’eenk’eenbak’, but is large and heavy-bodied and pale like an 
ii’ (focally the Gray Hawk, Buteo nitidus) and thus could be in that category. Maya 
discussions of such issues while away many a sleepy hour, and remind the visit- 
ing ethnographer of debates among ornithological taxonomists. 

One significant observation is that none of the wintering birds from North 
America is named. Though Yucatan is vitally important as a major wintering ground 
for many midcontinent species, with Chunhuhub alone playing host to thousands 
of birds, not one has a Yucatec Maya name. (One, the Indigo Bunting Passerina 
cyanea, has the Spanish name azulejo. In other areas of the Peninsula, migrant war- 


142 ANDERSON Vol. 20, No. 2 


blers are collectively referred to by the onomatopoeic word ts’ip, but I have not 
heard this word used by Chunhuhub Maya.) Instead, the migrants are the major 
beneficiaries of the loose extension of words like yankotij and chaktsi’tsi’. 

In short, nature has joints, but society sometimes sees every reason not to rec- 
ognize them. When birds are useful or too obvious to ignore, they get their own 
names, which cover exactly the same space as a Linnaean species. To the degree 
that birds are useless and otherwise nonsalient, they are lumped into progres- 
sively wider and vaguer categories. Most of these categories correspond to the 
larger Linnaean taxonomic units: genus, family. Then, as terms are extended out 
to birds that are not only insignificant but do not even breed in Maayab (“Maya 
land”), the terms cease to have any relation to Linnaean categories. Instead, they 
lump birds roughly by size and color. (As a matter of fact, the same was true of 
early European taxonomy, and Linnaeus himself did some broad lumping.) How- 
ever, all of them have a focal exemplar that is a real, well-recognized Linnaean 
species or tightly-knit group. The only exception is the catchall term chinchinbakal. 

In other words, almost all Maya taxa, when not loosely extended, correspond 
exactly with Linnaean taxa—at the species level, if the bird is salient; otherwise at 
the genus level (but only if the genus is tightly knit, with all local species similar) 
or at the family level. The less salient the birds, the more wide the Linnaean group 
that equates to the labeled group in Yucatec. Some families (hawks, flycatchers) 
are parceled out in ways not like those of international ornithology, but the parcel- 
ing does make a great deal of sense in terms of the realities of Chunhuhub. They 
accurately label natural-seeming groups, united by appearance and voice—even 
when they cut across Linnaean taxa (as they sometimes do—but only in marginal 
extensions of the terms). 

One concludes that classification is a social construction, but one that must 
take account of real natural differences if it is to be of any use at all (cf. Atran 1990; 
Berlin 1992; and literature reviewed therein). Since the Maya and contemporary 
international biologists are both trying to find useful labels that represent some 
sort of external reality, there are many similarities in the two systems. Since the 
uses in question are not the same, there are also differences—largely at the level of 
“lumping.” The Maya lump species that are unimportant to them. The biologists 
find all species equally important—at least in the Class Aves. However, biologists 
too lump things they do not find salient. I am told by colleagues that the few 
thousand recognized species of nematodes could probably be split into hundreds 
of thousands (if not millions) of species, if nematode taxonomy were as developed 
as avian taxonomy. Thus, one does not expect, and does not find, quite so good a 
fit as one would expect from some of the work of Boster (1987; Boster, Berlin and 
O'Neill 1986; Boster and d’Andrade 1989) or of Atran’s earlier theorizing. Maya 
extension of terms fits well with Boster’s findings that broad visual similarities 
serve as primary markers of relationship, and also with Boster’s observation that 
Native American peoples are prone to name birds from their vocalizations. This 
affects classification; flycatchers, for instance, are broken down as much by vocal- 
ization as by appearance. The Maya also consider behavior and habitat in making 


identifications and classifications. The term pujuy, for instance, is extended to birds 
that act like the focal pujuy. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 143 


MAYA BIRD USE 


Knowledge of the uses of birds is straightforward, but not without interest in 
the present connection. The most important use is as food. In addition to domestic 
fowl (chickens, ducks and turkeys), several wild species are hunted—especially 
quail, tinamous, chachalacas (bach, Ortalis vetula), and the very few larger game 
birds still found in the area. Wild birds are also kept as pets, especially parrots, 
parakeets, doves and pigeons, and-rarely now—large game birds. 

Birds for food are usually shot with shotguns or rifles. (Maya hunters wingshoot 
quail with ancient .22s, a feat that would awe any Anglo-American shooter.) How- 
ever, small birds, and all birds wanted as pets, are caught with traps and snares. 
Most common is a simple box trap, usually used by boys to get pets. Small birds 
are baited in, and the boy pulls a string that removes a twig holding up a small 
box. It falls over the birds. This is sometimes used more seriously, to get quail for 
food. Nooses, snares, and sticky materials are occasionally used to catch small 
birds. Sometimes a batea is staged: a hunt in which men form a long line and beat 
the bush for game. Birds, however, are not successfully hunted this way, since 
they fly off. 

Birds are occasionally used as indicators of time or the like. For instance, the 
Bright-rumped Attila (Attila spadiceus—one of the juiiro flycatchers) is sometimes 
called the pak’sak’al, “plant-the-brushfield,” because it sings loudly at the time of 
year when a farmer should be doing that. The noise of feeding birds can attract 
one to wild fruit. Last of all, some birds, especially parrots, parakeets, and jays, are 
often pests of the milpa fields. They must be controlled by scaring them away, 
and—in desperate cases—by traps, slingshots, and guns. The Maya of Chunhuhub 
love and cherish birds, and will not kill a pest bird unless its depredations become 
devastating. 

To this extent, knowledge is highly pragmatic. Social construction enters the 
picture to the extent that only the larger and tastier birds are defined as edible; no 
one would eat a hawk, toucan, or other large but non-choice species unless hun- 
ger was serious. 

However, a different kind of knowledge exists. Many birds are associated with 
various sorts of dark powers. These fall into two categories: Ominous birds and 
birds used in magic. 

Ominous birds are the nocturnal species, considered unlucky through both 
indigenous Mexico and traditional Spain. The Barn Owl (xooch’, Tyto alba) is par- 
ticularly feared; its loud and hideous shriek presages death. Even the common 
little pujuy (nightjar or pauraque, Nyctidromus albicollis) is worrisome. When it 
calls and jumps up after insects, it presages death. Since hundreds of pujuy call 
and jump all night, every night, in Chunhuhub, one would expect many deaths— 
and, sure enough, every day, several people die in Mexico. Since any death, 
anywhere, counts as a “hit,” the predictive value of the pujuy is confirmed. Some 
Maya also believe the loud, wild call of the peppershrike (ch’uyin, Cyclarhis 
Sujanensis) i is, ominous. 

CI 


1 


seer t y birds, but other areas of the Yucatan’s 
Maya world have nee such animals. From Chan Kom, the most intensively 
ethnographized community in the peninsula, we hear of the purple taankas par- 


144 ANDERSON Vol. 20, No. 2 


rot (Redfield and Villa Rojas 1934; taankas means any mental problem from numb- 
ness to frenzy) and the eagle witch (way kot; Re Cruz 1996), apparently a witch 
that can transform into an eagle. I have heard of a bird similar to the taankas 
parrot in other nearby communities. 

Other birds are useful in working magic. Magical practices are carefully and 
sharply distinguished from standard medical and pragmatic knowledge, by being 
labeled with the Spanish words magico or secretos. A specific magical practice is a 
secreto (and it is said that “women know seven secretos to men’s four”). This word 
is not used for practices, even esoteric ones that do not involve dealing with dark 
or suspect supernatural powers. 

Commonest of secretos is the use of hummingbirds, takay, and pujuy for love 
magic, in that order of abundance. The bird is caught on a Tuesday or Friday— 
these being the “bad days” of the Catholic church calendar—and dried. Dried 
hummingbirds are carried in the pockets of young men for love magic (as is true 
throughout Mexico). The powdered head of a dried hummingbird or takay, thrown 
on a girl as she enters church, makes her fall madly in love with the thrower—at 
least, if he knows and uses the right charms. A pujuy head is sometimes so used, 
or the pujuy powder can be used in cursing. The t’unkiya (another nightjar, 
Caprimulgus salvini) can also be used for this. Some magical medical charms in- 
volve these birds. 

Other witchcraft includes the magical introduction of live scorpions and the 
like into people, but birds seem not often involved in these practices. 

There were times when avian magical medicine was much more important. 
The Rituals of the Bacabs, a collection of long ritual curing chants that seem to be 
pre-Columbian, includes many birds. Jays, woodpeckers (kolonte’, che’hun), and 
above all macaws (moo’, Ara spp., now extinct in the Yucatan) were particularly 
important. They are invoked in many of the long chants. Often, they are associ- 
ated with fire, and with the curing of insanity. The extremely arcane and difficult 
Maya of the chants almost preclud i tudy at this time, but there is a major 
future study of Bacab biology to be done. 

Obviously, we have been moving farther and farther from anything that could 
be verified by actual experience with nature. The edibility of birds is common 
experience. Their value as pets is a matter of opinion, cultural as well as personal; 
at the least, some of them can be tamed and make affectionate housemates. The 
omen value of night birds is clearly nil to the outside scientific observer, but the 
Maya can point to an almost perfect correlation between nocturnal calls and some- 
one dying somewhere. This, then, is a judgment call in which “social construction” 
really does allow many different results. Love magic is more difficult to defend, 
since everyone admits that it rarely works. 

Finally, we enter a realm in which no amount of personal experience can al- 
low entry. It is quite safe to say that no one has really seen a purple taankas parrot 
or the flaming jays of the Bacab songs. No one (to my knowledge) believes in them 
in Chunhuhub; Chunhuhub is a particularly pragmatic, down-to-earth place. But 
Chunhuhubians believe in other supernaturals that would seem to the outsider to 
be just as difficult to observe, such as the aluxoob (tiny beings, usually thought to 
be ancient Maya sculptures that can be animated by the right methods). Some 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 145 


have seen the xtabay (the demon woman). However, it is admitted that one usu- 
ally sees the xtabay only after consumption of a large amount: of alcohol. This is 


traditionally thought to be because she finds drunkards vulnerable to 
her evil charms, but skeptical Maya are quite aware of the obvious alternative 
explanation. 


In short, there is a realm, marked off in Maya thought, in which social con- 
struction has really run far beyond any observable or verifiable reality. This is a 
realm in which love, death, and fear are paramount. There are countless anthropo- 
logical theories of magic, and it would be tedious and irrelevant to catalog them 
here. Suffice it to say that almost all agree that, in these areas, human fears and 
desires press irresistibly hard against the boundaries of observable reality. It is by 
no means clear if any culture, including the culture of professional psychologists 
and GOCtOrS; has ie solution to the problems of rains love and predicting death. 
This t st st people from believing they can “have dominion over Judg- 
ment Day” (as the ctaditionéd blues line has it), or at least over love. Exploring 
these issues is outside the realm of this paper. 

There is no explicit body of theory holding Maya bird knowledge together, 
but one could, with Gonzalez (1998), formulate assumptions. First, it is assumed 
that birds that look alike and sound alike are natural categories. If the birds are 
essentially identical, they must be in one category, and if lumped they are lumped 
with similar birds. No Maya, and probably no one on earth, would classify king- 
birds, horned owls and cormorants in one group opposed to another group made 
up of small flycatchers, barn owls and grebes. Social construction does not work 
that way. Second, there is an assumption that all things are potentially useful for 
filling material needs, and that all things large enough to be interesting should be 
explored for their value in these areas. This assumption has led to the accumula- 
tion of a great deal of lore about birds as food and as pets, and how to obtain them. 
Third, there is an assumption that love, harm, and some kinds of fate can be con- 
trolled by use of secretos, and that birds are useful in this enterprise. Certain birds 
are earmarked for the tasks of magic. 


DISCUSSION 


Culturally standardized, traditional knowledge is, by definition, 100% socially 
constructed. However, as Marx said of history: “Men make their own history, but 
they do not make it just as they please” (Marx 1986:277). Observed external reality 
provides constraints that cannot always be ignored. One cannot indefinitely be- 
lieve in the safety of consuming deadly poisons, or walking off cliffs. Even if an 
individual did so believe, a culture would not encode the belief. Experience to the 
contrary would be too commonly observed. 

The Yucatec Maya live as subsistence farmers in a harsh environment. They 
survive only through having a literally encyclopedic knowledge of soil, water, 
useful plants and animals, and useful farming techniques. Unlike academics at 
prestigious universities, they do not have the luxury of believing anything they 
wish or of dismissing the real world. Instead, they must constantly interact with 
nonhuman reality. They walk a razor edge; the least mistake, the least failure to 
invoke the correct strategy, can mean death. 


146 ANDERSON Vol. 20, No. 2 


Accurate knowledge does matter. Chunhuhub residents tell that some years 
ago, two young Dutch hikers got lost in the woods near Chunhuhub. They died of 
thirst in the waterless bush. The forest where they died was festooned with wild 
grapevines (saya ak’, Vitis spp.). Every experienced Maya knows these grape- 
vines, and knows that they store water, containing up to a cup or more of clear, 
pure water per linear meter of vine. The reason why this knowledge is so wide- 
spread is grimly obvious from the fate of the unknowing Dutch youths. 

e more one knows about farming and about baalche’ (“things of the trees” — 
wild animals), the better one lives. The forest provides, for those that truly know it 
well, a good living, and even a few luxuries such as pet birds. Moreover, the Maya 
yield to none in their enjoyment of the wild birds. They love the songs and color as 
much as medieval European poets seem to have done. Enjoyment, too, leads to 
knowledge and to its social construction. Many a Maya bird taxon appears to be 
widely recognized simply because the birds in question are so amusing, or beauti- 
ful, or delightful. This, too, is a use of nature, and a socially constructed one; but it 
requires the existence of the birds, and the potential to enjoy them. 

Interaction with nonhuman lives should not surprise those who believe in 
“the social construction of reality” (Berger and Luckmann 1967). After all, social 
construction can only arise from people interacting and discussing. It cannot exist 
unless people actually do see and respond to an external reality—the reality of the 
others they meet and the communication transactions they experience in dealing 
with those others. If people are interacting with each other and learning from that, 
it seems hard to deny that people interact with birds also, and learn something of 
the avian world. 

So ecological knowledge, like other knowledge, arises from practice (Nyerges 
1997). It arises from interaction between people who are interacting with the non- 
human world. It is phenomenological, but a phenomenology based on sensory 
experience (Abram 1996). 

en “nature fights back,” refusing to let people ignore it, society can con- 
struct knowledge only within strict limits. If people want to use birds, the need for 
an adequate classification system is strongly felt. This is a place where Nature 
really has joints, if not always clear and obvious ones. People need to “carve Na- 
ture at the joints” if they are to deal effectively with birds and communicate 
effectively about them. As a result, classification systems from around the world 
look somewhat alike. On the other hand, society and history play a role in deter- 
mining which birds are used, which are held salient, which are ignored. Social 
construction determines which are recognized as species, and which are lumped 
into broad vague categories. 

Berlin (1992) has demonstrated the similarity of classification systems around 
the world, and the similarity of many systems to modern scientific taxonomy. This 
he ascribes to a tendency of humans to perceive certain sorts of discontinuities 
and continuities in nature. It is perhaps more accurate to say that people perceive 
all sorts of things, but interact with humans and with other lives so much that 
everyone, eventually, tends to realize that some differences matter and some do 
not. The differences between different quail species are real, and matter to the 
Maya. The differences between small flycatcher species are equally real to a biolo- 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 147 


gist, but are of no special consequence to the Maya, who therefore ignore them (cf. 
Boster and d’Andrade 1989). Overall, the Maya data fit much better with the find- 
ings of Boster and his associates than with those of more social-constructionist 
scholars. However, it is noteworthy that the latter (e.g. Bulmer 1967; Ellen 1993; 
Forth 1996) have often been those who carried out research in east Indonesia or in 
Papua-New Guinea, areas where systems may be genuinely very different from 
both Maya and western models. 

However, different Maya groups, and even different Maya consultants within 
the same group, obviously classify birds in different ways. This is not so much a 
matter of failing to perceive relationships as of devising classifications that fit one’s 
own referential and ecological practice (Hanks 1990; Nyerges 1997). In particular, 
birds are lumped ad hoc if there is no special better reason to lump them, or if 
there is no pragmatic reason to see them as deeply and basically separate. 

Words, after all, are to talk with, and there is no sense providing a verbal label 
for something one does not talk about. Conversely, “utility” in the narrow sense 
originally adduced by Hunn (1982) did not exhaust the reasons why people might 
want to talk about something. They might want to talk about it only because it is 
common and has a pretty song, and is thus hard to ignore if one loves birds as 
much as the Maya do; thus there are not one but two names for the singularly 
“useless”—but pretty and songful—Yellow-green Vireo (Vireo flavoviridis). 

Even classification systems get confused with power relations, as Foucault 
(1971) showed for the Linnaean system; one need only look at its hierarchy, with 
“Kingdoms,” “Orders,” and “Families” duly arranged by relations of inclusion. I 
find no evidence that the Maya system was concocted with one eye to the State, 
even though the ancient Maya did have states. But one cannot be sure. If relations 
with the natural world and with fellow farmers are clearly reflected in the system, 
relations with the hierarchy may also be. The weird birdlore reflected in the Ritu- 
als of the Bacabs may well have a great deal to do with politics. We do not know. 

Moreover, as belief gets uncoupled from immediate observation, society can 
construct with a much freer hand. In international biological science—and, even 
more, in high-energy physics and in astrophysics—much high theory is purely 
speculative. Theorizing runs far ahead of observation. Conversely, sometimes a 
new theory is irrationally rejected for decades, until the buildup of supporting 
facts is so overwhelming that no one can deny it any more (see Oreskes 1999). 

Of course, the ideal of testing it is there; but by the time a theory is adequately 
tested, theorists have already gone on to even wilder flights of imagination. It 
should, then, surprise us not at all that the hardheaded and pragmatic Maya farm- 
ers believe some very improbable things about birds. 

To the dispassionate anthropologist, the mistakes people make seem remark- 
ably similar. As our felt needs for knowledge outrun our possibility of checking, 
we come to believe some very improbable things. In so far as a whole society is 
made up of people with such needs and such biases, a whole society can construct 
a whole system of knowledge that is far from observed reality. This is as true of 
20 century scientists as of Maya farmers. Against the Maya use of birds in love 
magic, we can set the enormous amount of speculation on love that fills rack after 
rack in any bookstore. Much of this material seems to the uninitiated to be as far 


148 ANDERSON Vol. 20, No. 2 


from any observed reality as are the beliefs about the use of powered takay heads. 
It is not only the Maya whose need to deal with love runs far beyond their ability 
to understand it. 

In Mayaland and in the modern laboratory, observations are usually good 
and accurate, unless driven by powerful antecedent beliefs. This is because people 
can check their observations against reality, on frequent occasions, and thus are 
disabused of the minor errors that derive from unquestioned assumptions, sheer 
ignorance, and mistake. Interpretations and explanations, in so far as they are 
decoupled from direct observation, are increasingly tentative. Accordingly, they 
must be more and more self-consciously tested against reality. At no stage is the 
process free of bias and social construction, but at no stage is the process so re- 
moved from reality-testing that it is pure construction in a vacuum. 


CONCLUSION 


There is, then, a universal search for truth. We can use the term “science” for 
this worldwide search for more and more accurate data and understanding. 

However, every culture, every society, has its own unique form of “science,” 
and systems of knowledge are indeed socially constructed, in a very literal sense. 
It would thus be possible to limit the term “science” to the activity defined by 
Bacon, Galileo, Boyle, et al; however, the restriction of the term to contemporary 

ig Science is absurd, and the restriction to formal, positivist work 
(a restriction still made by e.g. Cronk 1999) is not only absurd but eae vio- 
lated by almost all working scientists (Hacking 1999; Kitcher 1993; Kuhn 1962). 

Even the limitation to post-Baconian experimental practice may be seen as 
arbitrary and Eurocentric. “Science” is a highly prestigious label in modern soci- 
ety. Refusing to use Egyptian, Greek, Chinese, Near Eastern and Maya traditional 
knowledge systems seems undesirable, not only because it would add to the al- 
ready great amount of bias in the world, but also because it might lead 
contemporary scientists to slight traditional knowledge. 

owledge is socially constructed, but it is through the very process of social 

construction—inevitably involving interaction, checking, and feedback—that accu- 

rate, empirically useful knowledge can be increased, refined, corrected, and made more 

aluable. Mistake-making is an inevitable cost of this system. Science flourishes in 

so ie as people keep interacting with the world, to verify or disprove the specula- 
tions they have entertained and the conclusions they have reached. 

Because of differences in this and in entire social contexts, knowledge systems 
in different cultures can look very different. They can also look similar, especially 
when they are under constant tight control _ feedback from the actual “world 
out there.” The degree ystems, and the degree of arbitrari- 
ness that enters into socially constructed knowledge systems, are matters for 
empirical investigation. 


NOTES 


‘ Lavoid the term “western science,” because contemporary biology i is an piniernational, not 
a western, project; Chinese, African, Indian and oth 


tions to it. “Western” science, conversely, a includes a great deal of lore aig as wn 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 149 


humoral medical theory, still common in western folk societies) that is no longer part of 
formal oo science. And, anyway, the Maya live west of Europe. “Western” rr 
not to say prejudicial, term y's 


J 
global society. Writers such a as Wolpert (1993) restrict the term “science” to the west, usu- 
ally through ignorance of what other cultures are doing. Wolpert, for instance, states that 
“the Chinese, often his ay of as scientists, were expert eis but made negligible 
contributions to science. .. (Wolpert 1993:xii).” 
Even given Wolpert’s seclrintive definition of “science” Geaicaiy; post-1600 western ex- 
perimental science, but extended to include ancient Greek speculation and modern non- 
laboratory sciences), this statement is absolutely wrong, and a ein complete igno- 


rance of Chinese science and philosophy—ar y Wolpert’s 
wildly inaccurate discussion of nine (1993: 46-47). His opinion of all ’ ‘primitive’ and 
nonwestern traditions is summed u ..for thousands of years the mythology and cos- 


mology of almost all cultures entertained neither a critical tradition nor curiosity about 
nature (Wolpert 1993:54).” He equates nonwestern know lodge -ereking: inchiding Chinese 
and Islamic science, witha (1993:26). 
Yet—as an educated Englishman—he adulates the ancient Greeks, crediting them with the 
full Baconian-Galilean approach; this is, again, not accurate. It is surprising and depress- 
ing to find that claims of this sort can still be published in an academic work. Wolpert’s 
work is also confused and inconsistent. He defines science in various ways, loosely classi- 
fiable into a broader definition and a narrower one. By Wolpert s broader definition 
(thoughtful observation leadin intuitive” meaning, 
loosely, “consistent with everyday air IRE Ad and all”), all societies have science. 
(This is not helped by Wolpert’s lack of clarity about just what is counterintuitive.) By his 
narrower one, only certain post-1600 sciences count. The latter definition would rule out 
taxonomy—contemporary biological as well as Mayan. 


2 There is no previous systematic account of Yucatec Maya bird names. Existing accounts 
such as those of Pacheco Cruz (1958) and Hartig (1979) are incomplete, out of date, and 
seriously compromised by major errors. (Pacheco Cruz does include a great deal of cul- 
tural material that is of great value—including a very large amount of magic and folklore, 
— beyond any eng I encountered, ) pAtzaj | Maya, which i is virtually a dialect of Yucatec, 
Atran (1993, 
1999) has provided lists of terms, and Charles Hofling, with F. F. Tesuctin (1997), have 
provided an entire dictionary. This dictionary gives a list of bird names (pp. 72-77). This 
list breaks up the bird names into various categories, including use-categories, and pro- 
vides a number of different sorts of higher-level taxa that might be sone “folk families” 
(see above). One or two of these groupings seem highly idi 
psychologically there for the Yucatec. For instance, the Yucatec saeeyy not group anis with 
blackbirds. However, most of them are the same as the Yucatec groups. I have been more 
cautious in listing groups. For example, their category of ground game birds—named in 
Spanish but not in Itzaj—is probably real, in some sense, to the Yucatec too, but I have not 
listed it because it is not a Yucatec-named group. Presumably all of the groups listed in the 


nd are certainly not 


ent from anything familiar in Yucatec. Many names, too, have quite different usages from 
those common in Yucatec; for instance, ts’apim refers to orioles instead of saltators. They 
also use the diminutive ix- (equivalent to modern Yucatec x-) wherever it is commonly 
used in speech; but the diminutive is actually an optional addition to the name, so I have 
not indicated it. 


150 ANDERSON 


Vol. 20, No. 2 


ACKNOWLEDGEMENTS 


I gratefully acknowledge, above all, the bisik of Eugene Hunn, Felix Medina Tauc, and 


the people of Chunhuhub. William Balée and ti 


editorial input. 


dv aluable 
i © 


RATURE CITED 


LITE 
ABRAM, DAVID. 1996. The Spell of the 
Sensuous. Pantheon, New York. 
ALVAREZ, CRISTINA. bes een 
a Maya 


L Me ico. 
ANDERSON, E. N., and FELIX MEDINA 
TZUC. In prep. Animals and the Maya 
in Central Quintana Roo. Ms. 
pec MARIN, RAMON (editor). 
6. Calepino de Motul. UNAM, 
he co. 

~ 1987. a Ritual de los Bacabes. 

UNAM, Mex 
ATRAN, SCOTT. 1993. Itza Maya 
agroforestry. Current Anthropology 

0. 


. 1990. Cognitive Foundations of 
Natural History. Cambridge University 
Press, a ridge. 

Sessile 9. Itzaj Maya folkbiological 
Hasecies Co ognitive universals and 
cultural particulars. Pp. 119-204 in 
Folkbiology, Douglas Medin and Scott 
Atran (editors). MIT Press, Cambridge. 

BACON, FRANCIS. 1901 (orig. 16" cent.). 
Novum Organum. P. F. Collier and Son, 

York. 


TE and THOMAS 
KMANN. 1967. The Social 
Construction of Reality. Anchor Books, 


New York. 

BERLIN, BRENT. 1992. On Ethnobiological 
Classification. Stanford University 
Press, Stanford. 

BRICKER, VICTORIA. 1981. The Indian 
Christ, the Indian King. University of 
Texas Press, Austin. 

BOSTER, JAMES. 1987. Agreement between 
biological classification systems is not 


O’NEILL. 1986. The correspondence of 
Jivaroan to scientific ornithology. 
American Anthropologist 88:569-583. 


, and ROY D’ANDRADE. 1989. 
i and human sources of cross- 
cultural agreement in ornithological 
lassificati American Ant! logist 


91:132-142. 

BULMER, RALPH. 1967. Why is the 
cassowary not a bird? A problem of 
zoological taxonomy among the Karam 
of the New Guinea Highlands. Man 2:5- 


25. 

COLLINS, RANDALL. 1998. The Sociology 
of Philosophies. Harvard University 
Press, Cambridge. 

CONKLIN, HAROLD. 1962. Hanunoo 


CRONK, LEE. 1999. That Complex Whole. 
Westview Press, Boulder. 

CUSHING, FRANK. 1920. Zuni Breadstuff. 
Museum of the American Indian, Heye 
Foundation, New York. 

DUMOND, DAN. 1998. The Machete an 
the Cross. University of Nebraska Press, 


Lincoln. 

ELLEN, ROY. 1993. The Cultural Relations 
of sgpreawey Cambridge University 
Press, Cambridge. 

FEYERABEND, PAUL. 1987. Farewell to 
Reason. Verso, London 

FIRTH, RAYMOND. 1957. We the Tikopia. 
(second edition). George Allen and 


Unwin, London. 

FORTH, GREGORY. 1996. Nage birds: 
Issues in... the... analysis of 
pie eneeg Er classification. 
Anthropos 91:89-109. 

FOUCAULT, cL ay tke Order of 


Things. Pantheon, New 
FRAKE, CHARLES. 1980. es and 
Cultural Description. Stanford 


University Press, Stanford. 
GONZALEZ, ROBERTO. 1998. are 
science: Farming and food in 

Northern Sierra of Oaxaca, Mex 
Ph.D. dissertation LORIE AS 
University of California, Berkeley. 


Winter 2000 


GOODENOUGH, WARD. 1953. Native 
Astronomy in the Central Carolines. 
University of Pennsylvania, Museum o 
Anthropology, Philadelphia. 

HACKING, IAN. 1999. The Social 
Construction of What? Harvard 
University Press, Cambridge. 

HANKS, WILLIAM. 1990. Referential 
Practice. University of Chicago Press, 

hic 


HARRIS’ MARVIN. 1968. The Rise of 
pases Dees eo Science. Thomas Y. 
Crowell, New York. 

HARTIG, HELGA-MARTA. 1979. oe — 
de Yucatan: Nomenclatura e 
Espaniol- Ae rdienos Fondo Satria 
de Yucatan, Mexi 

HERVIK, PETER. 1999. Maya People within 
and beyond Boundaries. Harwood 
Academic Publishers, Amsterdam. 

HOFLING, CHARLES ANDREW and 
FELIX FERNANDO TESECUN. 1997. 
Itzaj Maya-Spanish-English Dictionary. 
oe 8 aa Salt Lake City. 

HUNN, E 1977. Tzeltal Folk 
Zoology. a Press, New Yor 

_—___—— . 1982. The utilitarian factor in folk 
She cl classification. American 
Anthropologist 84: 7. 

. The use of scare recordings 
as voucher eli mare and stimulus 
materials in ethnozoological research. 
Journal of Ethnobiology 12:187- 

KITCHER, PHILIP. 1985. Vaulting 
Ambition. MIT Press, Cambridge. 

—_—___—. 1993. The Advancement of 
Science. Oxford University Press, New 


ork. 
KUHN, THOMAS. 1962. The Structure of 
Scientific Revolutions. University of 
Chicago Press, Chicago. 
LAKATOS, IMRE. 1976. Proofs and 
Refutations: The Logic of Mathematical 
Discovery. Cambridge University Press, 


Cambridge. 

LANDA, FRIAR DIEGO DE. 1937 (Spanish 
orig. 16 century). Yucatan Before and 
After the Spanish Conquest. (translated 
2s Scat Gates). The Maya Society, 


EAUDARN, “LARRY. 1996. Beyond 
wheasteoaae and Relativism. Westview 
Press, Boulder 

MALINOWSKI, BRONISLAW. 1935. Coral 
Gardens and Their Magic. American 
Book Co., New York. 


JOURNAL OF ETHNOBIOLOGY 151 


MARX, KARL. 1986. Karl Marx: A Reader. 
(edited by Jon. Elster). Cambridge 
University Press, Cambridge. 

MILLS, C. WRIGHT. 1950. The Sociological 
Imagination. Oxford University Press, 

ew York. 

NADER, LAURA (editor). 1996. Naked 


Boundaries, Power and Knowledge. 


u York. 

NYERGES, ENDRE (editor). 1997. The 
Anthropology of Practice. Gordon and 
Breach, Amsterdam 

ORESKES, NAOMI. 1999, The Rejection of 
Continental Drift. Oxford University 
Press, New York. 

ORWELL, GEORGE. agi ace iv 
Nineteen Eighty-F 
University Press, New Yo 

PACHECO CRUZ, SALVADOR. 1958. 
Diccionario de la Fauna Yucateca. 

a, Mérida. 

PETERSON, ROGER TORY and EDWARD 
CHALIF. 1989. Aves oe México: Guia de 
Campo. Diana, Mexi 

RE CRUZ, ALICIA. 1996. "The Two Milpas 


re) 

REDFIELD, RC 
VILLA ROJAS. 1934. Chan Kom, A 
Maya Village. Carnegie aoe of 
Washington, Washington, 

RICHARDS, AUDREY. 1948. pias and 
Work in a Savage Tribe. Free Press, 

lencoe. 

ROSENBERG, ALEXANDER. 1992. 
Science of Diminishing Returns? 
Uinivebaity of Chicago Press, Chicago. 

ROYS, RALPH. 1965. Ritual of the Bacabs. 
University of Oklahoma Press, Norman. 

SHARER, ROBERT. 1994. The Ancient 
Maya. Stanford University Press, 


Stanford. 

SOKAL, ALAN. 1997. Impostumes 
Intellectuelles. O. Jacob, Paris 

SULLIVAN, PAUL. ntiisieed 
Conversations. University of California 
Press, Berkeley. 

WOLPERT, LEWIS. 1993. The Unnatural 

tu Science. Harvard University 

Press, Cambridge. 


152 ANDERSON Vol. 20, No. 2 


APPENDIX.—Chunhuhub Yucatec Maya Bird Names and Their Correspon- 
dence with Linnaean Nomenclature 


Maya is transcribed according to the system recently standardized and accepted 
for Maya languages. This system is still unfamiliar in Yucatan, but is winning rapid 
acceptance and is used in the newer literature. Only common, well-identified names 
are given. I have recorded several others that are either vague or need more re- 
search. Only the commonest Spanish names are provided. Unlike Hofling and 
Tesuctin, I have not bothered to respell Spanish names in Maya transcription (see 
e.g. “ixpaloomaj” above). The people of Chunhuhub are bilingual, and usually 
pronounce the Spanish without any Maya accent. To respell Spanish names seems 
pedantic. Like other tropical American peoples, the Maya are fond of naming birds 
from their call. In the forest, birds are far more often heard than seen. Often, indi- 
viduals do not even know the appearance of a bird well known by voice. 


Class Aves: ch’ich’ “bird” 
Arbitrarily arranged in Linnaean order; no obvious order or high-level groupings 


arise from the data. Vague and tentative “covert” or ad hoc categories are often 
proposed, but I prefer to be conservative, staying with unquestionable data. 


Tinamou cluster: Non 


Mankolom. Great Tinamou, Tinamus major. Does not occur locally, but known to 
locals who who have been farther south. 


Non (nom). Rufescent tinamou, Crypturellus cinnamomeus. Common; a game bird, 
but not often obtained because of its extreme wiliness. 


Ke’el non. Little tinamou, Crypturellus soui. In spite of a name that makes it sound 
like a subcategory of the foregoing, this is recognized as a different bird. 


Kamacho, Olivaceous Cormorant, Phalacrocorax olivaceous. Spanish-sounding ex- 
tension of mach, the more general Yucatec name. Extended to the Anhinga, Anhinga 
anhinga. I have heard the cormorant called jichkal but this seems nonstandard. 


Kuts ha’ “water turkey.” Muscovy Duck, Cairina moschata. (More commonly just 
called pato, the Spanish for “duck.” To distinguish it from the rarely found domes- 
tic mallard, it is called pato criollo “native duck.”) Common domestic and rare wild 
bird. Used for food and as a pet. 


Pijije. Black-bellied Whistling-duck, Dendrocygna autumnalis. Echoic. This is the 
Spanish name too, but it was probably borrowed from a Maya language or from 
Nahuatl. 


Ch’om “vulture.” One of the few named groups in which a true folk generic is 
broken down into folk specifics: 


Batab ch’om “chief vulture.” King Vulture, Sarcorhamphus papa. 
Box pool ch’om “black-headed vulture.” Black Vulture, Coragyps atratus. 
Chak pool ch’om “red-headed vulture.” Turkey Vulture, Cathartes aura. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 153 


Hawk group: All hawks are recognized as related, as is shown by the fact that they 
can all be covered by widely extending the terms ch’uy and ii’ and by the Spanish 
aguililla or gavilan. Careful speakers, however, break out several other categories. 


Ch’ uy “large hawk.” This term can cover any large hawk. 
Ek’pip. Black alate Spizaetus tyrannus. Extended to other hawk-eagles and 
large impressive hawks 


Ti’. Focally the Gray Hawk, Buteo nitidus, but used for any medium-sized hawk, 
especially pale-colored ones. 


Sak ii’ “white hawk.” The Gray Hawk in particular—or, sometimes, any light- 
colored hawk—as opposed to other ii’. 


Jonkuuk. Harpy Eagle, Harpia harpyja. Now extinct in the area, but the name is 
well known to local residents, who remember the bird and describe it accurately. 
It also appears in the Colonial dictionaries, with unmistakable descriptions. 


Koos. Laughing falcon, Herpetotheres cachinnans. Unlike the other hawk names, 
this one is not often extended. 


K’eenk’eenbak’. Small falcons. Apparently the most typical, or perhaps even focal, 
one is the Bat Falcon, Falco rufigularis. However, the term is extended to any small- 
ish, pointed-winged bird of prey, up to and including the White-tailed Kite, Elanus 
leucurus, which is also called ii’ and sak ii’. The male bat falcon is called kiris or 
kiklis. 

Bach. Chachalaca, Ortalis vetula. There is some possibility that the chachalaca is 
seen to be related to the following four, but I have no evidence of it. Common; 
food item but usually too wily to kill. Also called kobi or koba. 


Kox. Crested Guan, Penelope purpurascens. Food. Now very rare. 
K’ambul. Curassow, Crax rubra. Faisan in local Spanish. Food and pet. Rare. 


Kaax. Domestic fowl, Gallus domesticus. Name derived from Kastelan “Castilian,” 
a recognition of the introduction of the bird by the Spanish. A rooster is t’eel, which 
must once have meant a male bird or male game bird in general. 

Bech’ group: 

Bech’. Yucatan Bobwhite Quail, Colinus nigrogularis. Common. Potentially a food, 
but in practice too small and wary to be worth the trouble of hunting it. 

Chibilub. Singing Quail, eee thoracicus. Rare; potential food, actually too 
rare and well-hidden to hunt 

Turkey group: unlabeled but eee recognized, and terminologically united by 
sharing special terms for tom and hen. 

Uulum. Domestic Turkey, Meleagris gallopavo. Echoic name. Common; important 
food resource. Tom is tso’, hen is tuux 


154 ANDERSON Vol. 20, No. 2 


Kuts. Ocellated Turkey, Agriocharis ocellata. Formerly important game bird, now 
almost exterminated by overhunting. I believe the tom and hen are labeled as in 
the preceding. 


Gallinola. Gray-necked Wood-rail, Aramides cajanea. Also Northern Jacana, Jacana 
spinosa (when it is not given its proper Maya label). Extended to any other rails 
present (the only common one is the Sora Porzana carolina, a winter visitor). Water 
birds are so rare in interior Quintana Roo that Maya names have usually been 
replaced by Spanish ones—as in this case. 


Correa. Limpkin, Aramus guarauna. Spanish name; probably a variant of the com- 
moner Spanish carao. 


T’eel ha’ (“watercock”). Jacana, Jacana spinosa. Probably extends to similar birds. 
Pigeon cluster; all lumped as ukum or under the Spanish term paloma. 


Paloma. Rock Dove, Columba livia. Common tame bird. Since it is a Spanish intro- 
duction of no great age in the area, it has no Yucatec name. 


Chuukij. Scaled pigeon, Columba speciosa. 


Ukum (ukuch). Red-billed pigeon, Columba flavirostris. Echoic. This is the common 
pigeon of the area, and its name is routinely extended to mean “large pigeon in 
general,” i.e. to cover the preceding species. Also called kukut’kib, which name is 
also extended to the foregoing. Used for food, but rarely taken. 


Sakpakal. White-winged Dove, Zenaida asiatica. 


Tsutsuy. Leptotila doves and similar doves. Common is the White-tipped Dove, 
Leptotila verreauxi. Other species occur and are not distinguished terminologically, 
except for the Ruddy Quail-dove, Geotrygon montana, which is chak (red) tsutsuy 
or k’aankab (red-dirt) tsutsuy. 


Mukuy. Ground doves. Probably echoic. Three species: 
Chak mukuy “red ground-dove.” Ruddy Ground-dove, Columbina talpacoti. 
Abundant; occasional pet. 
Sojol mukuy “leaf-litter ground-dove.” Common Ground-dove, C. passerina. 
Rare. 


Tuch mukuy “ground-dove that calls tuch,” thus part-echoic. Blue Ground- 
dove, Claravis pretiosa. Common but shy and seldom seen. 


Parrot group: recognizable by being lumped collectively as t’uut. 


T’uut. White-fronted Parrot, Amazona albifrons. Common; frequent pet. Also a fre- 
quent pest of milpas, eating maize, fruit, and almost anything else well above 
ground level. 


Ek’xikin “black ear.” Yucatan Parrot, Amazona xantholora. The Maya name hits 
home—it points to the one field mark reliably distinguishing this uncommon bird 
from the preceding. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 155 


Kocha’. Red-lored Parrot, Amazona autumnalis. Pet, but rare in the area. Also called 
kulix. 


Taadi’. White-crowned Parrot, Pionus senilis. 


K’ili’. Aztec Parakeet, Aratinga nana. Abundant, and a very serious pest, descend- 
ing in flocks on maize and fruit. Sometimes shot with slingshots when caught in 
the act. (Chunhuhub Maya do not usually, otherwise, kill even the worst pests.) 
Kili’ are never called t’uut. 


Baakenchulul. Pheasant cuckoo, Dromococcyx phasianellus. Extended to cover the 
Lesser Roadrunner Geococcyx velox, rare and probably a recent arrival in the area 
(coming with large-scale clearing of forest). 


Kipchoo’. Squirrel cuckoo, Piaya cayana. Echoic. 


Chikbu’ul. Groove-billed Ani, Crotophaga sulcirostris. Echoic, but folk-etymologized 
in that bu’ul means “beans,” and anis often hide in bean vines. 


Owls would seem a natural cluster, and this may be shown by their uniformly 
ominous significance, but they are always kept terminologically distinct, so far as 
I have heard. 


Xooch’ (or xiich’). Barn owl, Tyto alba. Echoic. A bird of very bad omen; if it shrieks 
over a house, an inhabitant or relative will die. This common European belief may 
have been introduced by the Spanish. 


Tunkuruchu’. Great Horned Owl, Bubo virginianus. Echoic. Also called bujk’aanij 
and xo’chikin. A bad omen. 
Kulte’. Mottled Wood-owl, Ciccaba virgata. 


Chaxnuk (from chak xnuk, “little red old man”). Ferruginous Pygmy Owl, 
Glaucidium brasilianum. Also a bad omen, but so common and tame that no one 
takes it very seriously. Name extended to other small owls. Also called koak’ab, 
“the one who goes ko at night,” which is, obviously, a part-echoic name. 


Nightjar cluster: Identifiably a cluster because they are covered by the well-known, 
widely used Spanish term tapacamino. 

Pujuy. Paraque, Nyctidromus albicollis. Probably echoic. 

T’unkiya. Salvin’s Nightjar, Caprimulgus salvini. (Probably also covers the rare 
Yucatan Will, Nyctiphrynus yucatanicus.) Echoic. 

Jaap. Common Potoo, Nyctibius griseus. Echoic. 

Ts’unuun. Hummingbirds in general. The many species found in Chunhuhub are 
not terminologically distinguished. Apparently echoic of flight sound. 


Uulum k’aax “forest turkey.” Trogons, Trogon spp. Echoic; name from similarity of 
call to turkey’s common note. Several species occur and are seen as different, but 
they are not terminologically recognized. People in other areas say that kux is the 
correct name for the trogon. 


156 ANDERSON Vol. 20, No. 2 


Juj. Blue-crowned Motmot, Momotus momota. Echoic. 


Toj. Turquoise-crowed Motmot, Eumomota superciliosa. Echoic. The Spanish name, 
often used, is pajaro reloj—“ clock bird”—because this motmot regularly swings its 
long, pendulum-like tail from side to side. 


Toucan cluster; recognized because the name panch’el is used for both species. 
Panch’el. Collared Aracari, Pteroglossus torquatus. 

Pitoreal or tucan. Keel-billed Toucan, Ramphastos sulfuratus. 

Woodpecker cluster; collectively called either che’hum or kolonte’. 


Che’hun. Golden-fronted Woodpecker, Melanerpes aurifrons. Often extended to the 
Yucatan Woodpecker Melanerpes pygmaeus and sometimes to other species. 


Chi’pirix. Ladder-backed Woodpecker, Picoides scalaris. Name—or, usually, just the 
pirix—sometimes extended to the Yucatan Woodpecker (which looks like a Golden- 
fronted but is smaller, about the same size as the Ladder-back). Name also extended 
to the male genitalia, as is the Spanish picocarpintero (“woodpecker”) in Mexican 
folk speech. 


Kolonte’. Lineated Woodpecker, Dryocopus lineatus, and Guatemalan Ivorybill, 
Campephilus guatemalensis. These two woodpeckers are very similar and tend to 
occur together. Even those who see that they are separate species tell me that the 
birds are too similar to be worth distinguishing! Probably an echoic name. 


Tatak’che’ (tak’ak’che’). Woodcreepers, family Dendrocolaptidae. A collective term. 
It is extended to cover the Smoky-brown Woodpecker, Veniliornis fumigatus, which 
looks and acts more like a woodcreeper than a woodpecker—though it is some- 
times called che’hun, too. The several species of woodcreepers are uncommon and 
hard to spot, and—again—even those who see they are different see no reason to 
recognize that fact terminologically. Echoic, but of the birds’ pecking, not of their 
calls. 


Sob (or, more rarely, pu’). Barred Antshrike, Thamnophilus doliatus. 


Flycatcher group: united by loose and sloppy use of the following three names— 
especially the first and last—to cover the whole group. 


Bech’ lu’um. Black-faced Antthrush, Formicarius analis. Also called tsiimink’aax 
(“forest horse”)—a name also used, formerly at least, for the tapir. The reason for 
this naming is hard to imagine. 


Takay. (This name is always spoken with the diminutive suffix x: Xtakay. It is given 
that way in other works.) Large yellow-bellied flycatchers, focally the Couch’s 
Kingbird, Tyrannus couchi, but including many species. Echoic. 


Juiiro. Medium-sized brown forest flycatchers. Echoic; these all have calls that 
sound like juiiro. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 157 


Yaj. Small flycatchers. Echoic. Focal is the Olivaceous Flycatcher, Myiarchus 
tuberculifer, whose mournful whistle does sound absurdly like a small child call- 
ing “Yaj!” (“Thurt!”). 


K’eo. Masked Tityra, Tityra semifasciata. Echoic. Extended to other tityras and similar 
birds. Name sometimes extended to peelank’eolij. 


Kusuun (kusaam). Swallows and swifts, collectively (families Hirundinidae and 
Cypseluridae). 


Pa’ap. Brown Jay, Psilorhinus morio. Echoic. Never called ch’el or linked with 
ch’eloob in any way, so far as I can tell. 


Jay group: Ch’el. These could be thought of as two “folk species” of a “folk ge- 
neric,” or as two very closely related folk genera united in a broader group. In 
spite of its name, the aracari toucan does not seem to be regarded as a ch’el. 


Ya’ax ch’el. Green Jay, Cyanocorax yncas. 
Ch’el. Yucatan Jay, Cyanocorax yucatanica. Probably echoic. 


Yankotij. Wrens, and, by extension, all small brown birds. The focal one is the 
Tropical House Wren Troglodytes musculus, which is literally the “one under the 
wall” (see main text). Many other species occur but are not named separately. 


Po’okin. Black Catbird, Melanoptila glabrirostris. 
Chiik. Tropical Mockingbird, Mimus gilvus. Echoic. Often Hispanicized to chica. 


K’ok’. Clay-colored Robin, Turdus grayi. Echoic. By extension, any medium-sized 
brown bird that is at all similar, such as wintering thrush species from North 
America. Hispanicized to coquita. 


Ooxil. Yellow-green Vireo, Vireo flavoviridis. Name means “the one in the bread- 
nut tree.” Also called ts’ i‘kalants’i’, which is echoic of the bird’s commonest song 
phrase. One of the few cases of a bird with two names. 


Ch’uyin. Rufous-browed Peppershrike, Cyclarhis gujanensis. Echoic. Extended to 
other birds with songs vaguely like “chuyin. 


Sojlin. Ant-tanagers, Habia rubica and H. fuscicauda. 


Ts’apim. Saltators, Saltator spp. Possibly echoic. Two species occur but are not dis- 
tinguished. Name routinely extended to unknown birds that look even vaguely 
like saltators. 


Ya’ax bech’ lu’um (“green ground-quail”). Olive Sparrow and Green-backed Spar- 
row, Arremonops rufivirgatus and A. chloronotus. These two virtually identical birds 
are not distinguished. They are not regarded as related to the Black-faced Ant 
thrush, in spite of the similarity in name. 


Azulejo. Indigo Bunting, Passerina cyanea. A Spanish name; there is no Yucatec 
Maya name, as is usual with winter visitors. 


158 ANDERSON Vol. 20, No. 2 


Chinchinbakal. Any small yellowish bird, including goldfinches, warblers, tana- 
gers with yellow underparts, etc. 


Pich’. Melodious Blackbird, Dives dives. Extended to other blackbirds that may 
occasionally appear. 


K’aaw. Great-tailed Grackle, Quiscalus mexicanus. Echoic. Almost always said with 
the diminutive: xk’aaw. 


Ts’iu. Red-eyed Cowbird, Molothrus aeneus. Echoic. 


Yuyum. Large orioles, focally the Alta Mira Oriole, Icterus gularis. Often Hispani- 
cized to yuya. 


Jonxa’anij (“the one who nests in palmettos”). Smaller orioles, focally the Hooded 
Oriole, Icterus cucullatus, which is the one that really “nests in palms.” There are 
controversies about where the rarer orioles fit, but usually they are called yuyum. 


Mut’. Yellow-billed Cacique, Ambl holosericeus. This name appears to be the 
Yucatec reflex of the widespread Maya root mut “bird.” (Ch’ich’ is a Yucatec form 
that may reflect an ancient alternate root or may simply be onomatopoeic.) I do 
not know why the Cacique is “the” bird par excellence, but perhaps it is related to 
the tight pair-bonding of the birds (they always answer each other—the Maya 
assume one of the pair has died if a call is not answered). There are other indica- 
tions that this is a very important mythic bird; see Anderson and Medina Tzuc, 
forthcoming. 


K’uubul. Wagler’s Oropendola, Psarocolius wagleri. Echoic. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 159 


Ethnobotany: A Reader. Edited by Paul Minnis. University of Oklahoma Press, 
Norman. 2000. $18.95 (paper). ISBN 0-806-13180-2. 


Edited by Paul Minnis and intended as a review of important works in ethno- 
botany, this book aims to give the reader a broad impression of what the discipline 
encompasses. Designed as a reader to accompany textbooks for upper division 
coursework, the fourteen chapters in this volume come from articles previously 
found in the Journal of Ethnobiology. The editor highlights contemporary studies in 
ethnobotany to acquaint the readers with current methods and findings in the 
field. To this end, the book is organized into four sections, ethnoecology, folk 
classification, food and medicines, and agriculture, each with a short introduc- 
tion. 

In the first section, ethnoecology is introduced in three chapters as the study 
of human perceptions and management of ecological phenomena, a discipline with 
roots in human ecology and cultural ecology. A particularly strong theme in the 
chapters by Janis Alcorn, Gary Nabhan, and Kat Anderson is the concept of adap- 
tive management. In each of these studies ecological perturbations of plant 
environments are driven by human needs, but the outcomes for ecological com- 
munities as a whole are generally positive. In the language groups studied, new 
resource use patterns lead to greater richness in biological system diversity at the 
level of both plants and other organisms, such as birds and mammals. 

The folk classification section focuses on the ways that people in different lan- 
guage groups construct vocabularies related to plants, with particular emphasis 
on critiquing or adding to the approaches of Brent Berlin. In the introduction 
Cecil Brown presents Berlin’s most important ideas, folk classification as basically 
an intellectual exercise of organizing plants into series of hierarchical categories in 
the Linnean tradition. In the following two chapters, Brian Morris and Nancy 
Turner question the premise of intellectual rather than utilitarian motivation for 
the naming of plants in their respective studies of the Chewa in Malawi and Salish 
language groups. Eugene Hunn and David French find that Sahaptin hunter- 
gatherers do not organize their plant vocabulary into hierarchical series but 
coordinate organism names into focused groups or peripherally to similar organ- 
isms. 

The longest section of the book relates to food and medicines and focuses on 
human interactions with wild plants. Much ethnobotanical literature is oriented 
to the study of plants as products that can be used as commodities, for example in 
the pharmaceutical industry. Contrarily for this book, the authors are more inter- 
ested in studying the human-plant relationship to illuminate questions of 
conservation. Paul Minnis looks at famine foods in the desert borderlands be- 
tween the United States and Mexico and how ethnic conceptions of these plants 
change as new foods are adopted. Robert Bye examines the ethnoecology of main- 
taining early-succession plant the t f edible wild greens 
among the Tarahumara Indians. Eugene Hunn critiques representations in 
Murdoch's 1967 Ethnographic Atlas by presenting examples of female plant-gath- 
ering activities in the Columbia Plateau area. Jan Timbrook and Robert Voeks 
examine tl f human interaction with medicinal plants. Timbrook 
notes how certain plants move into or out of favor with Chumash people as a 


160 BOOK REVIEWS Vol. 20, No. 2 


result of active cultural exchange with other language groups, and Voeks describes 
how the African diaspora into Brazil resulted in the use of Yoruba religious deities 
to inform the medicinal uses of local flora. 

The agriculture section deals with the ethnoecology of plant modification and 
domestication. Gary Nabhan shows how plant domestication is an ongoing pro- 
cess among several aboriginal tribes in the southwestern United States. The 
maintenance of potato diversity in Peruvian highlands in the face of agricultural 
modernization leads Stephen Brush to conclude that we cannot conceptualize the 
Green Revolution simply as the replacement of pre-existing agricultural diversity 
with new domesticated varieties. George Estabrook employs the concept of invis- 
ible technology to explain why fuel-wood choices are specific to certain tasks in 
central Portugal. 

The main criticism of this book stems from its relatively narrow geographic 
focus. Of the fourteen chapters in the book, ten relate to North American lan- 
guage groups and only two treat groups outside of the Americas. This is 
unfortunate given the detailed and important coverage in the ethnobotanical lit- 
erature of diverse groups in Africa, Australia, and Asia. The absence of any 
discussion on the medicinal knowledge of China is a particularly glaring omis- 
sion in the section on food and medicines. 

The strength of this volume lies in its explicit treatment of hybridized ethnobo- 
tanical systems in situations where western influences lead to profound changes in 
the ways that humans interact with the botanical environment. Ethnic vocabularies 
and interactions with the plant world are not perceived as static, but as evolving 
and changing with the needs and experiences of the groups involved in their cre- 
ation. This approach is useful in conceptualizing how human perceptions of plant 
resources are changing, and in turn how conservation might best be realized. 


J. Anthony Abbot 
Department of Geography 
University of Minnesota 


Journal of Ethnobiology 20(2): 161-192 Winter 2000 


EASTERN SUMBANESE BIRD CLASSIFICATION 


GREGORY FORTH 
Department of Anthropology 
University of Alberta 
Edmonton, Alberta, Canada T6G 2H4 


To Oemboe Hina Kapita and to the memory of Louis Onvlee (1893-1986) 


ABSTRACT.—In regard to ethnozoological classification, the Austronesian- 
speaking area of insular Southeast Asia is one of the least documented parts of 
the world. Dictionaries of the language of eastern Sumba by Kapita (1982) and 
Onvlee (1984) include over fifty names for kinds of avifauna with glosses in 
Indonesian (Bahasa Indonesia) and Dutch as well 

mostly From septiiaiy pegmange by the naturalist Dammerman in the 1920s. 
G 


author 


in the domain of Rindi, the eastern Sumbanese classification of birds is discuseed 
with regard to nomenclature, internal structure, and its relation to a general 
ethnozoological taxonomy. On the basis of recent ornithological studies of this 
part of Indonesia, the association of Sumbanese categories with scientific taxa is 
also reviewed. Finally, the prominence of certain bird categories in the symbolic 
idioms of ritual speech, myth, and augury is considered as a factor hypothetically 
linked with eastern Sumbanese ethnoornithological classification. 

Key words: eastern Sumba, Rindi, naming and classification of birds, 
ethnozoological taxonomy, symbolism. 

RESUMEN.—E] area de habla austranesia del sudoeste insular de Asia es una de 
las partes merioe: spcamentades del mundo en on a la clasificién 

I 


Ka ita 


(1982) y Onvlee (1984), incluyen alrededor de cincuenta nombres de clases de 
aves, con términos en scree ape Bahasa Indonesia) y holandés, asi como 


tambié t el trabajo de campo 
ade Pee 4 Haweieues Dammerman en los ‘afios1920s. ‘Combinando estos 
datos con la inf ica recopilada por el autor de este articulo 


en el area de Rindi la dace de } pajaros del sumbanés del este es discutida 
en relaci6n a la nomenclatura, estructura interna, y su relacién a una taxonomia 
etnozooldégica general. Sobre la base de recientes estudios ornitologicos en esta 
parte de Indonesia, también se discute la asociacién de categorias sumbanesas 
con taxa cientifica. Pinannente, la prominencia de ciertas categorias de pajaros en 
va ritual, el mito ne spanceeaieas apnepcammgoiets como 


Pa 4 } BS 


del Este. 


RESUME.—La classification ethnozoologique des Austronésiens de la partie 
insulaire de l’Asie du sud-est est l’une des moins connues dans le monde. Les 
dictionnaires de Kapita (1982) et Onvlee (1984) sur le langage du Sumba de I’est 
contiennent plus de cinquante noms d’espéces aviaires traduits en indonésien et 


162 FORTH Vol. 20, No. 2 


en hollandais, ainsi que leurs identifications scientifiques, dont la plupart 
p . sa Pa Pan ae I 1 ‘, iots Dammerman. dans les années 
1920. A partir de ces données et de l'information ethnoornithologique recueillie 

nsi 


par l’auteur dans le domaine du Rindi, la lature, la structure interne, ains 
que relation de la classification des oi du Sumba de |’est avec une taxonomie 
ethnozoologique générale sont examinées. L’association des catégories 

banai t des taxa scientifiq t égal t 4 la lumiére de récentes 
études ornithologiques effectuées dans cette partie de |’Indonésie. Enfin, 
l’importance de certaines catégories d’oiseaux dans l’expression symbolique du 
discours rituel, du myth et de l’augure est considérée comme un facteur 
hypothétiquement relié a la classification etl ithologique du Sumba de l’est. 


INTRODUCTION 


To date no special study has been conducted into ethnozoological classifica- 
tion on the Indonesian island of Sumba. The several Sumbanese languages belong 
to the Austronesian family and more specifically to a Central Malayo-Polynesian 
grouping (Blust 1979). As part of general ethnographic research carried out in the 
eastern Sumbanese domain of Rindi in 1975 and 1976 (see Map 1), I recorded a 
number of names for bird kinds. Most of these, and some others besides, appear in 
dictionaries of the main eastern Sumbanese dialect of Kambera compiled by 
Oemboe Hina Kapita (1982), the principal Sumbanese expert on the culture and 
languages of the island, and by the late Louis Onvlee (1984), a linguist and Bible 
translator and the main Western expert on Sumbanese languages. Onvlee con- 
ducted research jointly with Kapita between 1926 and 1955. 

e objective of this paper is to review all information recorded so far con- 
cerning eastern Sumbanese ethnoornithological classification. In view of the 
common appearance of birds in symbolic idioms, for example in Sumbanese ritual 
language and myth, this topic is relevant to rather more than questions of 
ethnotaxonomy and nomenclature. Since Onvlee wrote in Dutch while Kapita’s 
work is in Bahasa Indonesia (the Indonesian national language), a particular pur- 
pose is to make these data available to a wider ethnobiological, linguistic, and 
anthropological audience not familiar with these languages. 

Another relevant source, also in Dutch, is the writings of the naturalist K.W. 
Dammerman (1926a, 1926b). On the basis of research conducted on Sumba be- 
tween 14 March and 26 May 1925 (Monk et al. 1997:882), Dammerman published 
32 bird names in eastern Sumbanese (Kambera) and the same number in the west- 
ern Sumbanese language of Laura (transcribed by Dammerman as ‘Laora’). 
Dammerman’s work is germane not only because he was the first Western scien- 
tist to identify ornithological species present on the island, including two 
Sumbanese endemics, but also because Onvlee, especially, relies heavily on 
Dammerman (1926a) in defining eastern Sumbanese categories. Onvlee’s dictio- 
nary thus includes just five scientific names that appear to be drawn from 
(unspecified) sources other than Dammerman. Although both Onvlee and Kapita 
significantly extend the list of Sumbanese taxa recorded by Dammerman, one un- 
fortunate result of the two lexicographers’ reliance on the early naturalist is that 
many of the Latin binomials incorporated in their dictionaries are now superseded. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 163 


Nevertheless, modern binomials are for the most part readily inferred from a re- 
cent comprehensive ornithological study of Sumba and other eastern Indonesian 
islands by B. Coates and K.D. Bishop (1997). 

Another pitfall of the two » lexicographers' reliance on : Dammerman i is of course 

lity that tl twas mistaken i in associ taxa wit 

particular scientific species and genera. Modern iio tateae on bird kinds present 
on the island, however, supported by information drawn from Onvlee and Kapita, 
as well as linguistic and ethnographic data compiled by the present author, sug- 
gest that Dammerman’s identifications, scientific as well as ethnozoological, were 
largely accurate. In this regard as well, the work of Coates and Bishop (1997) has 
proven especially useful. In identifying eastern Sumbanese bird taxa I have also 
been able to draw on information provided by several eastern Sumbanese I ques- 
tioned in 1999 in Kupang, the provincial capital located in western Timor.! With 
the aid of Coates and Bishop’s field guide, the Kupang informants were able to 
clarify a number of important issues concerning the identity of birds named by 
Sumbanese terms. 

In spite of possible remaining gaps and ambiguities, the data compiled here 
appear sufficiently complete to analyze eastern Sumbanese bird classification and 
to establish the general outlines of the system. A point of some relevance in this 
regard is the comprehensive nature of Onvlee’s dictionary. As a student of 
Sumbanese languages who resided on the island for over 20 years, it cannot easily 
be assumed that Onvlee would have been unfamiliar with many terms referring 
to birds, even if he had been unable to identify them scientifically. Also notewor- 
thy is the circumstance that Kapita, although a native Sumbanese and probably 
better able to draw on a local knowledge of birds, does not record any names that 
do not also appear in Onvlee’s dictionary. In fact, Onvlee’s work is slightly more 
complete. This is not to suggest that further research could not uncover additional 
names for birds. Indeed, three terms encountered in the course of my own enqui- 
ries, in Rindi and among Sumbanese in Kupang (landu witu, mabihi, rawa kawi, 
see Table 1), are not listed by either Onvlee or Kapita, nor can they obviously be 
accounted for as local variants of terms the two lexicographers do record. Even so, 
the total of nearly sixty-odd I discuss below (56 plus as many as ten unnumbered 
productive binomials, which total however includes a number of synonymous 
usages) compares favourably with the 66 bird names (or 59, if probable synonyms 
and terms with non-empirical referents are excluded) recorded for the Nage of 
Flores (Forth 1996, 1999), and the 54 terms recorded for the Nuaulu of Seram (Ellen 
1993b). The figure for Nuaulu should be taken in the context of a total of 195 spe- 
cies recorded for the island of Seram (Ellen 1993b:57). The comparable total for 
Sumba as a whole is 161 (see Appendix 1; cf. Monk et al. 1997:354, who list 103 
breeding species for Sumba).° In view of environmental differences between east- 
ern Sumba and the more heavily forested and better watered western part of the 
island, moreover, it can safely be assumed that the number for eastern Sumba is 
rather lower than this. 

However the results of the present enquiry are judged, one may hope that 
they will be of sufficient interest to spur others to advance the study of eastern 
Sumbanese ethnozoological classification. Indeed, publishing information on the 


164 FORTH Vol. 20, No. 2 


ethnology of Sepa birds i is at present a matter of some seca Owing 1 in 
part to the advance of th national language, | 

names for natural kinds i is reported to be decreasing, especially 2 among younger 
people. In addition, as a result of increased hunting (nowadays particularly with 
air rifles), trapping to supply the export trade in cage-birds, and the destruction of 
natural habitats caused by human population increase, clearing of forests for agri- 
culture and lumber, and modern development efforts, in some cases the species to 
which the indigenous names refer are themselves probably in decline (see Monk 
et al. 1997:821-35; Coates and Bishop 1997:39-40).* 


Qy 


as 
ie SiGe pee 
BALI pe 
ee BLEN 
TIMOR 
10°} Rindi Ku oo 
SEMAUJ? 


SAVU, 
o> , 
ROTI 


1 18E 118° 120° ie ro 
FIGURE 1.— The Lesser Sunda islands showing Sumba and Rindi 


BIRDS IN SUMBANESE ETHNOTAXONOMY 


main product of the present exercise is a list of Sumbanese names for 

birds with provisional identifications. These are set out in Table 1. From linguistic 
and etl compiled by the present author in 1975-76, supple- 
mented by. Kapita (1982) and Onvlee (1984), it is possible to locate these bird taxa 
within a broader context of folk taxonomy (see Figure 2). The Sumbanese classifi- 
cation of animal kinds can readily b th Jel of ethnobiological 
taxonomy developed by Berlin and his associates feel Berlin 1992). Berlin’s terms— 
unique beginner, life-form, intermediate, folk generic, and so on—thus provide a 
useful means of analyzing local categories and exploring their mutual relation- 
ship. The nature of eastern Sumbanese bird nomenclature also lends support to 
Berlin’ S approach SDORRE as it — a Classification based primarily on observ- 
eatures including vocal behaviour) rather than 

on non-perceptual criteria. All the same, ‘the Sumbanese categories are further re- 
lated in other, non-taxonomic ways, thus participating in a separate, symbolic 
classification (cf. Forth 1998b:190-91). Non-taxonomic articulations of bird catego- 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 165 


ries are discussed after a review of nomenclature. In the concluding section I briefly 
consider the possible influence of symbolic value on the ethnoornithological tax- 
onomy in general. 

Whether tern Suml tl 1 | classification i tes a term 
se Ai designating ‘animal(s) ‘thus a named “ unique beginner” (Ber- 
lin 1992:15)—is somewhat debatable. The main candidate is the expression 
makayidi-yadaku, ‘things that move,’ which both Onvlee and Kapita further gloss 
as ‘the whole of creation’ (or ‘all creatures,’ semua makhluk, Kapita 1982 s.v. 
kayidiku). The phrase is based on the compound yidi-yada, COmprininy we 
roughl ‘to move,’ and producing an allit 
symbolism comparable to English ‘topsy-turvy’ or ‘twist (and) turn’ and Bahasa 
Indonesia gerak gerik, which indeed translates the Sumbanese pair. In combina- 
tion the affixes ka- and -ku lend a repetitive or continuous quality to the basic 
verbal compound, while ma- (‘that, what, that which’) renders the nominal sense. 
Although logically makayidi-yadaku could include Homo sapiens, the phrase is 
not normally applied to human beings and is thus comparable, for example, to the 
BAG Adama English use of _— bid apete the word contrasts with ‘man, human.’ 
The sense of the Sumbanese phrase, that 
is, he Bel that it appears mostly to be used as a reference to ‘animals’ in general 
rather than to single individuals. Consistent with this, Kapita does not gloss 
makayidi-yadaku as binatang (‘animal,’ Bahasa Indonesia), nor does Onvlee trans- 
late it with Dutch dier or beest. (Also, the last author gives the phrase as da 
makayidi-yadaku, thus incorporating the plural article da.) Nevertheless, 
makayidi-yadaku is a term Sumbanese regularly employ to refer to animals, not 
an expression constructed in response to lexicographical questioning. That they 
possess a category of ‘animal’, moreover, is indicated by the numeral classifier 
ngiu (tail), which is used when ennumerating animals but not humans or other 
living things.° 

Although makayidi-yadaku applies to all non-human animals, its focus ap- 
pears to be undomesticated kinds. Interestingly, yada, the root of yadaku, can 
mean ‘wild, untamed, difficult to tame,’ as well as ‘to move, be capable of move- 
ment’ (Onvlee, Kapita s.v. yada). Yet this sense—probably involving a metonymy 
whereby a propensity to movement connotes the opposite of tameness—is not 
clearly decisive for its incorporation in the longer expression.® Domestic animals 
are collectively called banda. This however is a secondary meaning of a word, the 
main sense of which is ‘goods, possessions, wealth’ (cf. Bahasa Indonesia benda). 
As this derivation may suggest, the term moreover refers particularly to large live- 
stock, a principal form of wealth in the Sumbanese traditional economy. Some of 
my Rindi informants claimed that banda could be understood in the wider sense 
of ‘animal’ (Bahasa Indonesia binatang), with wild animals then being specified 
as banda matamba (wild banda); but neither Onvlee nor Kapita record the latter 
phrase and I suspect that, even at present, it is not a widespread or standard us- 
age. Whatever the case, and regardless of the extent to which makayidi-yadaku 
and banda may share common referents, the two categories are not obviously re- 
lated by taxonomic inclusion. By the same token, banda can be characterized as a 
utilitarian category, referring mostly if not entirely to a class of economic values, 


166 FORTH Vol. 20, No. 2 


while makayidi-yadaku is a descriptive phrase naming a category of living things 
distinguished explicitly on behavioural, and implicitly on morphological, grounds. 

Since makayidi-yadaku refers to an ability to move, it is significant that the 
taxon subsumes two major categories both of which are denoted by phrases refer- 
ring to specific kinds of movement. Both constitute “life-form” taxa, in the sense 
defined by Brown (1979) and Berlin (1992:15ff). One is mabei, ‘things that creep, 
crawl,’ a large and internally diverse taxon that can include insects, arachnids, 
reptiles, amphibians, and even fish. The other is mahawurungu, ‘things that fly.’ 
Not surprisingly, birds are focal to mahawurungu. Contrary to what the name 
would suggest, not every sort of aerial creature is included in the taxon. For ex- 
ample, the ‘Flying dragon’ (probably Draco volans, cf. Dammerman 1926a:218, in 
Rindi called kumbu lai hawurungu, ‘flying lizard’) is reckoned not to belong to the 
mahawurungu but rather to the mabei, together with other lizards. Some Rindi 
thought that flying insects—such as houseflies, wasps, and bees—should be 
counted as mahawurungu. However, because they crawl as well, the creatures are 
also—and probably more usually—classified as mabei. It almost goes without say- 
ing that bats are classified as mahawurungu. Since the term translates exactly as 
‘flying things’ it may be questioned whether Sumbanese, like most folk zoolo- 
gists, actually classify bats as kinds of ‘birds.’ That they do so is indicated by the 
fact that Rindi mentioned bats with birds when listing names of ‘flying things,’ as 
well as by a local belief that bats lay eggs. 

The derivation of mahawurungu requires comment. Hawurungu (to fly) com- 
prises a fused prefix, ha-, and wurungu, evidently a cognate of Malay (or Bahasa 
Indonesia) burung (bird) and, following some authors, a reflex of an Austronesian 
protoform referring to birds in general (see Dempwolff 1938; Lopez n.d., cited in 
Wurm and Wilson 1975). The same sources give no indication that wurungu re- 
flects protoforms meaning ‘to fly,’ and it may therefore be supposed that the 
Sumbanese word derives from a term that once denoted birds but has since, and 
with the addition of the prefix ha-, acquired a verbal sense which, by way of fur- 
ther prefixing, has as it were reverted to its original meaning.” There is however 
an alternative interpretation. Both Kapita and Onvlee indicate a derivation of 
hawurungu (to fly) from wuru, denoting the sound produced by the wings of a 
flying bird, or by an object that is thrown into the air. In that case, the eastern 
Sumbanese word for ‘to fly’ may even be based on an onomatopoeia, and its re- 
semblance with burung (bird) may be coincidental.® 

Connected with the opposed modes of locomotion to which the terms refer, 
mahawurungu and mabei comprise creatures that typically occupy areas located 
respectively above and below the human domain. Indeed, it is partly in this re- 
gard that one can comprehend the inclusion of fish (iyangu) among the mabei. For 
although fish do not actually ‘creep’ or ‘crawl, living in water they inhabit a re- 
gion beneath the space inhabited by humans. In addition, fish resemble other mabei, 
particularly reptiles, in several obvious morphological respects, thus suggesting a 
switch from behavioural criteria as a basis of classification.” Although they consti- 
tute two major named life-form taxa within th kayidi-yadaku (moving things), 
mabei and mahawurungu obviously do not exhaust the Sumbanese category of 
‘animals.’ Most noticeably excluded are mammals, both wild and domesticated. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 167 


These are designated only by individual terms (for example, ruha ‘deer;’ buti ‘mon- 
key;’ ringu ‘dugong’) which in most cases refer to terminal taxa coinciding with 
scientific species. The only distinction made within these categories is wild 
and domesticated varieties of what are idered single kinds. Thus, 
the wild cat and wild swine are called meo rumba and wei rumba (rumba is ‘grass, 
bush’) while their domestic counterparts are usually referred to simply as meo 
(cat) and wei (pig). As can be seen from Table 1, something similar is done when 
distinguishing wild and domestic kinds of fowls (manu) and ducks (rendi). 


2a (Tree Diagram) 


{unique beginner] 
makayidi-yadaku 


[life-forms] 
awurungu mabei (other animals, e.g. mammals) 
(flying things) (creeping things) 


[intermediates] 

rawa iRitu mdanginu (other birds 

(or 'Columbiformes') (small passerines) 

[folk generics] i 

rawa kamukumukitu marakuku manginu (other named 

rawa tana etc. (=Lonchura, etc.) generics) 
[varieties] 


manginu uhu, manginu wataru, etc. 


FIGURE 2.—Bird taxa in eastern Sumbanese ethnozoological classification 


168 FORTH Vol. 20, No. 2 


Since Sumbanese are quite clear that all bird inst f makayidi-yadaku, 
this category and mahawurungu are unambiguously related by taxonomic inclu- 
sion (see Figure 2). For the most part, the ‘bird’ taxon immediately includes a series 
of terminal generic taxa (using “generic” in the sense proposed by Berlin 1992:53- 
53) that are not further divided into named sub-types or varieties. The resulting 
structure of three levels is of course quite typical of folk classifications of living 
things. 

At the same time, the names recorded in Table 1 include some 28 binomials, 
and of these 16 appear to be productive in the sense that the second component 
specifies the referent as an instance of the class labelled by the first term. Thus, 
rawa tana, for example, specifies a member of the more inclusive category rawa. 
Other binomials are unproductive. Several comprise two words describing a fea- 
ture of the bird (e.g., katua wei, laleba nggangga, landu witu, mbera wurungu). 
The name totoru laka is also descriptive, combining a probable instance of ono- 
matopoeia with a colour term (laka, see Table 1). The six names that include kulu-, 
while formally similar to productive binomials, are not actually productive. De- 
spite the probable connection between kulu- and words in other Austronesian 
languages that mean ‘bird’ or a kind of bird (e.g., Nage/central Flores kolo ‘dove’ 
[Forth 1996:106]), tl I termd t denote any particular class of bird.1° 
As can be seen from Table 1, the birds thus named are quite various, and indeed, 
Rindi denied that they were related to one another, or were variants of a single 
kind. What is more, kulu- also occurs as a component of terms designating natural 
kinds other than birds (see kulu-kengu, millipede; kulu-nderi, a kind of grass; see 
also kulungu, a small sort of mouse and kulu, a kind of breadfruit, Artocarpus com- 
munis [Onvlee 1984]). In this respect, the morpheme is reminiscent of central Flores 
(Nage, Ngadha) kaka, which similarly forms part of bird names but further oc- 
curs in terms for other natural kinds (regarding Nage, see Forth 1996:101; also 
Verheijen 1963 on the same element in Manggarai). 

Most productive binomials form pairs, thus distinguishing just two taxa within 
the more inclusive kind (e.g., rendi manu and rendi yalangu). By far the most promi- 
nent instance of productive binomials are the six terms denoting kinds of rawa, all 
of which refer to members of the Columbidae (pigeons and doves). Not all mem- 
bers of this family, however, are specified with compounds of rawa. Others, 
particularly it seems smaller members, are named kulu-ndiha or mbara, a word 
that is itself modified to produce terms distinguishing different kinds of dove (see 
mbara manu and mbara nggela). None of the available evidence indicates that 
either mbara or kulu-ndiha is straightforwardly included within a broader taxon 
labelled rawa. At the same time, some of the referents of rawa, applying at the 
folk generic level, may overlap with those of mbara. Onvlee thus gives Treron 
teysmanni as the referent of both mbara and rawa ratu. (Kapita’s gloss, by con- 
trast, links only Streptopelia chinensis with mbara, whereas Onvlee, rather 

I ts thi ies Wi Sumk term.) Onvlee further equates 
this small dove is a probable 


. gly, co this species with 
rawa kakoruku with Geopelia maugei, while in Rindi 
referent of mbara nggela. 

The terms rawa and mbara are also comparable insofar as both are used with- 
out qualification to refer to particular kinds further named by compounds. For 
example, rawa refers especially to Ducula aenea (rawa kamukumu), the Imperial 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 169 


pigeon, a bird that in Rindi at least is further called rawa manu and is the largest 
of the Sumbanese Columbiformes. " The appearance of mbara in compound ex- 
pressions denoting creatures that g rice crops (see Table 2) strongly 
suggests that this term specifies Streptopelia and Geopelia, although the cuckoo- 
dove (Macropygia ruficeps) also consumes rice (Coates and Bishop 1997). Larger 
pigeons, including both the genera Ducula and Treron, are by contrast fruit-eaters. 
Hence, it is conceivable that Sumbanese apply rawa generally to Columbiformes 
while reserving mbara for particular instances, distinguished either absolutely or 
situationally, according to their dietary behaviour—a matter that bears on an ob- 
vious utilitarian or practical consideration. 

Whatever the exact relation between rawa and mbara, the former term can be 
seen as labelling an “intermediate” grouping, falling between the levels of life- 
form taxa and folk genera (Berlin 1992:139-160; see Figure 2). On the other hand, 
this status might more accurately be assigned to a larger, unnamed class of 
Columbiformes, most of which—but not all—are designated as rawa while others 
are called mbara (or by terms including these) or kulu-ndiha. In other words, all 
Columbiformes may be treated as a single, distinct—though strictly-speaking co- 
vert—intermediate category in eastern S | taxonomy 
(cf. Forth 1996). Another candidate for intermediate status is a group comprising 
most or all of the diurnal raptors. As noted in Table 1, Falconiformes are generally 
labelled as ikitu, although the term’s primary referent appears to be the Brahminy 
kite, a bird more specifically named as ikitu marakuku (‘White necked/throated 
ikitu’). Consistent with this broader use of ikitu are three western Sumbanese 
(Laura) terms for diurnal raptors listed by Dammerman (1926a), all of which in- 
clude the cognate wikita. These are wikita liza, wikita rewa koko, and wikita 
labo, and correspond respectively to eastern Sumbanese kapaha, ikitu/ikitu 
marakuku, and_mbaku/mbaku tehiku. 


ikitu 


ikitu tolungu (‘meat hawks’) 


ikitu mafakuku 
(Brahminy Kite) | mbaku kapaha tariku, etc. 


mbaku mbaku tehiku 


FIGURE 3.—A Rindi classification of diurnal raptors (ikitu) 


170 FORTH Vol. 20, No. 2 


According to the detailed report of a Rindi informant, ikitu, understood as a 
general term for diurnal raptors, comprises two divisions. One includes a single 
kind, the Brahminy kite (marakuku). The second, labelled as ikitu tolungu (roughly, 
‘meat hawks’), admits other named kinds (kapaha, mbaku, tariku; see Table 1), 
including members of both the Accipitridae and the Falconidae (see Figure 3).! 
The same source specified the following order of size among members of the sec- 
ond division: mbaku tehiku (Haliaeetus leucogaster, the largest), mbaku, kapaha, 
tariku (the smallest).!> Unfortunately, I was unable to determine how far this clas- 
sification of diurnal birds of prey is shared among eastern Sumbanese. Essentially, 
it separates the Brahminy kite (Haliastur indus), the raptor most closely associated 
with the name ikitu, from all other members of the broader taxon identified with 
the same term. Since Haliastur indus also eats flesh, the contrasting term “meat 
hawk’ does not illuminate the basis of the division. It is however possible that the 
bird’s greater reliance on scavenging rather than killing may be relevant.'* Also, 
while the Brahminy kite is often sighted inland—where, like other raptors, it is 
perceived by Sumbanese as a threat to poultry—it is more commonly found on 
the coast. This of course is also the preferred haunt of the sea-eagle (mbaku or 
mbaku tehiku). But the sea-eagle is nevertheless distinguished from the kite inso- 
far as, according to Rindi at least, the former is the one raptor that does not steal 
chickens. 

As elsewhere in Indonesia, on Sumba large raptors play a prominent role in 
creation mythology. In parts of Flores, it is the Brahminy kite in particular that is 
associated with a creator deity (Laubscher 1975; see also Freeman 1960 and Metcalf 
1976, regarding the Brahminy kite in Bornean cosmology and augury). In eastern 
Sumba, by contrast, this part is taken by Haliaeetus leucogaster, the White-bellied 
sea-eagle (see below). Yet Rindi descriptions of the mythical bird sometimes sug- 
gested features of the Brahminy kite. Relevant to a possible conflation of the two 
birds which this suggests is Onvlee’s gloss, which indicates that the large kite may 
be classified as a kind of mbaku, more particularly the ‘White-throated mbaku’ 
(mbaku bara kuku, see Table 1), a situation that recalls the sort of classificatory 
overlap already evidenced with regard to Columbiformes. Effecting an inversion 
of the relation of inclusion implied by Onvlee, my Rindi informant listed both 
mbaku and mbaku tehiku under ikitu tolungu. However, his description of mem- 
bers of the first taxon (mbaku) did not unambiguously indicate the Brahminy kite, 
and it may well be that, in Rindi at any rate, this term is applied to a variety of 
larger eagles and hawks. Regional variation in folk classification may be relevant 
in resolving these issues. So too may colour phases and environmental contexts of 
large raptors. For example, Haliastur indus (the Brahminy kite) may be classified 
as a kind of mbaku specifically when encountered near the sea (cf. Ellen 1993a). 

Another folk taxon represented as comprising a number of distinct types is 
manginu. Like Onvlee (1984), Rindi informants claimed there were numerous 
‘kinds’ (Bahasa Indonesia macam, jenis) of manginu.!© Mentioned among these 
were manginu uhu (‘rice manginu’), manginu wataru (‘maize manginu’), manginu 
tana (‘ground [-dwelling] manginu’), and manginu kulu-kataitaku; but there were 
reckoned to be many more besides, whose names were not known. With the ex- 
ception of kulu-kataitaku, a term used alone to label a generic taxon (see also 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 171 


manginu kadu, Table 1), these several qualifiers however suggest simple descrip- 
tors serving merely to distinguish varieties of a single basic kind. In its most focal 
sense, manginu denotes Estrildine finches, especially munias (genus Lonchura) and 
similar small birds that do damage to rice and other cereal crops. Thus, the com- 
pound mbara manginu, ‘doves and munias,’ is a standard expression for birds 
that destroy ripening cereals. Yet in a more inclusive application the term further 
refers to a large variety of generally small passerine birds (or “dicky-birds”; see 
Figure 2), in which context it suggests an intermediate grouping comparable to 
ikitu and rawa (cf. the Nage term peti, ana peti, Forth 1996, which is similarly 
paired with a term for Columbiformes, kolo, to refer to crop pests).!” At the same 
time, in its more inclusive sense manginu differs from these insofar as it appears 
not to be simultaneously identified with a single, undivided folk generic (as ex- 
emplified by ikitu marakuku and rawa kamukumnu). This broader usage of manginu 
would moreover account for the apparent absence from the eastern Sumbanese 
ethnoornithological lexicon of special (that is, folk generic) terms for small birds 
such as flowerpeckers, flycatchers, honeyeaters, sunbirds, titmice, wagtails, war- 
blers, white-eyes, and whistlers (see Appendix 1).'° Apart from the focal finches 
and other small birds designated by special names, I would estimate that as many 
as 25 species listed in Appendix 1 could be classified simply as manginu. 

Eastern Sumbanese categories include two other candidates for intermediate 
status. One is an implicit taxon comprising the two black birds named nggangga 
(Large-billed crow) and laleba nggangga (a drongo, probably the Wallacean 
drongo). That these form a set is suggested not only by their physical resemblance, 
particularly in regard to colour, but by the designation of one as the ‘sister’s child’ 
(laleba) of the other (regarding the use of kin terms as evidence of covert interme- 
diate taxa, see Berlin 1992:145). The other instance of a possible intermediate taxon 
is panii. Usages recorded by Onvlee indicate that this term serves both to name 
the Flying fox and as a label for a more inclusive class that also includes much 
smaller bats (e.g., those called pahomba in Rindi). By contrast, evidence from Rindi 
suggests that panii may there refer only to Flying foxes (Pteropus spp.) while smaller 
members of the Cheiroptera may consistently be named with other terms. 


NOMENCLATURE 


As mentioned above, several names comprising two lexemes refer to empiri- 
cal or reputed characteristics of the birds so named (e.g., katua wei), as do 
components of productive binomials (e.g., ikitu marakuku). Where the meaning 
of a name, or part of a name, is analyzable, this is indicated in Table 1. The six 
names comprising kulu- all have analyzable second elements. Of these, four refer 
to visible features (e.g., -kadu, ‘horn, horn-coloured’); one is onomatopoeic (- 
kawaki); while the other possibly refers to some general quality attributed to the 
bird (-ndiha, ‘good, attractive’). In contrast, among names constituted of single 
lexemes, only two—kola and mbaku—possesses an independent meaning that 
describes a morphological or behavioural feature of its avifaunal referent. Another 
possibility is nggokaria (heron), insofar as this may be a variant of nggokaru, ‘to 
stretch, crane the neck,’ which Onvlee further lists as the word for ‘heron’ in the 
Lewa dialect of eastern Sumba. (Alternatively, nggokaria may comprise two ele- 


172 FORTH Vol. 20, No. 2 


ments, nggoka and ria, the first of which recalls central Flores gako, ‘large heron,’ 
see Nage gako tasi, Forth 1996.) Laleba nggangga indirectly refers to a morpho- 
logical feature insofar as it alludes to a resemblance with the Large-billed crow, 
nggangga. By the same token, it is the only name that includes a kin term (laleba, 
‘sister’s child’). (Ana in ananjaki cannot be construed as ‘child’ in the sense of a 
relationship term.) About 17 of the names in Table 1 describe physical features of 
their referents. Others refer to i tal iati (see landu witu, mbaku 
tehiku, rawa tana). 

Only a minority of names—about seven—are locally recognized as wholly or 
partly onomatopoeic (koka, kui, kulu-kawaki, nggangga, rawa kamukumu, rawa 
kakoruku, tutuku). Judging from reported vocalizations, another eight are pos- 
sible onomatopoeia (see kahuhu, kahiku, kaluki, kutuku, kuu, pipi, pirihu, totoru 
laka). The large number of avifaunal names beginning with ka-, a fused prefix, 
reflects a general lexical feature of Sumbanese languages. However, in some cases 
(notably kamukumu and kakoruku, but see also, e.g., kahiku, kahuhu) the prefix 
specifies something producing a sound denoted by the root (mukumu, koru; see 
Table 1). In other instances, the fused suffix -ku appears to effect a similar result 
(see kutuku, tutuku). The bl bet ggokaria and nggonggali is prob- 
ably superficial. 

Of the nearly sixty terms listed in Table 1, 33 or about 60 per cent, appear to 
name single scientific species. A large majority of these are the single representa- 
tives of their genera present on Sumba. If Dammerman and the lexicographers are 
accurate, a further three probably refer to just two members of the same genera 
(ananjaki, kalewaru, powa). Eight names, including three designating taxa of in- 
termediate status, apparently refer to three or more species of the same genera or 
indeed two or more genera (ikitu, karata, manginu, mbara, mbera wurungu, 
nggokaria, pipi, rawa). In the remaining cases, information is insufficient to make 
a determination. 

How far names for folk generic and intermediate taxa are further applied, or 
“extended” (Ellen 1993b), to species and higher order groupings associated with 
scientific kinds listed in Table 1 cannot be decided without more research into 
Sumbanese knowledge of birds. There are, for example, five species of Hirundo 
(see mbera wurungu) on Sumba, numerous members of the Ardeidae (including 
Ardea, Egretta, and representatives of six other genera; see nggokaria), and at least 
eight species of the Scolopacidae (sandpipers, snipes and allies; see pipi, kahuhu). 
Yet one cannot know a priori how many members of these ornithological families 
and genera Sumbanese would regularly identify with the indigenous terms. It is 
similarly unclear whether less common Columbiformes (such as the White-throated 
pigeon, Little cuckoo-dove, Nicobar pigeon, and two species of Ptilinopus, or fruit- 
doves) would be classified as rawa or named with other, thus far unrecorded, 
terms. In accordance with the classification illustrated in Figure 3, it is a reason- 
able surmise that ikitu can be applied without further qualification to 
Falconiformes, including five members of the Accipitridae recorded on Sumba 
but not indicated as possible referents of terms listed in Table 1. In regard to size, 
these are either comparable to the Brahminy kite (ikitu marakuku) or White-bel- 
lied sea-eagle (mbaku tehiku, the largest Sumbanese raptor) or fall somewhere 
between the two. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 173 


These sorts of questions of course turn partly on the completeness of the bird 
names listed in Table 1, an issue addressed earlier. As suggested, it is probable that 
a large number of small passerine species are simply classified as manginu. Com- 
parative evidence supports this. For example, Ellen, writing on the Nuaulu of 
Seram, refers to an “under-differentiation of passerines” that is “quite astonish- 
ing” (1993b:79). (A more general “under-differentiation of avifauna”, or 


classificatory “lumping”, Ellen partly att and straggling.) Given 
that eastern Sumbanese are not a maritime people, one should also not be ‘Sur- 
prised that seabirds and species i I ts are not 


well represented in Table A. a Larger passerine birds recorded on Sumba which 
are not obv with known indigenous terms, but which one might 
expect to be. separately named, include bee-eaters, cuckoos, cuckoo-shrikes, and 
the dollarbird (see Appendix 1). Yet even some of these could conceivably be named 
by employing already attested categories. Smaller cuckoos, for example, could be 
classified with the koel (kutuku), as might the larger Channel-billed cuckoo 
(Scythrops novaehollandiae), while bee-eaters and other larger passerines are argu- 
ably not so large that they could not be included in the category manginu.*! A 
comparable case are small kingfishers (Alcedinidae), if these are not classified with 
the significantly larger Halycyonidae as kahiku. (Also not to be ignored is the fact 
that Sumbanese has a single life-form label—mahawurungu—that can simply be 
applied to identify any bird not further classifiable.) In marked contrast, the names 
listed in Table 1 include no fewer than five terms referring to parrots (kaka, kariku, 
katala, pirihu, wowangu). Not only do all of these apparently denote single scien- 
tific species, but the five kinds exhaust parrot species occurring on Sumba. Thus, 
even though they do not compose a distinct emu as grouping —or at least 
not one that is named—the Sumbanese Psittacida 
elaborated to an even greater degree . diurnal raptors (ikitu) and 
Columbiformes (rawa). 


TABLE 1.—Eastern Sumbanese bird names 


1. ananjaki (or ana njaki). One or more species of Anthus (D 12: Anthus rufulus). Two 
present on Sumba include A. novaeseelandiae (Richard's pipit) and A. gustavi (Pechora 
pipit). As in other eastern Indonesian languages ana, ‘child’, can also denote a small 
version or instance of something (cf. Nage ana go, probably A. novaeseelandiae, Forth 
1996). Njaki apparently has no independent meaning. 

ikitu Haliastur indus intermedius, Brahminy kite (D 30, Haliastur intermedius). In Rindi 
the term refers more generally to Falconiformes. Kapita glosses it as BI elan 

(‘hawk’) and ‘Palconidae’ (sic). 

ikitu marakuku. Also a reference to H.indus. oe means ‘white-neck(ed), 
throat(-ed).’ The bird is also called by this term alon 

kahiku. Halcyon chloris (D 19). The only other len kingfisher present on Sumba 
is H. australasia (C&B). Whether the Sumbanese term might also refer to other 
kingfishers is not known. In view of one cry of H. chloris reproduced as ‘kick kyew’ 
(C&B), the name, particularly the root hiku, is probably onomatopoeic. 

kahuhu. A small shorebird, sandpiper. Kapita identifies the bird with the species 
Dammerman lists for pipi (see below). The word is probably unrelated to huhu in the 
sense of ‘breast, milk’ and is possibly onomatopoeic (see ‘teu-hu-hu’, the call of the 
Common redshank, Tringa totanus, C&B). 


Hod 


ad 


» 


174 


3. 


> 


_ 


% 


so 


hw 
- 


~_ 
— 


[RS 
14. 


FORTH Vol. 20, No. 2 


kaka. Cacatua sulphurea citrinocristata, Yellow-crested cockatoo (D 24: Cacatua 
citrinocristata). Onvlee also lists kaka ratu, or ‘royal cockatoo’, as a reference to a 
cockatoo ‘with red eyes’, but this appears not to refer to a separate species. 
kalewaru. Collocalia spp. (D 18), swiftlets. Species occurring on Sumba include the 
Edible-nest swiftlet, C. fuciphaga, and the Glossy swiflet, C. esculenta. Nests of the 
former species are collected for sale and eventual export. The local name kalew 

(cf. Manggarai lawar, ‘swiftlets and swallows’, Verheijen 1963) is related to BI kelawar 
or kelelawar, referring to a small bat. It is therefore of some interest that both swiftlets 
and bats characteristically roost in caves, often the same caves. Onvlee glosses the 
almost identical name kaliwaru as ‘swallow’ and, referring to Dammerman (D 17), 
as Hirundo. Dammerman in fact gives only mbera wurungu (see below) as the eastern 
Sumbanese name for swallows, though for western Sumba he lists the cognate 
kalewara for both Hirundo and Collocalia 

kaluki. Megapodius reinwardt reinwardt (D 38: Megapodius duperreyi), Reinwardt’s 
scrubfowl. The name plausibly imitates part of the bird’s call, given by C&B as *kli- 
au-kau’ (see wundu, below). 

kapaha. A small falcon, kestrel (D 29: Cerchneis occidentalis). Following C & B and the 
descriptions given by Dammerman (1926a:214, 1926b:22), the term is likely to 
include Falco moluccensis, the Moluccan kestrel or Spotted kestrel. (Another small 
falcon is F. longipennis, the Australian hobby, but this has only once been recorded on 
Sumba.) Kapita similarly describes the bird as a small Falconiforme with speckled 
plumage. Whether the name is related to pahangu (=paha + -ngu), meaning ‘to drop 
(trans.), let drop’, is not indicated by the lexicographers. 

kapi padangu. Recorded in Rindi, the term does not appear in either Onvlee or 
Kapita. Kapi means ‘to flicker (of a light or fire)’; padangu is ‘plain, pasture.’ In view 
of kapi mama, ‘firefly’, the term possibly refers to an insect rather than a bird. 
kapiru. Described by Onvlee as a “small red bird, a ground thrush” (Dutch 
grondlijster) which lays eggs in “a hole in the ground”. Kapita’s gloss “Pittadae” (sic) 
indicates a pitta. Although not actually in holes, Pittas in general do nest on or near 
the ground (C&B). The only pitta recorded on Sumba is Pitta elegans maria, the 
Elegant pitta, which has a red belly and vent and is described as “locally common or 
moderately common” on Sumba (C&B). Kapita’s further gloss, kutilang, an Indone- 
sian (BI) name for a kind of bulbul (none of which are natural to Sumba), can 
probably be ignored. 


. karata. Terns (Laridae, sub-family Sterninae), probably including the Gull-billed 


ci Gelochelidon nilotica, and one or more species of Chlidonias and Sterna. Rindi 
ormants stated there were two kinds of karata but could not distinguish them by 
name. A similar account was given by a Kupang informant, who described a ‘pure 
white’ variety that occurs near inland lakes and paddy fields and another sort, 
cream-coloured with dark marks on the back of the head, which is found on the 
coast. Onvlee and Kapita appear mistaken in identifying karata with, respectively, 
gulls (Dutch zeemeeuw) and Jaegers (BI burung camar). There are no gulls (Larinae) 
on Sumba 
kariku. Eclectus roratus cornelia (D 26: Eclectus cornelia), the Eclectus parrot. Rindi 
distinguish red and green varieties (kariku rara and kariku muru). As Dammerman 
(1926a:213-14) notes, these are actually the female and male of the same species, a 
fact recognized by Rindi people as well. 
katala. Tanygnathus megalorynchos sumbensis (D 27), Great-billed parrot. 
katua wei. The name means ‘companion of the pig.’ Kapita further glosses it as ‘pig 
spirit’ (BI roh babi). Both he and Onvlee identify this as an owl whose call indicates 
the presence of wild pigs, a notion encountered elsewhere in Indonesia (Forth 
1998b). Information is insufficient to determine whether katua wei refers to a 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 175 


i 
o 


_ 
> 


~ 
™~ 


= 
~ 


~_ 
K=) 


) 
= 


No 
— 


particular species of owl or whether this is one of the Strigidae or the Tytonidae (cf. 
wangi below). Among the Strigidae, C&B report just one, unidentified, member of 
the genus Otus on Sumba, as well as Ninox rudolfi, the endemic Sumba boobook. 
Quite possibly, katua wei denotes one or more varieties of nocturnal sound, rather 
than a particular kind of visible owl. 

koka. Philemon buceroides neglectus (D 11; not cited by Onvlee), the Helmeted 
friarbird, the only Philemon species present on Sumba. The name, also rendered 
contextually as nggauka, is described as onomatopoeic. 

kola. A diurnal raptor, listed by Onvlee as ‘Astur torquatus’, distinguished by a ‘neck 
ring of feathers’ (cf. Latin ‘torquatus’, ‘wearing a twisted collar or necklace’). The 
name probably derives from kola in the sense of ‘speckled, flecked.’ Kapita glosses 
the term as ‘falcon, Peregrine falcon’ (BI alap-alap; Falco_peregrinus). 

kuu. Both Onvlee and Kapita identify this as a kind of kite (Dutch bastaard-wouw) 
and specifically as ‘Elanus hypoleucos’, an apparent reference to the Black-winged 
kite, Elanus caeruleus hypoleucos. Neither the name nor the bird is listed by 
Dammerman. As Onvlee notes, the call of this bird, usually heard in the evening, is 
considered inauspicious. In Rindi, it is more particularly regarded as a manifestation 
of a witch. Consistent with this association are the partly crepuscular habits of Elanus 
caeruleus (C&B 1997:247), since Sumbanese witches, too, are believed to zs Sey 
active at twilight. On the other hand, Rindi described kuu as a ‘black’, o 

coloured, bird, as did informants in Kupang. That this does not entirely cand with 
the plumage of the Black-winged kite may be explained by the bird’s nocturnal 
associations; indeed on this account Kupang informants claimed never to have 
clearly seen the bird. Alternatively, kuu might refer to another bird altogether. In 
Umalulu, a domain immediately to the north of Rindi, I was shown a photograph of 
a dead bird identified as a kuu which had been killed because of its inauspicious 
calling after dark and which, I recall, resembled a female koel (see kutuku, below). 
Kruyt (1922:559), apparently inaccurately, describes kuu (transcribed as ‘koeoe’) as 
another name for the owl otherwise called wangi (see below). He also characterizes 
the name as onomatopoeic, as did one Kupang informant. Noteworthy here is the 
arguable resemblance of kuu to a nocturnal call of the koel (‘kooeei or ko-el’, C&B). 
However, another cry of the bird, rendered by Kupang informants as ‘yeep’ or 
‘weep’, corresponds with vocalizations reported by C&B for the kite, Elanus 
caeruleus 

kui. A bird named after its call (Onvlee), but otherwise unidentified. Kapita de- 
scribes it as having green plumage and feeding on ripe mangoes and other fruits. If 
this description is accurate, a likely candidate is the glossy green Short-tailed 
starling, Aplonis minor, which is reported as ‘moderately common’ on Sumba (C&B p. 
468) and consumes fruit (see also Mason and Jarvis, 1989:47, regarding the papaya- 
eating habit of Balinese Aplonis panayensis). (Contrary to Forth 1981:113, kui seems 
not to be associated with witches. This idea apparently reflects confusion with kuu 
[see above].) 


. kulu-kadu. Saxicola caprata (D 9: Pratincola caprata), Pied bushchat (or Pied Chat, 


C&B). Kadu, ‘horn’, alludes to the largely black plumage of the male. A term 
mentioned by Kupang informants, manita watu (watu is stone, cf. BI batu), is 
possibly a dialectal name for the bushchat (cf. BI kucita batu 

kulu-kakuta. Oriolus chinensis broderipii (D 14: Oriolus broderipi), Black-naped oriole. 
Meaning ‘resembling betel (kuta),’ kakuta seems to refer to the bird’s appearance, 
although its plumage is predominantly yellow and blac 


. kulu-kanuhu. Terpsiphone paradisi sumbaensis (D 16: Terpsiphone sumbaensis), Asian 


paradise-flycatcher. Kanuhu, which refers to the horse colour called Isabella, may 
describe the male bird’s predominantly off-white plumage. Onvlee, however, further 


176 


nN 
os) 


bh 
to 


~ 
wn 


i) 
SN 


nN 
XI 


i) 
Go 


~) 
s© 


FORTH Vol. 20, No. 2 


glosses the term as ‘rolled combed cotton’, which recalls the bird’s exceptionally long 
tail feathers. A Rindi myth recounts how these were derived from strands of cotton. 


. kulu-kawaki. A rail. Given by Onvlee as Rallina fasciata (Red-legged crake), but this 


species has not been recorded on Sumba (C&B). In respect of its attributed vocaliza- 
tions, the bird is possibly Gallirallus philippensis, the Buff-banded rail, or Amaurornis 
phoenicurus, the White-breasted Waterhen. The second element of the name is 
onomatopoeic (Kapita). Reputed to be especially vocal just before the onset of the 
southwest monsoon, the bird is significant in Rindi as an index of seasonal change. 


. kulu-ndiha. A sort of pigeon (Kapita: BI merpati, burung dara, both general terms 


for ‘pigeon, dove’). The term is at least partly, and perhaps exclusively, applied to 
domestic pigeons. Onvlee gives as western Sumbanese equivalents rawa and rawa 
tana (see below). Dammerman (D 35) gives kuru ndasi (cf. Nage kolo dhasi, Domes- 
tic pigeon, Forth 1996:106) for ‘Turtur tigrinus’, or ‘turtle dove’, referring apparently 
to Streptopelia chinensis (tigrina is the name of the sub-species of S. chinensis found in 
Wallacea; see mbara). The term kuru ndasi is not found in either Onvlee or Kapita. 
The second element of kulu-ndiha possibly derives from ndiha in the sense of ‘good, 
tive.’ 


attractiv: 


. kulu-taitaku or kulu-kataitaku or manginu kulu-kataitaku. Recorded in Rindi. Not 


listed by Onvlee or Kapita, though Onvlee gives manginu taitaku (see below). 
Onvlee glosses taitaku as ‘to walk, run quickly’ (cf. Kapita who provides the same 
gloss for kataitaku), and describes manginu taitaku as a bird that moves by jump- 
ing. The most likely referent is Rhipidura rufifrons sumbensis, the Rufous fantail. This 
is supported by Dammerman (1926a:210, 1926b:79), who gives the Laura (western 
Sumbanese) name for ‘Rhipidura semicollaris’ (semicollaris is the name now given to 
the sub-species of R. rufifrons that occurs on Flores) as kela kataga, ‘dancing bird’, a 
term evidently cognate with kulu-kataitaku. 

kutuku. Eudynamys cyanocephala, Australian koel (D 21: Eudynamis everetti). Accord- 
ing to C&B, this is the only member of the genus occurring on Sumba. The Common 
koel, E. scolopacea, is not listed by these authors, who however note that it may be 
conspecific with E. cyanocephala (1997:353). A possible application of the term kuu to 
the koel was noted above (see entry no. 17). Since the suffix -ku can indicate redupli- 
cation, the name kutuku is conceivably explained as a reference to a bird that calls 
‘kutu kutu’ (cf. tutuku, below). 


. laleba nggangga. Kupang informants identified this bird as a drongo. It is most 


probably the Wallacean drongo, Dicrurus densus. The name literally means ‘sister’s 
child of the crow (nggangga).’ Accordingly, Rindi describe laleba nggangga as like a 
crow only smaller. Onvlee (s.v. nggangga), citing Dammerman, lists the term as a 
reference to a ‘small black bird’ which he identifies as Corvus enca. However, C. enca 
does not occur on Sumba; nor in fact does Dammerman (1926a:208) link this spe- 
cies—which can hardly be called ‘small’—with the Sumbanese name. 


. landu witu. From illustrations, Kupang informants identified this as a species of 


nightjar, probably Caprimulgus affinus. Their descriptions of the bird’s appearance 
and habits also support this identification. The term is translateable as ‘sign of (from) 
the long grass’ (see Onvlee, s.v. landu, which also means ‘crest’). The name does not 
appear in either Kapita or Onvlee. According to Kupang informants, the distinctive 
nocturnal cry of a nightjar, reproduced as ‘cheri-ki-ki-ki’, indicates the presence of a 
thief, an idea that may illuminate the sense of ‘sign’ (landu) in the bird’s name. 


. mabihi. Unidentified. An eastern Sumbanese name reported only by Kupang 


informants, who gave quite various accounts of the bird’s appearance. The name is 
not found in Onvlee or Kapita. The variant in the dialect of Mangili is mabahi. 
manginu. Small birds, kinds of Munia (D 13; cf. Lonchura). The focus of the 
Sumbanese category comprises several of the Estrildine finches, especially ones that 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 177 


Ww 
bd 


ny 
y 


Se) 
i) 


RS 


35. 


do damage to crops (see the Dutch name rijstdiefjes’ [Dammerman, Onvlee], ‘little 
rice thieves’). C&B record six species on Sumba, including four munias (Lonchura 
molucca, L. punctulata, L. quinticolor, L. pallida), the Red avadavat (Amandava 
amandava), and the Zebra finch (Taeniopygia guttata). The names of other small birds 
classified as manginu are qualified, as follows 

manginu kadu. A black, horn-coloured manginu ‘which however does not eat rice’ 
(Onvlee). Very probably another name for kulu-kadu (see above). 

manginu kani. Passer montanus, Tree sparrow (Kupang informant; kani, or uhu kani, 
is the cereal Panicum viride). According to C& B, the species was first recorded on 
Sumba in the 1940 

manginu taitaku (see kulu-taitaku, above) 


. manu. Gallus gallus, Domestic fow]; distinguished from manu tata (below) as manu 


mopu, ati fowl.’ Several varieties are distinguished according to colour, size or 
derivatio 


. manu pati Gallus varius (D 37), Green junglefowl, sometimes simply called tata (cf. 


Nage kat 

mbaku. Haliaeetus leucogaster, White-bellied sea-eagle (D 31: Haliaetus occas 
Probably further applied to other large eagles and hawks. Mbaku also 

float, soar, glide, hover’ (Onvlee; see also luku mbaku, ‘mbaku river’, as ao name of 
the Milky Way). 

mbaku bara kuku. Described by Onvlee as an eagle with a white neck, smaller than 
the sea-eagle (mbaku), and otherwise ‘orange’ in colour. This however describes the 
Brahminy kite (see above: ikitu, ikitu marakuku. Marakuku is synonymous with 
bara kuku). 

mbaku tehiku. Given by Onvlee as ‘large sea-eagle’, the designation appears to be 
merely a more elaborate name for Haliaeetus leucogaster. On the other hand, it could 
conceivably include another large coastal raptor, the osprey (Pandion haliaeetus), 
which is peer 2 in size between the larger sea-eagle and the Brahminy kite. 
Tehiku is ’ 


. mbara. A de According to Kapita, my own field notes, and identifications 


provided by Kupang informants, the term denotes Streptopelia chinensis, the Spotted 
dove, and possibly also Geopelia maugei (but see rawa kakoruku, below). Following 
Dammerman, Onvlee associates the name with Treron teysmannii (D 32: Osmotreron 
teysmanni), the endemic Sumba green pigeon. However, partly in view of Onvlee’s 
further identification of the scientific name with rawa ratu, this appears mistaken. 
mbara manu. A larger kind of mbara, the size of a domestic fowl (manu; Onvlee s.v. 
mbara). The term was also recorded in Rindi, where it probably specifies Streptopelia 
chinensis. 

mbara nggela In Rindi, a smaller kind of mbara, possibly Geopelia maugei. Onvlee 
(s.v. ngguku, nggela) describes mbara nggela as a dove smaller than a similar kind 
called ngguku nggela (see below). Both of the latter terms mean ‘to move up and 
down, to nod’ and refer to the Columbiforme habit of bobbing the head. Kapita and 
Onvlee further gloss ngguku as ‘to coo.’ In Sumbanese songs and narratives, the call 
of the mbara is rendered as turu tu tu (Wielenga 1909). 

mbera wurungu. Swallows, Hirundo spp. (D 17). The name translates as ‘broken 
fragment of a pot’ (Onvlee, Kapita) and thus is evidently not related to hawurungu in 
the sense of ‘to fly.’ It is a reasonable surmise that mbera wurungu is further applied 
to Wood swallows (Artamus leucorynchus) and swifts (Apus spp.; see Appendix 1), but 
this cannot be known from the available sources 

nggaha. Domestic goose (recently introduced). From BI angsa (goose). 

nggangga. Corvus macrorhynchos (D 8), Large-billed crow. Like its many cognates in 
Austronesian languages, the name is locally recognized as onomatopoeic. 


FORTH Vol. 20, No. 2 


37. nggokaria. Herons, Ardea spp. (D 40). The term probably also refers to Egrets 


vo 
% 


es) 


Ha 


rs 
- 


N 


ts 


a 


rs 
ot 


(Egretta spp.) and other members of the Ardeidae. Rindi informants stated there 
were two kinds of nggokaria but did not know names for these. A Kupang informant 
suggested that Australian pelicans (Pelecanus conspicillatus), occasional visitors to 
Sumbanese inland lakes, might be classified as nggokaria. Probably relevant here is 
their watery habitat, as well as the white and black plumage, shape of their heads 
and—as the informant himself pointed out—large bills. 

nggonggali. Rhyticeros everetti (D 20: Rhytidoceros everetti), Sumba hornbill. The 
species is a Sumbanese endemic. 
. ngguku, ngguku nggela. Apparently the same bird otherwise designated as mbara or 
mbara nggela (see above). In Rindi, ngguku nggela, which refers to Columbiformes’ 
habit of head-bobbing, was a war cry uttered periodically by victorious warriors, 
particularly it seems when returning to their village with enemy heads, and while 
preparing the heads for ritual use (see Kruyt 1922:561). A Kupang informant from 
the eastern Sumbanese domain of Lewa reported the name ngguku kulungu, which 
he identified from illustrations in C&B as Geopelia maugei (see mbara). 
. pipi. One or more kinds of sandpiper (Tringa spp.; D 41: Tringoides hypoleucus). 
Dammerman’s reference particularly suggests Actitis hypoleucos, the Common 
sandpiper, whose call C&B describe as ‘a piping tii-tee-tee’ (C&B). Onvlee and Kapita 
give the equivalent term in the Mangili dialect of eastern Sumba as ahu ramuku, 
‘pool dog’ (ramuku is ‘pool, pond, wallow’). Pipi may be synonymous or overlap 
with kahuhu (see above). 

pirihu. Trichoglossus haematodus (D 23), Rainbow lorikeet. The endemic Sumbanese 
sub-species is T. h. fortis. The name bears some resemblance to one of its calls, 
reproduced by C&B as ‘peaow, peaow, peow’, and so is possibly onomatopoeic. 

powa. Coturnix spp., quails (Onvlee). Two species occur on Sumba, C. ypsilophora 
pallidior and C. chinensis, the Brown quail and Blue-breasted (or Chinese) quail. 
Whether the term also applies to buttonquails (Turnicidae), two species of which 
(including one endemic) occur on Sumba, is not known. 
. rawa, rawa kamukumu. Ducula aenea (D 33: Carpophaga aenea), Green imperial 
pigeon. Dammerman’s description clearly fits D. aenea. The Sumbanese sub-species 
is D. a. polia. As both Onvlee and Kapita note, the bird is also simply denoted by the 
generic term rawa, thus indicating that the species is the focus of the Sumbanese 
category. Kamukumu is onomatopoeic. 

rawa kakoruku. Geopelia maugei (D 36), Barred dove (Onvlee). Kapita associates this 
term with BI perkutut, which McKinnon (1991), referring to Jawa and Bali, identifies 
as Geopelia striata. Rindi claim that if this bird calls at night it presages a death. The 
second element of the name is onomatopoeic (cf. koru, ‘to coo (of a dove)’; ka- and - 
ku are fused affixes). 
. rawa kawi. A kind of pigeon, otherwise unidentified. The name was recorded only 
in Rindi. Informants were unable to explain kawi, a word appearing in neither 
Onvlee nor Kapita, though they described rawa kawi as intermediate in size 
between rawa manu (see below)—the largest rawa—and rawa tana. 
. rawa manu. A kind of large pigeon, about the size of a domestic fowl (manu). The 
name was recorded in Rindi, where informants’ descriptions suggested it may be a 
local designation for the bird otherwise known as rawa kamukumu (Ducula aenea). 
rawa ratu. Treron teysmannii, Sumba green pigeon (following Onvlee, who cites D 
32, probably in regard to the western Sumbanese name ‘rawa ratoe’; cf. mbara 
above). The species is a Sumbanese endemic. Ratu refers to a high-ranking ceremo- 
nial leader. In view of its use in similar contexts (see e.g. ularu ratu, the Reticulated 
python; also kaka ratu under kaka above), the term probably alludes to the bird’s 
colourful plumage. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 179 


48. rawa tana. Chalcophaps indica (D 34), Emerald dove. In Rindi I was told that the bird 
is so named because it remains on or close to the ground (tana, also ‘land, earth, 
soil’) and never alights in trees. It is also described as silent or rarely vocal, unlike all 
other rawa. (This notion may derive from the circumstance that C. indica usually 
does not call when on the ground; see C&B 1997:316.) Owing to its reputedly quiet 
nature and iridescent green plumage, in ritual language the bird’s name symbolizes 
favourable qualities and spiritual beneficence. 

49. rendi. Anas spp. (D 42), ducks. Wild ducks and introduced, domestic varieties are 
distinguished respectively as rendi matamba and rendi mopu, ‘tame ducks.’ Accord- 
ing to Onvlee, domestic varieties are further distinguished with reference to their 
origins, as for example rendi jawa and rendi manila. The most common species of 
wild duck, according to Dammerman, is Anas superciliosa, the Pacific black duck. 
According to C&B, the only other species of Anatidae found regularly on Sumba is 
Anas gibberifrons, the Sunda teal. However, a member of the Dendrocygnidae, 
Dendrocygna arcuata, the Wandering whistling-duck, is also present and locally 
common. 


rendi manu. Recorded in Rindi. A kind of wild duck (manu, ‘domestic fowl’) 

rendi yalangu. Recorded in Rindi. A kind of wild duck, smaller than rendi manu. Yalangu 
is evidently a different word from yalangu, which Onvlee records as the name of a 
kind of eucalyptus tree (Melaleuca leucadendron). 

50. tariku. A kind of falcon or small kite (Onvlee, Kapita); otherwise unidentified. An 
apparent synonym is taripu 

51. totoru laka. Centropus bengalensis, Lesser coucal (D 22: Centropus javanicus). This is 
the only coucal that occurs on Sumba. The first part of the name is probably ono- 
matopoeic (cf. ‘totok, totok, totopuk, totopuk, totopuk’ C&B). Laka, denoting a red 
colour and a tree, the leaves of which are used to produce a red nail varnish, 
evidently refers to the bird’s rufous wings. Totoru laka does not appear in Kapita. 

52. tutuku. The name of the coucal given by Kupang informants (cf. totoru laka), who 
explained it as deriving from an imitation of its the bird’s call, rendered as ‘tutu 
tutu.’ The fused suffix ~ku indicates repetition of the preceding element. Tutuku, 
however, is not listed as the name of a bird by either Onvlee or Kapita. In view of the 
relatively close relation and similarity of size, form, and colour between coucals and 
koels (kutuku, see above), the phonological and morphological resemblance of the 
names tutuku and kutuku is a point of some interest. Another is names for the Lesser 
coucal in dialects of the Manggarai language of western Flores, where it is called 
kotok or totok (Verheijen 1963). 

53. wangi. Tyto alba sumbaensis, Barn owl (D 28: Dutch kerkuil, Strix flammea.) Another 
Sumbanese species of Tyto is T. longimembris, the Eastern grass ow]. Dammerman 
states that the bird is considered to manifest a punitive spirit, and that its ‘croaking’ 
or ‘cawing’ forebodes sickness or death. Rindi people associate wangi with witches 
and particularly with the spiritual essence of a witch, called wandi. A connection 

tween this term and wangi is however improbable (see Forth 1991:109 n6, 445). A 
more likely cognate of the bird’s name is suangi, a word that in Malay and other 
western Indonesian languages refers to a maleficent, nocturnal spirit (cf. eastern 
Indonesian Malay suangi or suanggi, ‘witch’). A Kupang informant saat wangi 
as designating all owls ‘that are seen’, thus implicitly contrasting the 
katua wei (see above). Even if this is correct, however, the available slp still 
seen to Tyto alba as the focus of wangi. 

nner Geoffroyus geoffroyi floresianus (D 25: Geoffroyus floresianus), Red-cheeked 


parro 
55. Aen Asynonym of kaluki (see above) 


180 FORTH Vol. 20, No. 2 


56. yapi. Gallinula spp. (D 39: Gallinula frontata; Onvlee, incorrectly citing Dammerman, 
gives ‘Gallinula phunicura’). Two species of Gallinula occur on Sumba, G. tenebrosa and 
G. chloropus, the Dusky moorhen and Common moorhen. For Sumbanese the bird’s 
most distinctive feature is the bright red bill, which appears in both species. Another 
red-billed water bird that occurs on the island is Porphyrio porphyrio, the Purple 
swamphen. From illustrations, Kupang informants identified both the latter and G. 
tenebrosa as yapi. Onvlee describes the bird as inhabiting paddy-fields and doing 
damage to rice and tubers. 


ADDENDUM: BATS 


pahomba. A — bat (possibly sant iste sp.), about the size of a swallow or large 
butterfly. The creatures are said to roost in the tops of banana trunks where, Rindi claim, 
they lay eggs about the size of a age s. Apparently referring to the same small bat, 
Onvlee (s.v. pani=Kapita’s panii) lists the terms pani ru_kalu (‘banana leaf bat’) and pani 
palinju wiki (‘bat that fouls itself’). Sometimes pahomba bats enter houses. In Rindi, 
they are considered a manifestation of spirits associated with clan shrines, also called 
pahomba. Being mystically powerful, the creatures are also able to assume human form. 
panii (pani, Onvlee). Flying fox (Pteropus spp., following Dammerman). The term also 
means ‘to talk, speak’, and probably alludes to chattering noises made by large fruit- 
bats. Rindi people reported two kinds which they distinguished only as ‘large’ and 
‘small’ (panii bokulu, panii kudu). These may correspond to the two species recorded by 
Dammerman (1926b:22) as ‘Pteropus morio’ (P. alecto morio?), described as almost entirely 
black, and ‘Pteropus gilvus’ (Dobsonia peronii?), which is yellow-brown in colour (see 
Forth 1998a, regarding two kinds of Flying fox distinguished by the Nage of central 
Flores). On the other hand, the reference may be to Flying foxes and much smaller bats 
respectively, especially in view of indications that panii also serves as a general term for 
bats (see pahomba above). 

panyonga makaweda. Recorded in Rindi. A small bat. The name means ‘tricks, fools 
elderly people.’ 


KEY: 

Onvlee=Onvlee 1984, Kapita=Kapita 1982. 

BI=Bahasa Indonesia, the Malay-based national language. 
C&B=Coates and Bishop 1997. 


D=Dammerman 1926a except where otherwise indicated. 


Numerals after ‘D’ indicat identified | erman (1926a). Latin 
names given by Dammerman, many of vahich 2 are now superseded, are not italicized. Where only a 
number is given bates ‘D’, the scientific name provided by Dammerman coincides with the one 
aco at prese 


‘Kupang informant(s)’ refers to Sumbanese consulted in Kupang, the capital of Nusa Tenggara Timur 
province, in 1999. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 181 


SYMBOLIC ASSOCIATION AND METAPHORICAL PAIRING 


Especially the composition of life-form taxa (named with reference to modes 
of locomotion), and of apparent intermediate taxa, indicate that men Sumbanese 
ethnozoological classification is primarily based on 
criteria. At the same time, several categories of birds are linked in non-taxonomic 
ways that may generally be called symbolic. Several ethnoornithological catego- 
ries are paired in the parallelistic idiom of ritual language. For example, the 
conjoined phrases pirihu pauli, kaka makanguhuru, ‘assembled parrots, collected 
cockatoos,’ refers to any large group of people who unite to expedite a ritual or 
some other customary undertaking. A number of pairings are listed in Table 2. 
Together these include 13—thus nearly a quarter—of the categories appearing in 
Table 1. 

Although the list is meant to be illustrative rather than exhaustive, a glance at 
Table 2 suggests that the three names associated with intermediate taxa (ikitu, 
manginu, rawa) are particularly salient in ritual speech. It may be no coincidence, 
moreover, that the most prominent of these, rawa, a term that pairs with at least 
four others (including plant and insect categories), is the focus of one of the most 
elaborate areas of eastern S The most 
frequently named bird in ritual idioms is in fact the domestic fow] ees Manu, 
however, is mostly coupled with wei, denoting the domestic pig, and the refer- 
ence is then to the value of both as domesticates, sacrificial victims, and (with 


TABLE 2.—Bird names included in ritual speech couplets 


manu//rendi, domestic fowl/ /duck 

manu/ /wei, domestic fowl/ /(domestic) pig 
mbara//manginu, dove//munia (or ‘small seed-eating bird’)* 
nggangga/ /ikitu, crow/ /hawk (or specifically, Brahminy kite) 
nggauka/ /rawa, friarbird (=koka)//pigeon 

pirihu/ /kaka, lorikeet/ /cockatoo 

rawa//moha, pigeon//moha tree (unidentified) 

rawa/ /ngginggi, pigeon/ /spider 

rawa/ /ngguku, pigeon (Imperial pigeon) / /dove 

rawa tana/ /ngginggi rara, Emerald dove//red spider 
tariku/ /ikitu, falcon//hawk (or specifically, Brahminy kite) 


*AS a general reference to ) crop pests, these two terms are : simply oh acre In the same context, 
ea with the pal ‘small mice and ra 


ale itt 


182 FORTH Vol. 20, No. 2 


regard to their intestines and livers respectively) as auguries revealing the will of 
ancestral spirits. The pairing of rawa and nggauka—a ritual language substitute 
for koka (friarbird)—evidently reflects the association of these two birds in cre- 
ation mythology (see below), in which context the first term refers specifically to 
the Imperial pigeon (rawa kamukumu).” By contrast, in one pair of phrases link- 
ing rawa with ngginggi (spider), the former is specified as rawa tana, the name of 
the Emerald dove (Chalcophaps indica), which is then more exactly paired with 
ngginggi rara (red spider), denoting a particular non-poisonous arachnid. In yet 
another pairing ngginggi is specifically linked with rawa muru, ‘green pigeon,’ 
which, though not a standard ethnoornithological fen probably also refers to 
the Emerald dove. On the other hand, in th , pakameli 
mohangu, ‘cooing like a pigeon, trembling like leaves of the moha tree’ (a refer- 
ence to spirits of the dead, Onvlee s.v. rawa), the Columbiforme in question is 
evidently the Imperial pigeon, since it is specified as making the sound kamu 
(=kamukumu 

Where Sumbanese ritual speech conjoins Hw bird categories, the names gen- 
erally denote kinds th ork lly similar. For example, 
Rindi explain the pairing of ‘duck’ and ‘domestic fow!’ (rendi and manu) with 
reference to their characteristically large broods. In fact, the only obvious excep- 
tion is the pair rawa and koka. Expressions featuring the couplet ikitu//tariku 
associate the two Falconiformes with contrasting environments—land and sea, or 
earth and sky. Yet the metaphorical import of these expressions turns less on the 
opposing environmental associations than the identical predatory habits of the 
two raptors. Indeed, since it is tariku rather than ikitu (a term most closely linked 
with the Brahminy kite) which is linked with the sea, the environmental associa- 
tions are contrary to ornithological fact. A similar complementarity of dry land 
and water is also implicit in the ritual speech coupling of domestic fowls and ducks, 
though in this case of course the environmental contrast is valid. 

Most of the ethnoornithological terms included in Table 2 designate kinds 
which are also prominent in Sumbanese myth. Among these are the Imperial pi- 
geon (rawa, rawa kh A ) and the friarbird (koka), who dispute over the length 
of day and night and the mortality of mankind (Forth 1992). Especially important 
in creation mythology is the White-bellied sea-eagle (mbaku). In parallel form 
named as i Mbongu i Mbaku (mbongu, ‘mist, dew;’ mbaku, ‘to float, glide, hover’), 
the sea-eagle flaps his great wings causing the waters of the primeval flood to 
subside and the dry land—specifically the island of Sumba—to appear. Also men- 
tioned in myths of creation are the crow (nggangga), cockatoo (kaka), and fantail 
(in Rindi called kulu-kataitaku or manginu kulu-taitaku), as well as a spider 
(ngginggi), a non-ornithological taxon which, interestingly enough, also appears 
in Table 2. The three bird kinds figure as well in an origin myth of the Rindi clan 
Kanatangu, which further recounts how various species acquired their character- 
istic plumage. Other birds appearing in this narrative include the oriole 
(kulu-kakuta), Asian paradise-flycatcher (kulu-kanuhu), Eclectus parrot (kariku), 
and Spotted dove (mbara). Several narratives recorded by Wielenga (1909)—mostly 
fables featuring animal kinds—similarly feature three Columbiformes (mbara, 
rawa, and a pigeon identified as ‘kuru ndiha,’ cf. kulu-ndiha), three parrots (kaka, 
kariku, pirihu), the crow, the friarbird, the junglefow] (manu tata; see also Wielenga 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 183 


1913), a heron (nggokaria), and ‘small birds’ (manginu). In the mythological genre 
called analalu—or ‘orphan’ tales—a dove, specified as mbara, sometimes appears 
as a messenger who, in a song, reveals the identity and relates the tribulations of 
an orphaned hero.”4 From these several traditions, it can be seen how mythically 
significant avifauna—including a large raptor, Columbiformes, and small birds 
classified as manginu—coincide to a significant degree with kinds composing hy- 
pothetical intermediate taxa, just as do the bird categories of parallelistic ritual 
speech. Also noteworthy in this regard are the several parrots and bird kinds whose 
names include the component kulu- (although, as demonstrated, kulu- does not 
actually label a divided taxon, nor for that matter a class of any kind). 

Another symbolic value attaching to several bird kinds concerns their signifi- 
cance as omens. The augural value of the ow] called katua wei, whose cry is thought 
to reveal the presence of wild pigs (see Table 1), of course pertains to hunting. 
Vocalizations of the kingfisher (kahiku) heard near a settlement indicate to Rindi 
that a thief is about. A similar significance is attributed to the distinctive nocturnal 
cry of the nightjar (landu witu, see Table 1). The cries of two other birds are espe- 
cially ominous because Sumbanese regard them as manifestations of witches. 
Variously described as birds ‘ridden by’ witches or as physical forms taken by the 
malevolent spirit (wandi) of a witch, these are the Large-billed crow (nggangga) 
and the bird called kuu (provisionally identified as the Black-winged kite, see Table 
1; Forth 1981:113; Kruyt 1922:559). If either of these birds calls near a house where 
someone is ill, then it is a sign that the illness is caused by a witch, and that the 
person will likely die. By the same token, a large flock of crows is a more generally 
negative portent. The owl called wangi is also considered an embodiment of a 
witch’s wandi (see Table 1 regarding the resemblance between these two terms), 
an idea that possibly illuminates the common belief that if an owl alights on a 
papaya tree, the tree will die.’ Because of their association with witches, one should 
not verbally abuse or throw stones at crows, owls, or the kuu. Nevertheless, it is 
permitted to kill a kuu if it makes too much noise after dark. 

According to Kruyt (1922:558-9), the cries or behaviour of several birds were 
formerly significant in the context of warfare and headhunting. An outgoing war 
party would rejoice if they encountered crows (nggangga) cawing. However, if 
they came across crows perched silently, this was considered an ill omen, and the 
party should return home. It was similarly inauspicious if either a crow or a bird 
of prey (ikitu) flew across the path of a group of warriors, as this would portend 
casualties and defeat. On the other hand, if birds of either kind followed a war 
party, then they could be confident of success. If a rawa—which from Kruyt’s 
description appears to refer to an Imperial pigeon (rawa kamukumu)—was heard 
calling in a village at night, this indicated that an enemy was preparing to attack. 
Similarly, if a mbara (glossed by Kruyt as ‘wood pigeon’) called in the evening or 
early in the morning—something the bird does not usually do—then people should 
not to leave their homes the following day. Were they | to do so, they would suffer 
some (unspecified) loss. Kruyt adds t f the mbara might 
alternatively indicate the presence of thieves in the vicinity, as might the noctur- 
nal screech of an ikitu (diurnal raptor). In Rindi I encountered a similar belief 
concerning the Columbiforme identified as rawa kakoruku (see Table 1, nos. 43, 
33, s.v. mbara), whose nocturnal cry can presage a death. Although the interpreta- 


184 FORTH Vol. 20, No. 2 


tion cannot be fully developed here, it seems there may be a more general connec- 
tion between Col y ones designated as ngguku and nggela 
(see Table 1, s.v. mbara, ngguku)—and headhunting. Apart from the fact that they 
commonly fall victim to birds of prey, this could be motivated by their apparently 
flexible necks, evidenced by their habit of bobbing their heads up and down, and 
the relative disattachment of head and body which this might suggest.7° 

Among birds whose cries or behaviour Sumbanese consider ominous, the oc- 
currence of neither owls nor the kingfisher has any particular relevance for their 
taxonomic status: both are simply called by terms occurring at the level of folk 
genera. On the other hand, Columbiformes and diurnal raptors, thus birds associ- 
ated with named intermediate taxa, figure quite prominently in this symbolic 
domain, as they do in myth and ritual speech idioms. Evidently the most ominous 
bird of all, the Large-billed crow (nggangga), moreover, participates in a hypo- 
thetical intermediate category together with a similarly dark bird, the drongo 
(laleba nggangga), which, being specified as its ‘sister’s child,’ shares part of its 
name. 


CONCLUSION 


Despite the provisional nature of several ornithological identifications of 
Sumbanese bird taxa given in Table 1, I have argued that the information available 
here is sufficient to offer a general characterization of their folk classification. Within 
the entire domain labelled by the term makayidi-yadaku (animals), the classifica- 
tion isolates two named life-form categories— flying things’ and ‘crawling things.’ 
Members of these two categories are the most strongly contrasted in terms of 
morphology, behaviour, habitat, and symbolism. Other animals, notably mam- 
mals, then figure as a residue of this binary partition. They are, to be sure, 
makayidi-yadaku, yet they occupy no separately named or otherwise clearly dis- 
tinguished grouping within this inclusive class. Relevant here may be the 
circumstance that there are relatively few mammals, especially large mammals, 
on Sumba, while those that are present (deer, wild pigs, macaques, several ro- 
dents, the palm civet, and a wid a) are quite various. The most numerous 

species ar are classified as—or with— birds.’ 
In other folk systems, ‘fish’ sometimes appear as another named life-form taxon 
(Brown 1979). But while Sumbanese possesses a general term for ‘fish’ (iyangu), 
and while they have names for over one hundred kinds (Forth 1981:429, note 28), 
Rindi classify these and other water creatures as instances of mabei (crawling or 
creeping things). 

Intervening between the life-form taxon mal g things) and the 
numerous folk generic taxa, eastern Sumbanese bird chansiticating: reveals three or 
more identifiable “intermediate” classes. Two, which partly at least are identified 
with the names rawa and ikitu, respectively comprise Columbiformes and 
Falconiformes. A third, labelled manginu, includes a variety of small passerine 
birds that have as their focus several species of Estrildine finches. Remarkable in 
this regard i is the overall resemblance between eastern Sumbanese bird classifica- 

nand the eth of the Nage people of central Flores 
(Forth 1996). Largely from evidence provided by free recall lists, I have previously 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 185 


Pa a re eG | 


shown how N. ral intermediate taxa. Most 
prominent among these, both in terms of the number of named folk generics they 
include and the priority usually given to them in free recall, are mostly covert 
categories coinciding with the scientific groupings labelled ‘Falconiformes’ and 
‘Columbiformes.’ In addition, the Nage category ana peti closely parallels 
Sumbanese manginu, being especially associated with the genus Lonchura and re- 
lated birds of very small size but contextually including many other small kinds 
besides, even to the extent that ana peti is sometimes used as a general term for 
‘bird.’ (Nage, it should be noted, have no term exactly corresponding to Sumbanese 
mahawurungu which unequivocally includes all birds). Another similarity with 
Nage concerns the relatively low number of onomatopoeic terms in Sumbanese 
bird nomenclature, which even including unconfirmed instances amount to no 
more than 25 per cent of names. For Nage the figure is approximately 30 per cent, 
which also appears quite low in comparison with some other languages (Forth 
1996:103). 

Sumbanese treatment of Columbiformes and Falconiformes, especially, bears 
on another general issue of ethnoornithological classification. Not only are these 
two groups taxonomically salient; they are equally prominent in the symbolic 
genres of parallelistic ritual speech, myth, and bird augury. With regard to ap- 
proaches Berlin (1992:143,149) calls utilitarian or functionalist, as well as his own 
observation that intermediate taxa may sometimes be grounded in “cultural” as 
opposed to morphological or behavioural factors, one needs to consider whether 
these two facts may be related. Relations between symbolism and taxonomy can- 
not be treated conclusively here, not least of all because it has not been possible to 
review all data relevant to the Sumbanese valorization of birds. In closing, how- 
ever, I would register several points. 

First, even where named by terms further associated with hypothetical inter- 
mediate taxa (e.g., rawa, ikitu), most—perhaps all—symbolically significant birds 
are actually identifiable with folk generics (e.g., rawa tana, ikitu marakuku), nearly 
all of which appear to correspond to single scientific species. It is therefore the 
most basic categories rather than more inclusive ones that possess distinctive sym- 
bolic value; hence it cannot be claimed that this sort of value crucially informs 
intermediate or higher groupings. The use of general names in symbolic contexts 
even where more specific designations are available might be ascribed to 
performative requirements of parallelistic language and traditional narrative, both 
of which favour single lexemes. A similar consideration could apply to standard 
admonitions regarding omen birds. That is, where a particular member of a di- 
vided class has a negative association, it might be thought prudent to extend this 
to all, empirically similar, members of the same class. It is just conceivable that 
distinctions may be made within a class in order to deny an omen contextually or 
to restrict its range absolutely (cf. Bulmer 1968:637-8, regarding a similar interpre- 
tation of New Guinean transformation beliefs). This, however, is merely a 
hypothetical possibility, and there is no obvious indication that such symbolic 
motivation of class division has been operative in eastern Sumbanese. 

A second consideration is that named intermediates are not only mythically, 
metaphorically, and augurally significant; they possess more pragmatic—func- 
tional or utilitarian—kinds of value as well. This should not be surprising, as both 


. ere | 
J dit TpPiicr uly 


186 FORTH Vol. 20, No. 2 


symbolic and utilitarian values attaching to avifauna typically relate, more or less 
directly, to perceptible physical properties, including the apr 
of particular birds. With one exception, all diurnal raptors (ikitu) thus prey on 
domestic fowls. Columbiformes, both rawa and mbara, are also common victims 
of raptors, while at the same time, among wild birds, pigeons and doves are espe- 
cially valued as food, and so fall prey to human hunters as well. Mbara, or smaller 
doves, further draw practical attention as crop pests, as do many small birds clas- 
sified, at the folk generic level, as manginu (a label further applying to another 
hypothetical intermediate taxon).”” It comes as no surprise, therefore, that ikitu, 
rawa, and mbara are categories of Sumbanese bird augury, especially in the con- 
text of warfare, and thus in relation to human competition and violent aggression. 

As the foregoing should suggest, while various sorts of interest in birds may 
affect the attention given to particular kinds in folk taxonomy, distinctions mani- 
fest in Sumbanese symbolic usage, like those pertaining to utilitarian concerns, 
are consistent with observable morphological and behavioural differences exist- 
ing independently of those interests. Where natural kinds differ from or resemble 
one another in regard to symbolic value or practical utility as well as empirical 
features, therefore, one cannot readily argue that one of the three sorts of factors is 
more determinant of their linguistic and cultural recognition than the others. In- 
deed, it is probable that the three interact in complex ways. Nevertheless, in view 
of their relative ontological independence, morphological and behavioural con- 
siderations are, in the long run, likely to prove the most important. Supporting 
this in the present case is the fact that the majority of Sumbanese birds are not of 
any practical value, nor are they symbolically significant. 

My final point concerns the very terms of the contrast implicit in the issue of 
symbolism. Contrary to what is often implied in debates over the relative impor- 
tance of perceptual versus non-perceptual factors in ethnobiological classification, 
the symbolism of natural kinds is not necessarily more culturally specific or con- 
tingent than is the taxonomic recognition (or mental representation) of salient 
natural features.”® This is indicated, for example, by the fact that ‘hawks’ and ‘doves’ 
form a metaphorical contrast in English-speaking cultures as well as in eastern 
Sumba, and by the extraordinarily widespread conception of owls and crows as 
birds of ill omen. Again, this undoubtedly stems from objective physical features 
of the kinds in question. Yet the fact that their metaphorical value (if not their 
specific interpretations) is cross-cultural attests as much to universal properties of 
human cognition as it does to the universal availability of physical avifaunal fea- 
tures for symbolic deployment. These observations tend to suggest that “symbolic 
value” and “psychological salience” are not as distinct or separate as is often sup- 
posed. For this reason alone, the question of whether bird symbolism exercises a 
decisive influence on aspects of ethnotaxonomy, in eastern Sumba or in general, 
must remain moot. 


Ol DEllIdvigUl 


NOTES 


1 Hereafter designated as ‘Kupang informants,’ these included Ibu Djukatana, who is a 
daughter of Oemboe Hina Kapita; her husband, Bapak Drs. Ng. Djukatana (Oemboe Juka 
Tana); Bapak Minggus Osa and Bapak Thomas Tagudodu, both associated with Nusa 
Cendana University; Bapak Petrus Yiwa, an Instructor in the Law Faculty at Artha Wacana 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 187 


University; and several eastern Sumbanese undergraduate students of the latter univer- 
sity. am most grateful to all of the foregoing for their help, and to Dr. Tom Therik, the 
Rector of Artha Wacana, who sponsored by visit and kindly assisted me in a variety of 
ways while in Kupang. 
2Sumbanes t ibed ding to th hy used by Kapita and Onvlee. 
Single ietees ae represent sounds similar to their English denotata. The /a/ (see 
ananjaki, Table 1) variously denotes the schwa or a sound like the /u/ in ‘duck.’ The /w/ 
is otter closer to English ep v/, especialy in medial positions (see rawa). The /b/ and /d/ 
y contrasting with /mb/ (see mbaku) and /nd/ (see kulu-ndiha). 
I follow Kapita i in employing ii and uu to indicate vowel lengthening (see panii and kuu), 
whereas Onvlee places an acute accent above the vowel in question. 


3 From lists provided by Verheijen (1963), dialects of the Manggarai language of western 
Flores would each appear to possess perhaps as many as 100 names for birds, including a 
fairly large number of productive binomials. The area however is relatively rich in avi- 
fauna; Verheijen’s estimate is 180 species, which he claims probably coincide with all those 
found on Flores island (1963:678). A count of species described in Coates and Bishop (1997) 
yields a total of 232 for Flores. For the Tobelo of the large Moluccan island of Halmahera, 
P.M. Taylor (1990) similarly records 111 bird categories, which also include a number of 
productive binomials. 


4 Reporting on his 1925 visit, Dammerman (1926b:24) remarked how cockatoos were al- 
ready extinct in the vicinity of Waingapu, eastern Sumba’s main port, owing to the large 
numbers caught for export to Java. 


5In his Dutch-Kambera wordlist, Onvlee (s.v. dier) refers to bohu, a word meaning ‘thiev- 
ish, voracious,’ and more specifically to mabohu, which he translates as ‘wild animals.’ As 
I know partly from my own experience in Rindi, however, the phrase refers not to wild 
animals in general but more specifically to relatively large and dangerous animals. Ac- 
cordingly, Onvlee exemplifies his initial gloss with ‘wild pig, snake, crocodile,’ while Kapita 
translates bohu with Bahasa Indonesia buas, a word that means ‘cruel, savage,’ and ‘wild’ 

nly in this restricted sense. Analyzable as ‘what is wild (savage, cruel)’, mabohu thus 
does not of itself necessarily denote animals. For example, tau bohu denotes a (human) 
thief. 


6 According to Onvlee, yada more specifically refers to a quick movement. He further glosses 
the word as ‘to teem, swarm’ and ‘to wriggle, fidget.’ Similarly, he describes yidiku as 
denoting a movement slower than yidi. 


7 An evident borrowing from Malay, mburungu occurs in compound expressions where it 
refers specifically to bird figures found, for example, on European coins (Onvlee 1984). 


8 Worth noting here is the form wururu, which also refers to the sound of bird’s wings or 
something being thrown, but further denotes a cry uttered at the beginning, or between 
segments, of ritual song, including mortuary song (cf. Onvlee 1984; Kapita 1982). When 
performed, the element ru is repeated not just twice but numerous times, thus effecting a 
sort of whirring sound. Whether this is meant to replicate the sound of a bird in flight, or 
anything else in particular, I was unable to establish from questioning. 


188 FORTH Vol. 20, No. 2 


9 Illustrating uses of makayidi-yadaku, Onvlee (s.v. yidi) records the phrase makayjidi- 
yadaku la wai, “everything that teems in the water”. While evidently including fish, and 
thus in a sense cross-cutting mabei, the expression differs from the two life-form terms by 
its inclusion of the term for ‘animal(s).’ 


10 Fernandez (1996:146) lists the Proto-Flores term for ‘bird’ as *kolon. 


11 The use of manu, ‘domestic fowl,’ to make distinctions within named ethnobiological 
categories appears to be quite widespread in eastern Indonesian languages, and not only 
to apply to birds. For example, among the Nage of central Flores, smaller varieties of the 
Green tree viper and the Monitor lizard are respectively called hiku manu and ghoa manu 
(Forth 1995:53, 66 n.4). On Sumba and elsewhere manu further appears in the names of 
plants, but this is mostly explained by resemblance to parts of domestic fowls. For ex- 
ample, pelu manu, ‘wattle (of a fowl),’ and tara manu, ‘cockspur,’ designate respectively a 
kind of wild grape and a thorny plant. 


12Two other raptors listed in Table 1, the kola and kuu, were not mentioned in this context, 
but were not explicitly excluded either. 


13 Kupang informants described kola, which was not included in this series, as signifi- 
cantly larger than kapaha and tariku and “almost as large as mbaku.” (Although Onvlee 
and Kapita describe the kola as relatively small, their wording suggests that the compari- 
son is with the Brahminy kite or another large hawk.) Also missing from the Rindi com- 
parison is the kuu, which Kupang sources described as the smallest diurnal raptor. 


14 Coates and Bishop (1997:247) describe Haliastur indus as a scavenger, and with regard to 
diet mention only “carrion, insects, fish, etc.” MacKinnon (1991:84) says that it feeds on 
“almost any animal material, dead or alive,” and that it “catches small animals, steals larger 
prey and scavenges along waterways...delicately picking up floating debris.” Referring to 
Bali, Mason and Jarvis (1989:45) note that the bird has a “reputation as a stealer of chick- 
ens,” but otherwise characterize it as a “general scavenger.” As regards Haliaeetus leucogaster, 
the same authors describe the sea-eagle as snatching fish and sea snakes from the water, 
occasionally feeding on carrion, and sometimes hunting fruit-bats. 


15 Major settlements in eastern Sumba are mostly located in proximity to rivers, and most 
are within several kilometres of the coast. 


16 Speaking their own language, eastern Sumbanese use banjaru, ‘row, line, group,’ to ex- 
press the idea of ‘(natural) kind.’ Ngia, ‘place, position,’ subserves the same function in 
some contexts. Thus, hangia hangia (ha-, ‘one, each’) means ‘all kinds (of things)’ (see 
further Onvlee, s.v. ngia). 


7 Also worth noting is Wielenga’s (1917:33) comparative listing of mango, a cognate of 
manginu, as the term for ‘bird’ in the western Sumbanese language of Lamboya. That 
manginu might include more than passerine birds was suggested by a Kupang informant, 
a young man from Lewa, who identified kahuhu (sandpipers) as an instance of the cat- 
egory. 


18TIn the report of his expedition, Dammerman (1926b) describes a honeyeater (Myzomela 
sp., p-79), a fantail (p. 79), a whistler (p. 24), and the yellow wagtail (p. 36). Although he 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 189 


observed the honeyeater and fantail in eastern Sumba, in his shorter article (1926a) 
Dammerman does not list eastern Sumbanese names for these species, only a western 
Sumbanese name for the fantail and another for a sunbird (Cinnyris buettikoferi, apparently 
Nectarinia buettikoferi). The whistler (identified as ‘Pachycephala fulviventris’) is evidently 
Pachycephala pectoralis, the Common golden whistler, the only whistler recorded on Sumba. 
Dammerman describes the bird as very common. 


1° Nggonggali probably reflects of Proto-Austronesian *’enggang (the initial /e/ represents 
e schwa; cf. Bahasa Indonesia enggang), ‘hornbill’ (Dempwolff 1938:49; cf. Wurm and 
Wilson 1975:104). Interpretations of nggokaria (heron) were mentioned earlier. 


20 None of categories in Table 1 apply exclusively to seabirds or species found only on the 
coast. From experience in Flores, I would guess that cormorants and grebes can be classi- 
fied with ducks as rendi. The classification of birds like plovers and pratincoles (see Ap- 
pendix 1) with sandpipers (kahuhu, pipi) would also not be surprising. 


21 In 1975-76 I sometimes observed flocks of bee-eaters (Merops_spp.) when travelling be- 
tween Rindi and the port town of Waingapu, but unfortunately never in the company of 
informants. A Sumbanese man in Kupang gave kahi as a term for bee-eaters, which he 
identified from illustrations and descriptions. But this name is probably not distinct from 
kahiku, a reference to kingfishers, which eaters in appearance, diet, and nesting 
behaviour. Among the Nage of Flores, who do have a special term for bee- eaters, speci- 
mens viewed at a distance, flying high overhead, are sometimes identified with the term 
for swallows and swifts (Forth 1996:92). Bee-eaters and the dollarbird are both non-breed- 
ing migrants on Sumba. 


Li 


2 The pairing occurs in the expression ka, hibu rawa, ‘nest of the friarbird, nest 
of the pigeon,’ a euphemism for the male genitalia (Onvlee, s.v. nggauka). If the specific 
referent is the male scrotum and testicles (tilu, also meaning ‘egg’), then evidently the nest 
of any bird could serve as me — vehicle. OWNER, ane fact that these two kinds 
in particular are selected can be ascribed to t of koka and rawa, as 
the two birds that contested 6 over such matters as whether or not humans should die and 
give birth, in order to replace themselves (see Forth 1992). Their association with repro- 
ductive organs in this ritual speech context is thus intelligible with reference to their asso- 
ciation in myth. 


23 Several popular similes feature yet other birds. Onvlee records the following: paana 
kalukingu, ‘to have (raise) children like a kaluki;’ pari kalukingu, ‘as strong as a kaluki;’ 
paren ngandu yapingn, ‘to have 2 mouth as red as (the bill of) a yapi’ (said of youngsters 
‘to cluster, huddle together like quails.’ 
The first expression alludes to the fact that Megapodes incubate their eggs under a large 
pile of debris, and therefore appear not to look after their offspring to the same extent as 
other birds. 


24 More often, songs of this sort are performed b haracters themselves. In one 
case (C. Forth 1982: 93-92), the dove cara takes the place of the hero, assuming his 
identity in the lyric. In another myth, the human hero is born in the form of a dove (mbara; 
Wielenga 1909). 


190 FORTH Vol. 20, No. 2 


25 This idea, recorded in Rindi, is also mentioned by Kruyt (1922:559-60). Kruyt describes 
the ow] as the “personification of the witch” and as the Sumbanese “bird of sickness an 
death.” An owl alighting on the roof of a house sreuegenate corte death for the —— = 
the Kambera region, when its nocturnal cry is heard, 

be placed on their side. One should also not comment on or respond to the sound, for this 
could result in death, construed as an indication that the person had “answered the call.” 


26 Kruyt (1922:559) says that owls were not —— Significant in times of war. How- 
ever, he also notes that if warriors he hing they should go under a tree and 
make an offering of betel and areca to sti le “the evil associated with this bird” from 
following them. 


27 The lumping of numerous small birds in the taxon labelled manginu might at first ap- 
pear to be an instance where utilitarian concerns have a preponderant influence on the 
emergence of an intermediate taxon. This is contradicted, however, by the inclusion in 
manginu of ornithological kinds that are known not to infest crops, but which especially in 
regard to size and form d ble the crop pests. Also, of course, by no means all avifau- 
nal destroyers of crops are classified as manginu. 


28 A similar argument could be made in regard to the opposition of empirical (or intellectu- 
alist) and utilitarian values. A more comprehensive, cognate question is whether symbol- 
ism is to be understood as an intellectual activity or product or, as Malinowski argued, a 
kind of utilitarianism. 


ACKNOWLEDGEMENTS 


The author’s research in Sumba was conducted for two years in 1975-76 and was 
sponsored by the Indonesian Institute of Sciences (LIPI) and Nusa Cendana University in 
upang. The research was funded from a grant awarded by the former Social Science 
Research Council of the United Kingdom to Professor Rodney Needham. My visit to Kupang 
in 1999 was funded from a grant awarded by the Social Sciences and Humanities Research 
bo of Canada. I am grateful to all these bodies for their support, as I am to Professor 
ham. 


LITERATURE CITED 

BERLIN, BRENT. 1992. Ethnobiological | COATES, BRIANJ.and K. DAVID BISHOP. 
Classification Prin of 1997. A Guide to the Birds of Wallacea: 
Categorization of Plants and Animals in Sulawesi, the Moluccas and Lesser 
Tradi al ieties. Princeton Sunda Islands, Indonesia. Do 
University Press, Princeton. Publications, Alderley, Australia. 

BLUST, ROBERT. 1979. Proto-Western DAMMERMAN, K.W. 1926a. 
Malayo-Polynesian Masini Bijdragen Soembaneesche dieren- en 
tot de Taal-, Land- en Volkenkunde 


plantennammen. Tijdschrift voor 
135(2-3):205-51. 


BROWN, C.H. 1979. Folk zoological life- 
forms: Their universality and growth. 
American Anthropologist 81:791-817. 

BULMER, R.N.H. 1968. Worms that croak 
and other mysteries of Kalam natural 
history. Mankind 6(12):621-39. 


Indische Taal-, Land- en Volkenkunde. 

66:205-239. 

. 1926b. Een cre naar Soemba. 
uygrok & Co., Bat. 

DEMPWOLFF, OTTO. 1938. Vergleichende 
Lautlehre des Austronesischen 
Wortschatzes. Dritt Band: 
Austronesisches Worterverzeichnis. 
Dietrich Reimer, Berlin 


Winter 2000 


ELLEN, ROY. 1993a. The Cultural Relations 
of Classification: An Analysis of Nuaulu 
Animal Categories from Central Seram. 
Cambridge University Press, 
Cambridge 

.1993b. Nuaulu Eoorodiogy, A 
Systematic Inventory. CSAC 
Monographs 6. Cae for Social 
Anthropology and Computing, 
University of Kent, Canterbury. 

FERNANDEZ, INYO YOS. 1996. Relasi 
Historis Kekerabatan Bahasa Flores: 
Kajian Linguistik Historis Komparatif 
Terhadap Sembilan Bahasa di Flores. 
Penerbit Nusa Indah, Ende, Indonesia. 

FORTH, CHRISTINE. E. sin An analysis 
of traditional narrative in eastern 
Sumba. Ph.D. dissertation, Uninenity of 


ford. 
FORTH, GREGORY. 1981. Rindi: An 
Ethnographic Study of a Traditional 
main in Eastern Sumba. 
ie acorenpea te van het Koninklijk 
Instituut vo Taal-, Land- en 
Volkenkunde No. 93. Martinus Nijhoff, 
e ree 
1992. The pigeon and the 
friarbird: The mythical origin of death 
and daylight in eastern Indonesia. 
Anthropos 87:423-41. 
ae Ethnozoological 
classification and _ classificatory 
anguage among the Nage of eastern 
Indonesia. Journal of Ethnobiology 
15(1):45-69. 

. 1996. Nage birds: Issues in the 
analysis of ethnoornithological 
classification. Anthropos 91:89-109 

98a. On deer and dolphins: 
Nage ideas regarding animal 
transformation. Oceania 68(4):271-293. 
—_______. 1998b. Things that go ‘po’ in the 
night: The classification of birds, sounds 
and spirits among the Nage of eastern 
Indonesia. Journal of Ethnobiology 
18(2):189-209. 
1999. sae Saison oie on 
Nage bird classificatio and 
ethnoornithology. pe easy 94:568- 


FREEMAN, J. D. 1960. Iban augury. Pp. 73- 
98 in The birds of Borneo, B. Smythies 
— ep and the Edinburgh. 

KAPITA, . 1982. Kamus Sumba/ 
idea . Percetakan 
Arnoldus, Ende, papecenny 


JOURNAL OF ETHNOBIOLOGY 191 


KRUYT, A.C. 1922. De Soembaneezen. 
Bijdragen tot de Taal-, Land- en 
Volkenkunde 78:466-608. 

LAUBSCHER, MATTHIAS SAMUEL. 1975. 


Gottesnamen in_ indonesischen, 
vorzugwei ostindonesischen 
popegr acreage pe 209-29 in Der 

n Stietencron 


(editor). Me ia ok Patinos Verap. 
LOPEZ, Studies on 
Dempwolff’s Vergleichende Lautlehre 
des Austronesischen Wortschatzes. 
Summer Institute of Sanne 
Philippines. Mimeographed (cited in 


Ae bie) 8 
, VICTOR and FRANK JARVIS. 
1989. Birds of Bali. Periplus hie 
Berkeley, California and Singa 
MACKINNON, JOHN. 1991. Field Guide 
to the Birds of Java and Bali. Gadjah 
Mada University Press, Yogyakarta. 
METCALF, PETER. 1976. Birds and deities 
in Borneo. Bijdragen tot de Taal-, Land- 
en Volkenkunde 132:96-123. 
MONK, KATHRYN, YANCE DE FRETES, 
and GAYATRI REKSODIHARJO- 
LILLEY. 1997. The Ecology of Nusa 
Tenggara and Maluku. The Ecology of 
Indonesia Series Volume V. Periplus 


Soembaas)- -Nederlands Woordenboek. 
Foris Publications Holland, Dordrecht. 
TAYLOR, PAUL MICHAEL. 1990. The folk 
biology of the Tobelo people. 
Smithsonian Contributions to 
Anthropology Number 34. Smithsonian 

Institution Press, Washington, D.C. 
VERHEIJJEN, J.A.J. 1963. Bird Names in 
rai, Flores, Indonesia. 

-718. 


WIELENGA, D.K. 1909. Schets van een 
Soembaneesce spraakkunst (naar ‘t 
dialect van Kambera). rina hiaagial 
Genootschap' van tisk 
ree Bata 

CIA 3. Soem’ caneeselie verhalen in 
' sets van Kambera, met vertalingen 


- 1917. _ Vergelijkende woordenlijst 


d 

Saeubs en eenige Soembaneesche 
spreekwijzen. Verhandelingen van het 
Bataviaasch Genootschap van Kunsten 
en Wetenschappen 61(5):1-96. 


192 FORTH 


pleonps es Pacific Linguistics Series 

Department of Linguistics, 
sat pier of Pacific Studies, The 
Australian National University, 
Canberra. 


Vol. 20, No. 2 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 193 


The Cultural Relations of Classification, an Analysis of Nualu Animal Catego- 
ries from Central Seram. Roy Ellen. Cambridge University Press, Cambridge. 
1993. Pp. 315. $80.00 (cloth). ISBN 0-521-4311-4. 


In The Cultural Relations of Classification, Roy Ellen has compiled an impressive 
collection of ethnozoological data complete with taxonomic charts, reviews of past 
theoretical approaches, appendices with local glosses and ecological zones, and 
his own definition of cognition as it relates to culture and classification. Although 
written in 1993, the book is still a relevant and important resource today with a 
resurgence of interest in the fields of ethnobiology and ethnoecology. The data for 
the book are drawn from a series of field visits to the Nualu of south central Seram, 
an island in eastern Indonesia. It is mteresting to note that although classic 
ethnobiology has been generally perceived as “scientific,” Bien describes his i im- 
pression of ethnobiology in the late 1970s dal, linking 
with cognitive processes. He states these processes are ‘intriguing to him because 
they link “socio-linguistic positivism with interpretive post-modernism” (1993:2). 
Given this description it is easily ani sotOod how Ellen aivespes from classic 
ethnobiological approaches. He focuses on t 
with fluid boundaries, overlapping classes and fuzziness, while many 
ethnobiologists would most likely be appalled at any discussion of the post-mod- 
ern in relation to ethnobiology. 

Throughout this work, Ellen both heeds the accomplishments of his predeces- 
sors and contemporaries in ethnobiology while he simultaneously criticizes the 
methodological approaches and analysis of some of those same colleagues, par- 
ticularly Berlin, Raven, and Bisediove (Ellen 1993, see also Berlin 1992). 

Ellen’s primary tl tical concern has been with classification as “situationally 
adapted and dynamic devices of practical importance to their users, reflecting an 
interaction...between culture, psychology and discontinuities in the concrete world; 
a lexical and semantic field firmly embedded in a wider context of beliefs and 
social practices” (1993:3). 

Two areas where Ellen diverges from traditional ethnobiological approaches 
are: 1) methods of data elicitation and 2) the interpretation of the language of clas- 
sification. The etic versus the emic view has been the subject of much debate in 
anthropology. Many believe that researchers tend to view cultures from an etic 
perspective even if they are skilled ethnographers. Ellen contends that the use of 
classic ethnobiological systematic methods, without unstructured ethnographic 
interviewing and observation may lead to faulty conclusions regarding classifica- 
tion and taxonomies. Furthermore, he believes that a predisposed belief in 
hierarchical structures such as the Linnaean system biases some ethnobiologists 
to assume that the societies they study do indeed possess a hierarchical system of 
classification. Ellen’s discussion of the language of classification attempts to pro- 
vide the reader with background on etl hes of the past and at 
the same time critiques these approaches in comparison with his own. One prob- 
lem with this critique is that his use of terms is often an inaccurate representation 
of the works he cites. Ellen’s main point in offering this background for the reader 
is both to acknowledge the vast body of ethnobiological research that has pre- 


194 BOOK REVIEWS Vol. 20, No. 2 


ceded The Cultural Relations of Classification, and at the same time provide the 
groundwork for his approach to ethnozoology and classification of the natural 
world. 

Ellen provides several specific cases that are intended to illustrate the biased 
methods he finds problematic. Here, I provide a brief description and counter- 
explanation of a few cases. Ellen gives an example (assuming he is replicating a 
biased classic ethnobiological approach) of the way in which the question “what 
is nakatua wekae (red-sided eclectus parrot) a kind of?” encodes an answer because 
the answer is nakatua. (1993:25). What Ellen fails to acknowledge is that in a sys- 
tematic ethnobiological study, the question may not be asked in that way, because 
a specimen could be pointed to without using the name nakatua at all (Brent Ber- 
lin, personal communication 1995, Berlin 1992). Another way of asking the question 
would be, “Does nakatua have any relatives?” Moreover, Ellen provides another 
example of what he considers a culturally inappropriate elicitation method with 
the question (again, assuming a hierarchically biased classic ethnobiological ap- 
proach), “’What is asu (dog, Canis familiaris) a kind of?’” (Ellen 1993:25). He points 
out that this is culturally inappropriate because a dog is not a kind of anything, 
except maybe an animal. At this point the reader is lacking information about 
whether or not there is more than one type of dog on the island of Seram. Later 
Ellen describes dog, asu, as one of Berlin’s unaffiliated generics, whereas in Berlin’s 
more recent approach, if there is only one type of dog, then the dog may be con- 
sidered by ethnobiologists to be a monotypic genera, that is a generic class with 
only one member (Berlin 1992:33). 

Other terms that are confused with current uses in ethnobiology are produc- 
tive, optional uninomial and binomial. It is entirely possible that Ellen was unaware 
of, or lacked access to, other ethnobiological research that occurred simultaneous 
to the time of his writing. Regardless of the reason for this divergence of terminol- 
ogy, it is important that the reader is aware that Ellen often provides misleading 
secondary explanations of other ethnobiological researchers’ usages of classifica- 
tion language. Another possible reason for differences in perspectives and 
approaches is that Ellen’s work is ethnozoological, whereas much of the work of 
ethnobiology has been concerned with ethnobotany. 

Ellen’s attempt to link the ideational and operative is indeed different from 
the ethnobiological studies with which he compares his work. Ellen (1993), Hunn 
(1985), Rappaport (1979), Nazarea-Sandoval (1995), and Bellon (1995) all attempt 
to link the cognitive processes with behavior and decision-making. Different ob- 
jectives seem to have motivated the various research approaches to which Ellen 
refers. 

Early pioneers in the fields of ethnoecology, Frake (1962) and Conklin (1969), 
were interested in both classification and behavior through a cultural relativist 
approach. Some later ethnobiologists were inspired by their work, but pursued 
another direction, in search of universal compartments in the human mind. With 
the search for a universal understanding of how humans order their natural world, 
the debate between utilitarian and intellectual basis for classification of plants and 
animals was spurred in the late 1960s and early 1970s. Ellen’s perspective clearly 
leans toward a utilitarian approach (Hunn 1985), but rather than rely solely on 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 195 


usefulness, and/or cultural salience in considering the utilitarian categories, Ellen 
adds the dimensions of habitat, behavior, sound, smell, religion, and cultural con- 
text to a traditional cognitive categorization primarily based on perception of 
morphological qualities (and occasionally sound, as in the case of birds (Berlin 
1995)). This tendency toward a more holistic ethnoecology is a valuable advance 
in the field. I find Ellen’s attempt to include habitat and biotopes in his analysis 
especially useful when considering the field of ethnoecology in relation to deci- 
sion-making regarding natural resource use. 

Ellen seems to follow Rappaport’s (1979) earlier attempts to include an analy- 
sis of ideational and operational basis for classification, a multilevel decision 
making process. In doing so he develops the theory of “prehension” which stresses 
the situational bias of classification. He believes that the kinds of cognitive pro- 
cesses that he has proposed are apparent in the “social construction of categories.” 
It is this combination of approaches in which I find both the strength and weak- 
ness of Ellen’s viewpoint. While the inclusion of cultural basis and a broader range 
of contributing factors in classification scene: of Asha lence bomction liberates " 
from a rigid ethnobiological approach, it also d | 
that examines the way the human brain fund: It is clear that Ellen believes in 
a heavy influence of the sociocultural construction of cognitive processes. Ellen 
acknowledges some type of hierarchical ordering is necessary in the human stor- 
age of knowledge, but he proposes a system of overlapping levels of hierarchy, 
and clearly states that some forms of classification among the Nualu are varied, 
therefore they fit more than one level at a time. 

I find the book to be a useful resource for ethnoecology, especially because 
Ellen has explored territories with limited previous research, but I propose cau- 
tion regarding comparisons of his work with other ethnobiological works because 
of the differences in terminology and Ellen’s sometimes misrepresented re-expla- 
nation of certain terminology and concepts. I also noted that Ellen’s references 
include few sources of publications from the 10 to 15 years prior to publication of 
the book; he seems to be responding to and drawing mostly from works of the 
1970s and early 1980s. 

One should consider the purpose of Ellen’s work along with Bellon (1995), 
Dove (1993), Frechi et. al (1989), Gragson and Blount (1999), Posey et al. (1984), 
Nazarea-Sandoval (1995), Nazarea (1999) and, Warren, et. al (1995), to name only 
a few, as examples of an integrative approach to understanding the cultural basis 
for classification and its implications for resource use. In these contexts, The Cul- 
tural Relations of Classification provides a functional reference for those interested 
in ethnoecology and ethnobiology, but readers should refer to other current re- 
search in cognition and ethnobiology (see Atran 1999) if they are more concerned 
with cognitive taxonomic classification. 


196 BOOK REVIEWS 


Vol. 20, No. 2 


LITERATURE CITED 


, SCOTT and DOUGLAS L. MEDIN 
(editors). 1999. Folkbiology. MIT Press, 
Cambridge. 

BELLON, MAURICIO. pies Farmers’ 
knowledge and ustainable 

agroecosystem ee ment: an 
operational definition and an example 
from Chiapas, ie Human 
Organization 54(3): 264- 

BERLIN, BRENT. 1995. Ethnobiological 
classification, principles of 
categorization of plants and animals in 
traditional societies. Princeton 


1969. An 
pera see ntie geal to shifting 
agriculture ent an 
Cultural iain AP. Ve (editor). 
The Natural History Press, Garden Ci 


relations in Pakistan. Population and 
Environment: ournal 
ee Studies, 15 (2). 
ELLEN, ROY. 1993. The cultural relations 
of wrpemmann an analysis of Nualu 


animal categories from central Seram. 
Cambri egy University Press, 
Cambridge. 

FRECHIONE, J.D. et al. 1989. The 


Amazon, an ethnoecology of Lake 
Coari. Advances in Economic Botan 

FRAKE, CHARLES O. 1962. Cultural 
Ecology and Ethnography. American 
Anthropologist 64 (1). 


GRAGSON, TED L. AND BEN G. BLOUNT 


ns, Ga. 
HUNN, EUGENE. 1985. The utilitarian 
factor in folk biological classification in 
Directions in Cognitive Anthropology. 
J. Dougherty (editor), The Cie. of 
Illinois Press, Urbana and Chica 
NAZAREA, VIRGINA D. (editor). “1999, 
Ethnoecology, situated knowledge / 
located lives. University of Arizona 
Press, Tucson. 
NAZAREA-SANDOVAL, VIRGINIA. 1995. 
Cognized models: ethnoagronomy and 
ethnogastronomy. Pp. 102-141 in Local 
Knowledge and Agricultural Decision 
Making in the Philippines: Gender, 
Class, and Resistance. Cornell 
University Press, Ithaca and London. 
POSEY, DARREL A. et al. 1984. 
Ethnoecology as applied anthropology, 
Amazonian developm n 
eels 43 (2):95-107. 
RAPPAPOR . 1979. On Cognized 
eas in Ecology, Meaning, and 
Religion. North Atlantic Books, 
Richmond. 
WARREN, D. MICHAEL et al. (editors). 


systems. Intermediate Technology 
Publications, London. 


Rebecca L. Austin 
Ph.D. candidate 
University of Georgia 
Research Associate 
Fort Lewis College 


Journal of Ethnobiology 20(2): 197-216 Winter 2000 


KNOWING, GATHERING AND EATING: KNOWLEDGE AND 
ATTITUDES ABOUT WILD FOOD IN AN ISAN VILLAGE IN 
NORTHEASTERN THAILAND 


PRAPIMPORN SOMNASANG 
Department of Community Medicine 
on Kaen University 
Khon Kaen 40002, Thailand 


GERALDINE MORENO-BLACK 
Department of Anthropology 
University of Oregon 
Eugene, Oregon 74403 


ABSTRACT. — In societies undergoing economic and social transformation, the 
level of knowledge about local resources, aie attitudes toward them, can be 
affected by a variet lidentity, i with local 
pean ne cultural transformations, economic s status, education level, age and 
gender. To address the topic of what factors affect traditional wild plant use and 
knowledge in Northeastern Thailand we interviewed and tested male and female 
villagers in different age categories. Each interviewee was asked to identify and 
provide. information about photographs of 40 wild food items. Additional 


information g grap hin the village. The results 
indicate that th gender diff in th and procurement of wild food 
items. However, most vill , despite their economic level, still prefer wild food 


over cultivated food. Using a knowledge and attitude test, it was also found that 
women are better able to identify items correctly, but that there are no gender 
differences in knowledge of other factors pertaining to the wild food items. 
Additionally, adults carmen oned ee | than children. Consequently age, 
and thus indirectly, exposure to t practices, also i is —— to 
knowledge about wild faodis resources. Our It t wild 
food is being lost within the community despite retention of the taste for these 
items and desire to retain them in the diet. 


Key words: Thailand, wild food, food preference, a age. 


RESUMEN.—En sociedades sometidas a t f y sociales, 
el nivel de conocimiento sobre recursos locales y actitudes sobre ella pail ser 
afectadas por una variedad de factores, entre ellas la identidad cultural, 
identificacién con tradiciones locales, transformaciones culturales, el estado 


econémico, nivel de educacion, edad sexo. Ent y varios 
1-¢ 1 1 £ 
4 > hd 1 ] > L. 4 1 ‘ e 1 . me ] 
afectan el uso tra y p j a region —— 
de Tailandia. Se el pidié a cada aldeano identifi tents foloe des 


de comida salvaje. Obtuvimos informacién adicional através de investigaciones 
etnograficas hechas en el mismo pueblo. Los resultados indicaron que existen 
diferencias en el uso y obtencidn de articulos de comida salvaje. Sin embargo, la 


198 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


mayoria de los aldeanos, a pesar de su nivel econdémico, prefieren comida salvaje 
a comida cultivada. La nica diferencia que se revel6 usando pruebas de 
conocimiento y aptitud fue que las mujeres ec Bees — resultados 
identificando los articulos de comida salvaje 

adultos dieron resultados mas altos que a nifios. La edad, e indirectamente la 
exposicién a practicas tradicionales de subsistencia, también estan relacionadas 
al conocimiento de comida salvaje se pierde ante la comunidad, a pesar de la 
retencién del saber de éstos articulos y el deseo de mantenerlos en la dieta. 


RESUME.—Dars les sociétés qui entreprennet des transformations, le niveau de 
connaissance sur les ressources locales et les attitudes envers ces ressources, sont 
affectés par une variété d’agents inculant l’identité culturelle, l’identification avec 
des traditions locales, des transformations culturelles, le statut économique, le 
niveau d’éducation, l’age et le sexe. Pour aborder le sujet des agents qui affectent 
l’usage ee des plantes sauvages at os: capaci re planites ong nord- 
est de la Thailande, 
des villages d’ges “dispetente On a demandé a aie ‘oe d’identifier et de 
donner des renseignements de quarante aliments sauvages qui o ont été 
photographié. Les informations supplémentaires ont été obtenu a travers la 
recherche ethnographique dans le village. Les resultants montrent qu’il y a des 
differénces entre les sexes dans l’acquisition et l’usage des aliments sauvages. 
Cependant, la plupart des habitants du village, malgré leur statut économique, 
préfeérent les aliments sauvages aux aliments cultivés. Employant un examen de 
connaissance et d’attitude, on a également noté que les femmes sont meilleures a 
identification précise des articles mais il n’existe pas une differénce de 
connaissance entre les seces concernant = ‘atte forteury a propos des articles 
sauvages. De plus, les marques des adulte hautes que 
celles des enfants. Par consequent, l’age, parent ainsi que exposition aux 
practiques traditionelles de subsistance, fait également partie de la connaissance 
sur les ressources de la nourriture sauvage. Les resultants suggérent que la 
connaissance des aliments sauvages est en train d’étre perdue en dedans de la 
communauté en dépit du fait qu’ils retiennent le godt pour ces articles et leur 
désir de les retenir dans leur régime. 


INTRODUCTION 


Human-plant interactions are one aspect of a society’s construction of nature 
and the landscape. Recently, researchers have begun to explore the factors that 
influence the knowledge people have about their environment. In particular, re- 
searchers have begun to ask questions that highlight why people know about some 
plants and not others (Nolan 1998) and what determines these perceptions. Cul- 
tural factors often take precedence over other considerations such as species 
availability or abundance. The process of choosing and obtaining specific plants 
or animals speaks to how s aepe Seals view themselves, each other and the environ- 
ment. Thus, social rel about the environment are enacted 
in the procurement of wild food resources. 

In this paper we explore the relationships among people, the natural environ- 
ment and the ways individuals preserve and transform their culture and 
environment. We specifically focus on knowledge of wild or semi-domesticated 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 199 


plants and animals and practices concerning the use of these resources because 
they create an intensive interaction with the physical and social environment. 

Since consumption usually occurs in the home it has often been assumed that 
women control the production of consumption as well as the food habits of the 
family (McIntosh and Zey 1989; Levin 1943). However, non-domesticated /gath- 
ered and semi-domesticated food enters the household through a variety of 
channels. Traditional foods, which still form an important part of the diet, may be 
procured by the female head of household, husband, male and female relatives, 
friends, neighbors and children. Within a community, knowledge, patterns of re- 
source use, and the landscape, are affected by gender, class, economic level and 
personal life experiences. Consequently, theories about the patterns of decisions 
and actions that occur must take these differences into account. Complex local 
histories of resource use will do much to increase our understanding of the ways 
that local systems of resource management transform themselves in response to 
global processes; in particular they can help us evaluate the ways in which the 
sustainability of rural production practices are ensured or undermined (Collins 
1991). One of the goals of this paper is to describe the variation in knowledge and 
resource use within a community. We specifically focus on gender; however, since 
knowledge of the environment is embedded in culture, social and economic fac- 
tors also are addressed. 


DESCRIPTION OF THE STUDY SITE 


Physical landscape. —Northeastern Thailand, also called Isan, provides an excel- 
lent setting to observe variation in knowledge of the environment and resource 
use in the context of gender roles and social relationships. Geographically, Isan is 
set off from other regions by mountains and is characterized by erratic rainfall and 
poor soils. This gently sloping plateau of undulating hills, terraces and flood plains 
also includes a zone of hills and upland areas in the west and the south (Hafner 
1990) that extract moisture from the southwest monsoon airstreams. Thus, while 
contributing to the biodiversity of the region, these hills also make the area more 
Sate: to alvesaec gle ee ey of erratic rainfall, nutrient poor soils 
withp moistur water combine to make 
the ee difficult for wet-rice panels [ia some of the earliest archaeo- 
logical sites in Asia with evidence of agriculture, pottery and bronze work are 
located in the Northeast (Higham 1982; Solheim 1968). The semi-arid environ- 
ment greatly influenced the traditional subsistence system and other adaptations 
to the habitat. 


Cultural landscape. —Nature’s impact on culture and personal identity has been 
great in Isan. Regional identity, which involves a sense of belonging and pride, as 
well as in-group and out-group categorization, is strong and tied to the landscape 
and wild resources, especially those that are involved in the cuisine of the region. 
Traditionally, the people in the Northeast adjusted to variability in these habitat 
factors through the development of a combined subsistence system, in which they 
complemented their reliance on the staple glutinous rice and other subsistence 


200 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


FIGURE 1.-The landscape surrounding the village. Paddy fields (background) and 
sugar cane cultivation area (foreground). 


crops with large inputs from wild food (Moreno-Black 1994; Phongphit and 
Hewison 1990; P et al. 1986; Somnasang et al. 1988; Tontisirin et al. 1986). 
Isan people have a great deal of traditional knowledge concerning the environ- 
ment, wild plant and animal resources. They are also knowledgeable about 
predicting climatic npg cropping practices, green manuring, and energy ex- 
traction (Rambo 1991). 

The rich flora and fauna in the Northeast provide a vast array of edible and 
useful plants and animals that are gathered for a wide variety of purposes, includ- 
ing food, building material, crafts, medicinal use, and religious purposes. These 
indigenous practices, and the knowledge that they represent, have been acquired 
over many generations and are deeply ingrained in regional Thai culture 
(Phithakpol 1990). The diet, characterized by a staple core of glutinous rice, fish, 
and fish products, is supplemented by a wide variety of local wild and semi-do- 
mesticated plants and animals (Moreno-Black et al. 1996; Moreno-Black 1994; 
Ngamsomsuke et al. 1987; Ngarmsak 1987; Pradipasen et al. 1986; Somnasang 1996; 
Somnasang et al.1998, 1988). These important items —collected from forests, up- 
land fields, rice paddies, gardens, house areas, canals, ponds, swamps, rivers, and 
dam areas —contribute valuable nutrients. Coupled with a variety of cooking 
methods, they add diversity to a potentially monotonous diet. Northeastern food 
has been one regional specialty that has begun to gain popular interest and de- 
mand in Bangkok (Van Esterik 1992). In fact, Isan food was characterized and 
romanticized in popular folk media and has acquired both national and interna- 
tional recognition with the initial publication, gain in popularity, and wide 
distribution of the novel Child of the Northeast (Boonthawee 1976). 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 201 


: aa eee 


; Ai fae ES : SO Be 
FIGURE 2.—-A scene from the village showing houses and dirt road. 


Life-ways are changing rapidly in Isan and villagers are being affected in terms 
of economics, social relationships and culture. At the local level, a growing influ- 
ence of the nationalized central Thai image, an increase in development projects, 
and a rising monetization of the economy are beginning to influence the regional 
lifestyle in a variety of ways. Local resources, which used to dominate home use, 


7 Ceo ; os 
~~. ied % 


at 


FIGURE 3.—A gathering party. 


202 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


FIGURE 4.—A village woman on her way to gather red ants. 


are being used as cash generators. At the same time the abundance of these re- 
sources is declining due to national economic and forestry programs that do not 
emphasize the local species. The local economy has expanded to emphasize cash 
cropping, wage earning and both temporary and permanent out-migration of 
adults. 


RESEARCH METHOD AND DESIGN 


Selection of research village. — The research village was selected from twelve poten- 
tial villages in the province of Khon Kaen. All of the potential sample villages 
were chosen using secondary data obtained from the Khon Kaen Policy and Plan- 
ning Division, The Khon Kaen Governor’s office and district-level extension offices. 
Additional information about the villages was obtained through interviews with 
government officials at provincial, district, and sub-district government. 

Rapid rural appraisals (RRA) (Chambers 1980; Lovelace, Sukesine and Sugin 
1988) were conducted in the twelve villages in the province of Khon Kaen. The 
headman in each village was interviewed in order to obtain information concern- 
ing the general profile of the village, the local environment, occupations of the 
residents, problems of concern within each village and the use of local wild food 
resources. Additionally, two or three households in each village were selected on 
the basis of economic level (poor, middle, rich). Semi-structured interviews 
(Grandstaff and Grandstaff 1987) were conducted with the individuals from each 
of these households to acquire information about wild food utilization. 

Analysis of the headman interview and villager interview data enabled us to 
select one village site for an in-depth study. The chosen village was selected be- 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 203 


cause it represented an average sized village, was characterized by high wild food 
use, and villagers obtained wild food from three main sources (forest, local water 
resources and paddy fields). Additionally, the villagers were not heavily involved 
in selling wild food at the market in the Khon Kaen. Finally, the village was mod- 
erately accessible all year round, but was not located on a paved highway. 


In-depth village study. — This part of the research involved intensive participant 
observation and in-depth interviewing in the study village (Figure 1). Our map- 
ping of the village showed that 105 of the 112 houses that were present were 
occupied. Census information was obtained from all of the 105 households. The 
census interview included demographic information as well as questions concern- 
ing household economics, agricultural practices, wild food use and transplanting 
activities. The environment surrounding the village was also surveyed in order to 
record the sites of forest, cropland, and water resources. The study sample house- 
holds were selected by stratified random sampling based on economic stratification 
developed in conjunction with the headman. The 64 households in the sample (3 
high income, 38 middle income and 23 low income) represent 60% of the total 


FIGURE 5.—Separating red ant 
eggs from red ants. 


204 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


households in the village. Individuals from these households were interviewed 
about wild food gathering practices, the types of wild food that are gathered, and 
how the food items are used. Participant observation, focusing on food procure- 
ment, processing and preparation activities, was used to amplify the interview 
data. The interviews were used to obtain information about gathering practices; 
knowledge of wild food habitats; the ways wild foods are used; and specific wild 
food management practices such as transplanting and propagation techniques. 
A “Knowledge” test and an “Attitude” test were administered to adults from 
the study sample and children who attended the one school in a nearby village 
village. Sixty-four adults (32 women and 32 men) and forty-one children (21 girls 
and 20 boys) were interviewed using a set of laminated photographs of 40 wild 
food items selected from information obtained during interviews and participant 
observation (Table 1, Appendix A). The forty food items were divided into four 
categories: plant (32 items), fish (5 items), insect (2 items) and snail (1 item). 


TABLE 1.—Age and gender distribution of “Knowledge and Attitude Test” 
participants. 


Age Female Male 
10-11 Zt 20 
15-25 8 8 
26-35 8 8 
36-45 8 8 
46-55+ 8 8 

otal 53 oz 
Mean age of school children = 11 years 

jean ag! f wy © years 


Each adult was asked to identify the item (identification test). These data were 

used in the odds ratio analysis and the scoring system described below was then 
utilized to compute the I score component of the knowledge test. The knowledge 
test was composed of several parts and individuals were scored on: ability to iden- 
tify an item (I score); culinary information, such as how to eat, prepare, and cook 
the food as well as its taste (C score); non-culinary uses (O score); horticultural 
practices, such as transplanting, maintaining or propagating the item (TP score); 
and knowledge of procurement practices (P score). Each person could score up to 
ten points per item (Table 2) and a total of 400 points for the complete test of 40 
items. 
For the attitude test individuals were also asked about their attitude toward 
each item especially in terms of taste qualities and consumption preferences. The 
children were given the same set of laminated pictures of the wild foods; however, 
the questions were simpler and shorter since they were only asked to identify 
each item and express their knowledge of and attitude toward the item. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 205 


TABLE 2.—Criteria and scoring system for the Wild Food Knowledge Test.” 


CRITERIA NUMBER OF POINTS 
No Knowledge Incomplete Knowledge Knowledge 

Item Identification (I score) 0 1 2 
Culinary Knowledge (C score) 1 2 
Procurement Knowledge (P Score) 0 1 2 
Other Use Knowledge (O score) 0 1 2 
Horticultural oe ee Score) 0 1 2 

Incomplete knowledge = = Intervi ither has i plete knowledge of the it 

Knowledge = Int qd trat full k led in t f all criteria 

dge 
RESULTS AND DISCUSSION 


In the Northeast, resources are recognized and perceived as useful within the 
context of the environmental and social reality of the icapie Rnowledge of local 
plants and animals, especiall y tl that consumed as food, 
accumulates over generations and reflects the way people learn from and about 
their environment. The villagers relied heavily on a variety of non-domesticated 
plants and animals. A diversity of habitats was utilized, including paddy fields, 
upland areas, forests, ponds, streams, swamps, rivers, and other water reservoirs. 
Commonly utilized items include leafy algae, green plants, fruits, mushrooms, 
amphibians, crustaceans, fish, birds, reptiles, insects and mammals. Wild foods 
were also used as condiments and often contribute to the distinctive flavor of Isan 
food. Wild food entered the household in a variety of ways: 1) production through 
family agricultural activities; 2) procurement through gathering, fishing and hunt- 
ing by household members; 2) gifts from relatives and neighbors, 3) exchange with 
other individuals in the village or nearby villages; and 4) purchase. Consequently 
many individuals can contribute to a household’s food consumption and men, 
women and children all have some involvement with wild food beyond consum- 
ing it. 


Shared traditions, beliefs and attitudes ing wild food use. —The majority of people 
in the village reported eating or using wild food at the present time or in the re- 
cent past. The majority of villagers indicated they liked to eat wild food, often 
preferring wild food to cultivated food and food from the market. Only 3 people 
(5%) reported they did not like wild food, while only 3 people felt that they like 
wild food as much as cultivated food. The villagers believe that wild food is nec- 
essary and that it is the most important food for everyday life. Analysis of the 
in-depth interviews revealed that males and females did not differ in their atti- 
tude ing wild food and both men and women preferred to consume wild 
food over cultivated food. 


206 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


TABLE 3.—Reasons for preferring wild food over cultivated food (n = 64) 


REASONS FOR PREFERRING WILD FOOD RESPONSES 
Female Male Total 

Taste Factor 

Taste: delicious, taste better, etc. 19 15 34 
Higher nutritional value, less fat 6 7 13 
Fresh, better than market food 6 6 12 
Natural 5 5 10 
Total 36 33 69 


Ease of Procurement and Safety 
Less poisonous agents, fewer chemical, 


less harmful 17 17 34 
Easy to obtain, can gather on their own 9 7 16 
Cleaner than market foo 6 3 9 
Total 32 27 59 
Economics 

No need to buy food, save money 15 14 29 
Total 15 14 29 


Note: Maximum answers = 3 per person 


The villagers gave a variety of reasons why they preferred wild food over 
cultivated food (Table 3). The most frequent reasons were related to qualities con- 
cerning: 1) taste; 2) ease and safety; and 3) economics. The concept of taste is 
obviously very important and included a number of important components. First, 
villagers often mentioned the fact that wild food is more delicious and tastes bet- 
ter than cultivated food. They also thought wild food was fresher and tasted more 
naturally sweet than market food. This is partially because of the inherent quali- 
ties of the food as well as the fact that villagers can gather wild food and consume 
it soon afterwards. Villagers also indicated that wild food was better because it 
grows naturally, has more nutrient value, especially vitamins and protein, and 
less fat. These specific nutrition-related characteristics, which some individuals 
are now ascribing to wild food, are most likely derived from information obtained 
from government sponsored health and nutrition education programs. 

The second group of reasons for preferring wild food revolved around the 
concept of ease and safety. Villagers preferred wild food because it was easy to 
obtain or they did not have to spend time or energy cultivating it; it is natural and 
grows by itself. Villagers consider wild food safe in part because they assume only 
cultivated food would be contaminated with fertilizers or insecticides. However, 
it is likely that many of these items, especially those growing in paddy fields and 
gardens, are contaminated with fertilizers and pesticides. Wild food is also con- 
sidered to be clean because it comes from the natural environment. It is not mixed 
with food that can become dirty at the market in town. 

The last set of reasons is related to economics. The villagers considered wild 
food to be good because they did not have to pay money for it, thus they were able 
to save money by eating wild food. Many villagers felt that poor people needed to 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 207 


FIGURE 6.—A typical dish made with red ant eggs. 


rely on wild food because they do not have much money to spend on food. How- 
ever, the villagers did not look down on individuals who relied on wild food. 
Many people also recognized that even rich people utilize wild food as a way to 
save on spending money for something that is available without monetary cost. 
Consequently, wild food was not stigmatized as a “food of poverty.” 

Procurement patterns were affected by time factors. Gathering is as commonly 
done in conjunction with other activities, such as gardening, agricultural wage 
labor or tending cattle, as it is done as its own activity. Gathering patterns are to a 
large extent dependent on both the seasonal availability of the food and seasonal 
workload of the villagers. In the rainy season two factors impact the amount of 
time spent gathering. First, because wild food is abundant, less gathering time is 
required. Secondly, in this season villagers are actively engaged in rice agricul- 
tural tasks so they tend to choose to gather food that is close at hand. Similarly for 
those households that are moving into cash oriented agriculture, such as growing 
asparagus or cucumbers for the commercial market, the opportunity to gather 
wild food is limited. Thus, it was not surprising that in the rainy season 53% of the 
women spent an hour or less gathering. On the other hand, in the cool season, 
when there are fewer agriculture-related demands, 64% of the women spent one 
to two hours gathering. In the hot season, however, the scarcity of wild food, more 
than time constraints from other activities, results in the village women spending 
more time gathering wild food, and 56% spent two or more hours in gathering 
activities. 

The selection of food is influenced not only by time constraints and preference 
but also by attitudes about the identity of individuals who are known to consume 


208 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


the food. Personal identity and food consumption are linked in powerful ways. 

The villagers in this study expressed a variety of opinions 

who consume wild food. These associations consciously and unconsciously affect 
the selection of these foods within the village context. Villagers indicated that they 
believed that wild food is essential for the poor. They indicated that the poorer 
people in the village have to depend on wild food, have more experience obtain- 
ing it, and are very knowledgeable about how and where to procure wild food. 
The villagers also expressed the sentiment that the poor also exchange wild food 
for other food items such as rice. However, villagers with all these opinions also 
indicated that they did sas eee down on individuals who gathered wild food; 

instead, they were and hardworking and often a degree of 
admiration was voiced. 

Conflicting beliefs were expressed when others in the village indicated they 
believed rich people consumed more wild food because they had money to buy it 
when it was not easy to obtain or when they were too busy to gather it themselves. 
A few individuals indicated they believed rich people ate more wild food because, 
unlike the poor people who had to engage in wage labor, wealthy individuals had 
time to obtain non-domesticated food. In these individuals’ minds, the poor people 
in the village relied on cheap, prepared foods from the village shops. For this group, 
purchased food was associated with poverty and was considered to be poor qual- 
ity foods. 

When asked how urban people view wild food, the villagers were of the opin- 
ion that town people like non-domesticated food and are often eager to purchase 
these items for ingredients in specific dishes, or as snacks. Villagers believed that 
wild food has a high market value, sells better than domesticated food and thus 
brings them a better earnings than domesticated food. A very small number of the 
interviewees (10 individuals) differed from the general opinion of the rest of the 
sample by thinking that towns-people had a poor attitude toward wild food, look 
down on village people who eat wild food or think that wild food, especially in- 
sects and some animals are not clean and are disgusting. These villagers also 
thought that the urban people may look down on villagers who eat this type of 
food. 


Variation in wild food knowledge. —Variation in knowledge of wild food was evi- 
dent in the study sample, although the majority of villagers stated a preference for 
wild food and continued to seek out and procure wild food items. The knowledge 
test was used to measure recognition, culinary knowledge, consumption, procure- 
ment, other uses, and transplanting and horticultural techniques (Table 2). 

An odds ratio (Agresti 1990) which interprets differences between two popu- 
lation proportions or possibilities, was employed to estimate how frequently one 
population identified a wild food correctly compared to the other (Identification 
test). We first compared men and women and then compared adults and children 
in terms of their ability to identify items in the wild food test (Table 4). In this 
analysis we grouped items into categories (plants, fish, and insects). The odds 
ratio analysis showed that, compared to men, women were more likely to be able 
to identify plants (1.38 times), insects (1.38 times) and fish (1.07 times). 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 209 


TABLE 4.—Gender based comparison of likelihood of correct identification of 
wild food. 


Gender Female Male Odd’s Ratio 
I N I N 

Adult 

Plant Group 626 1006 552 1014 1.38* 

Fish Group 59 129 64 145 1.07 

Insect Group 45 63 40 62 1.38* 

Total Wild Foods 730 1230 656 1253 RS 

Children 

Plant Group 175 326 155 312 ee a 

Fish Group 34 76 42 73 0.60 

Insect Group 16 2 13 32 1.80* 

Total Wild Foods 225 445 210 429 1.07 


Note: I = Total correct identifications 
N = Number of valid samples 
* = significant difference at p _.05 


Among children, girls were more likely to identify wild plant species correctly 
(1.17 times), and insects correctly (1.80 times), than boys. However, girls recog- 
nized fish less often (0.60 times). When the children and the adults were compared 
concerning their ability to identify the wild items, the odds ratio showed that adults 
were 1.31 times more likely to identify plants and 2.35 times more likely to cor- 
rectly identify insects. But the adults were less likely to identify fish correctly (odds 
ratio = 0.78) (Table 5). A total of 25 plants were used in the “attitude and knowl- 
edge” test. Eleven plants were correctly named by 80% of the children, but there 
were 16 plants that 20% or fewer of the children could name. However, a very 
large majority of the students (78%) said they consumed between 13 and 15 of 
these plants, and they also indicated they liked wild foods. 

In general, adult women and girls out-performed their male counterparts in 
identification of wild food items. Girls were 1.07 times more likely to identify the 
total three groups of wild food than boys, and adult women were 1.34 times more 
likely to identify all three groups correctly than the men (Table 4). 


TABLE 5.—Age based comparison of likelihood of correct identification of wild 
food (“identification” test). 


Wild Food Type Adult (N=64) Children (N=41) Odd’s ratio 
I N I N 

Plant group 1178 2020 330 638 1.31" 

Fish group 123 274 76 149 0.78 

Insect group 85 125 29 61 23557 

Total Wild Foods 1386 2419 435 848 


Note: I = Total correct identifications 
N = Number of valid samples 


= significant difference at p _.05 


210 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


The wild food knowledge test was also used to compare knowledge of wild 
food by comparing mean scores on the components of the knowledge test: identi- 
fication (I score), culinary knowledge (C score), procurement methods (P score), 
other uses (O score), transplanting and horticultural information (TP score) and 
total score (S score) (Table 2). The mean scores of each food group were calculated 
and compared between males and females and among the age groups using an 
en see of covariance: The analysis of covariance showed that there was no sig- 

der in the I, C, P OTP and S sores. Although women 
tended to have higher scores in each component, the differences were not statisti- 
cally significant. However, there were significant differences between the age 
groups for both males and females for all five categories of the knowledge score: I 
(p = .001), C (p = .009), P (p = .004), O (p= .001) TP (p = .001), and S (p = .001). Thus, 
it is clear that the older individuals have more knowledge about plants than the 
young. However, the age factor was not significant in terms of knowledge of in- 
sects or fish. 

Retention and loss of knowledge aus local d ticated resources -* an 
issue ¢ 1 with tai 
siteetvel diversity, and ethnobiological knowledge, and those interested in under- 
standing how culture is expressed and rendered meaningful. An examination of 
our data shows that gender and age are factors related to differences within this 
community in terms of knowledge of wild food. This finding is similar to research 
done by Wester and Yongvanit (1995). When they compared individuals from dif- 
ferent villages and levels of education in Isan, they also found that in almost all 
age groups women scored slightly higher than men on a test of wild plant knowl- 
edge. In their sample of 795 males and females (10 - 99 years of age), they also 
found that there was a general tendency for scores to increase with subject age 
until about 70 years, when scores of men showed a sharp decline. They further 
found, in marked contrast to scores of village populations, students, all of whom 
were younger than 30 years old, scored low. However, Ogle (1984) in her research 
in Swaziland, found that children recognized a large number of different wild 
species and reported high consumption of the items. Consequently, she concluded 
knowledge was not being lost to the extent feared. 

Differences in knowledge, both within and between communities and groups 
of individuals is to be expected, since men and women utilize and define the envi- 
ronment differently. The division of labor that occurs in agricultural communities 
leads to differentiation in work patterns, contact with resource areas and procure- 
ment of resources themselves. That children can have less familiarity or knowledge 
than elders is also not surprising since they have had less time to accumulate in- 
formation, fewer life experiences, fo are often not as involved as adults are in 
resource utilization. Add s adults are pulled into wage earning activities 
outside the village, opportunities ie communication of information also decrease 
or vanish completely. 

Differences in knowledge should not be accepted or dismissed lightly since 
the loss of traditional knowledge among many subsistence-oriented communities 
in many parts of the developing world has been noted. For example, Anderson 
(1993) has expressed concern about the perpetuation of such information among 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 211 


the hill tribes of northern Thailand and Works (1990) recorded that elders in a 
Peruvian community frequently lament that younger individuals are no longer 
interested in plants or gardens. Similarly, Maikhuri and Gangwar (1993) observed 
that knowledge of plants in younger individuals in the Khasi and Garo tribes of 
Northeastern India was judged to be poor. Similarly, the older villagers in our 
study often expressed concern about their perceptions of the loss of knowledge 
among the younger generation. Elders complained about their children and grand- 
children not being interested in learning about the procurement and preparation 
of wild food. 


CONCLUSIONS 


Loss of traditional knowledge among agricultural communities as they expe- 
rience the effects of globalization has been noted in many parts of the world. 
Nonetheless, many individuals remain connected to local practices, at least to some 
degree. In Isan, the strong connection between ethnic identity and cuisine encour- 
ages the preservation of local resources that imbue their taste, texture and odor to 
Isan cuisine. Many of these items are wild plants and animals. Additionally, many 
of the plant food items are also integrated into the local belief system regarding 
health and serve as medicinal plants. The continued reliance on important wild 
resources has led to items being utilized by different people at different times. 
Consequently the distinct interests that different segments of society have in the 
rural productive environment influence resource use and preservation (Collins 
1991). However, as suggested BY. neste and sone vanit (1995), es iaacioange or vio 
of traditional practices and | conscious choic 
It is sometimes an incidental result of new patterns of living. 

Adults are increasingly participating in the new economic patterns, which, 
rather than being embedded in the mixed subsistence practices, more and more 
involve cash cropping of introduced and domesticated crops as well as working 
for wages and both temporary and permanent out-migration. Children and young 
adults are also affected. Young adults are increasingly attracted to the trappings of 
the urban, cosmopolitan culture. Children who attend school, especially the higher 
grades outside the village, are occupied with studies that keep them from partici- 
pating in subsistence actives to the extent that children did in the past. It also 
exposes them to different ideas and activities. In the study reported here, the con- 
nection between land and life that was deeply embedded in daily survival in the 
past appears to be in the process of being altered as a result of the adoption of 
urban values and goals. Individuals are also absent from the locale during the 
periods of their life when they would haye been participating in activities that 
necessitated the accumulation of local I the d wild 
food resources. Although they still enjoy and prefer the tastes that these wild food 
items give to local dishes, and indeed connect them to local ethic identity, they are 
not as knowledgeable about them as the elders are. 

The information obtained in this study highlights the fact that there are vital 
connections between gender and age (and thus work patterns, division of labor, 
and participation in the wider national and global processes) and knowledge of 


212 SOMNASANG and MORENO-BLACK Vol. 20, No. 2 


local resources. Women were 1.34 times more likely than men to identify plants, 
insects, and fish correctly. The knowledge scores showed that women have greater 
knowledge than men in terms of recognition, gathering knowledge, preparation 
and consumption knowledge, and uses of wild food. However, the scores from 
the total | ge test indicate that there were ificant gender differences. 
There were significant differences in plant knowledge among “the different ages, 
with the older individuals scoring higher than young adults and children. These 
differences, which may be indicators of erosion in the local knowledge base, are 
potentially being exacerbated by both temporary and permanent out-migration, 
which results in fewer opportunities to learn about their native environment and 
the resources that are utilized. 

It is clear that factors such as gender roles, division of labor and the economic 
and social impact of nationalization and globalization determine the breadth and 
depth of knowledge about the habitat and local indigenous resources. These fac- 
tors are probably more important than resource abundance and diversity in the 
contemporary conditions of rapid economic and cultural change. The fact that 
wild food knowledge is largely a construct of such factors has important implica- 
tions for the survival of both knowledge about these resources, and ultimately the 
resources themselves. Villagers in the study are aware and concerned about the 
potential loss of knowledge. They frequently expressed a desire to preserve wild 
food for the younger generations. They mentioned that some types of wild food 
were rare, and they feared their children or grandchildren would not get to enjoy 
them. Villagers often proposed ideas to enhance retention, such as transplanting 
species, decreasing the amount of wild food gathered for sale, working with offi- 
cials to develop programs, willingness to comply with laws that would protect 

and habitats, and seeking to develop educational programs directly 
cngied at children. 

Our findings indicate that younger individuals have less knowledge than the 
elders in the village. It is important, especially from the perspective of the villag- 
ers, that local knowledge about wild plants and animals be maintained and 
documented. We believe government policymakers and development workers 
should consider ways to integrate local knowledge into the formal education sys- 
tem and incorporate it into relevant projects whenever possible. Efforts should be 
made to work with village elders to develop resource material such as illustrated 
pamphlets or monographs about local wild food resources for schools and public 
libraries. 

We also believe that villagers, forestry experts, and government officials could 
work together to determine ways to preserve indigenous species while still en- 
abling villagers to utilize these resources. Additionally, villagers should be 
encouraged to develop management strategies that will limit harvesting practices 
that are currently straining local resources. At the same time, it is vital that the 
concept of sharing be maintained, so that villagers can procure and consume wild 
food together, thus enjoying both the social and nutritional benefits that charac- 
terize [san cuisine and culture. 

Our study indicates that it is very important to begin obtaining dynamic ac- 
counts that relate women’s and men’s activities to the process of ecological change 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 210 


and the continuity of local traditions and knowledge. The preservation of knowl- 
edge about wild food plants appears to be the result of the continued connection 
with the local geography, and personal identification with the village or region. 
This is linked to specific food items or taste qualities, economic pressure, and in- 
trinsic family interest and motivation to preserve traditional patterns. In particular 
it is important that we recognize the ways in which different interests in the envi- 
ronment are structured by gender, age, class, caste, or ethnicity in order to identify 
individuals who are knowledgeable about local habitats and resources. Identifica- 
tion of important cultural influences in the construction of local knowledge will 
be invaluable for the design and application of conservation programs. 


ACKNOWLEDGMENTS 


This study was part of a larger project focusing on the marketing and use of non- 
domesticated, indigenous plants and animals in the northeastern part of Thailand. The 
project was — by grants from The Wenner Gren Foundation for Anthropological 
Research (G. M Foundation (G. M-B), a Margaret McNamara 
Memorial arg yeaa (P.S.), and a Ford Research Grant, NW Regional Consortium of 
Southeast Asian Studies (P.S.). 


We thank the staff of the National Research Council of Thailand for their assistance 
and willingness to allow this project to continue over an extended period of time. We are 
especially grateful to the villagers who participated in the project for their patience, help, 
information and hospitality. They were very generous with their time and their knowledge 
and openly shared their experiences with us. Special thanks go to Drs. G. Fry, C. Silverman 
and H. Wolcott for their helpful comments during the development of this paper. We also 
thank the anonymous reviewers. Their positive feedback is greatly appreciated. They also 
provided invaluable comments on this article. Finally, we are especially grateful to our 
families who willingly and patiently endured our absences, our work schedule and who 
supported our efforts throughout the project. 


LITERATURE CITED 
ANDERSON, EDWARD. 1993. Plants and COLLINS, JANE. 1991. Women and the 
People of the Golden Triangle: environment: Social reproduction and 
Ethnobotany of the Hill Tribes of sustainable development. In Women and 
Northern Thailand. Dioscorides Press, International Development Ann 
Portland. R.Gallin and A. Fergurson aie), Vol. 


AGRESTI, ALAN. 1990. Models for binary 2. Westview, Boulder. 
response variables. Pp. 79 - 129 in GRANDSTAFF, _ 5S.W. ‘ 
Categorical Data ee John Wiley GRANDSTAFF. 1987. “semi- structured 
and Sons, Ne 


7 


BOONTHAWEE, K. 1976. Child of the _ in RRA. Pp. 129 - 143 in Proceedings of 


Northeast. Duang Kamol, Bangko the 1985 International Conference on 

CHAMBERS, ROBERT. 1980. Rapid Rural Rapid Rural Appraisal. Rural Systems 

Appraisal: Rationale and Repertoire. IDS Research and Farming System Research 

Discussion Paper No. 155. Institute of Projects, Khon Kaen University, 
Thailand. 


Development Studies, Brighton. 


214 SOMNASANG and MORENO-BLACK 


HAENER, J. A. 1990. Forces and policy 
issues affecting forest use in ee 
Thailand 1900 -1985. Pp. 69 - 94 i 
Keepers of The Forest, M. Poflenberser 
(editor). Kumarian Press, West 


Hartford. 

HIGHAM, C.FE.W. 1982. Prehistoric rice 
cultivation in Southeast Asia. Scientific 
American 250:138-146. 

LEVIN, KURT. 1943. een jee et 

habits and methods of c e. Pp. 
65 in The Problem of cana Food 
Habits, Bull. No. 108. National Academy 
of Science, National research Council, 
Washington, D 

LOVELACE, G., Ss. SUKESINE, and S. 
SUJIN. 1988. Rapid Appraisal In 
Northeast Thailand: Case Studies. KKU- 
Ford Rural Systems Secerich i 
Khon Kaen University, Khon Kaen, 
Thailand. 

psi tin R.K. and A. K. GANGWAR. 


a Garo tribes of Meghalaya, 
Northeast India. Economic Botany 47: 
345 - 357. 


McINTOSH, ALEX and MARY ZEY. 1989. 
Jape nen of food 
Pp flepnied id Ha 
and acta 3(4):317 - 332. 
MORENO- BLACK, CERALDINE. 1994. 
Gathered food and culture change: 
traditions in transition in Northeastern 
Thailand. J. Home and Consumer 
Horticulture ies 3):93-107. 
rE MNASANG, and S. 
~THAMATHAWAN. 1996. Cultivating 
continuity and creating change: 
Women’s” garden practices 
Northeastern Thailand. acl and 
Human Values 13(3):3-12 
NGAMSOMSUKE, K., KAMOL, ¥ 
SAENCHAL, P. PROMBUROM, and B. 
SURAPORN. 1987. Bases attitudes 
toward forest plantation an 
conservation farming in  ealketed 
villages of the Phu Wiang valley, Khon 
Kaen. FAO/UNDP rite Integrated 
Development of t u Wiang 
Watershed Project, "hor Kaen 
University, Khon Kaen, Thailand. 


Vol. 20, No. 2 


NGARMSAK, TIPWANNA. 1987. Status 


geogra Ry and 
knowledge in the Oza 
highlands. Journal of éhucbioloay 
18(2):249 - 269. 

OGLE, BRITTA A. 1984. gee plant 
resources. Cares 101: 38 - 

PHONGPHIT, SERI ey KEVIN 
HEWISON. 1990. Thai Village Life: 
Culture and Transition in the Northeast. 
Village Foundation, Bangkok. 

PHITHAKPOL, BULAN. 1990. Preface. In 
Plants from The Markets of Thailand, C. 
Jacquat (editor). D. K. Bookhouse, 

angko 


PRADIPASEN, MANTANA, 


Dietary Survey. Institute for Population 
and Social Research, Mahidol 

University, i a a Thailand. 
—— O, TERRY. an Ecology 
Rural resource Ménagatiaht in 
oilinaont Thailand. Farming Systems 
a Project, Khon Kaen University, 

n Kaen, Thailan 

SOMNASANG, PRAPIMPORN. 1996. 
i se: Gender issues in 
h.D. 


dissertation, University of Oregon, 
Eugene 


' GERALDINE MORENO- 
~~ BLACK, and KUSUMA CHUSIL. 1998. 
Indigenous knowledge of wild food 
hunting and gathering in Northeast 
Thailand. Food and Nutrition Bulletin 
19 (4): 359 - 356. 

AGARAT RATHAKETTE and 
SUMALEE RATHANAPANYA. 1988. 


(editors). KKU-Ford Rural Systems 
Research Project, Khon Kaen University, 
Khon Kaen, Thailan 

SOLHEIM, W.G. IL. 1968. Early bronze in 
northeastern Thailand. Current 
Anthropolology 9:59-62. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 215 


VAN ESTERIK, P. 1992. From Marco-Polo 
to McDonald’s: Thai cuisine in 
transition. Food and Foodways 5: 177- 


TONTISIRIN, K. , J. YOUNG-AREE, 


PTONTIWATTASATION, K.SRIANUJATA, 
. SUKANGPLENG. 1986. Annual 
Raa 1985/1986: Thailand Food 
Habits Project. ASEAN Subcommittee 
on Protein: Good Habits Research and 
Development. ASEAN-Australian 
nomic Cooperation Program, 
Bangkok, Thailand. 


WESTER, LYNDON and SEKSON 
hear cicconale 1995. Biological diversity 
and community lore in northeastern 
Thailand. aod of Ethnobiology 15:71 


WORKS, MARTHA. 1990. Dooryard 
gardens in Moyobamba, Peru. Focus: 40: 
12-17. 


216 


APPENDIX A.—Wild food items used in the Knowledge and Attitude Test* 


SOMNASANG and MORENO-BLACK 


Botanical name Local name 
Plants 

Amaranthus gangeticus phak kaenkhom 
Amorphophallus spp. erok 
Antidesma acidum 


Butomopsis latifolia 
Calamus spp 


Centella asiatica 
Cratoxylon formosum 
Curcuma parviflora 
Cyclea peltata 
Dioscorea alanta 


mark mao 

pinoy 

whai (rattan) 
mark muay (fruit) 


dork grajeaw (flower) 
kruamanoi 
mon liam (tuber) 


Dioscorea hispida kloy (tuber) 
Emilia sonchifolia phak linpi 
Garcinia cowa somong 
Hydrocharis morsus-ranae yopae 
Irvingia malayan bak bok (fruit) 
Limnoccharis flava phak kanjong 
Limnophilia aromatica phak kayang 
Marsilea crenata phak waen 
Monochoria vaginalis ehin 
Ottelia alismoides obab 
Oroxylum indicum linfa (pod) 
Polygonum odoratum phak paew 
Sauropus androgynous kantong 
Solanum trilobatum mark kheng 
Stephania brevipes huabua 
Thyrsostachys siamensis normai huak (bamboo shoot) 
Wolffia globosa kipum 
— mark pipuan 
— liumpua 
Fungi 
Careya sphaerica hed phungtam 
Fresh water fish 
Cirrhinus jullieni pla khona 
Cirrhina microlepis pla suit 
Cultrops siamensis pla pap 
Solidago polyglossa pla khao huangleang 
Snail 
ai hoi sai 
ects 
Brachytropes portentosus 
ate) maeng huakuai 


*Dpl ee 


Poe % Ant A} 
7 
Homchoen at Khon Kaen University. 


consultation with Dr. Sompong Thamathawan and Dr. Samang 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 217 


Feeding the World. Vaclav Smil. MIT Press, Cambridge. 2000. Pp. xxviii, 360, 
many text figures, bibliography, index. $32.95 (cloth). ISBN 0-262-19432-5. 


This book is an absolute must for all interested in the world food situation and 
its future. It is the best up-to-date source I have seen on the subject. Smil defines 
his subject in the widest possible way, and brings together an amazing range of 
information on all of it. One stands in awe of his data retrieval system. (This is his 
15'* book, and the others are comparably data-rich. 

The best feature of the book, and intended so to be, is his focus on efficiency as 
the best way to deal with food shortages in the near future. Much of the book is a 
long litany of wastes: water and fertilizer wasted in the field, grain lost to weevils 
and rats in storage, grain fed to livestock that could eat grass, foodstuffs unneces- 
sarily thrown away in processing, and on to plate waste. This last grows ever 
worse as people live on takeout junk-food and no longer save leftovers. As he 
points out, we already have the world food problem solved, as far as production 
goes. We are producing enough food for all humans alive today, and could even 
provide for the entire population expected to be with us in 2050. The problem is 
all that loss. And his figures on that are conservative. He believes loss in storage 
to be around 10 percent to 15 percent; there are much higher estimates. 

Smil is a cautious optimist. He tries to steer a course between “cornucopians” 
and “catastrophists.” He dismisses the former (such as the late Julian Simon) with 
a single tart line: “If the global grain output were to continue growing only as fast 
as it has done during the 1980s (almost 2 percent a year), the annual harvest of 
cereals would surpass the Earth’s mass in less than 1,500 years...(p. xii).” The 
catastrophists are much more formidable foes. Much of the book is taken up by 
debates with Paul Ehrlich and Lester Brown, whose concerns cannot be written 
off. To be sure, their dire predictions have been wrong; he gives a series of Brown's 
now-invalidated ones (p. 12). But one might argue that the reason these predic- 
tions were wrong is that they scared people: into action. After all, they were usually 
couched in terms of “if nothing is done.. 

In any case, something was done and people are now better fed than ever 
before in history. About 1.2 billion people are hungry, but 1.2 billion are 
overnourished, so it balances out; the problem is clearly one of efficient allocation, 
not absolute shortage. (A more politically liberal observer than Smil might say 
that there is a bit of a redistribution problem there, too.) “If the rich world’s food 
losses could be held to 20 percent of the overall supply, the annual savings...would 
be equivalent to...nearly half of all cereals on the world market (p. 210).”. Mom 
was right to tell us to “think of all the starving people in Asia”— though, even at 
the age of eight, I wondered how my eating too much and getting fat was helping 
them. Smil has it right: we should stay thin and let the price of food fall. 

The bulk of the book consists of a truly incredible assemblage of information 
on the state we are in — so cebaiuiae fertilizers, crops, land base, soil erosion, stor- 
age, and on to proces , human nutritional needs, and plate waste. 
He notes, for ies that some of the gloomy Seedicione of the 1960s were based 
on assessments of human protein needs that we now know were far too high. We 
can get by on a little plant protein; we don’t need all that meat. But, if we want 


218 BOOK REVIEWS Vol. 20, No. 2 


meat, some meats (chickens, pigs) are far more efficiently produced than others 
(America’s adored beef is the worst). Eggs and milk are better still. The greatest 
value of this book to ethnobiologists, after its basic message of efficiency, is its use 
as a reference work; it is encyclopedic in coverage of a vast and often obscure 
literature on agriculture and food. 

o one human can bring so much together without making some dubious 
claims, however. Predictably, most of Smil’s are in the optimistic direction, but he 
has also missed some cheering thoughts. 

To begin with the over-optimism, Smil accepts the current projections (by the 
United Nations and other agencies) that world population will level off around 10 
billion in the next couple of generations. I do not believe this. The easy battles 
have been won: Europe is down to ZPG, East Asia is near it, and some other well- 
organized, highly educated countries have made a start. The rest of the war is 
going to be a great deal harder. Birth rates are falling slowly in South Asia and 
Latin America, but so are death rates. Birth rates are not falling, or not by much, in 
Africa and the Middle East. In these areas, little or nothing is being done to reduce 
population increase. China’s one-child rules are cracking and the system may 
crumble. Even the United States continues to grow rapidly, and current govern- 
mental policies are increasingly antithetical to demographic leveling off. Absent 
the most horrific of Malthusian checks, we will probably see rapid population 
growth throughout Latin America, Africa, and west and south Asia for the rest of 
this century at least, and appreciable growth in the United States. 

This is debatable. Much less debatable — indeed, a clear mistake — occurs on 
page 194 where Smil claims that “diets of several hundred million people are ap- 
preciably enriched by consumption of hunted and collected wild animal species” 
(apart from fish). Alas, overhunting and habitat destruction have made this state- 
ment obsolete. Only in the most remote and thinly populated areas — the Subarctic, 
the Australian outback, the inner Amazon — do people get significant game meat 
today. Much more typical is the Yucatan Peninsula where game was a staple food 
as recently as a generation ago, but now is virtually nonexistent. 

Another place where one might question Smil is his section on desertification. 
He says “...there is little doubt that virtually all early estimates have greatly over- 
estimated the impact of desertification, mainly because they mistook the cyclical 
nature of these changes for steady degradation.... Desert margins contribute rela- 
tively little to global food supply...” (p. 76) There are problems with both these 
claims. The cyclic waxing and waning of the Sahara against the Sahel was under- 
estimated in the late 20h century, but this does not greatly change the estimates. 
Overgrazing, deforestation, and overcultivation have been devastating. There are 
too many thousand photographs of “climate change” stopping short at a barbed- 
wire fence or a reserve border (see e.g. the magnificent collection in Jacobs 1995, or 
Charco 1999) to make “climate change” a believable explanation of the world’s 
desertification. I have personally seen thousands of cases, on four continents, of a 
desert landscape giving way—at a fence or other barrier—to a three-foot stand of 
lush grass or a dense brushland. This can take place on large scales: Even the 
rather thin protection that Israel gives the Negev has now made Israel's national 
border quite visible in satellite photographs. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY ae 


The same could be said for erosion. Smil correctly celebrates the really amaz- 
ing strides against soil erosion that have been made in the United States, Europe, 
and some other places, and concludes that soil erosion is not of major concern. Yet 
he is surely familiar enough with China to know the catastrophic state of erosion 
there. Perhaps he is less familiar with India and the dry parts of Africa. Clearly he 
is less familiar with Mexico and Latin America. Of course, there is very little good 
information on many of these areas, but what we have — and what anyone can 
see on the ground or from the air — is quite disturbing. 

Here, as in some other cases, Smil tends to assume that “no news is good 
news.” This assumption stands on somewhat believable ground when Smil notes 
that many national statistics understate production. (Maya subsistence farming 
in western Quintana Roo produce tens of thousands of tons of maize and fruit a 
year, none of which gets counted in national statistics.) However, the assumption 
is hard to credit when soil erosion is at issue. Here, the human tendency is the 
other way: to overlook and underestimate. Satellite pictures could improve our 
understanding, if we knew enough about interpreting them. 

So much for over-optimism — Smil’s one lapse into under-optimism is in pre- 
cisely our area. Smil seems only slightly aware of the enormous potential of 
underutilized and under-researched crops and cultivation systems, to say nothing 
of wild plants that could be cultivated. All readers of this journal will have their 
own pet examples and the cumulative total thereof (were we to pool our knowl- 
edge) would surely be enough to feed the world a few times over. Possibilities for 
expansion range from relatively well-known systems like Maya mixed orchards 
and Spanish olive groves to exotic potential crops like California’s tarweeds and 
meadowfoam, and from well-known but undervalued animals like guinea pigs to 
outside cases like oryx and addax antelopes. 

But is there a chance that all these measures will be adopted? Is Smil right, or 
will the catastrophists prove all too correct in the end? 

It is well to remember that, although “on average” the world is doing well, the 
most dreadful fantasies of the catastrophists are now the reality in many coun- 
tries. These include Ethiopia, Eritrea, Sudan, Somalia, the entire Sahel, and several 
other African countries, as well as Afghanistan, Uzbekistan, parts of Kazakhstan 
and Ukraine, North Korea, Haiti, and many more. These suffer from dense and 
fast-growing populations, collapse of food production, desertification (not caused 
by climate change!), lack of education and research, and, often, other environmen- 
tal catastrophes, from endemic warfare to Chernobyl. It is noteworthy, but hardly 
surprising, that the most environmentally devastated countries are also the coun- 
tries with the worst food problems. 

Conversely, the successes of Europe have gone beyond the wildest dreams of 
the optimists. Zero population growth and lavishly abundant food are accompa- 
nied by rapid improvement in the environmental outlook, as green consciousness 
spreads across the continent. Spain and Portugal are notable among countries 
that have seen explosive growth in production and income while actually improv- 
ing (at least locally) their environments. 

What accounts for these differences? The conventional wisdom provides us 
with three possibilities, all obviously wrong. First, most common among environ- 


220 BOOK REVIEWS Vol. 20, No. 2 


mentalists and still not uncommon among developers, is the idea that “capital- 
ism” is the source of all evil. This clearly does not account for the above picture. 
Among other things, many environmentalists seem to think that the rich nations 
are environmentally more trashed than the poor ones, because of high consump- 
tion. This is not the case. To see really ravaged environments, one needs to go to 
such localities as Uzbekistan, Ethiopia, or China. It is the most productive, food- 
exporting countries that also do the best by their environments. Second, there is 
the reverse view: Capitalism is what the world needs; socialism is the evil. This 
fails to account for ongoing and worsening problems of countries that have enthu- 
siastically bought into capitalism and accepted IMF discipline, including most of 
Latin America and southeast Asia. Third is the idea that dependency and global- 
ization are the culprits. If this were so, we would expect to find countries very 
tightly enmeshed in the dependency end of the global economy, such as Mexico, 
Taiwan, South Korea, and Thailand, to be the poor ones. They are not; it is the 
most isolated countries, such as Ethiopia, Somalia, Bhutan, and Laos, which are 
the worst off. 

There is one simple predictor. Strong yet d ith a strong 
tradition of accountability are always associated with progress in both ea pro- 
duction and environmental awareness. Scandinavia and the Low Countries are 
examples. Spain, Portugal, Greece and Hungary — the point by rapidly de- 
veloping food production and (except possibly inG l awareness 
in the wake of democratization. Weak yet authoritarian governments are at the 
opposite pole, characterizing the sad examples listed above. A change from de- 
mocracy to chaos or authoritarian rule accompanies environmental decline 
(Malaysia, Indonesia, Pakistan), which eventually must lead to food production 
failure (Guatemala, El Salvador, and elsewhere). It would seem that this correla- 
tion should be studied systematically by those interested in the problem. It has 
more to tell us than either the global optimists or the global catastrophists. 

Smil ends his book with a look at China, a country he knows extremely well. 
Here he crosses swords with Lester Brown whose book Who Will Feed China? Wake- 
up Call for a Small Planet (1995) made the catastrophist case in lurid detail. They 
both work from very similar factual bases, and (as I know from my own indepen- 
dent research on China) they are both quite reasonable in their interpretations of 
the data. The difference between them is really over something they never dis- 
cuss: The leadership China has and will have. Brown assumes that China’s 
ee will continue to be as it i snow. At present, the leaders do not oneal 
1 problems that might limit future food product nd the 
routinely i imprison those who raise the issue. Smil evidently hopes and sass that 
a new generation will have new ideas. 

Indeed, it appears that Smil’s cautious optimism, Brown’s worries (see also 
Brown et al. 2000), or the extreme optimism of the irrepressible and delightfully 
outrageous Libertarian Ronald Bailey (2000), have much less to do with the facts 
than with their take on human nature. They all say surprisingly similar things 
about what we are doing, what we can do, and what we need to do, technologically. 
They even have similar political views, seeing governments as far too prone to 
hinder rather than help. The difference is that Brown sees governments as inevi- 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 223 


table and frequently prone to act as they do in Sudan and Afghanistan. Smil looks 
at the governments of Europe and Canada, and hopes. Bailey dreams of abolish- 
ing government altogether. 

One wishes Bailey were right. If only people, released from the bonds of the 
State, would work together for love and profit. Unfortunately, the world is the 
way it is. I know Bailey is wrong. I hope Smil is right. But if I had to bet money, 
I’d bet with Brown. 


LITERATURE CITED 
BAILEY, RONALD (editor). 2000. Earth , CHRISTOPHER FLAVIN, and 
Report 2000: “pains. the True State "HILARY eee “grace 2000. State 
of the Planet. McGraw-Hill, New York. of the World 2 W. W. Norton for 
BROWN, LESTER. 1995. Who Will Feed Worldwatch emia, New York. 
China? Wake-up Call for a Small Planet. CHAKECO) TESUS- (1999. El Bosque 
W. W. Norton for Worldwatch Institute, Mediterraneo en el Norte de Africa. 
New York. Agencia Espanola de Cooperacién 
Internacional, Madrid. 


JACOBS, LYNN. 1995. Waste of the West. 
Author, Tucson. 


E. N. Anderson 
Department of Anthropology 
University of California Riverside 


Journal of Ethnobiology 20(2): 223-236 Winter 2000 


THE JAGUARS OF ALTAR Q, COPAN, HONDURAS: FAUNAL 
ANALYSIS, ARCHAEOLOGY, AND ECOLOGY 


DIANE A. BALLINGER 
Dallas VA, North Texas Health Care System 
Department of Physical Medicine and Rehabilitation 
UT Southwestern Medical Center 
D 


JEFFREY STOMPER 
College of Lake County 
Grayslake, IL 


ABSTRACT.—An excavation at Copan, Honduras, a Late Classic Maya site, 
revealed the ritual cache of bones of at least fourteen big cats associated with 
Altar Q. Several of the large cats were identified as jaguar, Panthera onca. 
Preliminary analysis showed that the animals were in good health at the time of 
their deaths. All but one were adults. Tail fans of several species of birds 
accompanied the feline bones. oe with od crypt of the felines were the 
smaller tomb burials of two macaws, Ara sp. Th 

that all the jaguars were procured locally because of environmental constraints. 


Keywords: Maya archaeology, zooarchaeology, jaguar, Copan, ritual 


RESUMEN.—La excavacion del escondite des huesos felinos en el sitio Maya con 
la fecha de eke tardio en re Honduras, ha revelado un entieramiento des 
losh a ,y otros gatos grandes, asociados con 
el Altar Q. El analisis ha mostrado que los animales estaban saludables quando 
murieron. Todos menos uno que eran adultos. Los huesos de los jaguares estaban 
acompanados por saat abanicos de cola de varios pajaros. Los huesos de dos 


han cerca dela crinta 


arcangas Arasp., 


x: 
de los j jaguares. Los autors concluyen que no es possible que los jaguares fueron 
obtinidos en el valle de Copan porque del constre(imientos cercania. 


RESUME. Redan i Copan Honduras un site Maya de Classique Tardif ,a 
revelé Panthera onca, quatorze 
chats grands, associés avec l’Altar oe sprees des ossments a monstré que les 
animaux etaint en bon santé au temps du mort. Il y a un jeune et trieze adults 
dans |’assemblage. Les ventails de la queue de les oiseaux a accompagné les 
ossments des chats grands. Associés avec le crypt des les animeaux il y ont deux 
petites enterrements de les deux oisieux, Ara sp. Les auteurs ont conclué que ce 
n’etait pas possible pour les jaguars Itre obtiner dans le vallée de Copan parce que 
des contraintes d’environnment. 


224 BALLINGER and STOMPER Vol. 20, No. 2 


INTRODUCTION 


The discovery of an offertory cache of feline bones yielded an exciting glimpse 
of ancient Maya ritual behavior to archaeologists. Feline bones filled the masonry 
crypt to the east of Altar Q at Copan, Honduras, an altar whose sides bear high 
relief portraits of the sixteen rulers of Copan’s Classic Period dynasty. The cache 
at the foot of Altar Q contained the remains of at least fourteen large felines, two 
macaws, and the tail fans of seven other birds. This is a report of the discovery and 
preliminary analysis of the offertory complex associated with Altar Q and Struc- 
ture 10L 16 in the Acropolis area of the Main Group. Jeffrey Stomper, then a graduate 
student under the supervision of Dr. William Fash, the Director of the Copan 
Acropolis Archaeological Project instituted under the auspices of the government 
of Honduras, excavated the offertory complex in 1988. The offering consisted of a 
sealed crypt containing the remains of at least 14 large felines, including Panthera 
onca, and macaws (Ara sp.) associated with a stone altar on a low, round platform 
that was placed on the central axis of the western side of Structure 10L 16 in the 
Main Group at Copan. 

Until now, the evidence that large felines were involved in Maya ritual has 
consisted of skeletons of single animals and portions of skeletons of cats buried in 
ritual contexts (Pohl 1983, 1990). Landa (Tozzer 1941) discussed animal sacrifices 
stating that animals were used in rituals and were sacrificed. They were presented 
to the gods either alive or not, sometimes dismembered but also whole (Tozzer 
1941). The cache at Copan is the largest cache of felidae bones discovered by Maya 
archaeologists to date. 


JAGUAR SYMBOLISM 


Maya art and iconography are rich with depictions of jaguars. The same is 
true of other Mesoamerican civilizations. Copan, Palenque, Uxmal, and Tikal are 
among the lowland Maya sites where jaguars are featured prominently (Morley, 
Brainerd, and Sharer 1983; Spinden 1975; Tozzer and Glover 1910). Spinden (1975) 
considered them second only to the snake in symbolic importance to the Maya. 
Coe (1972) pointed out the links between rulers and jaguars and the separation of 
king and commoner in native Mesoamerican religions. He further remarked on 
the antiquity of the jaguar as a religious icon and its ties to Mesoamerican reli- 
gions and the ruling lineage (Coe 1972). 

Images of jaguars frequently decorate ceramics recovered from Maya sites, 
appearing on a variety of vessels. On these, men often wear clothes with jaguar 
markings or jaguar pelts (Spinden 1975: 149). Many times jaguar symbolism is 
part of a ritual or religious context on vessels, such as one from Altar de Sacrificios. 
On this vessel, the ruler of Yaxchilan is dressed in jaguar skin trousers, mitts made 
of jaguar paws complete with claws, and a jaguar headdress. A second figure in 
jaguar regalia is near that has the arms, hands, tail and feet of the jaguar on a 
human body (Saunders 1989: 146). 

The jaguar epitomized two different kinds of strength to the Maya. The jaguar 
motif was associated with the underworld and its supernatural power and also 
with physical strength. The association with physical strength derived from the 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 225 


fact that jaguars are powerful, nocturnal hunters. Ideas of the supernatural power 
of the jaguar arose from the early totemic tradition of Mesoamerica and the jaguar 
nagual’s (spiritual co-essence) relationship to the shaman’s power. Possession of 
supernatural power and physical strength was important to Maya rulers because 
their political power rested on their ability to act as a priestly bridge between the 
ancestors, the underworld, and the living world (Schele and Freidel 1990). 

Maya artists juxtaposed rulers and warriors with jaguar symbolism in art. 
Strength and prowess of combat were required of both the ruler and the warrior 
but Span of the ruler. A fearsome beast of the tropical forest, the jaguar per- 
sonified a dual control of the supernatural, a necessary power for Maya 
kings, and the physical prowess needed by the successful warrior (Saunders 1989; 
Hassig 1985). 

Mesoamerican cultures from Olmec to Aztec revered the jaguar. The Olmec 
associated jaguars with shamanic power and filled their art with images of were- 
jaguars. The Aztecs linked the jaguar to war, sacrifice, and royalty (Saunders 1989: 
150; Hassig 1985). Furthermore, they associated jaguars with jade, rain, and fertil- 
ity (Saunders 1989). At the time of the Spanish conquest, Aztec (Mexica) traders 
routinely transported pelts and live animals from outlying parts of the empire to 
the capital. Pictures of both live animals and pelts appear on trade and tribute lists 
of goods moving from Soconusco, the colonial province located on the coastal 
plain of the state of Chiapas, Mexico, to the Aztec Empire (Voorhies 1989). 

Relicts of this symbolism are found today in remote areas of Central America, 
Mexico, and South America. Jaguar symbolism is most visible in masks and cer- 
emonies performed in isolated villages. Wearing a jaguar mask transforms the 
wearer into a new creature that combines animal, human, and | quali- 
ties (Saunders 1989). Thus, the jaguar is an ancient and potent symbol permeating 
native cultures of Mexico, Central, and South America. 


ARCHAEOLOGY 


As part of the first season’s work of the Copan Acropolis Archaeological Project, 
William Fash conducted preliminary investigations of Structure 10L-16 and the 
adjacent Plaza areas in 1988 (Fash 1991; Agurcia, Stone and Stomper 1989). During 
the spring of that year, excavations at the site of the western base of Structure 10L- 
16 and Altar Q were in progress, supervised by Jeffery Stomper and veteran local 
excavator, Ismael Gonzalez. Stomper concentrated the initial excavations on the 
area in front of and beneath Altar Q, anticipating finding the dedicatory offering 
or other remains of associated rituals at that locus. Other examples of dedicatory 
caches had been found either directly in front of or underneath altars and stelae 
elsewhere at Copan (Stromsvik 1941). An area was marked off directly west of the 
altar and excavated to a depth of 120 cm. Fearing for the integrity of the trench if 
he dug between the stone supports that uphold Altar Q, Stomper elected instead 
to tunnel beneath the altar from the eastern sidewall of the same pit. This mini- 
tunnel excavation beneath the altar produced no evidence of a cache, nor was 
there any evidence that the area under the altar had been disturbed. 


226 BALLINGER and STOMPER Vol. 20, No. 2 


4 em 


I 


a 


1g. 


rf 
sa te 
a; Lh) 


>>) 
1h 


Wi, : 
O—_— 
= 


| { 

P ; orte (today) 
‘ 

tt 


Corte (c.1900) 


iS, 


FIGURE 1.—The East Court, Main Grou 
h 


p, Copan, Honduras. Supplied by William and 
Barbara Fash. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY yf 


Stomper began another pit that mirrored the location of the previous one. 
Immediately, he found two features. The first was a plain, round altar, CPN 13470, 
with a diameter of 36 cm. Altars such as these were used as stands for incense 
burners elsewhere in Copan during the Late Classic period (Fash 1983:464). The 
second feature was what appeared to be several rough slabs of stone, Feature 8, in 
a line below the level of the last plaza floor. The excavation was expanded to un- 
cover the extent of this feature. 

The capstones were aligned in a north-south direction, sloping from east to 
west, and covering the masonry crypt that contained the animal bones. Probing 
between the stones revealed a hollow area approximately 1.3 m deep and at least 
1m wide. When Stomper removed the capstones, he found that debris from places 
where the walls had caved in filled the crypt. The crypt, measuring 131 cm long 
and 48 cm wide, had walls of eight courses of finely cut building stone rising to a 
height of 117 cm. 

Within the crypt, the excavators found animal bones. The removal of the first 
level of bones revealed an irregular intrusion of lime plaster in parts of the cist. 
Excavation of this layer revealed that more bones were embedded in the layer of 
plaster with still more bones below it. These layers were removed in the plaster 
matrix in large sections and kept separated. Stomper continued excavations into 
the fill under the cist to a depth of 3 m under the plaza level. He recovered only 7 
fragments of ceramics from under the cist. Approximately 319 cm below the origi- 
nal cist floor, the excavators uncovered an earlier plaster floor of the West Court. 
Excavations were terminated at this point. 

Two small shafts adjacent to the cist were also uncovered just outside the north- 
east and southeast corners of the cist. The inside of the roughly square shafts 
measured 22 cm on each side. At the bottom of one shaft were nine whole pris- 
matic obsidian bladelets and parts of two others. Located 25 cm above the obsidian 
were the bones of a medium-sized bird. The second shaft also contained the bones 
of a bird but no obsidian. Nothing else was found. 

Stomper excavated the entire area between Altar Q and Structure L10-16, re- 
vealing a round platform of small, faced stones two courses high in some places. 
Unfortunately, the whole platform was not preserved. Located in the center of the 
platform was an oval stone with a smooth upper surface, repeatedly charred by 
fire. Resting on the top of the platform was a small, highly polished fragment of 
jade. The area around the platform yielded incensario fragments, a ceramic in- 
cense burner. In an adjacent area to the west of the platform just below the level of 
the last plaza floor, a small cache of obsidian lancets was found. 


FAUNAL ANALYSIS 


During the summer of 1988, the faunal material was identified and recorded, 
and a preliminary report was filed at the Central Office of the Project in Copan 
(Ballinger 1988). The bones were counted, sorted into skeletal elements, and ex- 
amined for pathological conditions: and é anomalies. i Eenpaet used weight-bearing 
bones of th to detern umber of individuals (MNI) 
because weight-bearing bones have large areas of tee compact bone, and, hence, 
tend to be better preserved (Brain 1981). Left and right elements were identified 


228 BALLINGER and STOMPER Vol. 20, No. 2 


and counted. Ballinger matched the bones by size or age to determine if they be- 
longed to a single individual (Chaplain 1971). Juveniles were identified by the 
lack of epiphyseal closure. The analyst ignored most of the fragments because 
time was limited. The largest MNI of the elements was then determined as the 
MNI for the species (Klein and Cruz-Uribe 1984). Actual bone counts were made 
at Copan. Photographs of the best preserved crania were taken for later identifica- 
tion. Final identification to species level was made in the Zooarchaeology Lab at 
Indiana University, where a comparative collection is housed. 

Analysis was done under field conditions without the use of a comparative 
collection or manuals commonly used by faunal analysts. Neither a comparative 
collection nor library resources were available in 1988 at the Copan laboratory to 
aid in identification. Ballinger took notes supplemented with photographs and 
sketches. The initial identification of the bones as feline resulted from her exami- 
nation of the teeth, crania, scapulae, and femora while in Honduras.” 


Condition of the Bones.—Burial in a closed crypt resulted in good preservation. Al- 
though the bones were subjected to natural decay, they were protected from some 
of the taphonomic processes that radically change relationships between skeletal 
elements (Lyman 1982). Thus, while many of the bones were not articulated, they 
were close to the position in which they were placed in the crypt. The crypt walls 
kept them from being dispersed after burial. They were also protected from water 
and heat, the two most powerful agents in bone dissolution (von Endt and Ortner 
1980). The bones were dry and chalky but retained their shapes, so skeletal ele- 
ments were easily identified. Exfoliation was present on some of the bones but 
most of them were well preserved. 

An assessment of pathological lesions was made on the bones that had mini- 
mal flaking on them. The bones of the second level, excavated as a unit and curated 
as a unit, allowed Ballinger to determine the position of the jaguars of the second 
level in the crypt by the association of skeletal elements. The heads of some had 
been laid over the rear legs and feet of others. 


Results of the Faunal Analysis—The MNI of the felines was at least 14. This number 
is conservative because the analyst was unable to perform a complete examina- 
tion of all the faunal material. Ballinger found that many of the bones found in the 
crypt were Panthera onca. Differences in jaguars and puma lie in cranial morphol- 
ogy. According to Olsen (1968), jaguar crania have a sagittal concavity on the 
superior aspect of the cranium that rises to a pronounced lambdoidal crest that 
gives a slight s-shaped curve to the jaguar’s skull. The posterior crest gives the 
jaguar cranium a squared off appearance and the skull appears longer and more 
rectangular. The puma, however, has an oval skull lacking the massive, posterior 
cresting. Crania of jaguars and puma are similar in their anterior aspects and teeth 
but differ in the posterior aspect. It is the posterior features on the crania the dis- 
criminate between the species. The more complete crania from the crypt have 
distinctive nuchal robusticity and a more elongated architecture of the jaguar. Al- 
though there is not enough cranial material remaining to account for 14 jaguars, 
an estimated 6 animals in the assemblage were Panthera onca. The others are fe- 
lines but remain to be positively identified as jaguar. The remaining bone in the 
assemblage is bird bone and a few intrusive rodent bones. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 229 


The bones of the felines are very similar in size, indicating that the animals 
were similar in age and sex. They were also healthy animals. Assessment of indi- 
cators of general health routinely surveyed by investigators: cortical thickness, 
osteoporosis, and the frequency and severity of periosteal reactions, lesions of re- 
active bone growth resulting from localized and systemic infections, demonstrated 
that the cats were free from these pathological conditions that commonly mark 
the bones and indicate a decline in health status. 

Large cats are prone to bone diseases in captivity. Osteoporosis, thinning of 
the bones, is a problem for large felines in zoos. It results from inactivity, too little 
protein, old age, and metabolic disorders (Fowler 1986). Caged felidae are also 
highly susceptible to metabolic bone disease that results in a rickets-like bowing 
of the long bones (Fowler 1986). The cortices of the bones were thick and only one 
periosteal reaction was found. The single periosteal reaction was on the hind foot 
of one animal and had fused two metatarsals. Appendicular bones were robust 
with prominent muscle markings, and had no sign of rickets-like bowing. 

No cut marks, dismembering marks, or skinning marks were found on the 
feline bones that were examined. The removal of pelts results in a characteristic 
pattern of skinning marks. Skinning for pelts often makes cuts ringing the lower 
metapodial where the knife has circled the ankle or wrist to loosen the skin. Car- 
pals, tarsals, and the bones of the digits are then removed with the pelt and, thus, 
are missing from the assemblage. Ballinger found no evidence that the pelts were 
removed after death. Further work, however, should include careful examination 
of the bones for skinning and other butchering marks. 

In addition, the vertebrae must be examined. Ballinger concluded that crania 
may have been disposed of separately for some of the cats. The paucity of cranial 
fragments compared to the amount of post-cranial material leads Ballinger to the 
conclusion that crania may have | disposed of separately. Further analysis may 
reveal cut marks on the first or second cervical vertebrae if the heads were re- 
moved before burial. 

The avian bones in the assemblage were collected from two places, the small 
shafts adjacent to the crypt and from the crypt itself. The bones of an adult macaw, 
Ara sp., were found in each shaft. Both of the macaw skeletons were missing the 
pygostyle, the bone to which the tail fan attaches. Two pygostyles of the correct 
size were recovered from the crypt, possibly the ones missing from the birds in the 
shafts. The pygostyle is a fragile bone, however, and may have been destroyed by 
postmortem diagenesis. There are seven other pygostyles from other unidentified 
birds in the crypt. Three of these probably are the same species. The other four are 
two matching sets and may represent two more species. Lack of a comparative 
collection precluded the complete identification of the avian bones. In all, nine tail 
fans were buried with the jaguars. Other bird bones buried in the crypt included a 
caudal vertebra, a fragment of a tarsometarsus, a fragment of a proximal radius, a 
rib fragment, and two phalanges. All of these remain unidentified. There were no 
signs of rodent gnawing or cut marks on the avian bones. 

Preservation of the macaw bones differed for the two shafts. Burial 1 lacks 
cranial bones. The head may have been removed at the time of death but the re- 
mains were too broken to properly check for cut marks. The remains of more than 


230 BALLINGER and STOMPER Vol. 20, No. 2 


one bird may be present in the second shaft. The bones removed from the second 
shaft have more fragments of long bone and cranium than Burial 2. Differences 
between the two shafts’ contents, however, may have been affected the microenvi- 
ronments of each shaft. Ballinger identified the macaws by the presence of the 
beak in Burial 2 and a comparison of the two birds. It was clear that post-cranially 
they were the same (Hargrave 1970). However, all of the avian bone should be 
reanalyzed with a comparative collection at hand. 

In summary, a MNI of at least fourteen large felidae, some of them Panthera 
onca, were identified from the bones in the crypt. The animals were healthy with 
no indications of longterm protein deficiency or inactivity. Accompanying the fe- 
lines were the tailfans of nine birds, including two macaws. No evidence of 
butchering or mode of death was found in this analysis. A full study of the feline 
bones may reveal sex and age differences, less obvious evidence of disease, and 
the mode of death of the animals. Similarly, comparison of the avian material to 
comparative skeletal collections may reveal the species of the unidentified mate- 
rial. 


DISCUSSION 


Natural History and Ecology of the Jaguar—The jaguar (Panthera onca), is the largest 
of three species of spotted cat native to Central America (Burton 1987). Classed as 
a big cat, the jaguar has a shoulder height ranging from 110-155 cm (Burton 1987). 
The jaguar prefers a forest habitat but can live in savanna environments if there is 
enough brush cover. They also live in slightly arid areas. Good swimmers and 
climbers, jaguars are primarily nocturnal feeders, sleeping during the middle of 
the day (Burton 1987). 

Few investigators have studied the natural history of the jaguar in the wild so 
most information comes from zoo studies. Many of the details about breeding 
patterns come from studies of zoo animals. Jaguars are very easy to raise in cap- 
tivity. They breed easily and can live on two or three pounds of meat a day, 
according to David Ruhter,’ former Curator of Large Animals, Houston Zoo (Per- 
sonal communication via telephone, 1994). Less is known about their behavior in 
the wild. Large felidae are long-lived animals whose prey is normally about half 
their body weight (Sunquist and Sunquist 1989; Gittleman 1984; Packer 1986). They 
usually need large areas in which to forage and, except for lions, are solitary. 

Today, the jaguar has adapted to more crowded habitats in Central America. 
In 1983, Rabinowitz and Nottingham (1986) tracked the movements of nine jag- 
uars in Belize. The authors found that the home ranges of the jaguars overlapped 
but that as long as prey was available, they remained on them, avoiding each 
other. Analysis of scat determined that in Belize jaguars feed on seventeen species 
of prey (Rabinowitz and Nottingham 1986). This is consistent with reports from 
other areas to the south that jaguars feed on diverse prey: capybara, fish, peccary, 
and alligator (Ewer 1973). Generally, jaguars feed nocturnally but the female in 
the Belize study changed her feeding pattern to the daytime in order to exploit 
cattle as prey. This study suggests that the jaguar is flexible and able to adopt new 
habits as needed to survive (Rabinowitz and Nottingham 1986). 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 231 


Naturalists do not know much about the behavior of the puma in Central 
America. Felis concolor occupies a wider range of habitats than the jaguar, ranging 
from mountains to jungles to deserts (Ewer 1973). The puma is slightly smaller 
than the jaguar. Puma diet is omnivorous in tropical climates where they consume 
several types of rodents, fish, and other small game. The main component of their 
diet is deer and domesticated farm animals, although they have demonstrated 
behavior flexibility in the selection of prey species. 

The jaguar and the puma are in almost direct competition in Central America 
because of the similarity in size, habits, and diet. Puma are also nocturnal feeders 
unless forced to feed at other times. They are known to live near home ranges of 
jaguars (Rabinowitz and Nottingham 1986) in Belize, but in the North American 
west, their ranges are larger and do not overlap. 

The ecology of the jaguar has important implications for explanations of how 
the Maya acquired at least fourteen big cats for ritual use. Rue (1987) states that by 
the Late Classic, the valley was heavily deforested resulting in a loss of habitat for 
tropical forest animals. If, however, enough brushy areas still existed in the valley, 
jaguars could have survived there, given the presence of adequate prey. In gen- 
eral, species that live in savanna or parkland areas have larger populations than 
forest living animals (Berkoff et al. 1984), thus deforestation could lead to a slight 
increase in the population of cats in the valley. Jaguars have demonstrated their 
ability to survive crowded conditions and the ability to change feeding schedules. 
It is highly probably that they survived in a mosaic environment of parkland and 
brush. 

Ultimately, however, access to prey governs population size. A deforested but 
still brushy area could have supported sufficient deer and other species of prey to, 
in turn, support a small jaguar population. Similarly, a mosaic of brush and cleared 
spaces will support a white-tailed deer (Odocoileus virginianus) population whereas 
closed canopy forest will not (Smith 1975). Deer have small home ranges, often 
living near humans and thriving. Historically, deer have been an important part 
of Maya subsistence (Mandujano and Rico-Gray 1991) and only recently have de- 
clined in importance as numbers decreased. Both brocket deer and white-tailed 
deer feed in cleared areas of new growth near fields because tender shoots are 
present there. There also may be fewer insects in young forest (Mandujano and 
Rico-Gray 1991). Mandujano and Rico-Gray (1991) remarked that the decline of 
Yucatan’s deer population was directly attributed to over-hunting and loss of habi- 
tat, a relatively new situation. Population decline was exacerbated by the loss of 
native farming methods that provided browse each season after the fields were 
burned, cleared, and farmers severely trimmed brushy growth in and around the 
milpas. This growth sprouted anew with the rains. Pohl (1994) proposed that 
Copanecos were very likely to have raised deer in and around their homes and 
fields in the valley. 

Other animals available as prey are Brocket deer (Mazama sp.) and peccary 
(Tayassu tayacu). Both would have done well in this open, brushy habitat. Brocket 
deer browse on the same kinds of plants as white-tailed deer: tender twigs, shoots, 
and leaves of a variety of herbaceous plants and fruits. The peccary is omnivo- 
rous, living in a variety of tropical habitats, including forests and dry savannas 


22 BALLINGER and STOMPER Vol. 20, No. 2 


(Lawlor 1979). Smaller prey, such as paca, agouti, and armadillo are native to the 
area and can live in brushy environments. 

The Copan Valley could have supported a small population of big cats even if 
it were partially deforested. Whether it could have supported a population large 
enough to provide at least 14 adult big cats from local sources is another question. 
The Copan Valley is comprised of 26 square miles of territory. Of that, the heavily 
populated Copan pocket would have been too urban-like for jaguars or pumas to 
live there. Game such as deer would have been drawn to the areas surrounding 
fields further out rather than the kitchen gardens closer to the central site. Big cats 
would have lived farther out from the Main Group at Copan. 

Normally big cats have large home ranges of 15 square miles. If we assume 
that crowding has limited the size of the home range a home to 5 square miles, the 
Copan Valley would only provide ranges for five jaguars at a time. Avoidance 
behavior as demonstrated in Belize would not make it possible for more animals 
to survive unless even with prey populations of very high density. Thus, the large 
number of felines found in the crypt most likely resulted from a combination of 
trade, hunting, and hand raising. 


THE OFFERTORY COMPLEX AND THE JAGUAR BURIAL 


Yax Pasah, the last ruler of Copan, had begun an aggressive new building 
program by raising Temple 11 and making significant additions to the West Court, 
where Altar Q is located including Altar Q (Fash 1991). The altar is an illustration 
of the succession of the last ruling dynasty of the polity. Along the sides of the 
altar the names sixteen rulers are inscribed beginning with Yax Ku’k Mo’ (Blue or 
First Quetzel Macaw) and ending with Yax Pasah. Yax Pasah, by his choice of 
iconography for the West Court, indicated its relationship with the underworld, 
Xilbalba, and, thus, to his ancestors (Schele and Freidel 1990). 

Yax Pasah faced serious problems during his reign, including deforestation, a 
population that was shrinking, and a diminution of his power (Fash 1994). Schele 
and Freidel (1990) note that most of his monuments state the cosmic sanction of 
his rule, and hypothesize that his reign was marked by crises. His impressive sac- 
rifice and building program may have been an attempt to restore Copan to its 
previous place in the hierarchy of major sites. 

Structure 10L-16 was the final product of the remodeling in the West Court. 
The jaguar burial occurred at this time as a ceremonial cache for the dedication of 
the last version of Structure L10-16. The Copenecos placed Altar Q at the base of 
this structure. Yax Pasah buried at least 14 big cats in the crypt associated with 
Altar Q. Once the people of Copan placed the felines in the crypt, tail fans of birds 
were placed there, and the crypt was then covered with three capstones. A small, 
round, carved altar was placed next to it directly between the two shafts. A final 
plaza floor was then laid, covering the capstones. Jaguars and other spotted cats 
had an unknown but important ritual significance at Copan. Pohl (1994) remarks 
that while skeletons of spotted cats were often cached in ritual contexts by the 
Maya, Copan has more such caches than any other site. All of these have so far 
been found in elite contexts. Pohl (1994) considers them a measure of the high 


Winter 2000 JOURNAL OF ETHNOBIOLOGY Zao 


position of the site of Copan in the Maya hierarchy. The inclusion of macaws was 
ritually significant but their meaning is less clear. The name of the dynastic founder 
was macaw. Macaws occur frequently in the decoration of public ritual space at 
Copan, especially on the ball court. 

Questions of where the jaguars came from and how they were killed remain 
unanswered. The ecological conditions and size (over 75 km) of the Late Classic 
Copan Valley could have supported a small population of jaguars or pumas even 
if partially deforested. It was not, however, large enough to provide 13 adult and 
one semi-adult large cat. David Ruhter (Personal communication 1994) suggested 
that the easiest way to assemble that many jaguars would be to gather kits in the 
spring and raise them by hand. There is evidence that jaguar kits were given as 
gifts. A vase from Tikal shows a turbaned figure holding a kit and presenting it to 
the ruler (Culbert 1993). 

The feline bones, however, presented no evidence of long-term inactivity or 
protein deficiency, indicating that the Copanecos had taken good care of the ani- 
mals and that their caged time was short. At this time, it is impossible to determine 
whether the animals were raised by hand or captured as adults. 

We can only speculate about how the jaguars met their fates. Preliminary ex- 
amination revealed no cut marks on the bones to indicate that the jaguars had 
been skinned or dismembered. A more complete analysis of the bones may reveal 
skinning marks leading to determination of their modes of death. The presence of 
crania and numerous tarsals and metatarsals, carpals and metacarpals indicate 
that some heads and feet were not removed. Often on ceramic vessels, individuals 
are portrayed dressed in jaguar pelts with heads and paws still attached (Coe 1973; 
Schele and Miller 1986; Kerr and Kerr 1989). It appears that the valuable and ideo- 
logically significant skins were left on the animals. 


CONCLUSION 


Jaguars could have lived in the Copan Valley even after deforestation if a 
brushy, mosaic environment was present. The size of the valley, the amount of 
tilled fields, and even with deer management, the amount of prey limited the num- 
ber of jaguars and pumas that were living there. The flexibility of feeding patterns 

d the presence of small home ranges as demonstrated by modern jaguars in 
Belize indicate that jaguar populations in the past could have adjusted to smaller, 
overlapping ranges close to humans populations without undue stress. Jaguars 
would have been in direct competition with the Maya for scarce protein given 
their reliance on a maize-based diet. 

The lack of disease and stress indicators on the bones of the jaguars indicates 
that the bones are the remains of generally healthy animals that had not been 
captive for a long time. These animals had no chronic met that cause 
bowing of the leg bones, no osteoporosis, and only one periosteal reaction. Fur- 
thermore, all but one of the animals were adults with full epiphyseal closure. This 
indicates that healthy, adult cats were chosen for the cache. The cats could have 
been kept in good condition for as long as four to six months by being fed two or 
so turkeys each day (David Ruhter, Personal communication 1994). 


234 BALLINGER and STOMPER Vol. 20, No. 2 


Hopkins (1992), in her work on the animals bones removed from the Cenote 
of Sacrifice at Chichen Itza, argues against the assumption that the jaguar bones 
found at Chichen were solely the result of sacrifice because there are too many 
other reasons that the bones could have been deposited in the cenote. At Copan, 
the bones clearly are in a ritual context, one that is repeated many times at the site. 
The cache of the feline and bird bones represented a significant gift to the people 
of Copan. By placing his sacrifice in the West Court with all of its symbols of the 
underworld, Yax Pasach hoped that a continuous connection with the ancestors 
and the jaguars’ supernatural power would be forged. Thus, homage was paid to 
garner the aid of ancestors and gods to keep the polity strong and growing when 
many Maya cities were falling into decline. It was to no avail. Shortly after this, 
the people of Copan ceased to erect dated monuments and the population of the 
central valley declined. 

Future work should include analysis of the assemblage of feline bones. Mea- 
surements of the bones and assessment of small differences between the jaguar 
and the puma should be made. The analysis should also contain reconstruction of 
crania and pelves, where possible. Finally, a close examination for cut marks and 
any other butchering marks should be carried out. 


NOTES 


1 The jaguar bones are curated at the Central Laboratory in Copan Ruines, Honduras. This 
is also where the field reports, preliminary reports, manuscripts, theses, and dissertations 
are housed. The archives at Copan include drawings, photos, and a small library and are a 
good resource for investigators. 


2 Two students of Wm. Fash have examined the collection of animal bones but I have not 
been able to contact them by publication time. 


3 David Ruhter was curator of large animals at the Houston Zoo when I contacted him. He 
has since moved out of state and the personnel department at the Zoo would not release 
his address to me. 


ACKNOWLEDGEMENTS 


Barbara and Bill Fash provided the site map, read the draft, criticized constructively, 
and secured the permission to publish from IHAH. Many thanks. The reviewers made 
very good suggestions on improving the manuscript. Any errors are the authors’ own. 
Further thanks go to Rebecca Storey who first took me to Copan and permitted me to share 
housing with her in 1988. She has also helped me fulfill the governmental regulations that 
are necessary to work in another country. Ballinger: s } dissertation research at Copan in 
1988 was funded by a grant awarded by the D gy and the Graduate 
School, Indiana University. My thanks also go to Dick Adams who gave me lab space and 
let use the comparative collection in the Zooarchaeology Laboratory, Indiana University, 
several times. 


Winter 2000 


JOURNAL OF ETHNOBIOLOGY 235 


LITERATURE CITED 


STOMPER. 1989. 
rieiiie saat of Structure 10L-16, 
Copan, Honduras. Presented at the 55th 
annual meetings of the American 
Anthropological Association, 


AGTRE RICERDO. DONNA STONE 
nd JEF 


Washington D.C. 
BALLINGER, DIANE A. 1988. Preliminary 
a: oe Waa 1 Sat 1, f£ Altar 


Q. MS on file at the Proyecto Copan 
Laboratorio, Copan Ruines, Honduras. 
BERKHOFF, MARC, THOMAS J. DANIELS 
and JOHN L. GITTLEMAN. 1984. Life 
history patterns and png comparative 
social ecology of carnivores. Annual 
Review of Ecological Systeins, 15:191- 


232, 
BRAIN, C. K. 1981. The Hunter or the 
caste University of Chicago Press, 


Chica 

BURTON” JOHN A 1987. The Collins Guide 
to the Rare Mammals of the World. The 
Stephen Green Press, Lexington. 

CHAPLAIN, R. E. 1971. The Study of 
Animal Bones from a ae ta 
Sites. Seminar Press, New 

COE, MICHAEL D. 1973. The Maye Scribe 
and his World. The Grolier Club, New 


. 1972. Olmec jaguars and Olmec 
kings. In The Cult of the Feline, E. 
Benson (editor). Dumbarton Oaks 
Research Library and Collections, 
Washington, DC. 

CULBERT, T. PATRICK. 1993. Maya 
Civilization. Smithsonian Books, 
Washington, D 

EWER, R. F. 1973. The Carnivores. Cornell 
University Press, Ithaca, 

FASH, WILLIAM L. 1983. Reconocimiento 
y excavaciones en el valle. Pp. 229-469 
in Introducci6n a la Arquelogia de 
Copan, C.F. Baudez (editor). Volume 1 
Secretaria de Estado en el Despacho de 
reall 2 Turmiso, Tegucigalpa, 
Hondur 

ees 1991. Scribes, We 
Thames and — London 

. 1994, Changing perspectives on 
Maya civilization. Annual Review of 
Anthropology 23:181-208. 

FOWLER, MURRAY. E. 1986. Zoo and Wild 
Animal Medicine. 2nd edition. W. B. 
Saunders ap aon Philadelphia. 


d Kings 


GITTLEMAN, JOHN L. 1984. The 
behavioral ecology of carnivores. Ph.D. 
dissertation, University of Sussex, 
Brighton, England. 

HARGRAVE, LYNDON. 1970. Mexican 
Macaws: Comparative Osteology and 
messi 
University of Arizona Press, Tucson. 

HASSIG, ROSS. 1985. Trade, Tribute and 
Transportation: The Sixteenth Century 
Political Economy of the Valley of 
Mexico. University of Oklahoma Press, 


Norman. 

HOPKINS, MARY R. 1992. Mammalian 
remains. In Artifacts from the Cenote of 
Sacrifice, Chichen Itza, Yucatan: textiles 


Memoirs of the Peabody Museum of 
Archaeology and Ethnology, Harvard 
University, 10, (3): 369-385. 

KERR, JUSTIN and BARBARA KERR. 1989. 
The Maya Vase Book. Volume 1. Kerr 
Associates, New York. 

KLEIN, RICHARD and KATHRYN CRUZ- 
URIBE. 1984. The Analysis of Animal 
Bones from Archaeological Sites. 
University of Chicago Press, Chicago. 


LYMAN, R. LEE. 1982. Archaeofaunas and 
subsistence studies. P 31-393 in 
Advances in Archaeological Method 
and Theory, Volume 5, M. Schiffer 
(editor). Academic Press, New York. 

soto ot NO, 5. and V. RICO- ee 


Fics of the white-tailed dene 
(Odocoleus virginianus roc by the 
Maya of central Yucatan, Mexico. 
Journal of Ge itors ree 175-183. 
MORLEY, S. G., G. W. BRAINERD and 
ROBERT J. SHARER. ong pan Ancient 
Maya. Stanford University Press, 


Stanford. 
OLSEN, STANLEY J. 1968. Mammal 


Harvard university, Cambridge. 


236 BALLINGER and STOMPER 


PACKER, C. 1986. The ecology of sociality 
in felids. Pp. 429-451 in aa a 


> 
WD 
'S 

io) 

Nn 

2} 

=n 
WM. 
° 

Gi, 
= 
ies] 
< 

° 

ae 
fr 

oo 
_ 

ie) 

e 

o) 


oe Princeton University Press, 
Princeton. 
POHL, MARY D. 1994. Late Classic fauna 
an 


oo — consumption. Pp. 459- 
rest, and W; L 
Museum of peenese is and Ethnology, 


Pp. 146-174 in Excavations at Seibal, 
Volume 3, G.R. Willey (editor). Papers 
of the Peabody Museum of Archaeology 


and Ethnology , Harvard University, 
Cambridge. 
: 1983. Maya yrenest faunas: 


s, cahces, 


x d the vin elo 


Pp. 55-103 in Civilizations in the ancient 
Americas, R. M Leventhal and A.L. 
Kolata (editors). — of New 
Mexico Press, Albuque 

A: 


R 

HAM. 1986. cious and 
behavior of the jaguar, Panthera onca, in 

Belize, Central America. Journal of 
Zoology 210:149-59. 

RUE, DAVID J. 1987, Early p.snipiies and 
early postclassic Maya occupation in 
western Honduras. Nature 326:285-86. 

SAUNDERS, NICHOLAS J. 1989. People of 
the Jaguar: The Living Spirit of Ancient 

merica. Souvenir Press, New York 

SCHELE, LINDA and = DAVID 
FREIDEL.1990. A Forest of Kings: The 
Untold Story of Ancient Maya. Wm. 
Morrow & Co., or. 

and MARY | ELLEN MILLER. 
1986. The Blood of Kings: Dynasty and 
Ritual in Maya Art. Fort Worth Kimball 


Middle 
pi ie exploitation of animal 
populations. Papers of the Museum of 
peeneeobes No. 57, University of 
Michigan, Ann Arbor. 


Vol. 20, No. 2 


SPINDEN, Bile 1975. A Study of 
aya art. Reprint. Dover Publications, 


New Yo “ 

STROMSVIK, G. 1941. Sub-stelae Caches at 
Copan and Quirigua. Carnegie 
Institution Washington, 
Contributions of Anthropology and 
History, No ca arnegie Institution, 

Washington 

SUNQUIST, M. E and F. C. SUNQUIST. 
1989. Ecological restraints on predation 
by large felids. In Carnivore Behavior, 
Ecology and Evolution, J. L. Gittleman 
(editor). Cornell University Press, 


Ithaca. 

TOZZER, ALFRED M. 1941. Landa’s 
Relacién de las cosas de Yucatan. Papers 
of the Peabody Museum, 28. Harvard 
University, Cambridge. 

—__——. and M. ALLEN GLOVER. 1910. 
Animal figures in the Maya codices. 
Papers of the Peabody Museum 4(3). 
Harvard University, repre = 

VON ENDT, D. W. and, D. J. ORTNER. 
1980. Experimental sr of bone size 
and temperature on bone diagenesis. 

Journal of Archaeological Science 11: 


9-53. 
VOORHIES, BARBARA. 1989. Ancient 
Trade and Tribute. University of Utah 
Press, Salt Lake City. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 237 


El Bosque Mediterraneo en el Norte de Africa. Jestis Charco. Agencia Espajfiola 
de Cooperacién Internacional, Madrid (Avenida Reyes Catélicos, 4. 28040 
Madrid, Spain). 1999. Pp. 370. Many color and black-and-white photographs, 
maps, figures, tables. No price quoted. ISBN 84-7232-825-2. 


This magisterial work is far enough outside the normal scanning pattern of 
Western Hemisphere readers that it needs some attention here. Charco has pro- 
duced one of the most splendid studies of a Third World region’s forests and its 
conservation problems. North Africa still has large forested areas in the Atlas 
Mountains and a few scraps remain in the coastal lowlands of Morocco, Algeria 
and Tunisia. However, the vast majority of the historic forest area is gone, almost 
all the rest is degraded, and deforestation is proceeding. 

The forests of the Atlas are largely evergreen (cedar, pine, a few fir) higher up 
and largely oak lower down. The oaks are diverse, each species having its preferred 
habitat. S if at low altitudes; Tetraclinis articulata, a strange 
cypress-like plant, covers thousands of hectares. Fragments of wild olive forests 
and riparian groves exist. Among the most fascinating trees is the argan (Argania 
spinosa), endemic to Morocco (almost exclusively in the southwest), valuable for 
timber, fuel, forage, and the high-quality oil of the fruit. Its value has protected it, 
but not well enough; like all other trees, it is under assault. It grows in a strange 
subtropical forest at the west end of the Atlas, where its usual cohorts are other 
endemics or are Canary Island species that still have a tiny mainland foothold. 

The book is arranged by forest type, as defined by dominant tree. More spe- 
cifically, the system is the “phytosociology” of Braun-Blanquet and followers, which 
is almost universal in European botany though relatively little known in the West- 
ern Hemisphere. For each forest type, common species are indicated — not only 
other trees, but also shrubs, herbs, and fauna. Rare and endangered plants and 
animals receive attention. Ethnobotanists will find full accounts of the uses of the 
trees and of the varying levels of preservation that they have received. 

Northwest Africa has known agriculture and stock raising for 7,000 years. For 
3,000 of those years, states and cities have been present. The impact on the forest, 
especially the lowland forest, has been among the most severe found anywhere in 
the world. The Roman Empire exploited the forests and exterminated the native 
elephant. After its fall, unstable governments and an emphasis on animal hus- 
bandry led to progressive decline. The twentieth century saw the extermination of 
the lion, the Nile crocodile, and most other large animals, though a few leopards 
may survive. Deer have been kept available by stocking. The larger birds are simi- 
larly impacted. Even small animals are often endangered. 


On the other hand, Cl : the lands in cues 
tion give us a more hopeful picture than the earlier wexaeees works of Mikesell (1961) and 
McNeill (1992). He and ff-girt areas 
forests still cover thousands of hectares. Astonishing relictive forest turning up 
in dofd (Dracaena draco), previously believed endemic to 


the Canary Islands, was found in southwest Morocco as recently as 1995. 

Charco is emphatic in pointing out that human agency has done the damage. 
On the other hand, local systems have developed reasonably good ways of man- 
aging much of the landscape. Cultivation between standing trees, nondestructive 


238 BOOK REVIEWS Vol. 20, No. 2 


cork extraction from cork oaks, rational though thorough utilization of argan trees, 
careful terracing of slopes, and many other devices reduced the human impact. 
Religious beliefs and sanctions preserved forests in many places. The problem 
today is that very rapid population growth has gone along with equally rapid 
modernization, complete with roads, big dams, unregulated logging, and the rest 
of the litany. Yet economic growth, which would have brought pressures for more 
rational exploitation of resources, remains slow and uneven in the region. In addi- 
tion, Algeria has been racked by warfare. 

Recently, a revisionist view blames desertification on climate change. Charco 
provides many photographs of forests surviving in cemeteries, sacred sites, and 
reserves, and regenerating with wild abandon in fenced-off plots. It is clear that 
the damage is indeed the result of logging, firewood collection, and, above all, 
stock rearing — not climate change. The result, in loss of valuable plant products 
alone, has been catastrophic. To this one may add the loss of topsoil; much former 
forest is now eroded to bare rock. Water runs off where once it seeped into ground- 
water. Wildlife and wild herbs are gone. The economy has lost an incalculable 
amount of wealth. It is truly staggering to contemplate how much richer the three 
countries would be if they had been able to exploit the forests in anything like a 
sustainable manner. The time is not too late; protection would allow the forests to 
recover, eventually, in much of their former habitat. 

To a Californian, this book is thought-provoking (at the very least). The south- 
ern half of California is a near-perfect geographic match for northwest Africa. We 
too are using our environment in a destructive, non-sustainable way. The same 
desertification that affects North Africa is not far off, unless dramatic changes oc- 
cur. One wonders if North Africa’s poverty and instability will be duplicated here. 

This book is illustrated with I hs, charts, diagrams, and tables 
Several color photographs are presented for every forest type. The quality of these 
pictures is high. They are taken to show the vegetation and its fate, not just to fill up 
space with something “pretty” (as is the case in all too many books). The book lacks an 
index, but excellent organization and the many visual aids make up for that. 

In short, this is a book that everyone interested in forest use and management 
will want to see. Have no fear if your Spanish is limited; the photographs speak 
for themselves. 

This and many other ecological and ethnobotanical works are available from 
the Libreria Agricola, Fernando VI, 2. 28004 Madrid — a bookstore worth know- 
ing, especially if (like me) you can order books for your university library. 


LITERATURE CITED 


MCNEILL, J. 1992. The Mountains of the MIKESELL, MARVIN. 1961. Northern 
editerranean World. Cambridge Morocco: A Cultur raphy. 
University Press, Cambridge. University of California Press, Berkeley. 
University of California Publications in 

Geography, 14 


E. N. Anderson 
Department of Anthropology 
University of California Riverside 


Journal of Ethnobiology 20(2): 239-265 Winter 2000 


PERCEPTION AND MANAGEMENT OF CASSAVA (MANIHOT 
SCULENTA CRANTZ) DIVERSITY AMONG MAKUSHI 
AMERINDIANS OF GUYANA (SOUTH AMERICA) 


MARIANNE ELIAS 


cefe-cnrs 
1919 Route de Mende 
Montpellier cedex 5, Ftance 


LAURA RIVAL 
Department of Anthropology 
Eliot College, University of Kent 
Canterbury, Kent CT2 7NS, United Kingdom 


DOYLE MCKEY 
cefe-cnrs 
1919 Route de Mende 
Montpellier cedex 5, Ftance 


ABSTRACT.—This article presents the ways in which Makushi subsistence 
economy and its farming practices, food preparations, cultural knowledge and 
social processes have all played a role in bringing cassava varietal and genetic 
diversity into existence. After comparing cassava varietal diversity among the 
Makushi of Guyana with that found in the rest of Amazonia, the authors discuss 
the genetic implications of traditional management and show that evolution in 
populations of domesticated cassava results from the combined action of natural 
and human sElecHen. Various socio- cultural factors CRSTVIEsnE eve Pree, 


particu 
aan of seedlings and Sent coming from vegetative propagation, are 
examined. The approach adopted, which integrates indigenous botanical 
knowledge, elements of plant genetics and ecology, a that diversity 
cannot be reduced to a finite stock of well defined, varieties, 
but is, rather, a fluid and evolving process by which farm-grown varieties are 
continuously gained and lost. 


Key words: Cassava, M thot lenta, Makushi A indi Guyana, traditional 


agriculture 


RESUMEN.—Este articulo presenta la manera en que la economia de subsist 
de los Malushi y las practicas de cultivo, la prepararion de las comidas, el 
conocimiento cult ido a una importante 
diversidad genética y varietal de la yuca. Después de un andlisis comparativo i 
la diversiddd de la yuca cultivada por los Makushi de Guyana con la que 
encuentra = el resto de * Amazonia, ie articulo saci sobre la aiotleaacile 
genétic uestra que que la evolucién 
de las sb lackcints de yuca cultivada es la consecuencia de la accién combinada 


240 ELIAS et al. Vol. 20, No. 2 


de la seleccién natural y la selecci6n humana. Varios factores socio-culturales 
implicados en la oe en nl Sage anand los intercambios de estacas entre los 
euliivadores se je co planta nacida de semilla y la penis 
; siraekee Ea dak gracié 

indigenos, de elementos de genética y de ai muestra que la diversidad, 
lejos de estar oe aun cuyanty t = de entitades determinadas llamadas 
variedades, es a dinamico, por el cual las variedades 
cultivadas son continuamente adquiridas y perdiddas. 


RESUME.—Cet article présente la facon dont l’économie de subsistance des 

Makushi ainsi que les pratiques de culture, la préparation des mets, les 

connaissances culturelles et les mécanismes sociaux ont tous contribué a une 

importante iia variétale et génétique du caress Apres une analyse 
le 


d 
ariétale c u Nakiwuchi de Guyana avec 


celle que l’on trouve dans le reste de l’Amazonie, Varticle discute les implications 
geénetiques on pratiques de culture traditionnelles et montre que l’évolution de 

manioc domestiqué est la conséquence de l’action combinée de la 

sélection naturelle et la sélection humaine. Plusieurs facteurs socioculturels 

impliqués dans la sélection, en particulier les échanges de boutures entre les 

cultivateurs et Yopposition Sonceptiate entre plante issue de graine et plante 

L’approche adoptée, qui intégre 

les connaissances botaniques indigénes, des éléments de génétique et d’écologie, 

souligne que la diversité, loin d’étre réduite a un stock fini d’entités déterminées 

appelées variétés, est au ore un processus fluide et dynamique par lequel 


les variétés cultix t acquises et perdues. 


INTRODUCTION 


While present concerns about the conservation of genetic resources have led 
to the reassessment of the human side of plant/people interactions, the question- 
ing of the division between natural and artificial mechanisms of selection has 
prompted a growing number of researchers to pay particular attention to the ways 
in which people affect plant genetics (Salick 1995). These developments, which 
have given rise to a new type of economic botany that integrates ecological and 
evolutionary dimensions in the reinterpretation of plant domestication, cultiva- 

ion and management, have resulted in renewed interest in traditional farming 
systems, known for maintaining high levels of biological diversity (Boster 1983; 
Salick and Merrick 1990; Salick 1992a; Brush et al. 1994). Traditional farming sys- 
tems have so far been studied by geneticists, who have attempted to assess the 
level of genetic diversity found in Pont ecHOns | of cultivated plants, incding vari- 
eties, and by social scientists, who have car e g urveys. 
However, only a few studies have tried to connect both genetic and ethnobiological 
aspects of the maintenance of varietal diversity (e. g., Quiros et al. 1990; Viinerer 
1991; Salick 1992b; Louette et al. 1997; Souza et al. 1997; Emperaire et al. 1998). 

The overall objective of our investigation of cassava (Manihot esculenta Crantz, 
Euphorbiaceae) is to apply an integrative approach combining ethnological, eco- 
logical and genetic data in order to understand how the biological diversity of this 
cultivated plant is traditionally managed and maintained. For this, we have cho- 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 241 


sen to study bitter cassava cultivation in a Makushi community of the North 
Rupununi savannas of Guyana, South America (Figure 1). Some of the results of 
our genetic studies are now available (Elias et al. in press); ecological studies are 
still in progress. The specific objective of this paper is to document the cultural 
knowledge and practices that have brought the genetic diversity of cassava into 


N 
Fa 
4 
Pa 
2nN7 parima 
/ 
. ATLANTIC OCEAN 
‘ Baran 
ios 
VENEZUELA / 
%,, fPrv02 
Gp ~ Georgetown 
Mazaryp, 
f ALinden 
\ & £ 
‘ e ¢ 
4 - Xe) 
‘\ S 9 BY Q 
ge ee | = g 
‘N | 2 
/ } & fi rupuka 
/ rs spa@ug 
Ti geet *» 
\.? Taushida \ 
A Toka Apoteri * SURINAM 
(e) 
: \ 6 Annai @ 
a Mgssar¢ SRewa bs 
ne a D as 
a *, -y am 
\ a ee rrr | hoe 
&ethe 
Boa Vista ! s 
O . 8 § ) 
\ & iS a i) 
oer ks FA wo6 
\ © 3 
( coe es 
BRAZIL Ne as \ vatican 
‘ ~ F ie ! 
‘ os if 
i ‘ 
Pe ia 7a, . 
*, * Area where the study was conducted 100 km 
Zags s 


FIGURE 1.—Map of Guyana, showing the location of the Makushi communities where 
the study was conducted. 


242 ELIAS et al. Vol. 20, No. 2 


existence. This information on the cultural environment, combined with informa- 
tion on ecology, is essential to the interpretation of population genetics and 
evolutionary patterns (Elias et al. in press). 

Bitter cassava, characterised by high cyanogenic-glucoside content of the tu- 
berous roots, is the staple crop in the Amazon, where it has been cultivated for 
more than 3000 years (Renvoize 1972). Most cassava research to date has been 
conducted in the Northwest Amazon (see for example Hugh-Jones 1978; Boster 
1984a; Dufour 1985, 1988; Chernela 1987; Van der Hammen 1992; Salick et al. 1997), 
where the cultivation and processing of (mainly bitter) cassava have been meticu- 
lously described. Rival (in press) presents a comparison of cassava cultivation and 
processing between northwest ian groups and Amerindians of the Guyana 
shield. 


METHODS 


Site of study.Our study was mainly based in Rewa, a small Makushi community 
of the North Rupununi in Guyana, situated at the confluence of the rivers Rewa 
and Rupununi (forest area), 50 km WSW of Apoteri (4°02’ N, 58°35’ W). Marianne 
Elias spent 9 months over 3 field sessions in the Rupununi (April 1997, February — 
May 1998, September — December 1998); Laura Rival spent 5 weeks (2 field ses- 
sions in April 1997 and April 1998); and Doyle McKey spent one month (one field 
session in October 1998). In April 1998, there were 162 people living in Rewa (in- 
cluding three Wapishana men, six Wapishana women, and two Patamona women), 
forming 27 households. Because of its small size and relative isolation, Rewa is 
less subject to ial and political r than sava ities. Other 
Makushi villages, located in the savannah area, were also visited. Concerning the 
farming system, no major differences were found between these villages and Rewa, 
which can thus be considered representative of the Makushi farming system in 
this region. 


Collection of ethnographical data. —Our methods involved observations, participation 
in farming practices and food processing, open discussions, structured and semi- 
structured interviews and questionnaires. Symbolic and other cultural data were 
collected as part of a participatory research programme led by Laura Rival and 
involving the close collaboration of two remunerated Makushi women research- 
ers. We tried to work with as many farmers as possible; however, three female 
farmers (ages: 22, 35, 52) and two male farmers (ages: 41, 50) were identified as 
our main informants. As almost everybody in Rewa is fluent in English or Portu- 
guese; discussions and interview were conducted in these languages, including 
some Makushi words for critical points. Bilingual villagers helped us with people 
who spoke only Makushi. One villager in Rewa and two villagers in the savannah 
area helped us with Makushi spelling. 


Assessment of varietal diversity and of its distribution.—Varietal diversity was assessed 
by first asking farmers to bring leaves of every kind of cassava they cultivate, then 
by visiting farms and interviewing farmers. To estimate the equitability of diver- 
sity distribution among cassava farmers we used the index of equitability, which 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 243 


is often applied to estimate the “evenness” component of the diversity of biologi- 
cal assemblages. 
dpm p, 


n, om 
It is calculated as follows : F = ee , Where P; ao 3 te mn ,and n,; 


are the numbers of households that cultivate variety i (respectively, the number of 
varieties owned by household 1). 


MAKUSHI CASSAVA FARMING TODAY 


The Makushi, a Carib-speaking group, live in the Rio Branco-Rupununi re- 
gion, which is a region politically divided between Brazil (Roraima State) and 
Guyana (Region 9). There are approximately 20,000 Makushi today, of whom 7,000 
live in Guyana (CIR 1993). Historical records of Makushi presence in the Rio Branco- 
Rupununi region date back to the early part of the 18th century (Riviére 1963; 
CIDR 1989; Farage 1991; Hemming 1994, 1995; Santilli 1994). With cattle ranching 
expanding at the turn of the century, they experienced increased land shortages 
and pressure to work as domestic servants or cowboys, and many of them left the 
Roraima hills in Brazil for the Rupununi savannas of what is now Guyana (Farage 
1991), where they can still be found, living in relatively small communities, headed 
by a captain or “toushau.” Makushi families historically traded manufactured 
goods for cassava and cassava derivatives, particularly farine, a meal made of 
dried granules of grated cassava (Farabee 1924; Diniz 1966; Farage 1991). White 
settlers needed the Makushi as much for their agricultural products as they did 
for their labour force, and there is little doubt that such demands modified the 
indigenous agricultural system. Such influence accentuated the importance of 
horticulture over hunting and gathering, and reinforced the tendency towards 
sedentarisation in nucleated villages. If, like = sigs Amerindian groups, the 
Makushi had traditionally produced cassava o prepare fermented drinks 
for festive occasions, the condemnation of such Solition-Hietal activities by mis- 
sionaries, the new trade opportunities, and additional factors linked to interethnic 
contacts, led to the utilisation of cassava surpluses to make farine for sale, a trend 
which has influenced the choice of cultivated varieties. 

Bitter cassava cultivation is central to Guyanese Makushi slash-and-burn ag- 
riculture, which is still directed toward subsistence, rather than market, production. 
Many varieties of bitter cassava are maintained (Makushi Research Unit 1996), 
and the diet is supplemented by other starchy crops such as yams (Dioscorea spp.), 
corn (Zea mays L.), sweet potato (Ipomoea batatas (L.) Lam), sweet cassava (Manihot 
esculenta), plantains (Musa paradisiaca L.), or vegetables such as pumpkin (Cucurbita 
maxima Duch. ex Lam.), shallots (Allium cepa ‘aggregatum’ L.) and onions (Allium 
cepa ‘cepa’ L.), or fruits such as watermelon (Citrullus lanatus [Thunb.] Mansf.), as 
well as fish and meat (game and cattle). 

Agricultural activities are conditioned by climatic and edaphic factors. Wet 
(from May to September) and dry (from November to March) seasons are pro- 
nounced and interspersed with brief transitional periods. Two factors make 
savannah soils particularly unsuitable for crop cultivation. In addition to being 
particularly infertile, they are subjected to weather extremes; they are almost en- 


244 ELIAS et al. Vol. 20, No. 2 


tirely flooded during the rainy season, and parched under a scorching sun during 
the dry season. This explains why people traditionally lived in forest galleries 
along main rivers, where soils remain moist throughout the year, and used the 
savannah mainly for seasonal hunting. 

With the rare exception of plantain and cotton farms, Makushi farms are, on 
the whole, bitter cassava farms. cree cassava, igh sweet potatoes, plantains, 
pumpkin or wat | ter-cropped with bitter cassava, but these 
crops are rather marginal. Bitter cassava is consumed daily as farine (u’wi), cas- 
sava bread (kai), fermented drinks (parakiri, kasiri and wo’), casereep (kumast), 
a black, thick paste used throughout Guyana to cook meat and fish, and, finally, 
starch tapioca (imu yanasa) or porridge (Figure 2). 

ach year during the dry season, households clear new farms (ranging from 
400 m_ to more than one hectare) in old fallows or secondary forest, that is, on 
land that has already been used in the past to cultivate cassava. As the main prob- 
lem in farm management is protection of crops from predators and fluctuating 
climate, risk aversion, particularly the risk of flooding and of leaf-cutter ant inva- 
sion, seems to play a greater role than soil fertility in the choice of farm sites. 

Clearing a new farm (mi? ya’ti) is considered hard work, and is exclusively a 
male activity. It was traditionally performed by a man with the help of his rela- 
tives and friends (mayu), in exchange for food or drinks (parakiri or wo’). 
Cooperation in forest clearing now tends to be restricted to immediate kin, for 
example, father and son. New farms are burnt (mii po’ti) in March or April, just 
before the first rains. Fire is propagated with lit kokerite (Attalea regia [Anderson]) 
fronds, a process difficult to control and which may lead to forest fires and crop 


pulled 


see white or creamish 
roots 
scraped 
put in water 
led 
aa sie ne CASERERE 
oe kumasi 
mixed water 
squeezed i 
aerate aE 
; Starch 
night en i arched 
" ——» -TAP 
water + sqWeezed sifted mu yainasa 


starch backed and 


away — 2g Ps pieces \ 
soaked in put i a bucket 
ater of water 
hed 


CASSAVA PARAKARI wo’ drink 
EAD arakiri wo’ 
i 


FIGURE 2.—Processing and products made of cassava by Makushi Amerindians. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 245 


losses when weather conditions are particularly dry. Ground cleaning (mi? kui 
ma), the third stage in preparing a new cassava farm, is undertaken by the entire 
household, children included. The male farmer hoes (ya nu mii) the field, and 
shapes the soil into mounds (locally known as “banks”), in which cuttings (locally 
called “cassava sticks”, kisera in Makushi) are planted (soil mounding, a practice 
rather in Amazonia, is also found in the Upper Xingu [Carneiro 1961]). 

Female farmers, sometimes accompanied by their children, divide the long 
stems of freshly harvested cassava into cuttings. Although they store long stems 
in shady places or keep them for weeks, slightly buried in the ground before using 
them as planting material, farmers prefer to prepare cuttings directly from a living 
plant. Moreover, the selection of cuttings depends on whether a plant is healthy 
and whether it has produced a generous harvest of roots. Cutting the stems is a 
woman’s work, but planting is usually done by men, although this is not always 
the case in other villages (Mary Riley, University of Illinois at Chicago, USA, per- 
sonal communication). Three to five cuttings of the same variety are planted 
together in each mound, pointing to the west. Although most people are aware 
that cuttings planted eastward grow as well as those pointing westward, they still 
maintain that a westward orientation protects the plant from the sun and favours 
its growth. There may be a connection between this belief and the common Makushi 
practice of burying corpses with the feet pointing east, head west, and the face 
looking to the rising sun (data collected by Laura Rival in Massara, April 1997). 
Another common practice observed by Laura Rival in the field, and aimed at en- 
couraging growth and tuber production, is to plant a magical plant (generically 
known as bina in Guyana) in the middle of the field, or to chew the root of such a 
plant, and spit it over the mounds (see also Makushi Research Unit 1996). 

The time it takes a farmer to plant a new cassava farm depends on his avail- 
ability, and on how many stems the household has in stock; it thus varies greatly 
from farm to farm, and from individual to individual. Some farmers plant cassava 
every day for a week, and then stop for two or three weeks before continuing. As 
a result, several months can separate the youngest and the oldest plants in a single 
farm. This practice, as well as the planting of varieties with different maturation 
rates, ensures a constant supply of harvestable roots throughout the year. Cassava 
roots are harvested on average nine months after planting (range: 4 months to 2 
years), and the crop requires little care during this period. A first crop does not 
generally require weeding more than three times, but women may perform spot 
weeding every time they harvest roots (both weeding and harvesting are female 
tasks). 

Roots are harvested when and as they are needed. Stems of freshly harvested 
cassava are sometimes replanted in mounds hoed again for what the Makushi call 
the “second crop.” More commonly, they are taken to a new farm, where the best 
cuttings are selected and planted. The surplus is stored, hidden under kokerite 
fronds, or planted in tight bundles at the edge of the farm. Some may be given to 
neighbours, relatives or friends. Unused stems stored in bundles also grow and, if 
the weather is not too dry, develop tuberous roots nine months after. These roots 
are harvested, but the stems are usually discarded, being used as planting mate- 
rial only if the farmer is desperately short of cuttings. 


246 ELIAS et al. Vol. 20, No. 2 


After harvest, first crop farms are planted with a second crop of cassava. Sec- 
ond crop farms require greater weeding efforts, and their productivity is lesser. 
When harvested, they are not generally hoed again and replanted, except if the 
parcel cleared for the first crop is located in primary rainforest or old secondary 
forest, where the rich, deep forest soil allows for a third, and even sometimes a 
fourth crop. Abandoned farms are soon covered with fast growing pioneer veg- 
etation. Old farms are left fallow for two to twenty years, or more. Although farm 
land is not privately owned, old fallows are customarily left for the use of the 
families who first cultivated them. 

As in most Amazonian societies, cassava processing is the responsibility of 
women, and food intimately connected with gender specialisation. However, it is 
not uncommon to see a man helping his wife making edible products out of bitter 
cassava, which contains a high concentration of cyanogenic glucosides and must 
be detoxified before consumption. Roots are scraped, and the skin and inner peel 
(except in the preparation of parakiri and wo’) removed. They are then washed 
and grated. The grated pulp is squeezed in the long plaited cassava sleeve press, 
known in Guyana as matapi (tinki). To make farine, women first mix fresh grated 
cassava with roots that have fermented for three days, and then squeeze the mix- 
ture. The half-dry pulp is then used for preparing the final products (Figure 2). 
This process ensures that most of cyanide is removed (Dufour 1989, 1995) 

To sum up, the farming system so far described is broadly similar to those 
found among other Amazonian bitter cassava farmers (see in particular Dole 1963, 
1978; Yde 1965; Diniz 1966; Grenand and Haxaire 1977; Hugh-Jones 1978, 1979; 
Carneiro 1983; Dufour 1983; Chernela 1987; Mowat 1989; Van der Hammen 1992; 
Grenand 1993; Emperaire et al. 1998). We are fully aware that the farming system 
we have studied may be a recent development linked to sedentarisation. We sus- 
pect, for instance, that the present shortage of farmland has resulted in sharp 
reduction of fallow periods. This shortage, dramatic in the savannah, where farm- 
ers have to walk for hours or paddle for several days to reach their farms, is 
beginning to affect Rewa as well. Another consequence of sedentarisation is that 
farms must last longer, so people tend to select varieties that can stay in the ground 
longer, such as, for example, the popular “white man stick” that remains harvestable 
two years after planting. 


CASSAVA DIVERSITY AND ITS PERCEPTION BY THE MAKUSHI 


Cassava diversity in one Makushi village — Cassava varieties are distributed in farms 
either in a structured pattern (i.e. planted in contiguous monovarietal patches), or 
at random, the latter distribution being more frequent. Every variety has a Makushi 
name, of which the English translation is usually known. In Rewa, we collected 86 
different names of cassava varieties (Table 1), corresponding to 76 varieties (while 
some varieties given different names by different farmers, f knew 
several varieties under a single name). Varieties that farmers were unable to name 
were not included in the survey. Each household owns on average 16 varieties 
(Table 1). Varieties differ in their frequency of representation among households. 
While some are shared by almost all farmers (for example, paranakiri piye and 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 247 


kuraatuma piye), others are owned by only a few, or even by a single person (for 
example, oronki piye and dominko ye). The equitability index for cassava variet- 
ies is 0.63 (it would be equal to 1 if all varieties had the same frequency in the 
village), and 0.52 for households (it would be equal to 1 if all the households had 
the same number of varieties). No one in Rewa has an accurate or exhaustive know]- 
edge of the varietal diversity present in the village. 

Sweet cassava is planted either in the farm, together with bitter varieties (but 
the two types of roots are not mixed, as sweet cassava is not cultivated for the 
same purpose), or in the kitchen garden next to the house. Farmers say that sweet 
cassava roots develop more slowly than bitter ones, and that the plant grows taller. 
Four different types of sweet cassava, all called kana as opposed to kise (bitter 
cassava), are grown in Rewa. They all have white roots, and are generically re- 
ferred to with English names (“brown stick,” “four months,” “eighteen months,’ 
or “white stick”). The lack of a proper Makushi name confirms that sweet cassava 
is not regarded as “real” cassava; like yam or sweet potatoes, its place in Makushi 
diet is secondary (Makushi Research Unit 1996). Semi-quantitative tests based on 
a colorimetric method using alkaline picrate (Williams and Edwards 1980) con- 
firmed that all varieties designed as bitter by the Makushi have a high cyanide 
content, whereas so-called sweet varieties have a low cyanide content (Elias un- 
published data, see also Dufour 1988). 


Perception of bitter cassava diversity. Makushi lore includes several myths referring 
to cassava and its origin, as well as to Cassava Mother (kisera yan), the master 
spirit that owns the plant, looks after its well being, and ensures good harvests 
(Rival in press). Although myths are complex cultural representations that cannot 
be reduced to one single dimension or message, Makushi myths relating to cas- 
sava clearly convey the idea that this plant exists first and foremost as a cultivated, 
that is, a domesticated or cultural plant, whose inalterable blueprint is the master 
spirit Cassava Mother, and whose origin relates to the transformation of a human 
body. Wild cassava! is represented as a degenerated cultivar escaped from gar- 
dens, which has stopped producing tuberous roots, because it now grows in 
non-cultivated (i.e. non-cultural) spaces, such as hill tops in the savannah. 


Taxonomy.—Savanna-dwelling farmers of mixed origin (i.e. of Makushi and Black, 
locally known as “dougler”), and Makushi who have no direct knowledge of cas- 
sava cultivation, recognise only three kinds of cassava: yellow, cream and white 
varieties. They differentiate them by color and use, as cassava bread is made with 
the roots of white varieties, and farine with the roots of yellow varieties. The first 
morphological trait mentioned by a farmer is the color of the root, and its inten- 
sity. Three main categories are actually differentiated: yellow types, creamy types 
(which non-farmers confuse with yellow types), and white types. This classifica- 
tion, also found among other groups (Emperaire et al. 1998), plays a determinant 
role in evolutionary terms. This may explain why Makushi people tend to under- 
estimate their varietal diversity, and why outsiders are only aware of differences 
in root color. 

Named varieties constitute the second, and more ambiguous, level of classifi- 
cation. Varieties are named after animals, plants, objects, dishes, qualities, and 


Makushi names 


English names 


AM NE WE VA DP JM TA RE JE MA AE DH FW JA CS EK NI WA JH PH CH LE ZP HS 


ainis piye 
aknes piye 
akuriu ye 
amilton ye 
amo’ko piye = 
danal piye 
amuru piye 
ankela piye 
anra piye 
dominko ye 
eti piye 
eni piye 
esekwipo ye 
isman piye = 
sandra piye = 
amuru piye ? 
kaima piye = 
eri piye 
kanaima ye 
karmani piye 
kasiri piye 
kediam piye 


kini’ piye (2 types) = 


reni piye 
ko’ko piye 
kraiwa piye 
kari’na piye 
kompani piye 
krompi piye 
kumia ye 


Inez stick 
agnes stick 
agouti stick 
Hamilton stick 
grand father st. = 
Danal stick 
thick stick 
Angela stick 
crane stick 
Domingo stick 
Eddie stick 
Eni stick 


thick stick ? 
pumpkin stick = 
Ely stick 

jombie stick 
Carmani stick 
kashiri stick 
Kediam stick 
dry stick = 

Reni stick 


grand mother stick 


brazilian stick 
Carib stick 
company stick 
? 


fish stick 


x 
x 
4 
x x 
xX x x 
x 
»« 
x 
x 
x x x 
x 
x 
x x i & 
»4 
x 


Xx 


Meron em 


x 


‘saljtuey FZ Suoure UOTNQL]sIp I1ay} pure “eMay UT puNo}j saateA PARSSeD— [ FIAVL 


Makushi names English names AM NE WE VA DP JM TA RE JE MA AE DH FW JA CS EK NI WA JH PH CH LE ZP HS 
kunani piye fish poison st. x x x 
kuraatuma piye caiman stick 

2 types) ok Se eX ee x oF — 8 Se ee eS Cee ox x 
kurari piye curral stick x ox x x x =x x * i ee a 
kuraswa piye = Crash Water st = 
selia piye = Celia stick = 

waimko piye Waimko st. ae. x x xX oR x x x x x x 
lio piye Lio stick x x 
mai piye bitter stick x x x x x x 

maka piye maggah stick x 

makarpon ye Makar pond stick x 

marasi piye marudi stick x x x x 

mauri piye Mauri stick x x x 
meekoro piye black man stick x x x ek xX x x x 

mepriko ye Elfrida stick x . * 

omano piye Omano stick x 

oronki piye bamboo stick x 

paapa ye father stick x * x 

pakaima ye buffalo stick x x 

pali piye = Bali stick = 

kaiwan piye fat boy st 5 ata aS x x x xo oe x Be 
papiro ye Pablo stick x x Xx x Xx x x x x 
parakiri piye parakari stick x x x x 

paranakiri piye white man stick X XX MOK KX KX KM. K Mee MM ROR ee ke ey lk 
paranakiri piye white man 

itakon ye = stick cousin = 

naman piye Naman stick x x < oN x x x x x 
paranakiri piye white man 

perurupe stick seedling x x 
pinkiu ye peccarie stick ae x Xx Xx x x 
piraun piye Brown stick x 

pirikwa piye = bird stick = 

ipo ye sweet stick x << xs x ee x x x x “os x 


(panunuod) T aqeL. 


AM NE WE VA DP JM TA RE JE MA AE DH FW JA CS EK NI WA JH PH CH LE ZP HS 


Makushi names English names 
pirori piye Pearl stick x 
prona piye brown stick x x 
reki piye thick stick * 
rikitun piye black stick x 
rora piye green stick x Xx x 
sakari piye Zaccharie stick Xx 
saketa piye Sagda stick x 
sapri piye fine fish stick x x se x 
seruak piye 3 months stick x x 
siya piye Shea stick x x x x x x Xx 
siment piye cement stick pe Seay X X Xe ex KUM MS Se ee x x 
siwal piye Sea Wall stick x » 
sona piye Jona stick x x x 
supra piye cutlass stick Xx x x ee ae Mook ee x 
tare’kiya pimoi water turtlle egg 
piye = suyu ye = stick = yellow stick = 
five month stick = 5 months st = 
u’wi piye ? farine stick ? ee ae cae x * a x x 
tari ye black potatoes stick Xx 
tikiri piye ? x Xx 
toni piye Tony stick x 
urakasa ye pigeon stick x x 
usariu ye deer stick x 
u’wi piye farine stick x MM. Xx x Rk Ko x Xx x 
uyara piye macaw stick 
(cassava heart) x x 
waakiri piye I love stick x 
walakise piye Walax stick x 
wo’ ye drink stick Lk eee ae ¥ 


‘(panuryuod) [ a[qey, 


total number of varieties : 76 


10) 4250 4 16s 23 


ol 


14. 22. oe 22. 12. 21. 9. 2 ee a I 


oat 30 2 Oe 


Winter 2000 JOURNAL OF ETHNOBIOLOGY Zl 


according to the place of origin or the person from whom cuttings were obtained. 
Names derived from animals, plants, objects, dishes, and qualities are said to be 
more authentic and traditional than those based on Christian names and toponyms, 
with which they often overlap. For instance, the real name of “Ely stick” is “pump- 
kin stick,” but as the farmer who received it from Mrs. Ely had forgotten the real 
name, she chose to call the new variety after Mrs. Ely. Almost all the inhabitants of 
Rewa speak both Makushi and English, but bilingualism does not seem to affect 
the naming system, given that all Makushi names have an English translation. We 
were told that it is the husband’s, rather than the wife’s, responsibility to give 
names to new varieties. On the whole, the Makushi naming system is similar to 
those used by many other traditional Amazonian groups (Salick et al. 1997; 
Emperaire et al. 1998). 

Visits to various farms with different informants allowed us to confirm that 
farmers use the taxonomic classification outlined above fairly consistently. Eight 
times out of ten, they agree on what name to give to a particular variety. However, 
since the varietal make-up of each farm is different, a farmer visiting a neighbour’s 
farm may be unable to name some of the varieties. We also detected several cases 
of synonymy and of homonymy (Table 1). The first genetic analyses, which are the 
best tools to detect such events, have confirmed these observations (Elias et al. in 
press). 

Accuracy of taxonomy is of great importance in determining evolutionary 
pressures on cassava, since individual human selection acts on taxonomic units, 
locally identified as varieties. The fact that generic terms are increasingly used (at 
least in our informants’ perception) may lead to an impoverishment of the highly 
specific variety vocabulary. For example, a really yellow variety is now commonly 
referred to by the generic term “farine stick” and a variety hard to grate by the 
term “dry stick”, while an increasing number of varieties are called by the names 
of those from whom they were obtained. As a result, a farmer may have two or 
three es of “farine stick,” “dry stick,” or “Bali stick”. However, most farmers 
can still differentiate among homonymous varieties. They can, for example, dis- 
tinguish the “dry stick” with broad leaves from the “dry stick” with narrow leaves, 
and explain these differences accurately to the botanist. But we are not entirely 
certain that they are able to distinguish two morphologically close varieties with 
exactly the same properties, or coming from the same place, if they call them by 
the same name. The consequences of such taxonomic impoverishment are dis- 
cussed below. 


Recognition process.-The Makushi seem to identify their varieties all at once, just as 
they or we identify people we know. Several farmers told us that they cannot name 
a variety before checking the appearance and quality of the roots. This instanta- 
neous and integrative recognition process, which appears to depend entirely on 
the plant phenotype, was first identified by Shigeta (1996), who calls it “face-to- 


face recognition 
Our hypothesis i is s that the qecognition process operates on the basis of an un- 
conscious hi rs. This is best illustrated when a plant 


is hard to identify, because of phenotypic plasticity. The overall aspect of the stem 
is the first character observed, and the most important for defining the identity of 


252 ELIAS et al. Vol. 20, No. 2 


the plant. The next salient traits are, in decreasing order of importance, the aspect 
of the leaves, the color of the petiole, wee — aspect and color of the root, and, 
finally, the flowers. These ol t with those of Boster (1985) 
and of Emperaire et al. (1998). 

While certain varieties are preferred for particular uses, there is much func- 
tional redundancy among varieties, and there appears to be no practical reason 
for having so many varieties of bitter cassava. The Makushi seem to enjoy diver- 
sity for its own sake, and more for aesthetic and recreational reasons, or out of 
scientific curiosity, than for security purposes. Our obser te those 
of Carneiro (1983), who noted that the Kuikuru (Brazil) cantink explain why they 
have so many varieties; they just have them. Makushi farmers also say that they 
do not know, that they simply like seeing many different types of cassava in their 
farms. Like collectors, they seek to cultivate as many varieties as possible. They 
are driven by a deep-seated curiosity that pushes them to acquire new types con- 
tinuously, “to try them out.” This readiness to experiment has real implications 
for the structure and dynamics of cassava diversity. 


THE DYNAMICS OF DIVERSITY 


Cassava diversity is not static, and farmers experience intentional or uninten- 
tional losses of varieties, for which they compensate by acquiring new types. As 
stated before, acquiring new types can also be motivated simply by curiosity. We 
review here environmental and human selective factors involved in the dynamics 
of diversity. 


Environmental selective factors.-Severe droughts and floods are recurring climatic 
conditions which can lead to the loss of varieties, and to which Makushi people 
have learned to adapt. According to our informants and our own observations, 
exceptionally dry weather such as that caused by El Nifio from August 1997 to 
April 1998 kills recently planted and growing cassava alike. Drought affects root 
production, and can destroy all the propagation material. Varieties present in low 
densities, or owned by a few farmers only, are more likely to disappear. The 
Makushi have therefore developed special planting strategies to protect the cut- 
tings from drought, and, to a lesser extent, flood. Farmers, for example, are careful 
to keep in the soil cuttings which, at first sight, look dried-out but which will 
almost certainly sprout again with the first showers. Mounds are reshaped with 
taller profiles, and replanted with six or eight (instead of four) cuttings to maximise 
the chances of having at least two well-developing plants in each. The general 
strategy is to prioritise the long-term reproductive cycle. Rather than saving 
harvestable roots, farmers try to preserve the stems as “germplasm banks”. For 
this, they look for swampy areas, which are under normal circumstances flooded, 
and transport their best stems -sometimes over great distances- from their farms 
to the swamps, to stock them in large bunches there until it rains (Rival 1998). 
Whereas cassava varieties in many parts of South America and Africa are seri- 
ously affected by diseases (cassava bacterial blight, Boher and Verdier 1995; African 
cassava mosaic virus, Fauquet and Fargette 1990), varieties in Rewa do not seem 
to suffer much from disease. However, in 1998, a new plague locally called “white 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 253 


disease” (turere) caused by a small white insect (Aonidomytilus albus, Hemiptera: 
Diaspididae) which kills all affected plants struck all the high forest farms located 
three hours downriver from the village. One family with downriver farms lost all 
its cassava varieties. 

Farmers seem to have many problems with, and often complain about, herbi- 
vores (Table 2). Leaf-cutter ants Atta spp. (“acoushi ants”, kuinan), which often 
destroy entire farms, and are very difficult to get rid of, are identified by farmers 
as the most dangerous predator of cassava. Farmers may decide to abandon a 
farm altogether, rather than try to eliminate ants. Other herbivores feeding on 
leaves usually act sporadically, and rarely kill plants. But their predatory activities 
itla aff fect plant vigour and root , even caus- 
ing roots to become watery. Plants that are frequently attacked by herbivores may 
not be multiplied. The “carelessness” of peccaries and tapirs, which often trample 
and destroy everything when feeding in a farm, may also lead to variety loss. 
Farmers do not seem to be aware of any particular herbivore/variety association, 
and information collected from different farmers regarding perception of varietal 
resistance was contradictory, which could reflect either strong soil/ genotype in- 
teraction for resistance, great variability, or lack of interest in this feature. 


Human selection.—As a cultivated crop, cassava is under intense human selective 
pressure. Vegetative propagation allows for the instantaneous selection of pheno- 
types of interest. Farmers, who can decide whether or not to keep a variety, to a 
certain extent also control the relative frequency of each variety. If there is no con- 
scious selection for resistance te PRES, diseases, or climatic conditions, some 
varieties will , whereas others will decrease in frequency. 
As far as we were able to observe, there i is no directional selection on maturity rate 
either, since farmers need both precocious and late-bearing varieties in order to 
minimise risk and secure a continuous supply of harvestable roots. As scientists, 
we were even asked jokingly to invent a new and improved variety that would 
have such a broad maturity rate spectrum that there would be no need to grow 
any other variety. 


TABLE 2.—Main wild herbivores feeding on cassava in Rewa. 


class of species Makushi attacked importance 
herbivore name parts of damage 
Insects Atta spp. (leaf-cutter ants) kuinan leaves +++ 
Erinnyis ello (larvae of asphinx moth) —arari leaves ++ 
Birds unidentified anakwa leaves + 
Mammals Mazama americana (brocket deer) usari leaves + 
Dasyprocta agouti (red rumped agouti) akuri roots + 
Dasyprocta prymnolopha (black rumped 
gouti akuri roots + 
Agouti paca (paca) urana roots + 
Tayassu pecari (white-lipped peccary) pinki roots +++ 
Tayassu tajacu (collared peccary) piraka roots +++ 


Tapirus terrestris (tapir) waira roots the 


254 ELIAS et al. Vol. 20, No. 2 


Taking up Boster’s (1984a) hypothesis, McKey and Beckerman (1993) suggest 
that the productivity criteria include many other agronomic features. Human se- 
lection for productivity would combine with natural selection for survival and 
resistance. Like other Amazonian cassava cultivators (Boster 1985; Chernela 1987; 
Salick et al. 1997; Emperaire et al. 1998), the Makushi consciously select varieties 
primarily for their productivity. For instance, every household in Rewa has the 
paranakiri piye (“white man stick”) variety, which produces high yields. It is the 
most frequent variety in 17 of the 24 farms included in our census. Yield is, how- 
ever, highly variable among farmers and crops. Some varieties can be very 
productive in the first crop, but do poorly in the second, whereas others, which do 
not have a very high production in the first crop, do well in the second. 

The color of the root is another important criterion for selection. The main 
dish in traditional Makushi diet is cassava bread made with white varieties. But 
when ranchers settled in the Rupununi in the 1930s, demand for farine, a staple 
with which they fed their workers, soared. Farmers responded to the demand by 
preparing increasing quantities of farine, which is made with yellow varieties, 
and they also increased the proportion of farine in their own diet, thus multiply- 
ing yellow varieties at the expense of white ones. This shift from cassava bread to 
farine, and from white to yellow varieties, is widely recognised as a recent phe- 
nomenon (see in particular Yde 1965). People nevertheless say that they like farine, 
which is easy to store and process, and that they want yellow forms, hence their 
eagerness to acquire yellow varieties. Four “really yellow” varieties are found lo- 
cally, of which at least one is cultivated in great quantities. 

Varieties are also selected for their culinary or “processability” properties, but 
these criteria vary greatly from farmer to farmer. Some women we interviewed 
prefer watery roots, which are easier to grate, whereas others liked dry roots, richer 
in starch. Aesthetics also play a role in selection, and a variety with an unusual 
combination of morphological characters undeniably arouses the farmer’s curios- 
ity and interest. 

In addition to selecting varieties according to these criteria, farmers also pro- 
tect rare varieties, thus encouraging frequency-dependent selection. A variety is 
rarely discarded, even if it is not very productive. Low-yielding, rare varieties are 
simply kept at low density (i.e. one or two mounds per farm), and this is consid- 
ered enough to prevent their loss. Farmers explain that they do not like losing 
varieties, for a “bad” variety sometimes becomes “good” under different condi- 
tions. Rare varieties, however, become more vulnerable to loss by direct or natural 
selection. Finally, farmers lose varieties, not only because of environmental pres- 
sures or deliberate choice, but also because of bad space management. As each 
farm is limited in size and contains a finite number of mounds, there is sometimes 
no place left for experimental planting, and cuttings of marginal varieties may no 
longer be available when space becomes available again. If this occurs, the farmer 
has lost this variety. In sum, conscious human selection on cassava varieties is 
rather lax; it acts primarily to preserve diversity, rather than to maintain or aug- 
ment some particular desired traits. 

The exchange of cuttings and the t of volunteer plants grown from 
seedlings, which represent two means of acquiring new varieties or recovering 
lost ones, greatly contribute to the maintenance of cassava diversity. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 255 


Exchange networks. Farmers can recall the origin of all the varieties they have 
in their farms, no matter how far back they have to go. In former times, when the 
rule of uxorilocality and bride service was more generally applied, a young hus- 
band was expected to cultivate with his wife the farm of his parents-in-law, until 
his father-in-law gave him the permission to set up his own farm. The young hus- 
band would then receive a share of cuttings from his father-in-law, a stock which 
he complemented with cuttings brought from the farm of his own parents. The 
young wife would receive cuttings from her mother, sisters, mother-in-law and 
sisters-in law. The couples we interviewed always specified which varieties were 
brought into the conjugal farm by the husband, and which by the wife. 

It is perhaps because a transfer of cuttings is initiated by request from a farmer 
in need that farmers so accurately remember the origin of the cuttings they culti- 
vate. The most general term used to express the idea of transfer is “borrowing.” A 
farmer short of planting material or willing to try a new variety asks another farmer 
for stems, which he or she will “repay” at a later stage with stems of a different 
variety, or with farine or parakiri made with roots from the borrowed varieties. 
Delayed reciprocity has been observed among other Amerindian groups, such as 
the Aguaruna (Boster 1986). There is no specified rule on how long after having 
“borrowed” a farmer must “give back.” The only time when transfers are not re- 
ceiver-initiated, and when there is no pay back, is when a farmer donates cuttings 
to compensate damages, such as the destruction of part of a neighbour’s crops 
through uncontrolled fire. The exchange of cuttings between closely related kin 
and neighbours whose farms are contiguous and who still practice a form of shared 
labour (mayu) is less formal and generalised, in the sense that strict reciprocity is 
not an issue. Only very o lly will a farmer acquire cuttings of a rare variety 
by paying with cash, a cutlass, a bicycle or any other trade item. This type of ex- 
change is more likely to occur between unrelated farmers who do not live, and 
have no family connection, in the village. 

Two types of exchanges, one “massive” and the other “occasional,” can be 
distinguished. Farmers who need large amounts of planting material for a new 
farm borrow cuttings from just a few varieties, which they usually already pos- 
sess, but not in sufficient quantity. Those who want to try out a variety they do not 
have in their farm ask for a stem or two while visiting neighbours, friends or rela- 
tives. Farmers, who are always keen to acquire new varieties, carefully multiply 
the trial cuttings until reaching the desired density. The closer the locality from 
which a new variety originates, the more likely the retention of its real name will 
be. In contrast, a variety coming from a distant locality may be called after a top- 
onym, for example “Shea stick” or “Crash Water stick.” 

In contrast with Chernela (1987), who has reported exchanges over an area 
465 km wide, most Makushi cutting exchanges (and all massive exchanges) occur 
within the village community, in particular among immediate neighbours, who 
are usually related through descent and marriage (unpublished data). Asa result, 
some families never interact, while others are continuously exchanging cuttings. 
Frequent exchanges between the same families are expected to lead to taxonomic 
homogenisation (Boster 1986). According to informants, cuttings were not traded 
across ethnic boundaries in the past, and even inter-village exchanges were -and 
still are- restricted, which, of course, does not exclude acquisition through war- 


256 ELIAS et al. Vol. 20, No. 2 


fare, looting, and the taking over of another tribe’s old farms. Some farmers care- 
fully avoid asking for cuttings, as they derive great prestige from relying on their 
own stocks, while lavishingly giving away to borrowers. Others, who keep their 
farms at a distance, never invite visitors, and share only reluctantly, are consid- 
ered “stingy.” Yet others do not dare asking for coveted cuttings, which they 
surreptitiously pick from the farms of neighbours or hosts (a behaviour which 
may lead to generalised theft in times of drought and starvation). To summarize, 
while some families always experience a deficit of planting material, others al- 
most never borrow cuttings. And whereas some share their surpluses generously, 
others prefer to let their unused bundles of cuttings dry out. When examining the 
social networks underlying ive exchanges, we soon identified “source” fami- 
lies, whose efficient management of cassava production not only prevented them 
from experiencing shortages, but also ensured that they usually disposed of suffi- 
cient planting material to give away. “Sink” families, in contrast, managed their 
stocks poorly, often ran out of cuttings for their new farms, and heavily depended 
on borrowing. “Source” farmers are proud and respected community members, 
with a higher status than “sink” farmers. 

Tepuru piye. The cassava plant grown from spontaneous seedlings. New vari- 
eties are often acquired through the incorporation of volunteer cassava plants 
grown from seedlings, the products of sexual reproduction, that appear spontane- 
ously in farms (Makushi Research Unit 1996). Although cassava has long been 
propagated vegetatively, it has retained its ancestral capacity for sexual reproduc- 
tion. In Makushi farms, most varieties produce flowers, and these produce fruit 
which dehisce at maturity, dispersing their seeds before the plants are harvested. 
Seeds are projected on the ground by exploding capsules, and then secondarily 
dispersed by ants (Elias and McKey in press) and perhaps by other mechanisms. 
Although seed physiology is poorly documented, variable dormancy has been 
reported (N. Morante, Centre Internacional de Agricultura Tropical, Cali, Colom- 

ia, persona ication), and scattered anecdotal observations seem to show 
that preserving a vegetation cover prevents seed germination. 

Seeds germinate whenever a new farm is cut in an old fallow. Spontaneous 
seedlings, tepuru piye (from tepuru, seed) are found in places that were cultivated 
as long as 35 years ago. One farmer even found a tepuru piye plant in a farm he 
had just cleared in a high forest location three hours down river by canoe from 
Rewa, which was, according to oral tradition, last cultivated by a group of Caribs 
more than fifty years ago. He decided to multiply it, and called the new variety 
kari’na piye, “Carib stick.” The surprisingly long dormancy suggested by this 
observation and by Amuesha comments (Salick et al. 1997) can be explained by 
the presence of seed banks along with seed propensity for long survival (Elias and 
McKey in press). Dormancy of seeds from a seed bank must be broken by cues. 
Many light-demanding tropical pioneer species respond to changes in light qual- 
ity or soil temperature regimes following removal of vegetation. In others, 
germination is enhanced by the direct (high temperature) or indirect (higher con- 
centration of minerals in ash) consequences of fire (Garwood 1989). Some of the 
cues that break dormancy of wild Manihot species and cassava seeds have been 
identified; they involve high temperature (Ellis et al. 1982; Nassar and Teixeira 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 257 


1983) and scarification. As seedlings usually start growing before the first cuttings 
are planted, they do not suffer much competition from planted cassava. We have 
yet to gather information on the survival rate of seedlings. Up to 400 seedlings 
have been found in one young crop of 425 m_ (Elias and McKey in press), which is 
the highest density ever reported in the literature (Emperaire et al. 1998 report one 
or two seedlings per farm). 

Farmers pay special attention to plants grown from spontaneous seedlings, 
which they have no difficulty identifying. Although they may compete with, and 
affect the growth of, planted cuttings, seedlings are only rarely weeded, and usu- 
ally left to grow until they reach maturity. Like common varieties, they are harvested 
and their roots processed. If the farmer is satisfied with the yield, the color of the 
root, and any other characteristic, the stem is divided into cuttings which are soon 
replanted and multiplied in a specific location. If the tuberous roots are found 
unsatisfactory, the stem is generally discarded, although farmers keen to experi- 
ment clone it, hoping that it will become more productive after one cultivation 
cycle. Tepuru piye are thus multiplied over generations of planting, and, since they 
often present novel combinations of morphological characters, are usually treated 
as new varieties. Naming these new phenotypes is not easy. Audacious farmers 
create appropriate names, such as, for example, Mr Nathaniel Edwards in Rewa, 
who, without hesitation, named a “very yellow” variety from a spontaneous seed- 
ling “I love stick” (waakiri piye). Most farmers, however, take the view that all 
varieties are pre-existent, each with a fixed name, and SO prefer not to invent new 
names. Consequently, they keep the non-sp 1 piye, which 
they apply to different phenotypes. 

When the characteristics of a seedling closely match those of a known variety, 
the seedling, assumed to have grown from the seed of this particular variety, is 
assimilated to, and named after it (adding the term perurupe, such as in paranakiri 
piye perurupe, “seed of white man stick”). Seedlings which are considered en- 
tirely identical to a known variety are treated exactly like any other member of 
this variety. In the field, we were able to document four cases of such pseudo- 
reappearance of a known variety from a seedling. However, we suspect the 
frequency of complete assimilation of seedlings to known varieties to be much 
higher. Whereas it is easy to put one cutting aside in order to multiply a given 
variety, this is not the case when a great number _ cuttings from the same variety 
have to be distinguished, hence tl the onfusion and unintentional mix- 
ing of cutti rom seedlings with cuttings from pre-existing varieties. 
Farmers may not tii the seedling origin of particular stems, if the morpho- 
logical characteristics of the latter are not sufficiently distinctive. Some of the 
farmers we interviewed were sacra? aware of making mistakes when identify- 
ing varieties, and of t including new seedling pl thin known 
varieties. The assimilation of erik from seedlings into known aeetern is one of 
the reasons for intravarietal genetic diversity in cassava grown by the Makushi 
(Elias et al in press), which is associated with intravarietal phenotypic diversity. 
Adding to the frequency of such confusion between similar varieties is the fact 
that the phenotypes of a given variety also vary with environmental factors. 

Obtaining quantitative data on the incorporation of sexually produced indi- 


258 ELIAS et al. Vol. 20, No. 2 


viduals into the stock of material for vegetative propagation was extremely diffi- 
cult. One farmer, a highly respected widow with a level of education above average, 
told us that in the high-forest farms cultivated by her husband and herself over a 
period of 15 years, cuttings from seedlings came to represent 30 per cent of the 
varieties grown, against 15 per cent for the varieties with which they planted the 
first farm in the area, and 55 per cent for the varieties they acquired through ex- 
change with neighbours and relatives. We do not know whether this case is 
exceptional or representative. One would expect to find many varieties derived 
from seedlings in every farm, given the high density of seedlings growing in cas- 
sava farms, and the information volunteered by farmers, who say they multiply 
most of the tepuru piye they find in their farms. However, when asked for the 
varieties previously multiplied from tepuru piye, farmers only name on average 
one or two (the maximum was eight). Such a contradiction can be explained by 
the aforementioned phenomenon of assimilation of tepuru piye into other variet- 
ies. Another possible explanation is that these varieties, which are represented by 
a small number of individuals in the first generations, are easily lost. Besides, their 
identification requires a special memorisation effort on the part of farmers. 

edlings are not only the sole source of novel genotypes; they are also, at 
times, the only source of cuttings. In 1950, as reported by many old people, farm- 
ers in the savanna experienced a very severe drought, which lasted almost two 
years. Their crops dried out, and they soon ran out of planting material, which 
they recovered by clearing old farm locations, where seeds germinated, providing 
them with new stocks of cuttings. 

Local wisdom, according to which cuttings produce individuals simil hose 
from which they come (i.e. identical genotypes), is contradicted by the behaviour 
of tepuru piye, which rarely reproduce the characteristic features of the particular 
varieties from which the seeds originate, but display instead novel or unusual 
combinations of traits, due to recombination in a genome that is very heterozy- 
gous (Colombo 1997; Lefévre 1989), a property enhanced by allogamous 
reproduction (Rogers 1965). Makushi farmers, who find the unusual trait combi- 
nations of seedlings quite puzzling, explain them by presuming that a seed from a 
given variety, because of its small dimensions, is influenced by other varieties af- 
ter falling to the ground, and denatured. 

This perception may in turn explain why they never plant cassava seeds, but 
propagate clones of tepuru piye, despite their knowledge of seed planting, a tech- 
nique commonly used to grow crops such as papaya and corn. It may also explain 
why farmers never give away cuttings from spontaneous seedlings, but only cut- 
tings from third or fourth generation clones, which they have replanted in various 
types of soil, and observed. In any case, cuttings from tepuru piye are greatly ap- 
preciated for their “vitality,” their “youth.” As one farmer told us, normal cuttings 
(i.e. clones) get too “accustomed to the soil,” they are too “tamed,” and end up 
producing less and less, while cuttings from spont seedlings often produce 
increasingly better yields (see Rival [in press] for further disetiseicns af cultural 
representations associated with tepuru piye). 


Winter 2000 JOURNAL OF ETHNOBIOLOGY ooo 


DISCUSSION 


Makushi cassava diversity i in ~~ nEZON context.—Bitter cassava is the staple crop of 
most lowland A , and the Makushi, who possess at least 76 
varieties, are no exception. This high varietal diversity is comparable to the diver- 
sity encountered in other groups. Grenand (1993) counted 31 bitter varieties in a 
Wayapi community in French Guiana, and Carneiro (1983) 46 among the Kuikuru 
of Brazil; Emperaire et al. (1998) found 61 bitter varieties in one caboclo village, 
and a total of 140 names among all the villages they studied; Dufour and Wilson 
(1996) found more than 100 varieties among Tukanoans from Yapu in Colombia, 
and Chernela (1987) collected 137 different names among four communities along 
the Uaupés river in Colombia. A comparable level of diversity is encountered 
among sweet cassava farmers: 117 names were collected by Salick et al. (1997) in 
16 Amuesha communities, and more than 100 by Boster (1984b) among the 
Aguaruna in Peru. 


Genetic implications of traditional management.—Despite its peculiarities, the Makushi 
farming system, which shares many features with other native Amazonian cas- 
sava farming systems (slash-and-burn agriculture, strong ooiasapuepeia=iim pressure, 


conservative human selection, planting system, of seedlings, and so 
forth), can be used as a model to study the genetic ‘consequences of traditional 
management. 


sava, which grows in an ecosystem shaped by both environmental and 
cultural factors, is the target of two interacting types of selection, natural and hu- 
man. Human selection is either conscious or unconscious. Genotypes constitute 
ultimately the units of selection in both natural and unconscious human selection. 
In the case of deliberate human selection, however, the units of selection are the 
taxonomic units. One taxonomic unit can include several genotypes, given the 
assimilation into a single variety of different clones with similar phenotypes and 
of plants of sexual origin. If a farmer decides to multiply such a heterogeneous 
variety, she or he may multiply not only one genotype, but several, while, at the 
same time, taking the risk of losing other genotypes, because (1) genotypes shar- 
ing the same phenotypes are indistinguishable, and (2) no special effort is made to 
maintain all the intravarietal phenotypic variation (Boster 1985). 

Although human and natural selection have distinct origins, they neverthe- 
less act as similar agents of evolution (Salick 1995), and may even interact. Human 
deliberate selection on features such as productivity can be superimposed on, and 
reinforce, natural selection. In a given environmental context, selection for pro- 
ductivity can constitute selection for resistance to drought, herbivory, or other 
ecological factors (Johns 1990; McKey and Beckerman 1993). To understand the 
observed patterns of varietal diversity, therefore, both natural and artificial selec- 
tion must be taken into consideration. 

What are the consequences of natural and human selection, and of their inter- 
action, on genetic diversity? Pressures may either increase or decrease varietal 
diversity. At the farm and community level (intervarietal diversity), environmen- 
tal pressures may lead to local or short-term decreases in varietal diversity. Varieties 


260 ELIAS et al. Vol. 20, No. 2 


can be lost, for example, during a flood or after ant attacks. Human selection may 
also lead to decreased diversity, when a variety is accidentally lost because of lack 
of suitable space to plant it, or when it is deliberately discarded. Since criteria for 
discarding a variety are mainly based on productivity, human selection acts, in 
this case, in the same direction as natural selection. 

Human selection can also increase varietal diversity. Makushi farmers tend to 
favour new varieties that are more liable to disappear, for they are represented by 
a few individuals only. Since the environment is highly variable and unpredict- 
able, natural selection will not always favour the same genotypes. Makushi 
appreciation of diversity for its own sake leads them to keep many varieties, even 
if they are not currently very productive. Although this is not an explicit, deliber- 
ate strategy, the result is possession of a varietal pool globally resistant to many 
kinds of pressures. 

Unlike most tuber crops, cassava is propagated by stem cuttings, a material 
different from the edible part. The absence of use competition between material 
for propagation and for food enables farmers to be more selective about what is 
planted. With exchanges of planting material occurring widely among villagers, a 
variety accidentally lost in a farm is easily recovered, and the risk of losing variet- 
ies greatly diminished within the community. Such exchanges also allow farmers 
to acquire new varieties and increase their own varietal diversity. Furthermore, 
exchanges taking place between different communities lead to increased diversity 
at the village level. Intervarietal diversity is further increased with the multiplica- 
tion of volunteer plants grown from seedlings, tepuru piye, which create new 
genotypes. Aside from somatic mutations, probably of rare occurrence, tepuru piye 
are the only source of original diversity. 

Compared to many other Amazonian groups, the social context of Makushi 
farming is favourable to a high degree of varietal diversity. Firstly, in the Makushi 
farming system, each household manages varietal diversity on its own farms. In 
contrast, the Amuesha (Salick et al. 1997) delegate the management of diversity to 
their shamans, who not only must grow many more varieties than other farmers, 
but who are also responsible for experimenting with the plants grown from seed- 
lings. Such a centralised system based on a reduced number of specialists may 
have the advantage of ensuring a more homogeneous redistribution of diversity, 
but it is far more vulnerable. Secondly, and although they are said to be accultur- 
ated, having been converted to Christianity (but see Butt-Colson’s [1967] work on 
Pemong and Akawaio millenarist movements) and having lost many of their cus- 
toms and traditions, the Makushi have preserved a strong sense of collective 
identity and have maintained their traditional subsistence agriculture. Makushi 
choices on whether or not to plant a given variety, and on the frequency of plant- 
ing each variety, are still personal choices which are not yet dictated by the market 
economy or any other external factors. Their situation differs from that of 
detribalised and socially destabilised Tukanoans described by Grenand (1993), who 
have lost their knowledge of cassava cultivation and processing, a loss that has 
led to a dramatic impoverishment of cassava diversity in Tukano land. Thirdly, 
Rewa and other Makushi forest villages are not subjected to market forces. Vari- 
ous authors (Salick et al. 1997; Emperaire et al. 1998) have shown that markets 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 261 


push farmers to increase productivity and to cultivate a restricted range of com- 
mercial varieties, furthering the tendency to grow rine Ae varieties at 
the expense of rarer varieties that may, as a result, get lo los 

We have presented the ways in which intervarietal tic diversity is shaped 
by environmental and human pressures. But what are the genetic consequences at 
the intravarietal level? Scientists studying cassava genetic diversity commonly 
assume that varieties are clonal, because they are propagated vegetatively. How- 
ever, the incorporation of sexually produced cassava in a variety, and more 
generally, the confusion between two types of cassava that have similar pheno- 
types, lead to intravarietal genetic diversity (Colombo 1997, Elias et al. in press). 
Intravarietal diversity is observed despite the fact that each variety is subject to a 
phase of intense genetic bottleneck, when cuttings are selected for the next gen- 
eration. Since an adult plant can provide from two to fifteen cuttings, a farmer 
often has too many cuttings to plant, except when he or she is planting a new 
farm. Surplus cuttings may be given to neighbours or relatives who need them, 
pe the bulk is simply planted in large bundles at the edge of the farm. These 

ttings are functionally ‘dead,’ since they will either die out, or grow without 
being replanted. In other words, only a small prepernen of individuals in each 
variety fF tes in producing {1 5 be elimi- 
nated in this way through genetic drift, leading to a decrease of intravarietal genetic 
diversity at the farm level. Observed intravarietal diversity (Elias et al. in press) is 
thus the result of the balance between the frequency of confusion of plants sharing 
similar morphological characters, and the strength of genetic bottlenecks. 


CONCLUSION 


The results presented here illustrate the ways in which selective pressure is 
exercised by various socio-cultural factors. This study should be regarded as a 
first step in the proposed integrative approach, which will be used as a background 
for understanding forthcoming results of genetic analyses and ecological experi- 


ments. 
NOTES 


1 The put wild relative of cultivated cassava Manihot escul bsp. flabellifolia (Olsen 
and Schaal 1999) is not found around Rewa, but small sh aa exist around other vil- 
lages in the savannah area (at least 75 km away from Rewa). Wild cassava (kwana) cut- 
tings are not planted, nor are the tuberous roots used, although old people in the savanna 
report having eaten mixtures of wild cassava and cultivated caspave roots during times of 
starvation in the 1950s. Genetic data (Elias et al., in f flow from wild 
cassava is not a significant evolutionary factor in cultivated etn eee in Guyana, and 
that the local wild gene pool has contributed little to the diversity of the cultivated pool. 


ACKNOWLEDGEMENTS 


We wish to thank th tofG and ially the Ministry of Amerindian 
Affairs and the Environmental Protection Agency, for vessel us to carry out our fieldwork 
in Guyana. This study was supervised by the European Commission (DGVIII, Avenir des 


Peuples des Foréts Tropicales Programme), which provided funds for fieldwork, and also 


262 ELIAS et al. 


Vol. 20, No. 2 


supported by grants from the French government (Ministére de la Recherche et des 

Techniques, Bureau des Ressources Génétiques and Centre National de la Recherche 
Scientifique). We acknowledge the National Agronomic Research Institute (Georgetown, 
Guyana), the Amerindian Research Unit of the University of Guyana, the Conselho Indigena 
do Roraima, Ari Weiduschat, Dr. Carlos Borges and Victor Luria for their help. Many thanks 
to two anonymous reviewers, whose comments greatly improved this manuscript. Our 
greatest debt of gratitude is to the Makushi Amerindians of Rewa, Massara, Annai and 
Toka, for their hospitality and their kind participation in our study. 


LITERATURE CITED 


BOHER, B. and V. VERDIER. 1995. Cassava 
bacterial blight in Africa. The ee of 
knowledge and _ implicati for 
designing control ec nae Aidican 
Crop mene Journal 2:1- 

BOSTER, J. S. 1983. A comparison of the 
diversity of Jivaroan gardens with that 
of the tropical forest. Human Ecology 
11:47-68. 

. 1984a. Classification, cultivation, 
and selection o cultivars of 
Manihot esculenta (Euphorbiaceae). 


. Advances in 
. The New York 
setae eplan ee York. 
ee b. Inferring decision making 
from (erases and behaviour: = 


selection. Human Ecology 12(4): 343-358, 
Ee. SeleCUON Or Aig we 
distinctiveness: Evidence 


iL 


Economic gees! 39: 310-25 
Exchange of varieties and 
information be tween Aguaruna manioc 
cultivators. American Anthropologist 
88(2):428-436. 
BRUSH, S., R. KESSELI, R. ORTEGA, P. 


Conservation Biology 9(5):1189-1198. 
BUTT-COLSON, A., 1967. The birth of a 
religion: The origins of a semi-Christian 
religion among the Akawaio. In Gods 
and Rituals: Readings in Religious Belief 
and Practice, J. Middleton (editor). 
Natural History Press, New York. 


CARNEIRO R. L., 1961. Slash-and-burn 
cultivation among the Kuikuru and its 
implications for cultural development 
in 


Consequences, J. Wilbert (editor). 
Sociedad de Ciencias Naturales La Salle, 
Caracas. 

. 1983. The cultivation of cassava 
among the Kuikuru of the Upper Xingu. 
Pp. 65-111 in Adaptive Responses of 


ative Amazonians, R. B. Hames and 
W. T. Vickers (editors). Academic Press, 
New York. 


CHERNELA, J. M. 1987. Os cultivares de 


Histérico-Antropolégica 1. Centro de 
Informacao Diocese de Rordima, Boa 
Vista. 


CIR. 1993. Os indios no futuro de Roraima. 
Conselho Indigena de Roraima, Boa 
Vista. 


COLOMBO, C. — bite de la diversité 
génétique aniocs américains 
(Manihot Souinte Crantz) par les 
marqueurs moléculaires (RAPD et 
AFLP). Unpublished PhD dissertation, 

NSAM, Montpellier. 

DINIZ, E. S. 1966. O perfil de uma situacao 
interétnica. Antropologia. Boletim do 
Museu Paraense Emilio Goeldi 31:1-31. 

DOLE, G. E. 1963. Techniques of preparing 
manioc flour as a key to culture history 
in ps nee Spain Pp. 241-248 in Man 

nd Cult , A. Wallace (editor). 
Canvegay OE Pennsylvania Press, 
Philadelphia. 


Winter 2000 


—___—. 1978. The use of cassava among 
the Kuikuru: Some interpretations. Pp. 
217-247 in The Nature and Status of 
Ethnobotany, R. I. Ford (editor). 
Anthropol. Pap. Mus. Anthropol. Univ. 
Michigan 67. 

DUFOUR, D. L. 1983. Nutrition in the 
Northwest Amazon: Household pee 
intake and time-energy expenditure. Pp. 


Native: Amazcnanis, &. B. H 
W.TA ). Academic Press, 


New York. 

5. Manioc as a dietary staple: 
implications for the budgeting ut = 
and en n the northwest Am 


Schwerin (editors). Gordon and Breach, 
New wee 

8. Cyanide content of cassava 
are esculenta, Euphorbiaceae) 
cultivate use sed by fukanoan Indians in 


Z 


42: epi 
. 1989. Effectiveness of cassava 
detoxification techniques used by 
indi in Northwestern 
Amazonia. Interciencia 14(2): 88-91. 
aS els i A closer look at the 
nutritional li 


Laooa 


of Amazon 


(editor). The University of Arizona 
Press, Tucson & London 
and W. M. WILSON. 1996. La 


douceur de Pamertume: une 
P| 


par les Indiens Tukano ‘ ‘Amazonie. Pp. 
1231-1238 in L’alimentation en Forét 
Tropicale: Interactions Bioculturelles et 
Pp, as eS my, 1 4 — 


M. Hladik, A. Hladik, H. Pagezy, O. F. 
Linares, G. J. A. sob a ey Froment 
(editors). UNESCO, P. 

ELIAS, M., and D. Mc KEY. th Press. The 
unm managed reproductive ec ecology o 
domesticated plants i in traditional 


cassava “and a call for data. Acta 
Oecologica 


JOURNAL OF ETHNOBIOLOGY 263 


ELIAS, M., O. PANAUD, and T. ROBERT. 

ess. Assessment of genetic 

variability in a traditional cassava 

(Manihot esculenta Crantz) farming 

markers. Heredity. 
D. G and E. 

ROBERTS. 1982. An investigation of the 
influence of constant and alternating 
temperature on the germination of 
cassava seed using a two-dimensional 
temperature gradient plate. Annals of 
Botany, 49:241-246. 

EMPERAIRE, L., F. PINTON and G. 
SECOND. 1998. Une gestion dynamique 
de la diversité variétale du manioc en 
Amazonie du Nord-Ouest. Nature, 
Science et Société 6(2):27-42. 

FARABEE, W. C. 1924. The Central Caribs. 
Museum of ee Publications 
10. University of Pennsylviana, 
Philadelphia. 

FARAGE, N. 1991, As muralhas dos sertoes. 
Os povos indigenas no Rio Branco e a 
colonizacao. Paz e Terra, Sa6 Paulo. 

FAUQUET, C. and D. FARGETTE. 1990. 
African cassava mosaic virus: etiology, 
epidemiology and control. Plant Disease 
74:404-411. 

GARWOOD, C. N., 1989. Tropical seed 
banks: a review. Pp. 149-209 in Ecology 
of Soil Seed Bank, M. A. Leck, 
Parker and R. L. Simpson (editors). 
Academic Press, London. 

GRENAND, F. 1993. Bitter manioc in the 
lowlands of tropical America: from 
myth to commercialisation. Pp. 447-462 
in Tropical Forests: People and Food, C. 
a a A. Hladik, H. Pagezy, O. F. 

G. J. A. Koppert and A. Froment 

(eto. ee Paris. 
sarin HAXAIRE 1977. 
Monograph oi abattis Wayapi. Jatba 
24(4):28 
EM aa rs ae a ree! we and 
a. Pp. 39- 

ea a 

Roraima, P. Furley (editor). Routledge, 

New York. 

. 1995. Red Gold: The Conquest of 
the Brazilian Indians. Revised edition. 

Harvard University Press, Cambridge. 


264 ELIAS et al. 


pee ones C. 1978. Food for thought. 
tterns roducti and 


pene in Pira-Parana society. Pp. 
41-66 in Sex and Age as Principles o 
Social Ddifferentiation, J. Lafontaine, 
(editor). Academic Press, sccm 

. 1979. From the Milk River: Spatial 
and Temporal Processes in Saahles: 
Amazonia. Cambridge University Press, 


Cambridge. 

JOHNS, T. 1990. With Bitter Herbs They 
Shall Eat It. Chemical Ecology and the 
Origins of Human Diet and Medicine. 
University of Arizona Press, Tucson. 

LEFEVRE, F. 1989. Ressources Génétiques 
et Amélioration du Manioc, Manthot 
esculenta Crantz, en Afrique. Thése, 
IN aris. 

LOUETTE, D. A. CHARRIER and J. 
BERTHAUD. 1997. In situ conservation 
of maize in Mexico: genetic diversity 

and maize seed management in a 
traditional oo Economic 
Botany 51(1):20- 

USHI RESEARCH UNIT. 1996. 
Makusipe Komanto Iseru (Sustaining 
oo Way of Life). (Ed. J. Forte). 
Report of a _ research project 
soya eee for sven 
International Rainforest Program 
North Rupunini District Development 
Board, Georgetown, Guia 

MCKEY, D. and S. BE CKERMAN. 1993. 
Chemical ecology, plant evolution and 
traditional caceava cultivah ra 


Pp. 83-112 in L’alimentation en Forét 
Tropicale: Interactions Bioculturelles et 
D, eet 1 Ti 1 4 cc 


M. Hladik, A. Hladik, H. Pagezy, O. F. 
Linares, G. J. A. Koppert and A. Froment 
(editors). UNESCO, Paris. 

MOWAT, L. 1989. Cassava and Chicha. 
Bread and Beer of the Amazon Indians. 
Shire Publications, Aylesbury. 

NASSAR M. A. N. and R. P. TEIXEIRA. 
1983. A cuca da dorméncia da 
semente das espécies selvagens da 

andioca, Manihot spp. Ciéncia e 
Cultura co 630-632. 

OLSE B. A. Sage aioe 
Selec. on he ori cassa 
Phylogeography of Manihot ayy 
Proceedings of the National Academy 
of Science 96:5586-5591 


Vol. 20, No. 2 


QUIROS, Cc. E., $B. BRUSH, D.S. 
DOUCHES, K. S. MERER and G. 
HUESTIS. 1990. Biochemical and folk 
assessment of variability of Andean 
cultivated potatoes. Economic Botany 

-266 

RENVOIZE, B. S. 1972. The area of von 
of ss a as a crop plant —a 
review vidence. Eeaciotiae 
Botany 26: 352-360. 

RIVAL, L. 1998. El Nifio Crisis in the North 
Rupununi Savannas of Guyana. APFT 
Briefing Note 18. European Union, DG 
VILL, sr 

i aN press: Seed and clone. oa 


oe cultivation. In rarely as 
Visible d the Material: the 
Amerindianization of Society in the 
Work of Peter Riviere, L. Rival and N. 
Whitehead (editors). Oxford University 
Press, Oxford. 

RIVIERE, P. 1963. An ethnographic survey 
of the Indians on the divide of the 
Guianese and Amazon river systems. 
Unpublished PhD thesis, University of 
Oxford, Oxford. 

ROGERS, D. J. 1965. Some botanical and 
ethnological considerations of Manihot 
esculenta. Economic Botany 19:369-377. 

SALICK, J. 1992a. 


ana fo = 0 2 
Cmsarviiies of Neotropical Forests: 
Working with Traditional Resource Use, 
K. Redford and C. Padoch peered 
Columbia ose Press, New 

92b. Crop domestication pus 
the evolutionary npoaed of cocona 
(Solanum _ sessiliflorum Dunal) 
ceoner ers Biology 26:247-285. 

—_—__—. 1995. Toward an integration of 
evolutionary ecology and economic 
botany: Personal perspectives on plant/ 
people interactions. Annals of Missouri 
Botanical Garden 82:25-33. 

—_——— ., N. CELLINESE and S. KNAPP. 
1997. Indigenous diversity of cassava: 
Generation, maintenance, use and loss 
among the Amuesha, Peruvian upper 
Amazon. Economic Botany 51(1):6-19. 


Winter 2000 


—__——.. and L. MERRICK. 1990. Use and 
maintenance of genetic resources: Crops 
and their wild relatives. Ae es in 
Agroecology, C. R. Car 
Vandermeer and P. M. Ribcset (editors). 
McGraw-Hill, New York. 

SANTILLI, “s pages 1994. As Fronteiras 
da Repub Historia e Politica entre o 
Macuxi no Vale do Rio Branco. NHU- 
USP, FAPESP, Sao Paulo. 

SHIGETA, M. 1996. Creating landrace 
diversity: the case of the Ari people and 
Ensete (Ensete ae in Ethiopia. 
Pp. 233-268 in Redefining Nature: 
Ecology, Culture and Domestication, R. 
F. Ellen and K. Fukui (editors). Berg, 
Oxford. 

SOUZA, Vij: J: BAIN; Cx ‘SILVA;: VV: 
BOUCHET, A. VALERA, E. MARQUEZ 
and E...: EGUIARTE.....1997, 
ee Do agricultural 
practices modify the population 
structure of the nitrogen fixing bacteria 
Rhizobium etli biovar phaseoli? Journal of 
Ethnobiology, 17(2):249-266. 


JOURNAL OF ETHNOBIOLOGY 265 


VAN DER HAMMEN, M. C. 1992. El 
nejo del mundo: naturaleza y 
sociedad entre los Yukunas de la 
Amazonia Colombiana. Estudios en la 
Amazonia Colombiana IV. PhD 
dissertation. Tropenbos Colombia, 
ogota. 

WILLIAMS, H. J., and T. G. EDWARDS. 
1980. Estimation of cyanide with 
Alkaline Picrate. Journal of Sciences of 
Food and Agriculture 31:15-22. 

YDE, J. 1965. Material Culture of the Wai- 


a 
ZIMMERER K. i 1991. The regional 


in hi ighlan e Peru. 
Biogeography, 18:165-178. 


Journal of 


266 BOOK REVIEWS Vol. 20, No. 2 


Utilizacién y conservacién de los ecosistemas terrestres de México, pasado, 
presente y futuro. Antony Challenger with the collaboration of Javier Cabal- 
lero. Comisién para el Conocimiento y Uso de la Biodiversidad; Instituto de 
Biologia, Universidad Nacional Auténoma de México; Agrupacion Sierra 
Madre, S.C. 1998. 847 pp., maps, diags., photos, refs., and index. Paper. ISBN 
970-9000-02-0. 


In the preface of this book Antony Challenger explains how he set out to write 
this enormous tome. As he describes it, only someone young (he was 26), enthusi- 
astic, and inexperienced would have accepted the challenge to write a single boo 
that was both sufficiently detailed and broad enough in scope to serve as a basic 
text on conservation in Mexico. It took him seven years and 847 pages. The result 
is an extensive and invaluable overview of the political and cultural ecology of 
biodiversity in Mexico. 

The book consists of an introduction, a four-chapter section on the history of 
human uses of ecosystems, six chapters covering the biogeography, ecology, and 
human uses of the main terrestrial ecosystem types, and a conclusion addressing 
sustainable development in Mexico. 

the introductory chapter, Challenger e> thei f biodiversity, 


<pla 
summarizes the threats to biodiversity in Mexico, /and describes how indigenous 
and traditional farmers continue to make important contributions to Mexican 
biodiversity through, Se pia processes _ fee Sil ges. and adaptation of exist- 
ir lg crop varieties to d human needs. Specific topics include 
species relationships, co-evolution, ial: selection and the major activities threat- 
ening biodiversity in Mexico. In contrast to the destruction of Mexican ecosystems 
under modern production techniques, indigenous agricultural activities enhance 
biodiversity through ongoing processes of domestication and diversified produc- 
tion systems maintaining a heterogenous landscape. 

Chapter Two covers “primary production and the conservation of natural re- 
sources” from the Pleistocene to the Spanish Conquest, including the origins of 
agriculture in Mexico, and the agricultural basis of several pre-Columbian civili- 
zations in Mexico. Chapters 3, 4 and 5 address the Colonial period, independence, 
the Porfirian dictatorship, and modern Mexico from 1910 to 1994. Each of these 
chapters concludes with a map of Mexico illustrating the general distribution of 
agricultural, grazing, forestry, mining, and industrial activities and the ever-grow- 
ing extent of alterations to natural ecosytems. 

These chapters take a cultural ecology perspective in which society and na- 
ture are interwoven. For example, the culture of the Maya encompasses their 
agricultural systems and settlement patterns, and these have repercussions on 
vegetation and wildlife. In the same way, environmental Ananee alec syed 
and a number of theories for the collapse of M s hin 
ronmental change. In his discussion of the conquest, Challenger dieactibes a process 
of cultural and ecological transformation in Mexico following the introduction of 
new species, including human pathogens like small pox and scarlet fever. In the 
chapter covering modern Mexican history, as addresses the environmen- 
tal implications of topics such as land reforms, import substituti 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 267 


tropical colonization and the promotion of cattle ranching, agricultural policies, 
the debt crisis, and finally neoliberalism. 

Historically and currently, Mexican d ] tst ies are Pi amt 
Furthermore, they are actively destroying the bases from which Mexico could con- 
struct a sustainable development alternative. One of the greatest ‘eipailies of the 
Spanish Conquest and colonization, for example, was the loss of indigenous tech- 
nical knowledge, agricultural techniques, and perhaps crop varieties. These 
disappeared with the drastic re-organization of production around European plants 
and animals, mining, and export crops like dyes and sugar, and the collapse of 
indigenous populations. Currently, the North American Free Trade Agreement 
continues the process by pitting Mexico’s small-scale indigenous maize farmers 
against enormous and heavily subsidized agro-industries in the United States and 
Canada. 

After setting out the human history of land use in the first 250 pages of the 
book, Challenger is ready to describe the current situation of primary production 
and conservation and vegetation types. Chapters 6 through 11 focus on specific 
ecological zones. Topics include the sources of various taxa, profile drawings of 
different forest types, and descriptions of the main ecological processes shaping 
these ecosystems, such as forest succession. Challenger provides long lists of cur- 
rent and suggested protected areas in each of the five major ecosystems. Most 
importantly, each chapter mapas indigenous and modern systems of manage- 
ment in each ecosystem 

The final chapter cakes the value of indigenous technical knowledge and 
traditional environmental management systems. In contrast to green revolution 
agricultural techniques that homogenize the environment, rely on unsustainable 
chemical and fossil fuel energy inputs, deplete soil and water, poison people and 
face real risk of collapse, traditional agricultural systems maintain environmental 
heterogeneity and often have proven sustainability. Ethnoecology, therefore, has 
an important role to play in the search for sustainable environmental manage- 
ment. 

Challenger argues that sustainable development in Mexico requires the con- 
servation and intensification of traditional farming systems, including serious 
efforts to rehabilitate soils and forests. This, in turn, requires a radically different 
development strategy, one based on food self-sufficiency, not the current “market 
logic” of importing grains. Sustainable development requires a paradigm shift, a 
la Kuhn. A drastic change in thinking should accompany a global redefinition of 
— — to pensiautonemous national economies trading as equal 
partners. In Mexi t t would also require land reform, es- 


scala directed sans cattle ranches i in tropical zones. 

n his final paragraph, Challenger writes that the biggest challenge is not 
how to manage natural resources, but rather how to manage ourselves. This is the 
weakest aspect of the book. The power relations behind the market structures and 
government policies he criticizes remain opaque. In a brief section on plantation 
ba. for example, Challenger does not address the issue of how these subsi- 

benefit t lintegrated pulp and paper companies 
and fail to “reach the small-farmer actors he expects to use them to restore de- 


268 BOOK REVIEWS Vol. 20, No. 2 


graded environments. Similarly, he is very optimistic about the ability of biotech- 
nology to play a role in improved traditional systems, without considering the 
goals of the actors behind most biotechnology research. 

In another example of the book’s relative weakness on social issues, Chal- 
lenger calls for the establishment of more parks and the funds to delineate and 
patrol them as part of a broader process of ecological zoning and land use plan- 
ning. The United States park system remains a model suitable for emulation (p. 
785). He does not address the state of conservation within existing Mexican parks, 
nor the compelling and difficult issues of social justice, cross boundary, and other 
people management issues in Mexico’s parks, many of which are inhabited and 
nearly all of which are heavily used. 

Conversely, though, - description of Maxine’ s ecosystems, their natural his- 
tories, human impacts, an strategies omprise the strength 
of the book. Challenger ae ‘the value of ethnoecology for sustainable 
development, clarifies the cultural and ecological destructiveness of past and 
present development policies, and identifies potential techniques for better man- 
agemen 

Unfortunately, the book’s size and organization dilute these compelling mes- 
sages. The book would have benefited from better editing. The conclusion, for 
example, contains sections on human impacts on ecosystems and potential areas 
for parks that should have been included in the respective ecosystem chapters 
where there! is a material. The conclusion also contains lengthy discussions 
of , and organic coffee, but these 
too should have been contained in the ecosystem chapters with similar material. 
Similarly, a few tables could have replaced pages of description of protected areas 
throughout. 

Even with such editing, the book should be printed in two or more volumes. 
Incredibly, this 850-page book is published in a single paperback volume. This is a 
book that needs to be in every Mexican college library and accessible to every 
organization addressing conservation and development issues in Mexico. Unfor- 
tunately, even moderately-used copies will rapidly fall apart; my copy already 
has a cracked spine. It is too bad the book is not itself more sustainable. 

Despite the length, a thorough index and a detailed table of contents make the 
material accessible. Challenger maintains an author-date citation style through- 
out with references following each chapter, and this guarantees the utility of the 
book as an obligatory desk reference for all Latin Americanists with interests in 
the intersections between biodiversity, people, politics, and history. We are fortu- 
nate Challenger took on a Herculean task, and executed it so well. 


Daniel Klooster 
Department of Geography 
Florida State University 


Journal of Ethnobiology 20(2): 269-299 Winter 2000 


HISTORICAL ECOLOGY ve THE SOUTHEASTERN 
LONGLEAF AND SLASH PINE FLATWOODS: A SOUTHWEST 
FLORIDA PERSPECTIVE 


KAREN J. WALKER 
Florida Museum of Natural History 
Randell Research Center 
PO Box 117800, University of Florida 
Gainesville, FL 32611 


ABSTRACT.—Before E A ttl t of th tl t US., longleaf 
pine (Pinus palustris Mill.) was present and largely dominant on an estimated 85 
percent of all upland area within the longleaf’s botanical range. Today, longleaf is 
present on only about 2.6 percent of those uplands. In addition, uplands forested 
wee Bipeh eg Saud vince sneer) have been reduced from a pre- 
t 1993). This dramatic landscape 
change is a ae of long-term relations saibah yeas the ee prosystems and human 
activity. Understory plants, soil moisture, and periodi 1 factors 
while domestic animals, agriculture, the naval-stores an lumber industries, and 
fire reduction were human-related factors. Some of the S t’s last old-growth 
pine forests were logged in south Florida during the 1920s, 1930s, 1940s, and 1950s. 
Mostly of the pine flatwoods type, these were the southernmost forests in the 
longleaf pine’s range and they included both longleafs and the south Florida 
variety of slash pine (Pinus elliotti var. densa Little & Dorman). In southwest 
Florida’s Lee County, historic and oral-historic research focused on the pine 
Seheronds near Fost Myer, north and south off the Caloosahatchee River. South of 
the ri major component 
of oe 1924-1944 logging operation that greatly impacted the flatwoods of both 
areas. The results of this historical ecology research illustrate the heterogeneous 
process of landscape change at regional (Southeast U.S.), subregional (south 
Florida), and local (southwest Florida) scales. 


ey words: historical ecology, longleaf and south Florida slash pines, southwest 
Florida, oral history, archaeology. 


RESUMEN.—En el sudeste de los Estados Unidos, y antes de la colonizacion de 

los euro-americanos, la presencia de los pinos de hoja larga (Pinus palustris Mill) 

dominaban en gran parte el terreno elevado que quedaba dentro del area 

demarcada botdnicamente para este tipo de pino. Se estimaba que el area 

compendia un ochenta y cinco (85) por ciento del terreno. Hoy dia, tan solo el dos 

pine? seis (2. 6) pors ciento de los pines de hoja larga estan gepresentados dentro 
Ademias, las areas en 


mas altos dond 1entran los pinos cortados (Pinus elliottii Englem) han sido 


reducidas a atro (0.4) por ciento, en comparaci6n a el tres punto tres 
Se 2) Leedo ciento que e existia durante la epoca pie euro-americana or 1993). roe 


durante mucho tiempo entre el aurea tate de los pinos y la actividad 
humana. Est q medad en terreno, y los incendios 


270 WALKER Vol. 20, No. 2 


que occurieron periddicamente, fueron los factores ecolégicos. Los factores 
humanos que contribuyeron a éste cambio fueron, los animals domésticos, la 
agricultura, las tiendas de tipo marino o nautico, las industrias de madera, y la 
reduccién de los incendios. En el sudeste se encuentra el crecimiento de algunos 
de los bosques de pino mas viejos y que fueran registrados en el sur de la Florida 
durante los afios 1920, 1930, 1940, y 1950. En su mayoria, los pinos del tipo se 
encuentra en las areas de terrenos llanos estan en la parte sur de Florida y son de 
hoja larga, asi como la variedad de pino cortado (Pinus elliotti var. densa Little & 
Dorman). En el Condado de Lee, que se encuentra en el sudoeste de la Florida, 
hay estudios histéricos y de historia oral donde se enfoca el tema de los pinos en 
las llanuras cerca de Fort Myers y en la parte norte y sur del Rio Caloosahatchee. 
En un estudio arqueolégico que se realizé al sur del rio, se hizo possible el 
documentar los restos de uno de los componentes principales en la operacién de 
la extracci6n de madera durante los aioe de 1924 a 1944 y lo que caus6 un gran 
impacto en los bosques q en los terrenos llanos de ambas 4reas. 
Ea una inspeccion de tipo pintinico-ecoligion se ude documentar el Lpmecnse 


raAienie 


dela region (sudeste de los Estados l Unidos), la sub-region (sur de la Florida), y la 
parte local (al suroeste de la Florida). 


RESUME.—Avant l’imp] ti iro-amé€ricaine dans le sud-est des Etats-Unis, 
le pin des marais (Pinus alias Mill.) était courant et prédominait largement 
avec une estimation de 85 pour cent de tout le haut pays classé dans la variété 
botanique du pin des marais. Aujourd’hui, le pin des marais se trouve seulement 
dans 2,6 pour cent du haut pays. De plus, les hautes terres boisées de pitchpins 
américains (Pinus elliottii Bes ose ont été réduites d’un pourcentage preéuro- 
améri pour t 0,4 pour cent (Gel de 1993). Ce changement 
dramatique de paysage est le résultat de relations a longs termes entre les 
sia acini du pin e Tachvie humaine. Les pane des sous-bois, l/’humidité 
s facteurs écologiques alors 
que les animaux domestiques, agriculture, l’€quipement naval et les industries 
du bois, la réduction de feu, furent les facteurs relatifs 4 l‘homme. Certaines des 
derniéres anciennes foréts de pins du sud-est furent abattues dans le sud de la 
Floride dans les années 1920, 1930, 1940 et 1950. Saved sap a? ties de pins, on 
les trouvait le plus au sud sous la variété de 
a la fois les pins des marais et la variété de pitchpins américains (Pinus elliotti var. 
densa Little & Dorman) de Floride du sud. Dans le County Lee de Floride du sud- 
ouest, la recherché historique et orale historique s’est focalisée sur les foréts de 
pins pres de Fort Myers, au nord et au sud de la riviére Caloosahatchee. Au sud 
de la riviére, un étude archéologique a révélé les restes d’un élément majeur de 
l'opération de 1924-1944 sur l’exploitation du bois qui a grandement influencé les 
foréts de chacune des régions. Les résultants de cette recherche écologique 
historique illustre le processus hétérogéne de changement de paysage a l’échelle 
régionale (le sud-est des Etats-Unis), sous-régionale (le sud de la Floride) et locale 
(le sud-ouest de la Floride). 


INTRODUCTION 


Historical ecology, as defined by Crunaley (1994a, 1994b, 1998) and: others (Balée 
1998; Headland 1997; Winterhalder 1994), i 


J? 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 271 


of the dialectical relations between people and the physical environment. This 
approach views the cause of cultural and ecosystem change as interactive rather 
than deterministic. Crumley (1994b:6-7) states that “long-term sequences may be 
traced through the study of changing landscapes, defined as the material manifes- 
tation of the relation between humans and the environment.” Examination of 
landscape change at more than one temporal and spatial scale is crucial to the 
analysis because the process of change at le may not be the same at another 
scale (Marquardt and Crumley 1987:2-9). Combinations of archaeology, 
ethnohistory, ethnography, ethnoecology, ethnobiology, history, geography, and 
the environmental sciences are appropriate to the integrative study called for by a 
historical ecology approach. Ethnobiology, for example, focuses on the relations 
between people anid pa and animals but does not emphasize the historical 
(including arcl continuum or landscape elements other than plants and 
animals. Historical ‘ecology is broad in scope, potendally. eee passing the 
multiscalar past and present, and multiscalar landscape elements such as climate, 

fire, geomorphology, soils, plants, animals, and humans. 

Employing the approach of historical ecology, I examine a landscape change 
that occurred across the Coastal Plain region of the U.S. Southeast—the greatly 
diminished forest ecosystems of the longleaf pine (Pinus palustris Mill.) and the 
slash pine (Pinus elliottii Engelm.) (Little 1971; Wunderlin 1998)—but with a local- 
scale focus on the pine flatwoods of southwest Florida’s Lee County. Longleaf 
pines were once so abundant in the Atlantic and Gulf Coastal Plain states that 
they and their plant and animal associates composed one of the dominant forest 
ecosystems of the region (Frost 1993; Wahlenberg 1946; Walker 1991). Old-growth 
longleaf and slash pine forests greeted early European and EuroAmerican explor- 
ers, travelers, and settlers to the Southeast; these once-seemingly endless forests 
were described as open stands of pines towering over a low understory often domi- 
nated by grasses or saw palmetto (Serenoa repens W. Bartram). Deforestation of the 
region’s old-growth pine forests was a long process encompassing several hun- 
dreds of years but intensifying primarily Curing | - eighteenth through twentieth 
centuries. Frost (1993) presents an j tal history of the 
longleaf at this long-term regional scale. 

Examining the longleaf pine from a south Florida perspective is also important 
because this subregion supported the po ihenrnnost forests of longleaf and their 
penetration into Florida’s sul ted or understood. Longleaf 
pine forests in south Florida were and are of the flatwoods type, the land generally 
being too low to support the sand-hills longleaf forest type. In addition, the 
subregion’s slash pine is Pinus elliottli var. densa (Little & Dorman), distinct from the 
typical northern variety, Pinus elliottii var. elliottii; the former has some characteris- 
tics similar to longleaf (Abrahamson and Hartnett 1990:112; Moyroud 1996-1997:11; 
Small 1930; Snyder et al. 1990). Earlier in the twentieth century, the south Florida 
slash pine was thought to be Pinus caribaea Morelet, the Caribbean pine (e.g., 
Harshberger 1914; Small 1930:42). Indeed, the southernmost slash pinelands (e.g., 
Everglades National Park) exhibit a distinct assemblage of plant taxa owing to their 
subtropical location (Snyder et al. 1990). The distributions of longleaf and south 
Florida slash pines overlap at least in the northernmost areas of south Florida (e.g., 


272 WALKER Vol. 20, No. 2 


Atlantic 
Ocean 


Highlands Co. 
, Glades Co. 


Gulf EE 
Caloosabatchee River pe © Lake 
~ Okeechobee 
Mexico Sa 
i Homestead | 
Slater Mill 


ooo "Noel and es \ 


aan of Mexico 


FIGURE 1.—Map showing estimated pre-EuroAmerican Southeast U.S. range of longleaf 
pine (Pinus palustris Mill.) and botanical ranges of typical slash pine (Pinus elliottii elliottii 
Engelm.) and south Florida slash pine (Pinus elliottii densa Little and Doonan). The longleaf 
range is generally based on Frost’s t 1umMerous sources 
(1993:Figure 2). The more detailed southwest Florida range is Solid on Harshberger (1914) 
and Sudworth (1913:Map 35). The slash pine ranges are from Little (1971, 1977). Inset m map 
is of Lee County showing the Hickey Creek Mitigation Park (HCMP) and the Cape Coral 
and Hickey’s Creek/Lehigh components of the McWilliams /Dowling & Camp logging 
system (as reconstructed by James Pickens from 1944 aerial photographs), Slater Mill, and 
other locations mentioned in the text. The shaded areas are hypothesized to have been 
forested with a mix of old-growth south Florida slash pines and longleaf pines. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 273 


Lee County, Highlands County). A third native pine, the sand pine (Pinus clausa 
Chapm.), is found in the western half of Lee County with its southernmost occur- 
rence in extreme western Collier County (Harshberger 1914:Map; Little 1978:Map 
4). South Florida was one of the last areas of the Southeast to experience intensive 
EuroAmerican settlement. Thus, the subregion’s pine forests were some of the last 
of the Southeast’s old-growth pine forests to be logged. Clear-cut logging, the final 
phase in the Southeast’s pine-deforestation process, did not begin in southwest 
Florida until the 1920s (Zeiss 1983), continuing to as late as 1956 (Tebeau 1957). Thus, 
a few individuals with first-hand knowledge of south Florida’s old-growth forests 
and their destruction are still living today, representing valuable oral-historic re- 
sources. And logging-related features and archaeological deposits are still evident 
on the landscape, allowing documentation. 


THE PRE-EUROAMERICAN PINE FORESTS 


A Problematic Documentation.—Researching historical documents concerning the 
southern pines is problematic (Frost 1993:18; Wahlenberg 1946:268). This is largely 
due to the botanical similarity of the four yellow pines—longleaf, slash (two vari- 
eties), shortleaf (Pinus echinata Mill.), and loblolly (Pinus taeda L.) (Wunderlin 
1998:62)—and their often overlapping distributions (Little 1978:Maps 5, 6, 8, and 
10). Of these four pines, however, only the south Florida slash and longleaf pines 
are native in south Florida. Even so, whether referring to south Florida or areas to 
the north, early land surveys, maps, and travelers’ accounts seldom specify the 
species of pine recorded. 

A plethora of common names have been used at any one time for these pines, 
all described as “yellow” because of their wood color (Record and Hess 1943). 
Wahlenberg (1946:268) explains that patterns of geography and sometimes eco- 
nomics (i.e., pine products) could be observed in the variation of names. For 
example, longleaf pine was generally called “fat” pine in the deep south, 
“longleaved” and “longstraw” pine in the Atlantic states, “turpentine” and “rose- 
mary” pine in North Carolina, “brown” pine in Tennessee, and “orchard” pine in 
Texas. Loggers and lumbermen variously called longleaf “yellow” pine, “heart” 
pine, “southern” pine, “hard” pine, and “pitch” pine (see also Mohr 1896:28; 
Panshin and deZeeuw 1980; Record and Hess 1943). Mohr (1896:28) lists “slash 
pine,” “swamp pine,” “bastard pine,” “meadow pine,” and “she pine” as com- 
mon names used for slash pine. 

Most bothersome to researchers, the word “longleaf” was sometimes used in 
the lumber industry to indicate any of the yellow pines that met lumber standards 
of high quality. To Wahlenberg (1946:268), this confusion was understandable from 
a lumberman’ 8 pot of vEW asics the yellow pines that are easily distinguished 

hed (anatomically) by their wood (see 

also “Record and Hess [1943] and Panshin and deZeeuw [1980] for examples of 

osperm keys that reflect this problem). In addition, early forestry surveys 

often combined longleaf and slash pines in a category called “turpentine pines” 

when reporting acreages (Wahlenberg 1946:xiii-xiv, 1), in part due to intergrading 
(i.e., mixed stands) of the two species. 


274 WALKER Vol. 20, No. 2 


Archaeological and paleoecological documentation of the pines is equally as 
problematic, if not more so, as historical and ethnobotanical documentation. The 
most frequently recovered archaeological plant remains are in the form of small 
fragments of charred wood, often found in great quantities. Although « charred wood 
fragments often can be identified to species under , wood 
anatomists and archaeobotanists are not able to distinguish between the southern 
species of Pinus (Panshin and deZeeuw 1980; Record and Hess 1943). Unfortu- 
ss this aAsity also apples to preserved, waterlogged wooden artifacts. 

y of pine pollen is also limited to the genus level, as pollen from 
the various species are “difficult or impossible” to distinguish (Watts 1993:15). 
However, one promising, indirect, avenue of identifying past longleaf woodlands 
is the determination of the mass and relative abundances of associated understory 
plants based on phytoliths recovered from soils (Kalisz et al. 1986:187). 


cone of Acreage and Range. = Despite the difficulties of historical research, recon- 
g PE ted for pre Puronmencen pos, 
especially for longleaf pine. Reported esti for tl 
forests range from 50 to 92 million (e.g., Frost 1993; Landers et al. 1995; Wahlenberg 
1946:8; Walker 1991:128). For example, Frost (1993) calculates that 92 million acres of 
the region’s woodlands included “ some longleaf pine” and of that acreage perhaps 
roughly 74 milli f-dominated woodlands. One writer reports that 
only .002 percent of the co. forests remains (Winn 1996:15). Estimates for cur- 
rent acreages range from 1 to 5 million (e.g., FCMP 1995; Landers et al. 1995; Longleaf 
Alliance n.d.). A 1995 systematic inventory by county of longleaf pine (comprising 
more than 50 percent of the tree cover) resulted in an estimate of 2.95 million acres 
(Outcalt and Sheffield 1996:2). Of the current longleaf acreage, Virginia has none and 
Florida has the most, almost one million acres (Outcalt and Sheffield 1996:20). 
Estimates of longleaf’s pre-EuroAmerican areal distribution also vary. 
Wahlenberg (1946:46) distinguishes between a botanical range (potential range) 
and a commercial range (range of exploitable forests), pointing out that most re- 
constructed distributions were probably based on commercial (i.e., exploitable) 
ranges, resulting in conservative boundaries (e.g., Mohr 1896; Sargent 1884). Thus, 
he concludes that the pre-EuroAmerican longleaf-forest boundaries lay somewhere 
between the two ranges. Frost’s (1993:18) recent reconstruction of longleaf’s range 
may be the best to date at the regional scale because it is a synthesis of the major 
studies published between 1861 and 1971. But it does not depict the true nature of 
longleaf’s southernmost distribution. Wahlenberg (1946:49-50) notes that longleaf 
is restricted in it by snow, which is dangerously heavy when 
accumulated on the tree’s long needles. However, competition from deciduous 
species may be a more important factor. Generally, longleaf pine extended across 
the Coastal Plain (Figure 1), from southeastern Virginia across to portions of Loui- 
siana and a small area of eastern Texas (Frost 1993). Distribution maps also 
consistently show that longleaf pine was found throughout Florida’s panhandle, 
and its north and central peninsular regions. Typical slash pine had a more re- 
stricted, even more southern range, generally distributed from southern South 
Carolina to central Florida and west to southeast Louisiana (Little 1971; Figure 1), 
often characterized as concentrating along the coastal areas (e.g., Sargent 1884:520). 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 275 


The southern longleaf boundary may be the more difficult of the two to recon- 
struct because the distribution of the south Florida slash pine overlaps with the 
southernmost longleafs (Figure 1) and the similarity of the two yellow pines has 
resulted in an often ambiguous historical record. Apparently. it is increased soil 
moisture that marks the longleaf’ tl and Hartnett 
1990:111-112; Peet and Allard 1993:61). Like typical slash pine, south Florida slash 
pine is more tolerant of poorly-drained soils and as a result is the more dominant 
pine across south Florida. The majority of pre- and post-EuroAmerican maps de- 
pict longleaf’s range as halting northwest of Lake Okeechobee in south-central 
Florida and at the Caloosahatchee River in southwest Florida, limited to the main- 
land (e.g., Frost 1993:18; Little 1978:Map 8; Schwarz 1907; Wahlenberg 1946:44). It 
may be that these south Florida boundaries were “commercially drawn,” as 
Wahlenberg called it, and therefore are conservative. (This is certainly the case 
with the forest-survey maps of Mohr [1896] and Sargent [1884].) 

For example, University of Florida herbarium records document scattered 
longleafs in the Estero area (FLAS 120603, collected 1975) of southwestern Lee 
County and an “extensive open stand of [longleaf] trees” on Pine Island (FLAS 
82831, collected 1961), west of mainland Lee County (Figure 1 inset). Outcalt and 
Sheffield’s (1996:19) inventory shows acreages of longleaf-dominated forest in two 
south Florida counties, Glades and Highlands, west and northwest of Lake 
Okeechobee (Figure 1). Frost’s (1993:18) reconstruction includes this Okeechobee 
locale, depicting it as part of a division called “scattered longleaf pine in slash 
pine areas transitional to south Florida communities. 

otanist John Harshberger (1914:89) traveled through Lee County 
(including what is today Collier County) early in the last century and reported 
that “on the west coast, south and north of the Caloosahatchee River, the slash- 
pine mingles with the long-leaf pine, Pinus palustris Mill.” and in another entry, 
“scattered growths of longleaf-pines, Pinus palustris Mill., continue south of the 
Caloosahatchee River into Lee County on the authority of J. A. Davison, an engi- 
neer, as far as Surveyor’s Creek, and the tree has been reported at Henderson’s 
Creek, but it is not an important element of the forest, which consists of the slash- 
pine, Pinus caribaea Morelet [today known as Pinus elliottii var. densa] and associated 
species.” Surveyor’s Creek, today known as the Imperial River (Grismer 1982:330), 
is located in southernmost Lee County (Figure 1 inset). Henderson’s Creek is lo- 
cated even farther south, between Naples and Marco Island, in today’s Collier 
County. Sudworth’s (1913:Map No. 35) botanical range for longleaf pine includes 
most of Cape Coral. It also extends south of the Caloosahatchee River including a 
locale overlapping eastern Lee County and western Hendry County, a band along 
the river, Pine Island, and a locale in the Estero area of southern Lee County. Based 
on Harshberger and Sudworth, Frost’s presettlement transitional mixed longleaf- 
slash zone should be extended to include parts of southern Lee County in order to 
depict more accurately longleaf’s southernmost botanical range, as I have indi- 
cated in Figure 1. 
Longleaf and Slash Pine Forest Ecosystems. —Eighteenth and nineteenth-century ac- 


counts of travels through the Southeast paint images of extensive open forests of 
tall pines (e.g., Bartram 1791:43, 186, 191; Brinton 1869:95, 104; Romans 1775:14- 


276 WALKER Vol. 20, No. 2 


17; Vignoles 1823:86-87). One could see for a great distance into the forests. It was 
thus also easy to travel through them and to hunt game animals, described as 
abundant. In some cases, longleaf was clearly the dominant tree being described 
(e.g., Bartram 1791:33, 52; Romans 1775:16) but more commonly, only t the generic 
“pines,” “pinelands,” “pine flatwoods,” etc. indicated. Similarly, t 
(1914:90) and Small (1930) described the south Florida slash pine forests as “an 
usually open” with an unobstructed view, and “endless.” These early accounts 
and others suggest that pre-EuroAmerican slash- and especially longleaf-domi- 
nated forest ecosystems may have been characterized by a lower understory than 
most pine forests of today. The interpretation is far from certain (Myers 1990:182), 
however, because by the eighteenth century, feral and free-ranging European-in- 
troduced hogs and cattle were abundant in the pine forestlands, grazing and 
foraging in the understory (e.g., Romans 1775:16). 

General characteristics of mature longleaf-dominated pine ecosystems include: 
low longleaf stand density; minor hardwood component, mostly oaks; grass-domi- 
nated groundlayer; high plant species richness; frequent surface fire; occurrence 
across a wide geomorphic and hydrologic gradient (although well-drained sandy 
soils are most common); and stands of uneven-aged trees (Landers et al. 1995:40; 
Palik 1995:6; Schwarz 1907:3-17). An important difference between longleaf and 
slash forests is the much slower rate of longleaf growth while in the seedling stage, 
leading to the undeserved reputation of being slow to reach timber size (Franklin 
1997:5; Landers et al. 1995:42). Longleaf forests are often vieibty. aut =m slash 
pine forests in that bunch grasses (especially the ta Michx. 
in the north and Aristida beyrichiana Trin. & Rupr. in the southernmost areas) are 
the dominant understory plant of the former while saw palmetto and to a lesser 
extent gallberry (Ilex glabra L.) typically dominate in a slash pine forest. However, 
recent studies recognize a wide diversity of longleaf ecosystems based on vegeta- 
tional composition and soil moisture (e.g., Harcombe et al. 1993; Peet and Allard 
1993), including a longleaf system with saw palmetto along the northern Gulf 
Coastal Plain (Peet and Allard 1993:57, 58). Most of Florida’s longleaf forests of the 
Gulf Coastal Plain, including those of southwest Florida were or are probably of 
the “southern longleaf flatwood” type, described as often including slash pine 
and saw palmetto in the relatively wetter areas (Peet and Allard 1993:61, 65). What- 
ever the dominant pine, “natural” flatwoods generally are highly stratified with a 
high tree canopy (pines drop their lower limbs, sometimes a result of fire) and a 
low plant understory. 

Longleaf pine itself is most readily distinguished from other southern pines 
by its long needles, 10 to 15" (25-38 cm), and large cones, 6 to 10” (15-25 cm) (Harrar 
and Harrar 1962:51-60; Little 1980:291; Wahlenberg 1946:3). Longleaf has the po- 
tential to live 500 years or more but usually trees are victims of storms, if not 
humans, long before reaching such an age (Bengtson et al. 1993; Landers et al. 
1995:39-40). Compared to other southern pines, longleaf is the most resistant to 
disease, insects, and rot, adding to its value as timber wood. South Florida slash 
pine is less resistant than longleaf but more resistant than typical slash pine. 

Longleaf pines are intolerant of competition but remarkably tolerant of sur- 
face fire; thus, frequent—at least once a decade and optimally every 2-3 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 2ry 


years—low-intensity fires are the key to controlling the growth of competitors 
such as hardwoods and even slash pines (Abrahamson and Hartnett 1990:132; 
Landers et al. 1995:40; MacLaren and Stevenson 1993:407; Rebertus et al. 1993). 
South Florida slash pine is less fire resistant than longleaf but more fire resistant 
than typical slash pine (Abrahamson and Hartnett 1990:112, 131; Snyder et al. 
1990:259). Along with fallen pine needles, highly flammable wiregrasses (Moore 
1996a:18; Peet and Allard 1993:46-47) and saw palmetto (Arahamson and Hartnett 
1990:129) provide fuel for the fires, usually ignited by lightning strikes. In the ab- 
sence of human influence (either Indian or EuroAmerican), fires would have been 
seasonal, primarily limited to the summer lightning season of April to mid Au- 
gust (Myers 1990:185). In pre-EuroAmerican times, a single-ignition fire could burn 
extensively without the limitations of roads and other human-made barriers. The 
pines themselves withstand fire in part because of their multi-layered fire-resis- 
tant bark (Snyder et al. 1990:259). Longleaf seedlings also regularly survive fire; 
the seedlings of south Florida slash pine have a lower survival rate yet fare better 
than those of typical slash pine (Small 1930:42; Snyder et al. 1990:259). Thus, longleaf 
and South Florida slash flatwoods are especially fire-maintained and fire-depen- 
dent. A high frequency of 2 to 3 fires a year would enhance and expand longleaf 
stands (Rebertus et al. 1993) and slash pine stands as well. In addition to reducing 
woody competitors, fire contributes to the germination of seeds (especially of 
longleaf and the understory grasses) by producing appropriate soil conditions; to 
turnover of litter, humus, and nutrients; and to increased vigor of some species 
populations (Abrahamson and Hartnett 1990:129; Myers 1990:178). 

In addition to wiregrasses, a high diversity of fire-adapted groundcover plants 
in both longleaf- and south Florida slash-dominated flatwoods sustains a diverse 
animal life (Abrahamson and Hartnett 1990:116; Engstrom 1993; Guyer and Bailey 
1993; Johnson 1995; Moore 1996b:19). This is in part because many of the fire- 
adapted plants produce new growth, providing food, soon after a fire has burned 
through the forest. Pine seeds also provide food for many birds and small mam- 
mals (Frost 1993:31; Wahlenberg 1946:179). Gopher tortoise (Gopherus polyphemus), 
box turtle (Terrepene carolina), eastern diamondback rattlesnake (Crotalus 
adamanteus), black racer (Coluber constrictor), pine woods tree frog (Hyla femoralis), 
great horned owl (Bubo virginianus), bobwhite quail (Colinus virginianus), red- 
cockaded woodpecker (Picoides borealis), turkey (Meleagris gallopavo), fox squirrel 
(Sciurus ete feria nd eel er deer (Odocoileus virginianus) are some of the ani- 

oods. Most, if not all, benefit from periodic fire. For example, 
gopher else more typical of high pinelands (Myers 1990:186) but also present 
in the drier flatwoods and scrubby flatwoods ( and Hartnett 1990:119), 
cannot survive dense woody vegetation. The underground burrows of tortoises 
serve as fire refuges not only for the tortoises but also for over 300 other vertebrate 
and invertebrate animals (e.g., Dodd 1995; Folkerts et al. 1993:165-166, 181-182; 
Myers 1990:186). Early EuroAmerican observers also recorded bison, black bear, 
panther, red wolves, and even elk in the longleaf forests of the Southeast (Engstrom 
1993:128). 

Today there is general agreement among researchers that pre-EuroAmerican 
pine forests differed from most present-day ones in that they had higher fire fre- 


278 WALKER Vol. 20, No. 2 


quencies, more uneven age structure, and a more open understory with greater 
grass components and less shrub plants (Abrahamson and Hartnett 1990:104). 
Researchers also agree that the reduction of fire frequency may be responsible for 
much of the difference (Abrahamson and Hartnett 1990:104; Frost 1993:21, 34-35). 


The American Indian Factor —The occurrence and distribution of woodlands (pine 
and mixed hardwood) and other plant communities and how they changed 
throughout pre-EuroAmerican history are increasingly being linked to human in- 
fluence, and in particular to human use of fire (Delcourt and Delcourt 1997, 1998; 
Delcourt et al. 1998; Pyne 1998). While there are many reasons recorded in historic 
accounts (Wagner in press) for why American Indians set fires in eastern North 
America, perhaps two of the most important ones were to sti ] plar its 
for attracting wildlife and to drive game. While traveling in north Florida, Bartram 
(1791:139) stated that “fires are set almost every day throughout the year in some 
part or other, by the Indians, for the purpose of raising the game, as also by the 
lightning.” Attracting wildlife may have been the primary reason for American 
Indian management of Florida’s pine flatwoods, especially in pre-agricultural times 
(generally before A.D. 1200 in north Florida). In south Florida where crop agricul- 
ture was not practiced, attracting wildlife and improving visibility for hunting 
undoubtedly would have been the primary reason for setting fires. White-tailed 
deer and other game animals of the pine forests are highly visually oriented, need- 
ing to see their surroundings (Johnson 1995:29). 

To date, little research has focused on American Indian use of woodland fire 
in Florida. One study by Kalisz et al. (1986), however, identified a spatial correla- 
tion between archaeological sites associated with non-agricultural Indians and 
present-day longleaf stands (occurring as “islands” in a landscape of predomi- 
nantly sand pines) in north-central Florida’s Ocala National Forest. In addition, 
quantification of wiregrass phytoliths in the soils beyond the present-day longleaf 
stands strongly suggests that they were once more extensive. Kalisz et al. (1986:191) 
hypothesize that “the longleaf pine islands were maintained through annual or 
frequent burning by early humans; longleaf pine islands are prehistoric cultural 
features.” Change in the natural fire regime of either sandhill pine stands (as in 
the Ocala case) or pine flatwoods due to an increase in the number of fires and the 
addition of a second burn season (winter dry season), if maintained, would have 
resulted in forest expansion, especially where longleaf. 
were present. 

Fifty-six years earlier, in his study of south Florida slash pine “islands” within 
the Everglades (“Everglade Keys”), botanist John K. Small (1930:41-42) hypoth- 
esized about the ecological influence of American Indians: 


or south Florida slash pines 


...when the aborigines first occupied the Everglade Keys, they doubtless 
found them clothed with hammock. ...without doubt, the aborigines pur- 
posely set fire to the hammocks in order to drive the game into the open 
places, thus facilitating their primitive means of hunting game. ... But there 
had been developed plants that were fire-proof, so to speak, just for such 
regions...the Caribbean-pine (Pinus caribaea)...the seedling pine-trees after 
several years of uninterrupted growth will survive fire, and when a little 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 279 


older they are normally perfectly fire-proof. Thus the pinewoods were 
developed and have spread as the hammock retreated. 


DEFORESTATION OF THE SOUTHEASTERN AND SOUTH FLORIDA PINE 
FLATWOODS 


Human-related factors involved in the complex process of pine deforestation 
include American Indian agriculture, introduced European animals, the naval- 
stores and logging industries, EuroAmerican agriculture, and reduction of fire. 
Both American Indians and EuroAmericans contributed to the landscape change, 
although clearly the latter played the greater role. Importantly, African Ameri- 
cans, masked by the EuroAmerican economic histories, comprised the greater 
percentage of the labor force for EuroA g | produc- 
tion and for the naval-stores and logging industries. 


American Indian Agriculture—In prehistoric times, ES ee Serica Indians 
may have cleared portions of the more fertile ts have been 
made to estimate how much pineland was impacted i in the southeast 1 region. Stud- 
ies that identify and estimate agricultural lands surrounding large 
Mississippian-period population centers are on the increase, but so far these have 
focused on areas outside of the longleaf and slash pine ranges (see summary in 
Wagner in press). Frost (1993:28) notes that Alabama Indian farmers may have 
cleared much longleaf pineland for their ext Itural fields. Many towns 
of these Mississippian-period agriculturalists were palisaded, representing an 
additional impact on forests (Wagner in press), possibly including pinelands. 
Moreover, palisades were replaced, sometimes several times over the occupation 
of a site. Alabama’s Moundville, for example, was palisaded at least three times 
using a minimum of 10,000 logs each time (Scarry and Steponaitis 1997). Maize 
agriculture spread throughout north and central Florida after about A.D. 1200 and 
may have impacted pinelands of these subregions. South Florida’s prehistoric In- 
dians, on the other hand, did not practice agriculture. 


Introduced European Animals.—Except for the possibility of Indian agriculture as a 
significant factor, one might argue that the pine deforestation process, in a broad 
sense, began in 1539 with the Spanish expedition led by Hernando de Soto (Smith 
1968). De Soto entered the Southeast in west central Florida and brought with him 
a food supply that included droves of pigs (Milanich and Hudson 1993:38), herd- 
ing them along the exploration route throughout much of the southeastern range 
of longleaf and slash pines. In addition to the resultant, immediate short-term 
foraging and grazing of the forest groundlayer, unknown numbers of pigs are 
believed to have escaped, forming the basis for a non-native feral population, one 
that proliferated in the pine flatwoods. The use of pinelands for grazing contin- 
ued and diversified when an area’s first EuroAmerican settlers learned—perhaps 
from American Indians—that purposely set surface fires in the woods, especially 
those with longleafs and south Florida slash pines, reduced the shrub layer (saw 
palmetto, etc.) and produced new grass forage for their grazing animals. Romans 
(1775:16) wrote of the north Florida longleaf forests “that immense stocks of cattle 


280 WALKER Vol. 20, No. 2 


are maintained, although the most natural grass on this soil is of a very harsh 
nature, and the cattle not at all fond of it, it is known by the name of wire grass; 
and they only eat it while young...the woods are frequently fired, and at different 
seasons, in order to have a succession of young grass.” The periodic burning of 
the forest floor by Indians and EuroAmericans benefitted the forests as did fires 
ignited by lightning, and especially in the case of longleaf and south Florida slash 
pine forests, perhaps even expanded them if their burning episodes represented 
ane increase in fr Overs fire hin, wea? eee there was generally an important 

Indian and E forest t. Prehistoric and 
many eee pease Indians “fire-managed” pine forests primarily to increase 
the abundance of native wildlife which ey | hunted for food. Hie inae th grasses, 
wildlife, and fire were elements of the native flatwoo tem, EuroAmerican 
livestock was not. Feral and domestic hogs and cattle and even sheep and goats 
(in some areas), free from fencing as late as the 1950s in south Florida, fed on the 
many grasses and pine seedlings in these open woodlands (Sargent 1884:492). 
Departing from the pattern, however, historic-period American Indians in Florida, 
notably the Seminole, also engaged in cattle-raising on the open range, first in 
north and central Florida and later in south Florida. Great numbers of feral cattle, 
many from Spanish origins, roamed the pinelands free for the taking. 

The feral hog population had reached a saturation point across most of the 
longleaf range by 1850, and probably earlier although pre-1840 documentation 
doesn’t exist (Frost 1993:32). While the grasses may have benefited from hog and 
cattle grazing, the collective rooting, grazing, and trampling of the non-native 
animals proved to be too much for the pine seedlings, especially those of the slow- 
growing longleafs. It is reported that a single hog in one hour can root as far as 30 
feet, eating some eighty starch-laden longleaf seedlings (Walker 1991:129, 192-193). 
Thus, feral hogs, in particular, were responsible for the destruction of countless 
longleaf seedlings, preventing forest regeneration (Frost 1993:30-34; Schwarz 
1907:94; Wahlenberg 1946:178-179). In addition, soil compaction and trampling 
caused by these animals contributed to the inability of seedlings to survive 
(Abrahamson and Hartnett 1990:146). 

South Florida was still in many ways a frontier during the first half of the 
twentieth century. For example, many south Florida cattlemen continued centu- 
ries-old burning practices in the pine woods so that their stock could graze on 
new grass growth (Akerman 1976:246-247; Franklin 1997:19; Zeiss 1983:118-119), a 
practice that was compatible with pine forests if seedlings survived their fire-in- 
tolerant stage. Wild pigs, on the other hand, still very populous in the 1940s and 
1950s in south Florida, continued to consume pine seedlings in massive quanti- 
ties, significantly ae the region’s source of forest regeneration. 


L. 


Naval Stores and Logging. American settl realized more lucrative uses 
for the longleaf and slash pine forests. The naval-stores industry faced trees (as 
many as three or four sides of mature trees) and attached cups or boxes to collect 
resin that was used for the production of rosin, pitch, tar, and turpentine (Butler 
1998; Frost 1993:24-27; Mohr 1896:69; Wahlenberg 1946; Walker 1991:77, 146-151). 
The first three products were enormously important to the shipbuilding industry, 
while the numerous uses for turpentine varied from lamp oil to laxatives. The 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 281 


1834 introduction of the copper still for turpentine distillation resulted in a prolif- 
eration of turpentine operations (Butler 1998:72-73; Frost 1993:26-27). The still 
allowed the resin to be reduced to turpentine at the extraction sites and thus saved 
significant shipping costs. Mature stands of longleaf often produced for only about 
four years (Mohr 1896:70). Pine trees tolerated extraction of resin but were weak- 
ened significantly and thus became more vulnerable to fire, insects, and storms 
(Mohr 1896:61, 72). 

The most lucrative and most destructive of all the pine industries was timber- 
ing. The tall, straight longleaf pines with their rot- and insect-resistant wood, for 
example, made excellent ship masts, long-lasting dock pilings, and when milled, 
made beautiful homes. Southern longleaf pine, in general, had the reputation in 
European, Caribbean, and South American markets of being North America’s stron- 
gest wood due to its density (Mohr 1896:53). Initially, transporting longleaf and 
slash pine logs to the mills was a a slow and difficult task. Logs were floated via 
natural and human-excavated waterways thus, the area of forest that could 
be logged was limited to that which had access to the waterways. 

That limitation vanished with the nineteenth-century arrival of the steam- 
driven locomotive and railroads to the southeastern forests. In addition to the 
locomotive, steam-powered log skidders, sawmills, and circular saws contributed 
significantly to the new logging technology. Almost as soon as the main rail lines 
were laid by railroad companies, lumber panies leased logging rights or bought 
extensive acres of forested lands adjacent to the lines. Logs were taken from the 
woods to the sawmills by railcars pulled by a steam locomotive. Due to this accel- 
eration of the logging industry based on steam technology, most of the region’s 
remaining old-growth longleaf and slash pines forests were clearcut between 1870 
and 1920 (Frost 1993; Wahlenberg 1946). Just as EuroA ttl t had been 
late coming to Florida, especially the southern half of the peninsula, the state was 
late in receiving attention from the railroads. The logging of south Florida’s pine 
forests began in the 1920s. Old-growth pines were still being logged in this subre- 
gion in the 1950s although much of the focus had shifted to cypress in the Big 
Cypresss Swamp and Fakahatchee Strand (Tebeau 1957). 


EuroAmerican Agriculture. Bagi broad-scale logging, many pinelands were 
I fields 


cleared by E the purpose of 
Much of the landscape across the region was converted to cotton plantations in 
the 1800s. Later, especially after 1940, many logged pinelands and old plantation 
lands were planted in slash or loblolly pines. Slash (primarily the typical P. elliottii 
elliottii) and loblolly were thought to be fast-growing (due to their early rapid 
growth) compared to the longleaf, and thus were considered more economical to 
grow, ignoring the higher quality of longleaf wood. Dense plantations of slash 
and loblolly, with trees planted in neat rows, became the accepted management 
approach in forestry practices on public-, industry-, and other private-owned lands. 
In still other areas of the Southeast, including parts of south Florida, citrus groves 
and non-woodland cattle pastures replaced the old-growth flatwoods. 


Reduction of Fire-—The reduction of fire frequency in the Southeast’s pine forests 
intensified with the progression of EuroAmerican settlement. As roads and agri- 


282 WALKER Vol. 20, No. 2 


cultural fields became more numerous, the pine woodlands became more frag- 
mented, requiring a higher frequency of fire ignitions to burn large areas. Prior to 
fragmentation, a single lightning ignition could burn extensively across the land- 
scape. With fragmentation, fire was effectively eliminated from many parcels of 
pine forests (Frost 1993:34). Thus, early fire suppression was perhaps an uninten- 
tional result of EuroAmerican settlement. Many of the logged Southeast lands, 
including longleaf woodlands, experienced serious erosion and flooding (Walker 
1991:170-175). This situation, combined with poor agricultural practices, led to the 
Southeast’s navigable rivers being muddied and even clogged. As a result, the 
federal government began in 1911 to buy the logged lands to protect the Southeast’s 
watersheds. In this manner, over 10 million southern acres were added to the Na- 
tional Forest system, and trained foresters took on their management (Walker 1991). 
Nonetheless, many millions of acres, especially those forestlands that supported 
longleaf pine, were not allowed to regenerate naturally. 

Perhaps the most critical barrier to regeneration was what might be called the 
“Smokey Bear Myth.” Although purposeful fire-suppression steadily followed the 
progression of EuroAmerican settlement, the U.S. Forest Service’s Smokey Bear 
campaign, culminating in the 1950s, left no doubt in the minds of Americans that 
all forest fires were destructive and dangerous, and were not to be allowed under 
any circumstances (Landers et al. 1995:41; Moore 1996c:22; Walker 1991). Because 
foresters did not understand the beneficial role of frequent surface fires (e.g., Mohr 
1896:62), they unknowingly contributed to the degradation of the pine forests. 
Without frequent surface fire, the forest floor became thick with pine needles and 
cones and the shrub layer grew dense, all providing fuel for highly destructive 
fires when fires did occur. Without fire, the longleaf pines were eventually out- 
competed by other pines and hardwoods, the slash pines were often out-competed 
by hardwoods, and the various understory plants and animals specifically adapted 
to the longleaf and slash forests declined in abundance (Peet and Allard 1993:46). 
Even in the relatively remote rock pinelands of today’s Everglades National Park, 
twentieth-century fire suppression resulted in a reversal of Small’s (1930) hypoth- 
esized scenario in that a succession toward hardwood hammock has occurred 
(Hofstetter 1974:203). 


DEFORESTATION OF SOUTHWEST FLORIDA'S PINE FLATWOODS 


Archaeological Survey and Historical Research of the HCMP.—During January of 1996, 
Robin Denson (Gulf Archaeology Research Institute) and I conducted an archaeo- 
logical survey on a tract of Lee County-owned land just south of the Caloosahatchee 
River and east of Fort Myers in southwest Florida (Figure 1 inset) (Walker et al. 
1996). Prior to and during this same time, I also conducted historical research and 
a series of interviews with long-time local residents. Much of the area today is 
characterized by seasonally wet south Florida slash pine/saw palmetto flatwoods 
and dense saw-palmetto prairies. The county property, known as “Hickey Creek 
Mitigation Park” (HCMP), was named for Hickey’s Creek (after nineteenth-cen- 
tury settler Dennis O. Hickey) which runs through it toward the Caloosahatchee. 
In part, the park is intended to be a preserve for gopher tortoises in perpetuity to 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 283 


offset tortoise habitat destroyed elsewhere in southwest Florida (Roger Clark, per- 
sonal communication, 1996; Riley et al. 1993), hence, the use of the word 
“Mitigation.” 

Our archaeological survey documented five American Indian archaeological 
sites on the park property. Artifact collections include primarily a few pottery 
sherds, one bone pin, and one bone point; no other faunal remains or other date- 
able organic materials were found. The sherds are all of the Sand-tempered Plain 
type, also known as “Glades Plain,” and are only roughly diagnostic of time pe- 
riod. Because they are not very thick, a post-A.D. 500 date is suggested. These are 
all small sites and four are associated with the banks of Hickey’s Creek (Walker et 
al. 1996). One site tenuously was based on a single chert flake likely produced 
from working or reworking a projectile point. Unlike other sites, it is located in the 
middle of today’s slash pine/saw palmetto flatwoods. Larger sites are reported 
for the mouth of Hickey’s Creek on the Caloosahatchee River and just to the south 
of the park property on Hickey’s Creek. The latter produced a relatively large 
sample of pottery sherds that suggest a post-A.D. 500 habitation, more long-lived 
than the small sites within the park. It is possible that all sites are contemporane- 
ous. The two large sites may have been the main habitation villages for the area 
while the smaller kside sit y] | short-term hunting / fishing camps. 
The chert flake may have been lost during a hunting episode in the flatwoods. The 
bone point also suggests food procurement, associated with either fishing or hunt- 
ing. Freshwater and periodically estuarine fishes would have been available in 
Hickey’s Creek and white-tailed deer, raccoon, opossum, turkey, gopher tortoise, 
quail, and other game animals would have inhabited the flatwoods, all offering 
substantial food resources for the Indian residents. 

The EuroAmerican homesteader of the Hickey’s Creek area was Dennis O. 
Hickey (Little in Walker et al. 1996:Appendix A) who during the post-Civil War 
decades farmed, growing “large crops of cabbage, eggplant and squash” (Grismer 
1982:109), “raised” cattle in the woodland tradition and also operated a store in 
Fort Myers (Little in Walker et al. 1996:Appendix A). Also, during the period of 
1870-1926, cattle drives (Dodrill 1993:10), some led by Hickey, regularly pushed 
through both the Hickey’s Creek (Little in Walker et al. 1996) and Cape Coral (Zeiss 
1983:26; 111-113) areas grazing and trampling in the pine woods on their way to 
Punta Rassa where the animals were then shipped to Cuba. Hickey’s descendent, 
Mrs. Beverly Little, believes the location of Hickey’s home, however, was beyond 
the boundaries of our survey parcel. 

The park includes the archaeological remains of a logging rail system, two 
logging camps, and associated refuse dumps, all dating to the 1930s and 1940s. 
Only the younger of the two camps had been recorded with the Florida Site File. 
Our primary informant, Mr. Dan Garner (Figure 2), told us that an earlier, 1930s 
camp and rail line had existed, and he took us to this location in what today is a 
dense, high saw-palmetto prairie (Walker et al. 1996: Appendix D). There, the sur- 
vey crew found a few surface artifacts reflecting the decade. 

We soon learned that the Hickey’s Creek area was an important part of what 
once was an extensive logging network run first (1924-1929) by the J. W. McWilliams 
Lumber Company and later (1929-1944) by the Dowling & Camp Company (Pickens 


284 WALKER Vol. 20, No. 2 


in Walker et al. 1996: Appendices B and C). Two brothers, William and James, were 
sons of Thomas Dowling, who ran a logging operation in north Florida along the 
Suwannee River centered at Dowling Park (Anonymous 1988; Doris Dowling 
Crews, personal communication, 2000). Vaughn Camp was of the Camp family, 
which centered its extensive operations in Franklin, Virginia (Rouse 1988). Dowling 
and Camp’s logging network included what are today two major population ar- 
eas of Lee County—Cape Coral and Lehigh Acres—the former located on the north 
side of the Caloosahatchee and the latter located just to the south of Hickey’s Creek. 

At the beginning of the HCMP survey project, we assumed that only south 
Florida slash pine had been logged from the Hickey’s Creek and Cape Coral areas. 
But after our initial historical and oral history work, we began to consider that the 
logged forest adjacent to and south of Hickey’s Creek also may have included 
significant longleaf pine and wiregrass components (Walker 1997; Walker et al. 
1996). Both areas share in large part a common soil association, the Pineda-Boca- 
Oldsmar, which falls into the category of nearly level, poorly drained, deep sandy 
soils with a pine flatwoods association (USDA SCS 1984). 

Despite the poorly drained soil association, the land south of the river was 
recorded by Vignoles as “high pine” land on his 1823 natural history map of Florida. 
He typically used “high pine” to refer to longleaf pinelands similar to its use to- 
day (Myers 1990:153, 174). Botanist John Harshberger (1914) was more explicit 
when he stated that longleaf occurred mixed with the more dominant south Florida 
slash pine, both north and south of the Caloosahatchee. Efforts to locate company 
records that might more clearly identify the species of logged pines—through 


FIGURE 2.—Author’s primary informant, lumberman and cattleman Mr. Dan Garner of 
Alva, Florida, was interviewed in January of 1996 near Hickey’s Creek. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 285 


Dowling relatives and other avenues—were unsuccessful. A Fort Myers 1926-1927 
telephone directory listed the McWilliams Company as manufacturers of “Rough 
& Dressed South Florida Dense Long Leaf Yellow Pine” lumber (Walker et al. 
1996:47). During the time of this listing, the McWilliams Company was logging 
Cape Coral (Zeiss 1983:98-108). Interpretation of the listing is not straight-forward. 
Both south Florida slash and the longleaf pine produced wood that was more 
dense than the northern slash pine. Might McWilliams have been advertising both 
south Florida slash and longleaf pine with no distinction, in light of Harshberger’s 
mixed longleaf/slash record for Lee County and Wahlenberg’s (1943:268) point 
that high quality pine wood was often sold as “longleaf,” regardless of species? 
The name “longleaved yellow pine” is listed by Mohr (1896:13) as one of the com- 
mon names for longleaf and thus suggests that at least some of the Cape Coral 
pine was longleaf. And furthermore, Sudworth’s map records the presence of 
longleaf in the Hickey’s Creek area but only slash pine to the south in the Lehigh 
Acres area, suggesting a longleaf component there. It is probably no coincidence 
that the areas targeted for logging first by McWilliams and later by Dowling and 
Camp were areas indicated on Sudworth’s U.S. Forest Service map as including 
longleaf pine. 

A lifelong local resident, lumberman/cattleman Dan Garner (Walker et al. 
1996:Appendix D) (Figure 2), during the archaeological survey, described the old- 
growth forest just south of the Caloosahatchee at Hickey’s Creek: 


That was the most beautiful pine you ever seen in your life. You just go 
out there, and you could see a turkey and anything else...there weren’t no 
weed, no palmettos, no nothing. Heart pine. Big heart pine. ...it wasn’t 
near this rough [with high saw palmetto like today]...lots of tortoises and 
hogs out here...deer, turkey, bobcat...when I was a boy, this was the best 
place in the world...you could kill all the game in the world. 


Unfortunately, Mr. Garner and other local residents of the area knew these 
pine trees only as “heart pine” or “yellow pine.” (Mr. Garner intended to take me 
to see a mature pine forest in the Lake Okeechobee area—one that is very similar 
to how he remembered Hickey’s Creek’s old-growth forest, but he died before we 
could go.) The same common-language problem is true of the Cape Coral oral 
histories that Zeiss (1983) collected. The phrases “virgin pine,” “first growth trees,” 
and “heartwood” appear throughout—but no mention of species. Most of Cape 
Coral was described as “high pineland” by early residents (Zeiss 1983:180). 

The pre-logged areas of Cape Coral and Hickey’s Creek may be characterized 
best by seasonally wet mixed south Florida slash and longleaf flatwoods. The wetter 
Lehigh Acres locale probably supported mostly slash pine and both the Hickey’s 
Creek and Lehigh Acres locales included some areas of pond cypress wetland. 
Based on Sudworth (1913) and Harshberger (1914), Lee County’s pre-logged 
flatwoods, while many included longleaf, were dominated by the south Florida 
slash pine. This characterization is a revision of my earlier hypothesis of longleaf- 
dominated flatwoods for northern Lee County (Walker 1997; Walker et al. 1996). 


Cape Coral and Hickey’s Creek/Lehigh Acres Logging Operations.—Typically, lumber 
companies clear cut southeastern old-growth pine forests, moved on to the next 


286 WALKER Vol. 20, No. 2 


FIGURE 3.—Photograph taken in north Florida of a mule-drawn high-wheeled log cart 
(with a longleaf pine log) fitting cattheman Mark Bateman’s description of the circa-1940- 
1944 carts at Hickey’s Creek. 


area to be logged, and sold the logged land as soon as possible. The Cape Coral 
and Hickey’s Creek/Lehigh Acres operations followed this pattern. Once the At- 
lantic Coast Line completed a line to Fort Myers and later the Seaboard Air Line 
Railway Company completed a line from Fort Myers east into interior south Florida 
(Grismer 1982:233-234; Turner 1999:33-36; Walker et al. 1996: Appendices B and Kk), 
nearby pinelands were purchased or leased by the lumber companies. McWilliams 
began logging in 1924 and cut pine to build a large sawmill and houses at Slater 
(Zeiss 1983:99) in what is now North Fort Myers (Figure 1, inset). McWilliams 
and, after 1929, Dowling & Camp logged the pine flatwoods of Cape Coral. Dowling 
& Camp later logged the pine flatwoods of the Hickey’s Creek and Lehigh Acres 
areas from 1932 to 1935 and 1940 to 1944 (Walker et al. 1996). The intervening 
years were spent logging an area in neighboring Hendry County also on the south 
side of the Caloosahatchee River. This may be in part a locale depicted by Sudworth 
(1913:Map 35). 

Company rail crews laid “spurs” into the pine flatwoods; the rails were laid 
on ties hewn from pine. A logging crew of about 100 men cut 100,000 board feet a 
day, about 800 to 1,000 trees a day in the Hickey’s/ Lehigh area (Garner in Walker 
et al. 1996:56:Appendix D). Estimates of 50,000 to 120,000 board feet a day are 
reported for Cape Coral (Board and Bartlett 1985:115; Zeiss 1983:100). Trees were 
felled by axe or reciprocating saw and logs were chained to high-wheeled carts, 
and then pulled, dragging one end, by teams of mules to the rail spur (Figure 3). 
Cattleman Mr. Mark Bateman (Walker et al. 1996: Appendix H), a local resident, 
recalls the scene from his youth: 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 287 


What I was impressed with — because as a young kid, watching the mules 
pull the logs out to the road...all the leather and chains [of the big-wheel 
log carts] and everything going together and hearing the mule skinner 
with the whips and what have you. ... they had the big chain wheels, you 
know, so high...sand wheels and they’d back over the logs. ... They had 
the steam engine. ... But they snaked everything to the edge with mules. ... 
That was something to see. I can hear it and see it just as plain as you and 
I talking right now. 


The 1940s logging episode saw the addition of at least one Caterpillar tractor, 
operated by Mr. Garner, to the Hickey’s/Lehigh operation (Garner in Walker et al. 
1996:Appendix D); one artifact collected during the archaeological survey is a ca. 
1940s Caterpillar clutch disc. Mules, however, continued to be the primary haul- 
ers of logs out of the woods. Mr. Garner also noted the addition of an electric saw 
toward the end of the operation, ca. 1943-1944. Logs were loaded onto flatcars 
using steam-powered draglines and a company-owned steam locomotive (fueled 
by pine slabs) then pulled the logs to Slater Mill. At one time, Dowling & Camp 
operated with ten locomotives. In 1944, seven remained. Engine #103 (Figure 4) 
was used to remove logs from the Hickey’s/Lehigh area, taking them to Slater. 

As soon as an area was “cutover,” rail crews picked up the iron spurs and re- 
laid them in new, uncut areas of forest (Garner in Walker et al. 1996: Appendix D; 
Zeiss 1983:102). The railroads and their rail spurs, even when taken up, left visible 
grades, especially in south Florida where beds often were raised to avoid the sea- 


7 


FIGURE 4.—Dowling & Camp’s Engine 103 hauled pine logs from the Hickey’s Creek 
operation to the mill at Slater. Photo courtesy of James Pickens. 


288 WALKER Vol. 20, No. 2 


sonally flooded lowlands. The grades are usually paralleled by excavation ditches 
as is the case at Hickey’s Creek. Lost railroad spikes and spent ties are often found 
in the ditches. In addition, as the logs were dragged from the woods, they left 
linear “scars” in the ground, all leading to the closest rail spur. Studied from aerial 
views, the spurs and log scars can be traced, revealing dendritic or feather-like 
patterns (Pickens in Walker et al. 1996: Appendix B). A series of aerial photos taken 
in 1944 covering the two Lee County areas documents the spurs and log scars, 
which allowed Mr. James Pickens to reconstruct the logging system (Figure 1, in- 
set). The feathery patterns show the two major components of the system. The 
eastern Hickey’s/ Lehigh component is the smaller of the two. The larger, western, 
Cape Coral component originated at Slater Mill where logs from both areas were 
milled until the mill and all logging closed down in 1944 (Board and Bartlett 
1985:115; Godown and Rawchuck 1975:108; Walker et al. 1996:Appendix F; Zeiss 
1983:99). 


Cape Coral and Hickey’s Creek Logging Camps.—Temporary camps for the logging 
and rail crews and their families were established in the woods. Typically, only 
one woods camp would exist at a time. Zeiss interviewed several individuals who 
remembered various camps in the Cape Coral area. Locations for at least four 
camps were described (Zeiss 1983:103, 105). One of these consisted of “shacks” 
and others used boxcars or railroad passenger cars for housing. Detailed memo- 
ries of the Hickey’s/Lehigh logging operation and its camps come from Mr. Garner 


FIGURE 5.—Photograph taken in a west Florida longleaf forest shows a boxcar logging 
camp similar to those described for Hickey Creek circa 1932-1935 and 1940-1944 (mules 
were used at Hickey’s Creek instead of oxen). Photo courtesy of Florida State Archives, 
Tallahassee, FL. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 289 


(in Walker et al. 1996: Appendix D). When about 10 years old, Mr. Garner frequented 
the ca. 1932-1935 camp and while in his teens he worked with the logging crew of 
the ca. 1940-1944 camp. Both camps consisted of railroad boxcars serving as year- 
round, portable homes for the logging and rail crews and their families. Both crews 
of both camps were African American. The crew supervisors were EuroAmerican 
and lived in the nearby town of Alva and elsewhere. Mr. Frank Gay at one point 
supervised the Hickey’s Creek crew (Mrs. Serena Gay, personal communication, 
1996). A photograph taken in a northwest Florida longleaf forest shows a boxcar 
logging camp (Figure 5) similar to the one described for Hickey’s Creek except 
that mules were used instead of oxen. The camps had outhouses, and although 
temporary, the 1940s camp had substantial government [WPA]-built privies with 
cement foundations. 

Both camps had commissaries for purchasing groceries, dry goods, and per- 
sonal items. The 1930s commissary, like the workers’ homes, was a boxcar. This 
was probably also the case with the Cape Coral camps since there was a large 
commissary not far away at Slater. The 1940s Hickey’s Creek commissary, on the 
other hand, was a substantial one-story structure built of “heart pine” lumber. 
Workers were paid with company “scrip” and aluminum tokens, a common prac- 
tice among logging companies, particularly during the Depression era. Children 
rode a bus to attend school in Fort Myers. A medical doctor visited once a week 
from Fort Myers and administered medicines contained in bottles such as those 
found during our survey (Walker et al. 1996). Mr. Garner describes camp life with 
images of children, baseball, sour-orange wine, whiskey made from cane-skim- 
mings, and “good times.” Vegetable gardens, i y pork and beef, and local 
wildlife including gopher tortoises, raccoons, and fish, were central to the diet of 
the woods community. 


Post-Logging Decades.—Like many of the Southeast’s pine flatwoods, those of the 
Cape Coral and Hickey’s/Lehigh areas were clear cut. In addition to removing 
the seed source, the logging activity greatly disturbed seedlings that were present, 
along with the seedbed itself. Combined with the destructive feeding behavior of 
feral pigs, the competition from fast-growing oaks, the reduction of fire, the intro- 
duction of citrus and other agricultural crops, and open-range cattle grazing, the 
mixed longleaf/slash pine forests had little opportunity to regenerate. The remain- 
ing old-growth pine stumps at Cape Coral were extracted from the land and 
transported to Mississippi and to Brunswick, Georgia for use in naval-stores prod- 
ucts (Zeiss 1983:180). At some point, stumps at Hickey’s Creek also may have been 
taken out (Roger Clark, personal communication, 1996; Riley et al. 1993:22); we 
observed telltale depressions in the ground during our survey. Taking advantage 
of the highly desired dense pine to the very end, landowners salvaged the lumber 
out of the old Hickey’s Creek commissary building during the 1950s (Crawford in 
Walker et al. 1996:Appendix I) to use elsewhere. 

For a while, the land that today is the county’s HCMP and is largely in south 
Florida slash pine, scrub oaks, and saw palmetto, was used for cattle grazing by 
cattlemen, including Mr. Garner. Through the late 1940s, the 50s, 60s, 70s, and 80s, 
Garner and others conducted burns in order to provide new grass growth for their 
cattle, a longstanding woodland-grazing tradition (Garner in Walker et al. 1996:Ap- 


290 WALKER Vol. 20, No. 2 


pendix D). Despite these burns, however, the Hickey’s Creek pine forest only par- 
tially recovered from the clear-cut logging. During these same decades, feral pigs 
were still in abundance and citrus groves were planted in some of the area (Little 
in Walker et al. 1996:Appendix A). 

During the 1940s and 1950s, cattle also continued to be an important element 
of the Cape Coral and Lehigh Acres landscapes but this use of those logged lands 
came to an end during the latter part of the 1950s. Lee County’s human popula- 
tion increased dramatically in the post-war years, a time of housing shortages. 
And many WWIIservicemen who had been stationed in Fort Myers returned with 
their families to establish new homes. So, not surprisingly, most of the cleared 
land in the Lehigh Acres locale, first transformed into ranchland, soon (by 1954) 
ended up under the ownership of a development firm initially called Lee County 
Land and Title Company, and later, Lehigh Development Corporation (Dodrill 
1993:6). The developers’ marketing strategy to lure families to Lehigh Acres in- 
cluded a 1961 promotion in which a new home was offered as Grand Prize on the 
TV show “The Price is Right” (Figure 6) (Board and Bartlett 1985:186). Similarly, in 
1958, a massive housing development was initiated in the western sector of Lee 
County’s logging system (Dodrill 1993; Zeiss 1983). Today Cape Coral (Figure 1, 
inset) has become, landwise, the second largest city in area in the south next to 
Jacksonville, Florida (Gainesville Sun, Sept. 11, 2000). 


FIGURE 6.—In 1961, TV game show The Price is Right offered as Grand Prize a new 
south Florida (Lehigh Acres) home located in the logged pinelands that were part of the 
Hickey’s Creek/Lehigh pine logging system. Photo from Board and Bartlett (1985). 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 291 


SCALAR PERSPECTIVES 


Following the introduction of European domestic animals, the degradation of 
old-growth forests accelerated and largely followed the transgression of non-Span- 
ish EuroAmerican settlement (Frost 1993; Wahlenberg 1946; Walker 1991). The 
process was slow at first, in the eighteenth century, and intensified with the ar- 
rival of railroads in the nineteenth and tietl turies that were pushing farther 
and farther into the southern states. Thus, while southeastern Virginia was the 
first subregion to lose the longleafs on a massive scale, mostly in the eighteenth 
century, south Florida was the last, losing its old-growth longleafs and south Florida 
slash pines in the 1920s through the 1950s. 

The local historical ecology of Lee County’s pine forests at Cape Coral and 
Hickey’s Creek/Lehigh Acres may be largely typical of the process of landscape 
change that occurred with other south Florida pine forests. One important differ- 
ence, however, stands out. The majority of Lee County’s pre-EuroAmerican pine 
flatwoods may have been characterized by a mixture of south Florida slash and 
longleaf pines, with longleaf representing the southernmost limit of its range. It 
may be more appropriate to conceive of two south Florida subregions in terms of 
pine forests. One is the transitional south Florida where longleaf diminishes in 
dominance, mixes with south Florida slash until a point is reached when only 
slash occurs. The latter situation of “pure” south Florida slash flatwoods is the 
second south Florida subregion. 

The reconstructed pre-E American position of south Florida’s pinelands 
is in reality nothing more than a reconstruction of one ecological episode in the 
historical continuum. Representing today’s southernmost extent of longleaf, this 
marginal subregion is the ideal area to test for the long-term climatic episodes— 
commonly known as the Roman Optimum, Vandal Minimum, Warm Medieval 
Period, and Little Ice Age—of the past two millennia. During the cooler/drier 
periods (VM, LIA), longleaf may have expanded farther into south Florida while 
during the warmer /wetter episodes (RO, WMP), longleaf may | treated north 
The nineteenth and early twentieth centuries correspond with the end of the LIA; 
thus our perception of a reconstructed pre-EuroAmerican forest might better be 
situated in the LIA, an episode of hypothesized longleaf expansion. And our con- 
cept of a twenty-first-century range of south Florida pine flatwoods and their 
composition might better be situated in our current warm and wet trend with a 
hypoth 1 retreating longleaf distribution. Unfortunately, tracking of fluctuat- 
ing pine forest composition through time awaits the development of methods to 
identify the archaeological and paleoecological remains of longleaf versus slash 


e. 

At the local scale, the historical ecology of Lee County’s pinelands is generally 
similar to that of the greater southeastern Coastal Plain region, but important dif- 
ferences exist. First, although it remains to be tested (if possible), I hypothesize 
that like many subregions of the Southeast, Lee County’s American Indians fire- 
managed their local pine flatwoods. However, whereas in other areas of the 
Southeast, clearing for agriculture by American Indians may have been a factor, it 
wasn’t in south Florida. Rather, here the purpose likely would have been for main- 
taining game populations, especially those of white-tailed deer. 


292 WALKER Vol. 20, No. 2 


The impact of cattle and especially pigs may have been longer, extending later 
in time in south Florida than in other southeast subregions. Still the frontier in the 
nineteenth and early twentieth centuries, south Florida continued its open-range 
tradition (historic American Indian and EuroAmerican) and cattle drives 
(EuroAmerican) through both the Cape Coral and Hickey’s/Lehigh locales on the 
way to Punta Rassa for shipment to Cuba as late as the 1920s. Even so, it might be 
argued that cattle and pinelands may have been compatible rather than in conflict 
with the pinelands. Although today most of the cattle industry exists to the east in 
interior lands of south Florida, feral pigs are still a challenge for management and 
restoration of the HCMP pinelands. 

One el tin the I J le Sout} t trajectory that may be largely miss- 
ing from Lee County’s forest history is naval-stores production. Despite the fact 
that the Hickey’s Creek property at one time was owned by Consolidated Naval 
Stores Corporation (Walker et al. 1996:69-70), I found no record or memory of ac- 
tual turpentining. Zeiss’s (1983:98) explanation for the absence of turpentining in 
the Cape Coral area is that the pines were more valuable as lumber for building 
material because it “was loaded with pitch, which served to protect it against dry 
rot as well as from invasion by termites.” Perhaps by the time broad scale indus- 
trial exploitation of forests reached south Florida, the importance of turpentining 
had faded and clear-cut logging was economically more desirable. 

Another difference is that fire suppression may not have been as important a 
factor in the inability of the Cape Coral and especially Hickey’s Creek forests to 
regenerate: during the post-logging years, the area’s cattlemen regularly burned 
the logged lands. For Cape Coral and Hickey’s Creek, the impact of clear-cut log- 
ging (destruction of the seed source) followed by the pressures of cattle and 
feral-hog grazing, trampling, and rooting, the introduction of citrus trees and other 
agriculture (in some areas), was too great for any remaining longleaf seedlings. 
Furthermore, Cape Coral and the southern portion of the Hickey’s Creek logging 
system (Lehigh Acres) were quickly transformed by developers into residential 
communities. During this time (1950s), however, a close watch was kept and fires 
were suppressed in the Cape Coral area, as more and more new residents arrived. 

Another difference, more temporally related, is that logging everywhere in 
south Florida was more rapid than in more northern subregions. This was due, at 
least in part, to advances in logging technology during the 1940s. The operation at 
Hickey’s Creek combined the old ways—axe, mule and cart, railroad, locomo- 
tive—with some of the new ways—electric saw, tractor—although the old still 
dominated. By the 1950s, trucks were regularly replacing the need for railroads 
and locomotives in some areas of south Florida (e.g., Collier County). Again, we 
see two south Florida logging histories, one characterized by a transition in tech- 
nology, the other by an essentially modern technology. 


CONCLUSION 


What became of the once extensive old-growth southeastern pine forests in- 
volved a long process of dynamic interplay between numerous environmental 
and cultural factors possibly beginning as early as A.D. 800 in some parts of the 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 293 


region. Generally (i.e., at the long-term regional scale), the same process of land- 
scape change happened across the entire Southeast distribution of longleaf pine. 
A historical ecology approach to southeastern pine deforestation, however, con- 
tributes to the recognition of heterogeneity within the process of this broad-scale 
landscape change. In particular, examination of the southernmost margin of 
longleaf clarifies the extent of its pre-EuroAmerican penetration into southwest 
Florida (at least for the LIA). The study of Lee County’s pine flatwoods from a 
historical ecology approach has resulted in the hypothesis that longleaf pine was a 
component of Cape Coral’s and Hickey’s Creek’s pine forests. Intergrading with 
south Florida slash pines, these longleafs would have been the southernmost of 
their range. Harris (1999) makes the point that south Florida’s tropical forests have 
been under documented and thus under appreciated. The same can be said for 
south Florida’s pine forests. 

Southwest Florida experienced the longest history of pre-logging pine defor- 
estation with perhaps one of th t of logging It was a subregion 
of transition where longleaf and south Florida slash pines intergraded and where 
old and new logging technology came together, but also an area where the 
longstanding tradition of compatible fire-managed woodland grazing persisted 
into modern decades. To cap the processual continuum, large portions of Lee 
County’s logged old-growth pinelands were transformed into two of the earliest 
post-war massive suburban housing developments, the beginning of a new era 
for south Florida—one of enormous human migration to the Florida’s subtropics. 

Estimates for upland landscape changes are presented by Frost ( 1993:19-20). 
An astonishing 85 percent of the Coastal Plain’s pre-EuroAmerican uplands in- 
cluded longleaf pines (71 percent consisted of longleaf-dominated uplands). Slash 
pine, on the other hand, is estimated to have characterized only 3.3 percent of the 

re-EuroAmerican uplands. Estimates for 1990 are a stunning 2.6 percent for “natu- 
ral” longleaf (2.1 percent for longleaf-dominated uplands) and 0.4 percent for 
“natural” slash pine uplands, with successional mixed hardwood-pine forests (44 
percent), croplands (20.8 percent), pine plantations (15.2 percent), developed lands 
(10.2 percent), and pasture (6.4 percent) having replaced the old-growth native 
pine forests. 

According to a 1995 inventory, longleaf pine acreage continues to decline in 
the greater Southeast and in Florida (Outcalt and Sheffield 1996:2, 20). Most losses 
have occurred on privately owned lands. Because remaining stands on private 
lands are continuing to reach saw-timber size, losses will most probably continue 
at a high rate. Based on a study of North Carolina longleaf, Frost (1993:21) figures 
that few existing stands are being fire-maintained and as a result the majority of 
stands are heavily invaded by hardwood paces. If this pattern is typical of the 
t less than 0.7 percent of the pre-EuroAmerican 


Southeast region, F a a 
longleaf forests remains under’ “natural” conditions : t efforts on county, 
state, federal, and try and p , Boyette 
1996). However, of the longleaf states, only Texas shows small i increases on both 
public and industry lands (Outcalt and Sheffield 1996:20). No increases are shown 


for private lands. 
Restoration efforts aimed at both longleaf and slash pine forests include new 


294 WALKER Vol. 20, No. 2 


management plans that emphasize periodic burning of the forest ground layers. 
Efforts by conservation | groups large and small, such as The Nature Conservancy, 
Tall Timbers R (north of Tallahassee, FL), Longleaf Alliance Johnson 
1996; Longleaf Alliance n.d.) of Auburn University’s School of Forestry, and the 
Longleaf Partners Funds/Longneedle Press (Moore and Goodwin 1995, 1996) and 
Longleaf Ecology and Forestry Society (LEAFS), both of Gainesville, Florida, are 
educating the public and landowners of the values of restoring native longleaf 
ecosystems. For example, a recently published management guide for landown- 
ers (Franklin 1997) provides guidelines for burning practices and for compatible 
timber and cattle production, once again following the centuries-old tradition of 
pineland grazing. The developing trend in landowner education is the promotion 
of compatibility between longleaf reforestation and economic viability (e.g., 
Franklin 1997; Landers et al. 1995). Modern studies show that with appropriate 
management, overall longleaf growth rates are comparable to the other pines on 
most lands (Franklin 1997:5). 

Southwest Florida’s Lee County together with the Florida Game and Fresh 
Water Fish Commission have initiated reforestation in the new HCMP, planting a 
mix of south Florida slash and longleaf pines. A restored, fire-managed pine forest 
would be good habitat for a gopher-tortoise preserve, fulfilling one conservation 
goal of the HCMP. In addition, an archaeological National Register nomination 
(for the multiple historic logging sites) and a public education program including 
on-site ecological and historical interpretation and trails are being considered for 
the near future. 


ACKNOWLEDGMENTS 


This paper is in part based on the 1996 final report for the Hickey’s Creek Archaeological 
Survey project, co-authored with Robin L. Denson and Gary D. Ellis of the Gulf Archaeology 
Research Institute (GARI) and submitted to Lee County’s Division of Public Parks & 
Recreation Services, Fort Myers, Florida. It is an expansion and revision of the author’s 
earlier hypotheses concerning the presence and extent of longleaf pine at the HCMP. 
Numerous agencies, groups, and individuals contributed to the Hickey’s Creek project. 
Listed alphabetically, some of the most prominent are Gloria Andrews, Mark Bateman, Jan 
and Robin Brown, Roger Clark (Lee County Parks & Recreation), Raymond Crawford, 
Russell Dorsey (GARI), Charles Foster (Alva Museum), Dan Garner, Bill Gifford (GARI), 
Carol Goodwin (Goodwin Heart Pine), Larry Harris (UF), Bud and Shirley House (Randell 
Research Center [RRC]), Beverly and Bobby Little, Kevin Lollar (Fort Myers News Press), 
William Marquardt (Florida Museum of Natural History [FLMNH]), Kent Perkins (FLAS/ 
FLMNH), James Pickens, Donna Ruhl (FLMNH), Gloria Sajgo and Annette Snapp (Lee 
County Planning), Anna and Ray Stober (RRC), Jim Radz (GARI), Mark Renz, Self & Rost, 
Inc. Engineers, Southwest Florida Archaeological Society, Southwest Florida Historical 
Society, Don Taggart, Fred Tyers, Ken Wishlow, and Howard Yamataki (Soil Conservation 
Service). In addition, Sue Ellen Hunter produced Figure 1, Myrna Sulsona translated the 
abstract, and Donna Ruhl, William Marquardt, Doria Gordon, Roger Clark, Gail Wagner, 
and anonymous reviewers suggested improvements to the article. 


Winter 2000 


JOURNAL OF ETHNOBIOLOGY 295 


LITERATURE CITED 


ABRAHAMSON, WARREN G., and 
DAVID C. HARTNETT. 1990. Pine 
flatwoods and dry prairies. Pp. 103-149 


University of Central Florida Press, 


Orlando. 
gp eat Tk; ICE A: 1976. Florida 


Part Sten sae Cattleman’s 
Association, Kissimm 
ANONYMOUS. 1988. “The Village: 


Commemorating 75 Years of Christian 
Commitment and Compassion 1913- 
1988. Advent Christian Village, Dowling 


BALEE, WILLIAM (editor). 1998. Advances 
in Historical Ecology. Columbia 
University Press, New York. 

BARTRAM, WILLIAM. 1791. The Travels 
of William Bartram (M. oS Doren, 
editor, 1955). Dover, bigs 

BENGTSON, GEORG , JOHN DUPRE, 
WILLIAM TWOMEY, and ROBERT 
HOOPER. 1993. Longleaf ecosystem 
restoration in the wake of Hurricane 
Hugo. Pp. 339-347 in Proceedings, Tall 
Timbers Fire Ecology Conference No. 


Timbers Research Station, Tallahassee. 
BOARD, PRUDY TAYLOR and PATRICIA 
POPE BARTLETT. 1985. Lee County: A 
Saad History. The Donning 
mpany, Norfolk. 
BOYETTE, WARREN G. 1996. Results of 
leaf Pine 


I, II, 11). North Carolina Division of 
Forest Resources, Raleigh. 

RINTON, DANIEL G. 1869. Guide-Book 
of Florida and the South, for Tourists, 
Invalids and Emigrants, with a Map o 
the St. John River (1978 edition). The 
University Presses of Florida, 
Gainesville. 

BUTLER, CARROLL B. 1998. Treasures of 
the Longleaf Pines Naval Stores. Tarkel 
Publishing, Shalimar. 


CRUMLEY, CAROLE L. 1994a. Preface. Pp. 
xiii-xiv in Historical Ecology: Cultural 
Knowledge and Changing Landscapes, 

arole L. Crumley (editor). bees of 
American Research Press, Sa 

. 1994b. Historical Ecology: a 

multidimensional ecological 

orientation. Pp. 1-16 in Historical 

Ecology: Cultural Knowledge and 

Changing Landscapes, Carole L. 

Crumley (editor). School of American 

Research Press, Santa Fe. 

8. Foreword. Pp. ix-xiv in 
Advances in Historical Recta William 
Balée (editor). Columbia University 
Press, New Yor 

DELCOURT, HAZEL R. and PAUL A. 
DELCOURT. 1997. Pre- columbian 
Native fi 


Appalachian PADS. Conservation 
:1010-1014. 


DELCOURT, PAUL A. and HAZEL R. 
DELCOURT. 1998. The influence of 
prehistoric human-set fires on oak- 
chestnut forests in the southern 
Appalachians. Castanea 63(3):337-345. 

eee = ISON, 
WILLIAM E. SHARP, and KRISTEN J. 
GREMILLION. 1998. Prehistoric human 
use of fire, the eastern agricultural 
complex, and Appalachian oak- 
chestnutforests: Fhavisam ats of Cliff 
Palace Pond, ucky. American 
Antiouity 63(2): 768-278, 

DODD, JR., C. cane dah 1995. Reptiles 
and amphibians n the endangered 
longleaf pine cca eten Pp. 129-131 in 


and Health of U.S. Plants, Animals, and 
Ecosystems, E. LaRoe, G. Farris, C. 
Puckett, P. Doran, and M. Mac (editors). 
U.S. Department of the Interior, 
National Biological Service, 
Washington, D.C. 

DODRILL, DAVID E. 1993. Selling the 
Dream: The Gulf American Corporation 
and the Building of Cape Coral, Florida. 
The University of Alabama Press, 
Tuscaloosa 


296 WALKER 


ENGSTROM, . -B.:.... TODD..:., 1993. 
Characteristic mammals and birds of 
longleaf pine forests. Pp. 127-138 in 
Proceedings, Tall Timbers Fire Ecolog 
Conference No. 18, The Longleaf Pine 
Ecosystem: Ecology, Restoration, and 
Management, Sharon M. Hermann 
(editor). iia Timbers Research Station, 
Tallahas 

FLORIDA COASTAL MANAGEMENT 
PROGRAM (FCMP). 1995. Protecting 
Florida’s Coastal Ecosystems: 
Conservation Through Local Land 
Acquisition and Management. Florida 
i fossa of Community Affairs, 
Tallahas 

FOLKERTS, "GEORGE W., MARK A 
DEYRUP, and D. CLAY SISSON. 1993. 
Arthropods associated with xeric 
longleaf pine habitats in the 
southeastern United States: a brief 
overview. Pp. 159-192 in Proceedings, 
Tall Timbers pain Ecology Conference 

No. 18, The Longleaf Pine Ecosystem: 
Ecology, yg hii and Management, 
Sharon M. Hermann (editor). Tall 
Timbers Research Seton. Tallahassee 

FRANKLIN, ROBERT M._ 1997. 
Stewardship of Longleaf Pine Forests: 

e 


Ecosystem: Ecology, Restoration, ~ 
Management, Sharon M. Herman 
(editor). ~ Timbers Sankt Station, 
Tallahasse 

GODOWN, MARIAN B. and ALBERTA C. 
RAWCHUCK. 1975. [serpy a s Fort 

Myers. Press Printing, Fort Mye 

GUYER, CRAIG and MARK A. BAILEY. 
1993. Amphibians and reptiles of 
longleaf pine communities. Pp. 139-158 
in Proceedings, Tall Timbers Fire 
Ecology Conference No. 18, The 
Longleaf Pine Ecosystem: Ecology, 
Restoration, and Management, Sharon 

. Hermann (editor). Tall Timbers 
Research Station, Tallahassee. 


Vol. 20, No. 2 


GRISMER, KARL H. 1982. The Story of Fort 
Myers: The History of the Land of the 
Cc 1 1 ro | ic ral <T1 pe 


A facsimile reproduction of the 1949 
edition. The Island Press Publishers, 
Fort Myers Beac 

HARCOMBE, P. A., J. S. GLITZENSTEIN, 
R. G. KNOX, S. L. ORZELL, and E. L. 
BRIDGES. 1993. Vegetation of the 
longleaf pine region of the west Gulf 
Coastal Plain. Pp. 83-104 in Proceedings, 
Tall Timbers Fire Ecology Conference 


Timbers oye Station, Tallahassee. 
HARRAR, ELLWOOD S. and J. GEORGE 

yea 1962. Guide to Southern 

Trees. Dover Publications, Inc., New 


Yor 

HARRIS, LARRY D. 1999. peak tuarked 
Florida’s ancient forests: old Flori 
words and pictures. Florida Phteaders 
of the Environment Special Bulletin, 


Summer. 

HARSHBERGER, JOHN W. 1914. The 
vegetation of south Florida south of 27° 
30' north, exclusive of the Florida Keys. 
Transactions of the Wagner Free 
Institute of Science of Philadelphia Vol. 


VII(3). 
HEADLAND, — THOMAS N. 1997. 


Current Anthropology : “ie 605-609. 
HOFSTETTER, RON 1974. The 

effect of fire on he Le td ps and 

Sawgrass communities of southern 


Society Memoir 
Environments of South Florida: Present 
and sts Patrick J. Gleason (editor and 
compiler). 

JOHNSON, RHETT. 1995. Game 
management in the longleaf pine forest 
type. Alabama’s Treasured Forests 
(summer):28-30. 

. 1996. Longleaf pine: a southern 
legacy. ee s Treasured Forests 
Su -9 

KALISZ, PAULJ., ALAN W. DORIAN, and 

EARLL. STONE. 1986. Prehistoric land- 
use and the distribution of longleaf pine 
on the Ocala National Forest, Florida: 
an interdisciplinary synthesis. The 

Florida Anthropologist 39(3):183-193. 


Winter 2000 


LANDERS, J. LARRY, DAVID H. VAN 
LEAR, and WILLIAM D. BOYER. 1995. 
The longleaf pine forests of the 
southeast: requiem or renaissance? 
Journal of Forestry 93(11):39-44. 

LITTLE, ELBERT L., JR. 1971. Atlas of 
United States Trees. Volume 1: Conifers 


1146. U.S. Government Printing Office, 

Washington, D.C. 

. 1978. Atlas of United seen Trees: 

Volume 5: Florida. U.S. Forest Service 

“parrgmosoranae Publication ae 1361. 
2. nment Printing Office, 


Washington, D 

_______ , 1980. The Audubon Society Field 
Guide to North American Trees: Eastern 
Region. Alfred A. Knopf, Inc., New 


York. 

LONGLEAF ALLIANCE. n.d. The Longleaf 
Alliance: Longleaf Pine...A Southern 
re Ha Papbe Foci Auburn University, 


MARQUARDT, WILLIAM H. and 
CAROLE. -L. ‘CRUMLEY. © 1987. 
Theoretical issues in the analysis of 
spatial patterning. Pp. 1-18 in Regional 


MACLAREN, PATRICIA A. and JAMES A. 
STEVENSON. 1993. Florida 
Department of Natural Resources 
management of longleaf pine 
ecosystems. P. 407 in Piecetings: Tall 
Timbers reste Ecology Conference Ae 
18, The Longleaf Pine Ecosyste 
Ecology, Restoration, and Mariageisiont, 
Sharon M. Hermann (editor). Tall 
Timbers Research Station, Tallahassee. 

MILANICH, JERALD T., and CHARLES 

. 1993. H to and 
Indians of —— University Pei of 
Florida, Gaines 

MORR, CHARLES. 1896. The Timber Pines 
of the oe United States. U.S. 
Departm f Agricu — Division of 
Forestry, Bulletin’ No. 

MOORE, JULIE. esas ees of the 
longleaf forest. P. 18 in Longleaf 
Legacies: pele Pine...We Can Save 
it for Profit and Pleasure, Julie Moo 
and Carol Goodwin (editors). Longleaf 
Partners Funds, Gainesville. 


JOURNAL OF ETHNOBIOLOGY 297 


hiconiiem S99G6D, The groundcover: where 
the diversity i is found. P. 19 in Longleaf 
Legacies: Longleaf Pine...We Can Save 
it for Profit and Pleasure, Julie Moore 
and Carol Goodwin —. Longleaf 
neg Funds, Gainesville 

pith role of fire in 
the eases e. P. 22 in Longleaf 
Legacies: Longleaf Pine...We Can Save 
it for Profit and Pleasure, Julie Moore 
and Carol Goodwin (editors). Longleaf 
Partners Funds, Gainesville. 

and CAROL GOODWIN. 1996. 
~~ Longleaf Legacies: Longleaf Pine...We 
Can Save it for Profit and Pleasure, A 
Calendar for 1996. Long Needle Press, 
Gainesville, FL. 

MOYROUD, RICHARD. 1996-1997. South 
Florida slash pine: Pinus elliottii variety 
densa. The Palmetto, winter:11-12. 

MYERS, RONALD L. 1990. Scrub and high 
pine. Pp. 150-193 in Ecosystems of 
Florida, Ronald L. Myers and John J. 
Ewel (editors). University of Central 

Florida Press, Orlando. 
OUTCALT, KENNETH W. and RAYMOND 
FFIELD. 1996. The Longleaf Pine 
Forest: Trends and Current Conditions. 
Resource Bulletin SRS-9. U.S. 
Department of Agriculture, Forest 
Service, Southern Research Station, 

sheville. 
PALIK, BRIAN. 1995. aba ait of 
n Longlea 


it for Profit and Pleasure, A Calendar for 
1996, Julie Moore and Carol Goodwin 
Long Needle Press, 


ville. 

PANSHIN, A. J. and C. DEZEEUW. 1980. 
Textbook Wood Technology: 
Structure, Identification, Properties, and 
Uses of the Commercial Woods of the 
United States and Canada. McGraw- 
Hill Book Co on Hem New York. 

PEET, ROBERT K. and DOROTHY J. 
ALLARD. 1993. Longleaf pine 
vegetation of the southern Atlantic and 
eastern Coast regions: a 
preliminary classification. Pp. 45-81 in 

Proceedings, Tall Timbers Fire Ecology 
Conference No. 18, The Longleaf Pine 
Ecosystem: —— Restoration, and 
Management, Sharon M. Herm 
eos — aber oss Station, 
Tallaha 


298 WALKER 


PYNE, STEPHEN J. 1998. Forged in fire: 


Ecology, William Balée henseen 
Columbia University Press, New York 
REBERTUS, ALAN J., G. BRUCE 
WILLIAMSON, and WILLIAM J. 

PLATT. 1993. Impact of temporal 


eavanna 


and pines. Pp. 215-225 in Proceedings, 
Tall Timbers ste Ecology Conference 
No. 18, The Longleaf Pine Ecosystem 
Ecology, Restoration, and Management, 
Sharon M. Hermann (editor). Tall 
Timbers Research Station, Tallahassee. 
RECORD, SAMUEL and ROBERT HESS. 
1943. Timbers of the New World. Yale 
University Press, London. 
RILEY, L., R. CLARK, K. FORSYTH, K. 
DRYDEN, and M. ALLEN. 1993. Florida 
Communities Trust Preservation 2000 
Grant Application for the Lee County 
Hickey Creek Mitigation Park. 
ROMANS, BERNARD. — A Concise 
Natural History of East and West 
Florida (a facsimile speaacane 1962). 
University of Florida Press, Gainesville. 
ROUSE, PARKE, JR. 1988. The Timber 
Tycoons: The Camp Families of Virginia 
and Florida and Their Empire 1887- 
1987. The William Byrd Press, 


ichmond. 

SCHWARZ, G. FREDERICK. 1907. The 
Longleaf Pine in be rk Forest: A Silvical 
Study. John Wiley & Sons, London. 

SARGENT, CHARLES S. 1884. Beoart on 
the Forests of North America (Exclusive 
of Mexico). Department of the Interior, 
Census Office, Washington, D.C. 

SCARRY, C. MARGARET, and VINCAS P. 
STEPONAITIS. 1997. Between 
farmstead and center: the natural and 
social landscape of Moundville. In 
People, Plants, and Landscapes: Studies 
in Paleoethnobotany, Kristen J 
Gremillion (editor). University of 
Alabama Press, Tuscaloosa. 

SMALL, JOHN K. 1930. Vegetation and 
erosion on the ste Keys. The 
Scientific Monthly 30:33-49. 

SMITH, BUCKINGHAM (trans.). 1968. 
Narratives of De Soto in the Conquest 
of Florida as Told by A Gentleman of 
Elvas and in a Relation by Luys 
Hernandez de Biedma (orig. trans. 
1866). Palmetto Books, Gainesville. 


Vol. 20, No. 2 


SNYDER, JAMES R., ALAN HERNDON, 
and WILLIAM B. ROBERTSON, JR. 
1990. South Florida ‘nockland. Pp. 230- 

Florida, Ronald L. 

Myers and John : Ewel (editors). 

University of Central Florida Press, 


Keo xzvetame 


Orlando. 

SUDWORTH, GEORGE B. 1913. Forest 
Atlas: Geographic Distribution of North 
American Trees, Part 1. Pines. U.S.D.A. 
Forest Service, Washington, D.C. 

TEBEAU, CHARLETON W. 1957. Florida’s 
Last Frontier: The History of Collier 
County. University of Miami Press, 


Miami. 

TURNER, GREGG M. 1999. Images of 
America: Railroads of Southwest 
Florida. Arcadia Publishing, Charleston. 


Food and Agricultural ‘Sciences, 
Agricultur al 
Soil Science Department, and Florida 
Department of Agriculture and 
Consumer Services, U.S. Government 
Printing Office, Washington, D.C. 

VIGNOLES, CHARLES. 1823. Observations 
Upon the Floridas (a facsimile 
reproduction 1977). The University 
Presses of Florida, Gainesville. 

WAGNER, GAIL E. In press. Eastern 
woodlands anthropogenic ecology. In 
People and Plants in Ancient North 

merica, Paul Minnis (editor). 

Smithsonian Instititution Press. 
Washington, D. 

WAHLENBERG, W. &. 1946. Longleaf Pine: 


Lathrop Pack Forestry 
Foundation and U.S. a of 
Agriculture, Washington, D.C. 

WALKER, LAWRENCE C. 1991. The 
Southern Forest: A Chronicle. 
University of Texas Press, Austin. 

WALKER, KAREN J. 1997. Historical 


p south Florida perspec 
Palmetto 17(2):16-19. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 299 


ROBIN L. DENSON, and GARY WINTERHALDER, BRUCE. 1994. Concepts 


DE ELLIS. 1996. Archaeological Survey in historical ecology: the view from 
of the Hickey Creek Mitigation Park evolutionary ecol 7-41 in 
Report submitted to the Division of Historical Ecology: Cultura al Knowledge 
Recreation and Parks Services, Lee and Changing Landscapes (Carole L. 
County, FL. Crumley, editor). School of American 
WATTS, W. A. 1993. The history of longleaf Research Press, Santa Fe. 
pine in Florida. P. 15, Abstract, in ©WUNDERLIN, RICHARD. 1998. Guide to 
Proceedings, Tall Timbers Fire Ecology the Vascular Plants of Florida. 
Conference No. 18, The Longleaf Pine University Press of Florida, Gainesville. 
Ecosystem: Ecology, Restoration, se ZEISS, BETSY. 1983. The Other Side of the 
Management, Sharon M. Herman River: Historical Cape Coral. Cape 
on ay Timbers Research Station, Coral. 
Tallaha 
WINN, JOHN. 1996. A longleaf pine 
restoration project. The Palmetto, 


Winter 1996/1997: 15-15. 


300 BOOK REVIEWS Vol. 20, No. 2 


Biodiversity and Native America. Minnis, Paul E. and Wayne J. Elisens (editors). 
University of Oklahoma Press, Norman. Pp 310, x, maps, figures, and illustra- 
tions, index. $34.95 cloth. ISBN 0-8061-3232-9. 


Biodiveristy and Native America is a significant and. essential read for students 
and researchers interested in past and present ips among 
Aboriginal peoples in North America. The book spans most of the geography of 
the United States, with representative articles covering portions of Mexico and 
Canada. This book is a beginning of what will hopefully be many books on the 
subject, the editorial product of Paul Minnis and Wayne Elisens, University of 
Oklahoma. The papers largely came together as a result of a 1997 symposium 
workshop organized around the topic of “Biodiversity and Native North America.” 
The book showcases 10 articles reflecting a variety of geographical and cultural 
perspectives, set in three sections. 

Section one: Issues and Overviews contains three articles that examine First 
Nations’ management and conservation (Sonora Desert), ethnobotony (Mexico) 
and ethnopharmacology (broad U.S. overview with implications for Peru). The 
first article by Gary Paul Nabhan bridges issues from li gy with 
conservation biology. Robert Bye and Edelmira Linares offer a fine paper summa- 
rizing the complex and evolving ethnobotanical relations among the over 54 
Indigneous language groups in Mexico. These groups have extensive knowledge 
for the Holarctic and Neotropic plant kingdoms. Walter Lewis presents an infor- 
mative, but narrow, discussion of ethnopharmacology and a possible future built 
on collaborative agreements. Lewis does not discuss how the influence of tremen- 
dous amounts of capital on traditional systems, including issues of ownership (is 
knowledge of medicinal plants individual or collective property), will be worked 
out. 

Section two: Ethnographic Case Studies, gives the greatest representation of 
“biodiversity and Native America” in this volume. The three papers represent the 
sampled knowledge of Northern Paiute, Owens Valley Paiute, Southern Paiute, 
Timbisha (Panamint), Shoshone, Ute, and Washoe; Stl’atl’imx (Lillooet / Lil’ wat); 
and Raradmuri. Catherine Fowler recounts in her paper how fieldwork with Numic 
speaking Great Basin Indian people in the 1960’s and 1970’s brought forward the 
concept “we live by them.” This “Native knowledge” may be gathered and fo- 
cussed as ethnobiological constructs, but it is embedded and expressed in the 
cultural practices and daily lives of untold numbers of Aboriginal peoples from 
whom she learned/studied. The article by Sandra Peacock and Nancy Turner is 
an excellent example of collaborative ethnobotanical research. The authors bal- 
ance academic/scholarly knowledge with traditional plant knowledge to 
understand traditional resource management and biodiversity conservation for a 
portion of the traditional territory of the Secwepeme, Stl’atl’imx, Nlaka’pamux, 
and ae people. In the third paper in this section, Enrique Salm6én exam- 
ines the Raramuri t of iwigara. The paper is a well researched and important 
paper that made me questions the role of traditional environmental knowledge. 

Many of the papers in this edition advocate changing western land manage- 
ment practices and thinking (and I support such efforts). However, if the role of 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 301 


ancient knowledge really is to reform science and western constructs we need to 
know how they will and can function within our commercialized modern world. 
What the potential and real impacts on how the Rardmuri are able to practice 
iwigara in the northern Sierra Madre Occidental is left unstated. A dominant view 
among most Indigenous groups is that ancient knowledge has intrinsic and cul- 
tural value, which scientists have a hard time understanding and accepting. 

Section three, Prehistory and Biodiversity, contains three interesting papers. 
This section will disappoint those readers who may have grown somewhat accus- 
tomed to the culturally specific, situated, and interdisciplinary tone of the volume 
to this point. The three papers in this section are more general with an over-riding 
anthropological perspective. Furthermore, the contributions in this section reflect 
a much narrower geographic focus, which does not fit with the rest of the book. 
With this said the three papers should not disappoint readers, as they offer signifi- 
cant contributions. Focussing his discussions on Northern New Mexico, Richard 
Ford examines the significance of human disturbance on biodiversity, arguing that 
“it is a mistake to regard Native Americans as insignificant managers of biotic 
resources or as passive a in the shaping of the landscape and the diver- 
sification of habitats” (219). G tzd through 
archaeological research for es pe cover a broad area of the eastern United States 
and a portion of southern Ontario. Fritz’s paper suggests the difficulties that bi- 
ologists and anthropologists run into when assessing the scale of environmental 
impacts and changes to anthropogenic influences. Unfortunately, this paper ap- 
pears to reflect a classical positivi st resea earch approach BY failing to involve or even 
consult local knowledge in ing prehistoric changes. While this may be 
the least informative paper eae Traditional knowledge, Fritz is able to dis- 
pel myths that Eastern Amerindians were non-agrarian nomadic peoples, and so 
it is nonetheless an important paper for readers to consider. The final paper in this 
edition by Julia Hammett, an already published journal article (was originally her 
master’s thesis), examines the ethnohistory of the southeastern United States. 
Hammett cautions that historical accounts are “loaded with distortions, biases, 
and contradictions” and suggests that it is important to understand the cultural 
context of the original authors, an ambitious project to say the least (p. 253). This 
paper is both informative and provocative and completes the book in a way that 
urges readers on to further research. 


Chris Hannibal-Paci 
First Nations Studies 
University of Northern British Columbia 


Journal of Ethnobiology 20(2): 303-325 Winter 2000 


A CLADISTIC APPROACH TO Dr ny 
ETHNOBOTAN 


T 
DYE PLANTS OF THE SOUTHWESTERN UNITED STATES 


KIMBERLY HAMBLIN HART 
Department of Botany and Range Science 
Brigham Young University 
Provo, Utah 84602 USA 


PAUL ALAN COX 
National Tropical Botanical Garden 
3530 Papalina Road 
Kalaheo, Hawati 96741 USA 


ABSTRACT.—An intensive review of the ethnobotanical literature on dye plants 
used by 11 indigenous tribes in the Southwestern region of the United States 
revealed that 108 plants have been used to manufacture dyes for coloring wool, 
leather, cotton and other plant fibers. seme pee ee are also used to obtain 
pigments for pottery and body paint used to color food. Of the 11 
different plant dye traditions evaluated in this ay the Navajos use the greatest 
number of plants (n=69) for dye purposes. Considering innovations in dye plant 
traditions shared among tribes to be analogous to shared derived characters in 
phylogenetic analyses (termed “synapomorphies”), a cladistic analysis shows that 
traditions of dye plants are most derived among the Navajo and Hopi tribes. The 
traditions of dye plants of these two tribes are also more closely related to each 
other than either tradition is to dye plant traditions from other tribes. The cladistic 
approach of analyzing shared derived technologies appears to be a useful way of 
generating hypotheses concerning cultural diffusion of plant uses in other 
ethnobotanical studies. 


Key words: cladistics, dye plants, ethnobotany, Southwestern Native Americans. 


las plantas 


RESUMEN.—Una revision intensiva de la literatura ent 

del tinte usados por 11 tribus indigenas en la region al sudoeste de los Estados 
Unidos revelé que 108 plantas se han utilizado para fabricar los tintes para las 
lanas del colorante, el cuero, el algod6n, y otras fibras de la planta. Un ciertas 
especies de la planta también se utilizan para obtener los pigmentos para la 
cerdmica y la pintura de cuerpo en ane otras se utilizan para colorear el 
alimento. De las 11 trib io, la tribu de Navajo utiliza el 
numero mas grande de las plantas (n=69) para los propésitos del tinte. 
Considerando innovaciones en las plantas del tinte compartidas entre las tribus 
para. ser el equivalente si fermip pepe se dice “synamorphies,” un analisis 
el tribus de Navajo y de Hopi son seradhe 


mas de las plantas del tinte. Estas do 

uno al otro en sus Lao de la planta del tinte que estan a pas ei otra 
tribu. El acercamiento cladistic de analizar tecnologias derivadas compartidas 
aparece ser una manera ttil de generar hipétesis referentes a la difusi6n cultural 
de las aplicaciones de la planta en otros estudios ethnobotanical. 


304 HART and COX Vol. 20, No. 2 


RESUME. Une | revue approfondie de la literature ethnobotanique est presenté 
sur 108 pl tribus indigénes a la region suroeste 
des Etats Unis. Elles sont utilisées pour teindre de la laine, le cuir, le coton, et 
quelques autres fibres vegetales. La tribu Navajo utilis le plus grand nombre des 
plantes ¢ comme seiniunes hams = 69). Une analyse cladistique mnchigie ae i lined 


comme teintures et aussi elles sont plus similares entre se. 


INTRODUCTION 


The Southwestern region of the United States is considered ethnobotanically 
to be “the best studied area in the world” (Ford 1985:401). In this region, compre- 
hensive studies have been made of the plants used by indigenous people for 
medicine, food, clothing, and art (Bell and Castetter 1937; Castetter, Bell and Grove 
1938; Dennis 1939; Dunmire and Tierney 1995; Fewkes 1896; Kent 1957; Palmer 
1878; Sauer 1950; Standley 1911; Winter 1974). Other studies have focused on the 
ethnobotany of particular tribes (Castetter and Underhill 1953; Cook 1930; Elmore 
1943; Ford 1968; Hough 1897; Jones 1931, 1948; Mathews 1886; Reagan 1929; 
Robbins, Harrington and Freire-Marreco 1916; Stevenson 1915; Swank 1932; Ves- 
tal 1952; White 1945; Whiting 1939; Wyman and Harris 1941, 1951). However, 
comparative ethnobotanical studies are rare. In the early 1960’s, Whiting identi- 
fied an urgent need for “summary reports, comparative historical studies, and 
broadly based reviews of comparable data throughout the area” (Whiting 1966:318). 
Doebley (1984) responded to this call with comparative studies of wild grasses, 
yet few other similar studies have been done. Twenty years after Whiting made 
his statement, Richard Ford (1985) and Robert Bye (1985) both noted that there 
remains a void in the area of comparative work. 

We have compared use of plants for dyes and paint among different south- 
western indigenous tribes based on historical and contemporary accounts. For 
this purpose we considered all plants used to color wool, cotton, and leather, for 
food coloring, as well as for pigments for body and pottery paint. The purpose of 
our study is two-fold: Q) to Provide a comprehensive review and comparison of 
dye plants used by dians, and (2) to show how cladistic analy- 
ses may be used to generate hypotheses concerning cultural diffusion of plant 
uses between tribes. 

Linguists, systematists, and biogeographers have previously used cladistic 
techniques to study common origins of languages, biological species, and biogeo- 
graphical regions mpspertively, Unlike comparative methods that rely on overall 
similarity, s such diagrams (also 
know as cladograms) based on shared derived features or characters 
(synapomorphies). Thus, although ph 
lizards are more closely related t to ‘each other than either are to birds because of 
overall similarity, cladistic analyses group birds with crocodiles because of shared 
derived features of skull anatomy (Ridley 1993). In biology, characters used for 
cladistic analyses can be different features of anatomy, molecular sequence, be- 
havior, physiology and so forth. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 305 


We believe that cladistic analysis might be a useful method for cross-cultural 
ethnobotanical comparisons. A unique technological innovation that is subse- 
quently shared by different cultures could be considered a shared derived feature, 
called in cladistic terminology a “synapomorphy.” For example, if use of a par- 
ticular plant as a medicine originated with a single individual, but subsequently 
spread to different cultures through time, that use could be considered to be a 
synapomorphy for those cultures. Synapomorphies are used in cladistic analyses 
to indicate possible branching patterns in cladistic trees. Such shared derived in- 
novations can then be used to generate relationship trees for the technology of 
interest (such as dye plants, medicinal plants, crop varieties, etc.). Diagrams of 
these relationships, presented as trees, are termed “cladograms.” 

Technological features in common to different cultures that do not share a 
common unique derivation could be termed “symplesiomorphies.” For example, 
the use of conifers as firewood is probably common to all cultures where conifers 
occur, but likely cannot be traced to a single unique innovation, and hence is an 
example of a symplesiomorphy. Symplesiomorphies unfortunately, are of little or 
no value in determining relationship trees or cladograms. 

Some cultures may produce technological innovations that do not spread to 
other cultures. Such unique unshared innovations are termed “autapomorphies.” 
For example, use of an endemic species of algae by the Hawaiian people cannot 
possibly have spread to other islands, and hence could be considered an 
autapomorphy. Autapomorphies, while interesting for a particular culture, do not 
shed light on relationships to other cultures. 

Characters used for cladistic analyses in cross-cultural ethnobotanical studies 
could include technological, medicinal, artistic, architectural, ritual innovations. 
It is not necessary to compare biological entities; we here study plant uses because 
as ethnobotanists our interests are focused on the interactions between plants and 
people. Cladistic studies require that observable information is translated into dis- 
crete characters (Kitching et al. 1998). In cross-cultural ethnobotanical studies one 
can easily identify plants as used or not used, making such characters prime can- 
didates for cladistic analyses. Thus, we are proposing to evaluate relationships 
between uses of plants by different tribes based on shared technological innova- 
tions of dye plant use rather than grouping these uses on the basis of overall 
similarity. It is important to note that we are not, however, attempting to consider 
genetic or cultural relationships of the tribes themselves. It is only the plant uses, 
and not the people themselves, which are the objects of our analysis. Thus, while 
our diagrams of plant use relationships are not intended to suggest genetic or 
cultural relationships between different tribes, they can be used to generate hy- 
potheses of how different discoveries of new dye plants might h P through 
various cultures. : 

While cladistic techniques are simple, and for a limited number of different 
traditions of plant use (three or four) can easily be done by hand, the number of 
possible alternative relationships trees (and hence the number of calculations) in- 
creases exponentially with the number of tribes. As a result, we have had to use a 
computer program to evaluate the number of trees. As will be described shortly, 
the program basically determines which, of all possible relationship trees, is the 


306 HART and COX Vol. 20, No. 2 


most parsimonious- the one requiring the least number of steps of culture trans- 
mission, parallel innovation, and culture loss. This most parsimonious tree is then 
proposed as a candidate for evaluation by other researchers. Often, with a large 
number of taxa (here considered to be different tribal traditions of plant dye use), 
different trees of equal number of steps are discovered during the computer algo- 
rithm. We have here chosen to present a summary of the features in which all of 
these most simple trees agree: such a diagram is called a strict consensus tree. 
Further information on cladistic techinques can be obtained from a variety of text- 
books in systematic biology. 


METHODS 


General Comparison.—As a means of understanding native American traditions of 
dye plants use, we conducted interviews with Navajo weavers on the Navajo res- 
ervation in Southern Utah and Northern Arizona and observed some collections 
of dye species and dying techniques. We then expanded our study to a regional 
basis by conducting an intensive literature review, compiling ethnobotanical in- 
formation on 11 different tribes: Eastern Keres, Hopi, Jemez (Towa), Navajo, Papago, 
Pima, Southern Tiwa, Tewa, Western Apache, Western Keres (Acoma and Laguna), 
and Zuni. We chose to study the dye plant traditions of these tribes because of the 
geographical proximity of the tribes to each other, their pattern of cross-cultural 
interactions, and the availability of previous ethnobotanical studies. 

Some of the dye plants used in the past are no longer used today, yet for our 
analysis we include both historical and contemporary uses with no effort to dis- 
tinguish between the two. In our study we selected from literature accounts only 
those plants identified to the level of both genus and species, since records from 
different tribes of a plant identified only by a generic epithet might conflate differ- 
ent species, skewing our analysis. For consistency, plants identified beyond the 
species level to the varietal level were truncated to species. Appendix 1 lists each 
plant and the tribes that used it. Figure 1 illustrates approximate tribal boundaries 
and the number of dye plants use by each tribe. Ow definition of tribal bound- 
aries is somewhat arbitrary since these ver been static but vary 
in time with changes in culture, modes of transportation, and the colonization/ 
reservation boundaries forced upon different indigenous groups. For this reason, 
we used a slightly modified version of regional boundaries defined in The Hand- 
book of North American Indians (Ortiz 1983). 


Cladistic Analysis.—A cladistic analysis based on shared derived characters 
(synapomorphies), in this case, shared cultural innovations in use of dye plants, 
was performed by coding each of the 108 dye plant species as either used or not 
used for each of the 11 tribes. Our data matrix is provided in Appendix 2. No effort 
was made to differentiate between plants used to dye wool or other materials for 
two reasons: (1) we are presuming that one plant used for one particular material 
would most likely be tried on other materials as well, therefore not be exclusive to 
wool, cotton, leather, or other materials, and (2) literature accounts tend to focus 
on the plants used rather than on the types of materials dyed. Our coded data 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 307 


FIGURE 1.—Map showing the geographic proximity of tribal regions. Number of dye 
plant species used by each tribe are indicated (adapted from Ortiz 1983). 


matrix was analyzed with the computer program HENNIG86 (Farris 1988). In the 
analysis we gave each dye plant species an initial weight of one and selected the 
non-additive option. The complete search algorithm, implicit enumeration (ie), 
was used to generate relationship trees of minimal length. A strict consensus tree 
was obtained for the trees obtained from implicit enumeration of the unweighted 
characters (Figure 2). We then found equally parsimonious trees by using the xsteps 
command with the w option utilized, thus applying species weights according to 
their fit to the trees. Weights applied were calculated by the program as the prod- 


308 HART and COX Vol. 20, No. 2 


uct of character consistency index, ci (Kluge & Farris 1969) and the retention in- 
dex, ri (Farris 1989a, 1989b). Weightings were applied in successive rounds of 
implicit enumeration until no changes in tree length, consistency index, or reten- 
tion index could be obtained from successive rounds. We then obtained a strict 
consensus tree for the weighted sample. 

In a strict cladistic sense, we make no claim about the monophyletic nature of 
the traditions we have here analyzed; in fact the uses we analyze may be 
paraphyletic because 1) we do not know if all of these plant dye uses can some- 
how be traced back to a singular innovation in the uses of plants as dyes, and 
hence share the same ancestral tradition, and 2) it is doubtful if we have here in- 
cluded all possible traditions derived from an ancestral tradition; little is known, 
for example, about Anasazi use of dye plants. 

In cladistic analyses, often an outgroup possessing the “primitive” state is 
chosen in order to determine character polarities. Not wishing to make any state- 
ment about relative age and technological status of any of the 11 tribes we studied 
by claiming that one tribe’s use of a plant somehow preceded or was ancestral to 
another tribe’s use of the same plant, we rooted our analysis in the uses of plants 
by a hypothetical tribe that has never used any dye plants: hence all character 


Primitive 


Papago 


Becker 


ih Sie W. Apache 
2 Zuni 


Jemez 


W. Keres 


avajo 


Hopi 


FIGURE 2.— Cladistic relationships of dye plant traditions of southwestern Amerindian 
tribes; strict consensus tree of unweighted characters, length= 131, consistency index = 
0.82; retention index = 0.51 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 309 


States begin at zero. We note that alternative methods of cladistic analysis that 
include unrooted networks are available, but such analyses do not change the 
topology of our resultant trees, and we believe our postulation of a zero-use cul- 
tural antecedent to current Amerindian dye uses is, by reductio ad absurdum true: if 
we were to go back far enough in time (at the extreme, the first aboriginal immi- 
grants to North America), we would eventually find a group of people who did 
not use any North American plants for dyes. This group would be the most “primi- 
tive” group as far as dye technology is considered. Our subsequent analysis 
assumes that knowledge of how to use dye plants is passed from generation to 
generation rather than being independently recreated de novo each generation— 
the cultural equivalent of recurrent homoplasy in the cladistic sense. 


RESULTS 


Enumeration of Dye Plant Species—A total of 108 species, including 103 vascular 
plants, two fungi and three lichens, have been recorded as sources of dye pig- 
ments for wool, cotton, leather, body and pottery paints, and the coloring of food 
by the 11 tribes (Appendix 1). The 103 vascular plants represent 38 different fami- 
lies. The majority of the dye plant species are used to dye wool. Of these 108 species, 
the Navajo use 69, the Hopi use 24, the Western Keres use 14, the Tewa and Zuni 
use 10, the Jemez use eight, the Western Apache use seven, the Papago use six, the 
Southern Tiwa use four, and the Eastern Keres and Pima both use three species 
(Figure 1). 


Cladistic Analysis.—Our cladistic analysis based on shared cultural innovation 
(synapomorphies) in use of dye plant species initially resulted in nine trees, each 
requiring 131 steps, a consistency index of 0.82 and a retention index of 0.51. A 
strict consensus tree, which presents all features on which these nine trees agree, 
showed a basal unresolved trichotomy, but we sought to improve the consistency 
and retention indices by successive character weightings. We then performed two 
rounds of successive approximations weighting which was analyzed by implicit 
enumeration, and seven trees of different topologies (Figure 2) were obtained with 


TABLE 1.—The 11 most commonly used dye plants and the associated tribes 
that use those plants. 


Plant species Tribes that use them 

Alnus tenuifolia Jemez, Navajo, S. Tiwa, Tewa, W. Apache, W. Keres, Zuni 
Cercocarpus montanus E. Keres, Jemez, Navajo, S. Tiwa, W. Keres 
Chrysothamnus nauseous Navajo, Tewa, W. Apache, W. Keres, Zuni 
Cleome serrulata E. Keres, Navajo, S. Tiwa, Tewa, Zuni 
Pinus edulis Hopi, Jemez, Navajo, W. Keres 

Atriplex canescens Hopi, Navajo, Tewa 

Betula occidentalis Hopi, Jemez, Tewa 

Castilleja integra Navajo, W. Apache, Zuni 

Descurainia pinnata Hopi, Jemez, Tewa 

Psilotrophe tagetina W. Apache, W. Keres, Zuni 


Rhus aromatica Hopi, Navajo, W. Keres 


310 HART and COX Vol. 20, No. 2 


a higher consistency index of 0.98 and a retention index of 0.90, all with 940 steps. 
Although the strict consensus tree of the weighted samples reduced resolution 
from the unweighted analysis by collapsing the original basal trichotomy into a 
basal hexatomy, all other topological features of the tree remained the same as the 
unweighted tree (in fact, the tree produced from character weighting, is, topologi- 
cally, still a subset of the unweighted tree.). We note that the consistency index 
(but not the retention index) may be an overestimate of the robustness of our analy- 
sis since this statistic is sensitive to autapomorphies (characters restricted to one 
tribe, in our analysis, uniquely derived plant uses not shared with other tribes), in 
which some traditions we studied, particularly that of the Navajo, abound. 

Of the 108 plant species used as characters, only 27 are synapomorphies. This 
level of autapomorphy which, as mentioned above, does affect the consistency 


Primitive 


Papago 


aaa Pima 


E. Keres 


S. Tiwa 


Tewa 


23 W. Apache 
wi 


Zuni 


Jemez 


Vi W. Keres 


87 avajo 
15,52 


Hopi 


99 


FIGURE 3.—Cladistic relationships of dye plant traditions of southwestern Amerindian 
tribes; strict consensus tree of weighted characters, with two successive rounds of 
implict enumeration; length= 940, consistency index = 0.98; retention index = 0.90. The 
synapomorphies are indicated by a number which refers to specific plant species as 
identified in Appendix 1. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 311 


index. Yet, including all of the data does not affect global parsimony or successive 
weighting methods, and, of course, leaves the tree morphology unaltered. How- 
ever, many of the nodes of the consensus tree are supported by a relatively few 
number of synapomorphies, so it is conceivable that the topology of the consen- 
sus tree could change as plant uses from other additional tribes outside of our 
study area are added to the sample. 

A strict consensus tree (Figure 3), which combines the features on which that 
all of the seven most parsimonious trees agree, shows dye plant use of the Hopi 
and the Navajo to be more closely related to each other than the use of plants by 
either tribe is to their sister group, plant used among the Western Keres. 
Synapomorphies (shared characters or innovation in use of a plant species for 
dye) linking the Hopi and Navajo include Carthamus tinctorius (an introduced spe- 
cies), Juniperus osteosperma, Rumex hymenosepalus, Thelesperma megapotamicum, and 
Thelesperma subnudum. Dye use among members of the larger clade consisting of 
the Navajo, Hopi, and Western Keres was more closely related to dye use among 
the Jemez than to any of the other tribes considered. The synapomorphy (shared 
innovation) linking the clade composed of the Navajo, Hopi, and Western Keres is 
Rhus aromatica. Dye use among the clade consisting of the Navajo, Hopi, Western 
Keres, and Jemez was more closely related to each other than to all other tribes on 
the basis of Pinus edulis as a synapomorphy. The other clades consistently grouped 
in the strict consensus tree were the Western Apache and Zuni linked by the 
synapomorphy of Coreopsis cardaminefolia. Use of Chysothamnus nauseosus link the 
Western Apache, Zuni, and Tewa, although our analysis indicates an independent 
origin for the use of this species among the Navajo and Western Keres. A less 
parsimonious solution is, of course, that the other tribes lost this knowledge. Such 
homoplasy may disappear from the cladogram as plant used for dyes from more 
tribes are added to the data set, and, in an adapation of cladistic biogeography, as 
comparative cladograms for plants used for different purposes (i.e. medicinal, 
ritual, etc.) are overlaid with dye plant use. The Papago and Pima share two 
synapomorphies—Krameria parviflora and Prosopis velutina. However, the pattern 
of branching cannot be resolved in the strict consensus tree for the Eastern Keres 
and Southern Tiwa. However, in the unweighted tree they form a sister group to 
the Papago and Pima. 


DISCUSSION 


Enumeration of Dye Plant Species.—Certain questions are raised from our study in 
both the enumeration of plant uses and in the subsequent cladistic analysis. Why 
do the Navajo use so many unique plants (cultural E phies), especially in 
comparison to the other tribes? We believe that the importance of dye plants in the 
Navajo economy, specifically in weaving, creates an incentive for Navajos to use 
more dye plants. For the Navajo, weaving has been, and continues to be, an im- 
portant source of income (Hedlund 1992; Roessel 1983). Weaving as a source of 
commercial income for the Navajo was established by 1900 (Wheat 1979). Indeed, 
at that time the Navajo rug was the only handwoven good from natives of the 
Southwest that still had significant trade value (Minge 1979). The Navajo have 


312 HART and COX Vol. 20, No. 2 


been praised for the highest quality of weaving observed among regional indig- 
enous groups. Some have estimated that the Navajos emerged as premier weavers 
by the 1800’s (Mathews 1891; Wheat 1979). The Navajo adopted weaving about 
300 years ago and yet they didn’t use a great number of dye plants until the begin- 
ning of the 20th century (Hedlund 1992). Indeed, one of the earliest recordings of 
dye plant use among the Navajo only mentions seven dye plants (Mathews 1891). 
Aniline dyes were also employed during the early part of this century, but by the 
1930’s there was a resurgence of interest in natural dyes (Reichard 1936), and in 
today’s market a weaver can get a better price for a rug made with vegetal dyes 
than one that is made with aniline dyes. For these reasons we believe the Navajo 
have a stronger incentive to use vegetal dyes and to continue experimenting and 
finding more plants that produce good dyes, even looking outside their own cul- 
tural knowledge of dye plant use. This incentive may have also contributed to the 
Navajo looking to Anglo/ Western sources for plant dye information, as found in 
Amsden’s Navajo Weaving (1940). Our interviews with different weavers and trad- 
ers show a general consensus that experimentation with new plants to find new 
dyes is common today. This is also supported in the literature (Hedlund 1992; 
Jones 1948). Hence there is an economic motivation for use of plant dyes. This 
motivation may be a determining factor in the continued use of natural dyes and 
may contribute to the fact that many weavers today are continually experiment- 
ing with new plants and combinations of plants for unique dyes. This economic 
incentive may be significant in the large difference of dye plants used between the 
Navajo and other tribes. 

Tribal population size could also influence the variation in dye flora sizes 
among tribes assuming that larger tribes, having more people, had greater collec- 
tive knowledge about what plants make good dye plants. If this were the case, we 
would expect larger tribes to use more plants. Today the Navajo tribe is the largest 
of the tribes studied, but it is difficult to assess and correlate fluctuations in tribal 
size with fluctuations in dye plant use. 


Cladistic Analysis.—Of interest in the cladistic analysis is the absence of 
symplesiomorphies common to all tribes, i.e., dye plants that all 11 tribes use and 
were derived from some earlier tradition of use or people not included in our 
analyses. The most commonly used plant is Alnus tenuifolia. Seven of the 11 tribes 
use this plant. The four tribes that do not use it are the Hopi, Eastern Keres, Papago, 
and Pima. Table 1 shows the 11 most commonly used plants and which tribes use 
them. 

Does the absence of symplesiomorphies mean that different clades (tribes) 
independently invented the use of dye plants, or some tribes lost the use of a 
particular plant, or that each tribe merely utilized those plants that were most 
common and therefore readily available? Obviously the latter hypothesis cannot 
be true for every tribe, especially when the use of non-native species is consid- 
ered. But for those tribes only using a few dye plants, independent development 
of plant dyes is possible. The absence of symplesiomorphies could indicate that 
different tribes lost the use of a particular plant as acculturation through the influ- 
ence of Western culture increased with the movement of more European-Americans 
into their regions. In the case of Alnus tenuifolia we can assume that each of the 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 313 


nevert tribes independently invented the use of this plant, but a more parsimoni- 
ous h thesis would be that Alnus tenuifolia is actually a symplesiomorphy which 
was “lost” four separate times by the Eastern Keres, Hopi, Papago and Pima. 

As we consider other commonly used plants like Cercocarpus montanus or Cleome 
serrulata, the question becomes more problematic. These two plants are used by 
five of the 11 tribes. Were they each once used by all tribes, thus being a 
symplesiomorphy? If so, the knowledge would have been lost six times. Or is it 
more likely that the five tribes independently came to use these two plants? Use 
and diffusion of plant knowledge of such plants may be difficult to assess. Yet 
some plants lend th Chrysothamnus nauseosus could 
easily be placed on the cladogram below the Tewa, and use of it could have been 
lost by both the Jemez and Hopi. 

The Navajo have 51 autapomorphies (plants used by only that tribe—a 
uniquely derived, but unshared, innovation). The rest of the tribes have notice- 
ably fewer autapomorphies and are as follows: Hopi-12, Western Keres-six, 
Tewa-four, Papago-three, Western Apache and Jemez-two, Pima-one, Eastern 
Keres, Southern Tiwa and Zuni-zero. The presence of unique cultural uses of dye 
plants suggests that some indigenous groups are putting more energy into find- 
ing dye plants, while others are content to use fewer plants and have less variety 
in their range of color for dyed materials. The large number of sence ame 
that the Navajo have correlates well with their cultural and p 
woven rugs as discussed above. 

This cladistic analysis provides some hypotheses on the cross-cultural diffu- 
sion of dye plant use/knowledge. It seems plausible that the Navajo and Hopi 
would be closely related in dye plant use because of their geographical proximity 
to each other and the similarity of the environment in which they live. It is feasible 
that as the Nava tern region they learned about 
plant use from theti nearest t neighbors—the Hopi. Clearly, some knowledge was 
being shared between tribes—the Navajo learned to weave from the Pueblo people. 
And through their contact with other southwestern tribes, like the Hopi, it is likely 
that the Navajo learned about plant use, in this case dye plant use. 

The relationship between the Western Apache and Zuni plant dye use is sur- 
prising at first, given their distinct language differences. But as one closely examines 
their environments, both live within the White Mountain range which contains a 
distinctly different flora from the high plateau deserts where tribes that are cultur- 
ally more similar live. Thus their shared relationship in dye plant use appears to 
be a function of their shared environment, rather than a closely shared culture. 

The Papago and Pima relationship of plant dye use is no surprise—their tribal 
regions are much further west and south than the Pueblo tribes and the Navajo/ 
Western Apache. It would be expected that their flora is the most different of all 
tribes studied based on the ecology of their homeland. Indeed, of all the tribes 
studied, they have the smallest potential dye flora within their ecological bound- 
aries. Also, the Papago and Pima come from the Uto-Aztecan language stock, as 
do the Hopi, but the Hopi live in much closer proximity to the Puebloan tribes and 
share many cultural traditions with them. The Papago and Pima are more unique 
in their cultural background and it would be expected that they would emerge as 
more closely related to each other in dye plant use than to other tribes. 


314 HART and COX Vol. 20, No. 2 


CONCLUSIONS 


This comparative study shows a wide range of plants used by Native Ameri- 
cans for dye purposes. Such variation suggests several scenarios in the evolution 
of dye plant use: (1) those tribes that place a greater emphasis on dyeing, due to 
factors such as the economics of dyed materials or cultural significance, may have 
actively sought to find plants that yield pigments and thus increased their overall 
dye flora, (2) some tribes may have lost dye plant knowledge through accultura- 
tion and assimilation into the Western culture, (3) some tribes could have 
independently invented the use of certain plants for dyes, and (4) larger tribes 
may have retained more inf tion about their tribal dye flora whereas dye plant 
use may decrease as tribal size decreases over time. Most likely, a combination of 
these factors account for the variation seen among the eleven tribes considered in 
this study. 

The fact that some tribes use very few plants is as telling as those tribes that 
use many dye plants. The cultural importance of weaving, dyeing and painting 
varies between tribes. We might assume that those tribes that place a higher sig- 
nificance on such activities will have a larger dye flora. And conversely, those 
tribes who use few plants may place a lesser value on weaving and dyeing. By 
comparing plant use in other areas, we could piece together potential cultural 
values for each tribe, based on size of flora used for different means (medicinal, 
agricultural, ceremonial/ritual, building, etc.). Dye use is merely one piece of a 
larger picture that helps us understand not only cultural uses of plants, but those 
things that are important in different cultures as well. 

Cladistic analyses can generate hypotheses of cross-cultural diffusion of dye 
plant use hat might not be readily apparent if one were to limit cultural compari- 
sons to overall similarities. Again, we reiterate that this analysis does not suggest 
overall cultural relationships between the eleven tribes studied since we consid- 
ered only one small aspect of material culture: dye plant use. Our analysis does, 
however, suggest hypotheses on how dye plant knowledge may have spread be- 
tween the different tribes and which tribes haring ethnobotanical knowledge. 
We find a strong ethnobotanical link between the Hopi and Navajo, the Zuni and 
Western Apache, and the Papago and Pima. These different indigenous groups 
could have been sharing information about dye plants with each other, both po- 
tentially enlarging their own dye flora from the others’ ethnobotanical knowledge. 
The exact history of use and knowledge will not be known, but hypothetical situ- 
ations can be generated by cladistic studies which are amenable to falsification by 
archaeological or ethnohistorical data. 

Further cladistic analyses on different ethnobotanical uses—such as medici- 
nal and agricultural plants, plants used for clothing, shelter and tools, and plants 
with ritual significance—could be overlaid in the same way that vicariate bio- 
geographers overlay different plant and animal phylogenies to discover 
relationships between diverse geographical areas. Such iterative cladistic analy- 
ses (towards which our study is only a small step) could provide fascinating clues 
and trends into ethnobotanical cross-cultural interactions. By overlaying such analy- 
ses we might generate hypotheses of cultural interactions that may not be readily 
apparent otherwise. 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 315 


As indigenous knowledge systems throughout the world continue to disap- 
pear, it is important to understand how ethnobotanical knowledge diffuses across 
cultural boundaries. Using plants as shared innovations and comparing tribal use 
of plant species using cladistic analyses may provide one key to understanding 
such knowledge transfer. It is a simple technique that can clarify relationships 
between indigenous cultures and elucidate the exchange of knowledge and tech- 
nologies. Cladistic analyses may also render insights on plant technologies that 
were independently invented versus those that were exchanged across cultural 
boundaries. 


LITERATURE CITED 


AMSDEN, CHARLES AVERY. 1949. Naxajo 
Weaving, its Technique and History. 
oe New Mexico Srcae 

Albuquerque 

BELL, WILLIS H. ., and EDWARD F. 
CASTETTER. 1937. The utilization of 
mesquite and screwbean by the 
aborigines i in the American sei 
Southwest V. University of Nes vena 
Bulletin on Biological Series 5:3-55. 

BYE, ROBERT A., JR. 1985. Botanical 
a of ph tae of the 
greater Southwest. Economic Botany 
39:375-386. 

CARTER, GEORGE F. 1945. Plant 
Geography and Culture History in the 
American Southwest. The Viking Fund, 


c., New York. 
CASTETTER, EDWARD F., WILLIS H. 
BELL, and ALVIN R. GROVE. 1938. The 
early utilization and the distribution of 
Agave i in the American | oaurey ert: 


Southwest VI. University 0 of N ew 
Mexico, Bulletin 335, Biological Series 
5:3-92. 


RUTH M. UNDERHILL. 


New eevee Bulletin 275, Biological 
Series 

COLTON, “IARY-RUSSELL FERRELL. 
1965. Hopi Dyes. Museum of Northern 
Arizona Press, Flagstaff. 

COOK, SARAH LOUISE. 1930. The 
ethnobotany of the Jemez Indians 
Unpublished MA thesis. University oi 
New Mexico, Albuquerque. 


DENNIS, MARY E. 1939. Plants and 
animals used as sources of dye, paint, 
and skin dressing in the Southwest. 
— MS thesis. University of 

New Mexico, Albuquerque 

DOEBLEY, JOHN F. 1984. “Seeds” of wild 
grasses: A major food of Southwestern 
Indians. Economic Botany 38:52-64. 

DUNMIRE, WILLIAM W. and GAIL D. 
TIERNEY. 1995. Wild Plants of the 
Pueblo Province. Museum of New 
Mexico Press, Santa Fe. 

ELMORE, FRANCIS H. 1943. ey 
of the Navajo. The University of N 
Mexico Bulletin, Monograph Series Vol. 


1 no-7. 

FARRIS, JAMES S. 1988. HENNIG86 
Reference. Version 1.5. Software and 
cane publnee by author. 

989a. The retention index and 
index. 


the caled consistency 
Cladistics 5:417-419. 
89b. The retention index and 
eo ei excess. Systematic Zoology 
38:406-407. 
FEWKES, J. WALTER. 1896. en 
ethnobotany. e American 
Anthropologist IX:14-21. 
FORD, RICHARD I. 1968. An ecological 
] eae: foo? al et _ — 


Juan Pueblo, New Mexico. Ph.D. 
Dissertation, University of Michigan, 
Ann Arbor. 


Anthea olen 

perspective of ethnobota any in the 
greater eae Economic 
Botany 39:400-415. 

FRANCISCAN FATHERS. 1910. An 
Ethnologic Dictionary of the Navaho 
Language. St. Michael’s, Arizona. 


316 HART and COX 


HEDLUND, ANN LANE. 1992. Reflections 

of the weaver’s world: the Gloria F. Ross 

peony of paayreiy a ae 
eaving. Denver Art Muse nv 

HOUGH, WALTER. 1897. The Hopi in 
relation to their plant environment. 
American oat st 10:33-44. 

Environmental 
ei in Arizona. American 
arora 11: 133-155. 

JEANCON, JEAN ALLARD and F. H. 
DOUGLAS. aden aoe spinning, 
dyeing and weaving. Denver Art 
Museum, Dapertinent of Indian Art, 
leaflet no. 3, Denver. 

JONES, VOLNEY H. 1931. The ethnobotany 
of the Isleta Indians. Unpublished 
master’s thesis, univer of New 
Mexico, Sate e 


unusual Navajo 
dye (Endothia aust ian 21:17- 


KENT, KATE PECK. 1957. The cultivation 


Southweiterh United — 
Transactions of the American 
Philosophical rag 47:459-733. 
KITCHING, IAN J., PETER L. FOREY, 
CHRISTOPHER J. HUMPHRIES, and 
DAVID M. WILLIAMS. 1998. Cladistics: 
The Theory and Practice of Parsimony 
Analysis. Second Edition. Oxford 
University Press, Oxford. 
KLUCKHOHN, CLYDE. 1968. Navajo 
Material Culture. Belknap Press, 


ambridge. 
KLUGE, ARNOLD G. and JAMES S. 
FARRIS. 1969. Sra phyletics 
and the evolu of anurans. 

Systematic Jockey 18: 1-32. 

MATHEWS, WASHINGTON. 1886. Navajo 
names for plants. American Naturalist 

776-777. 


. 1891. Navajo dye stuffs. 
Smithsonian Institution Annual Report 
1890-1891: 613-615. 

MAYES, VERNON O. and BARBARA 
BAYL i Navajo 
Herbal. Navajo Community College 


Press, Tsaile. 

MINGE, WARD ALAN. 1979. Effectos del 
pais: A history of tha along the Rio 
Grande. Pp. 8-28 in Spanish Textile 
Tradition o Nes Mexics and Colorado, 
tee bb nes or haut of New 
Mexico Press, Sant 


Vol. 20, No. 2 


ORTIZ, ALFONSO ap as eta rae 

Handbook of North Am 

oo Vol. 10. pare mare 
Institution, Washington. 

PALMER, EDWARD. 1878. Plants used by 
the Indians of the United States. 
American Naturalist 12:593-606, 646- 
655. 


PEPPER, GEORGE H. 1903. Native Navajo 
dyes. The Papoose 1:1-12 

REAGAN, ALBERT B. 1929. Plants used by 
the White Mountain Apache Indians of 
Arizona. Wisconsin Archeologist 8:143- 


REICHARD, GLADYS A. 1936. Navajo 
Shepherd and Weaver. J. J. Augustin 
Publisher, New York. 

RIDLEY, MARK. 1993. Evolution. Blackwell 
Scientific Publications, Boston. 

ROBBINS, WILFRED WILLIAM, JOHN 
PEABODY HARRINGTON 
BARBARA FREIRE-MARRECO. 1916. 
Ethnobotany of the Tewa Indians. 
peony Institution, Bureau of 
American Ethnology, Bulletin 

ROESSEL, RUTH. 1983. Navajo arts and 
crafts. Pp. 592-604 in Handbook of 
North American Indians, Vol. 10, A 
Ortiz, (editor). Smithsonian Institution, 


ashington. 
RUSSEL, FRANK. 1908. The Pima Indians. 
a of barr ares Ethnology, 26th 

nnual Report: 
SAUER, JONATHON D. 1950. Amaranths 


Southwestern Journal of Anthropology 


6:412-415. 

STANDLEY, PAUL C. 1911. Some useful 

snes plants of New Mexico. 
mithsonian Institution Report, 1911. 

STEVENSON. MATILDA COXE. 1915. 
Ethnobotany of the Zuni Indians. 
Bureau of American Ethnology Annual 
Report 30:31-102. 

SWANK, GEORGE R. 
ethnobotany of the Acoma and Laguna 
Indians. Unpublished “MA thesis. 
University of New Mexico, 


ise The 


Albuquerque. 

VESTAL, PAUL A. 1940. Notes on a 
collection of plants from the Hopi 
Indian region of Arizona made by J. G. 
Owens in 1891. Harvard Museum 
Leaflets 8:153-168. 


Winter 2000 


1952. Ethnobotany of the Ramah 
Tae Reports of the Ramah Project, 
Papers of the Peabody Museum of 
American Archaeology ee Ethnology, 
Harvard University 11:1 

WHEAT, JOE BEN. 1979. Rio Grande, 
Pueblo, and Navajo weavers: Cross- 
-36 in Spanish 


Colorado, Nora Fisher, (editor). 
Museum of New Mexico Press, Santa Fe. 

WHITE, LESLIE A. 1945. Notes on the 
ethnobotany of the Keres. ina of the 
Michigan Academy rts, and 
Letters 30:557-568. 

WHITING, ALFRED F. 1939. Ethnobotany 
of the Hopi. Museum of Northern 
Arizona gps No. 15. 

. The present status of 
canitotas ny in the Southwest. 
Economic Botany 20:316-325. 

WINTER, JOSEPH CHARLES. 1974. 
Gare ge 1 * el i eee. | tL ‘ 


and Great Basin. Unpublished PhD 
dissertation. University of Utah, Salt 
ty. 


JOURNAL OF ETHNOBIOLOGY 317 


WYMAN, LELAND C. and STUART K. 
ARRIS. 1941. Navajo Indian medical 
ethnobotany. University of New Mexico 
Bulletin No. 366. 
. 1951. The ethnobotany of the 
Kayenta Navaho. Univ. of New Mexico 
Bulletin No. 366. 
na aera Saag (5): 1-76. 
YOUNG, STELLA. 1940. Navajo Native 
Dyes, Their net and Use 
Chilocco Agricultural rt Printing, 
Dept., Chilocco, Oklahom 
'To whom ogee fa cence ‘should be 
addres 


318 HART and COX Vol. 20, No. 2 


APPENDIX 1.—Plants used for dye purposes and corresponding tribes that use(d) them. 
Plants are used to dye wool, unless otherwise indicated. Numbers in each box refer to 
reference(s) that indicated tribal use of each plant. 


7) wae oO 7) 
4 | = 2 § © me ols s| x — 
— © Se] Ee = = las Ole © 
SST eT etre Se he lea sR 
= dea (eke Seka e-toc 
© (3 ras ® 
uJ = fa) = 
ASTERACEAE 37 
1. Actinea gaillardia 
2. Actinea leptociada 37 
SCROPHULARIACEAE ee 
3. Adenostegia wrightii paint 
1,7,9,12, 30 
BETULACEAE 6 |15,19,20 16 FAT: 7.23\\ sth 7,23 
4. Alnus tenuifolia leather oy a5.) a ©| leather 
2,3 
AMARANTHACEAE aon 29 
5. Amaranthus ‘aula wafer 
cruentus . bread 
13,14 7 
6. Amaranthus palmeri wafer wafer 
bread bread 
ASTERACEAE 37 
7. Artemisia tridentata 
GRAMINEAE a7 
8. Arundo donax : 
YOR 
acetal ree 14 18,32, 
Atriplex canescens wate 37 725 
bread 
|10.Atriplex rosea 18 
|BERBERIDACEAE 20 
11.Berberis fremontii 729 
| 12.Berberis repens 20,37 8 
BETULACEAE 7,14 6 14 
13.Betula occidentalis leather | leather leather 
14.Carduus 1 
occidentalis 
i — 7,10,13, 
14,32,34 7 
afer 
soe bread 
SCROPHULARIACEAE 37 7,29 
16.Castilleja integra 23 inate 
17.Castilleja 34 
linariaefolia 


Winter 2000 


JOURNAL OF ETHNOBIOLOGY 


319 


Eastern Keres 


Hopi 
Jemez (Towa) 
Navajo 


Papago 


Pima 


Southern Tiwa 


Tewa 


Western 
Apache 


Western Keres 


Zuni 


LINACEAE 
18.Cathartolinum 
puberulum 


MN 
Ww 
o 


paint 


ULMACEAE 
19.Celtis reticulata 


breviflorus 


21.Cercocarpus 
tanus 


leather | 20,22,24 | 
28,3 


16 
leather 


30 
leathe 


ASTERACEAE 
22.Chrysothamnus 
latisquamena 


23.Chrysothamnus 
nauseosus 


20,32,37 


7,23 


729 


24.Chrysothamnus 
parryi 


body 
paint 


25.Chrysothamnus 
viscidiflorus 


9 
plant 
materia 


CAPPARACEAE 
26.Cleome serrulata 


Ww 
Ww 


20,37 


16,33 


7ikks 
25,35 
paint 


27 .Coreopsis 
cardaminefolia 


ROSACEAE 
28.Cowania mexicana 


CUCURBITACEAE 
129.Cucumis melo 
(introduced) 


body 
paint 


30.Cucurbita 
foetidissima 


CHENOPODIACEAE 
31.Cycloloma 
atriplicifolium 


RANUNCULACEAE 
|32.Delphinium 
scaposum 


24,37 


|CRUCIFERAE 
133.Descurainia pinnata 


8 
paint 


720 
genus 
only 


320 HART and COX Vol. 20, No. 
8 g S é 
o to) ° ro) be © eo 
ol Se KR — te) o Sot eo) oe nee 
vee 
. e| =| a = =<) 2 
© ® ro) o 
LJ = ” = 
IASTERACEAE 47 
34.Encelia farinosa ; 
35.Endothia singularis 7 
(fungus) 
GNETACEAE 912 
36.Ephedra trifurca ‘ 
37.Ephedra viridis 37 
38.Erysimum 8,30 
OLEACEAE 6 
39.Forestiera body | 37 
neomexicana paint 
ERICACEAE 
40 eria 72 
humifusa 
ASTERACEAE 
41.Gutierrezia 18 
sarothrae 
42.Helenium hoopesii = 
43.Helianthus annuus 9 
44 Helianthus faa, 
petiolaris 14 
SAXIFRAGACEAE i058 
45.Heuchera bracteata ee 
46.Hymenoxys 7,37 
metcalfei 
IRIDACEAE 
ee AAO eg 20 
47. Iris missouriensis 
| JUGLANDACEAE 
48.Juglans major 1237 
49.Juglans regia " 
(introduced) 
|CUPRESSACEAE 18 
50.Juniperus deppeana | 


Winter 2000 


JOURNAL OF ETHNOBIOLOGY 


Eastern Keres 


Hopi 


Jemez (Towa) 


Papago 
Pima 


Southern Tiwa 


Tewa 


Western 
Apache 


Zuni 


51 Juniperus 
monosperma 


. é SIWestern Keres 


52 — 
osteosperm 


body 
paint 


— 


53.Juniperus 
scopulorum 


FABACEAE 
54.Krameria parvifolia 


47 
cotton 


7,26 
a Pris leather 


ZYGOPHYLLACEAE 
55.Larrea tridentata 


47 
tattoo 


56.Letharia vulpina 
(lichen) 


FABACEAE 
57.Lupinus kingii 


58. Medicago sativa 
(cultivated) 


NYCTAGINACEAE 
59.Mirabilis multiflora 


LILIACEAE 
60.Nolina microcarpa 


CACTACEAE 
61.Opuntia 


paint 


anni 
62.Opuntia 
phaecantha 


63.Opuntia polycantha 


64.Parmelia 
molliuscula (lichen) 


1937 


FABACEAE 
65.Parryella filifolia 


AMPELIDACEAE 
.Parthenocissus 
vitacea 


body 
paint 


ASTERACEAE 
67.Pectis angustifolia 


68.Petradoria pumila 


S22 HART and COX Vol. 20, No. 2 
8 g E é 
© oO fo) oO | ood S 2 @® 
seal ae ee ee ow 0 e c S igs =< a 
Se; 3S N = a £ o eine & = 
o| = o S oO aX < — |©o a o Ni 
D = a s =< 2 
Ar} s 4 = 
FABACEAE 
69.Phaseolus vulgaris 3,5,34 
(cultivated) 
LORANTHACEAE 
70.Phoradendron 9,23 
juniperinum 
PINACEAE 9 
71.Picea pungens 
TSI5, 
; : 19,20, 
72.Pinus edulis 34 6 22°32 30 
CAPPARACEAE 
73.Polanisia 8,25 
FABACEAE 7,10 one 
74.Prosopis velutina paint hair dye 
ROSACEAE 16 
75.Prunus americana — leather 
76.Prunus emarginata 9 
77.Prunus 37 
melanocarpa 
78.Prunus persica . 
(introduced) 
79.Prunus virginiana 20 
UMBELLIFERAE 
0. Pseudocymopterus 37 
montanus 
81.Psilotrophe 23 | 8,30 | 7,8,29 
a 
MONOTROPACEAE 
82.Pterospora 37 
andromedea 
PYROLACEAE 36 
83.Pyrola chlorantha paint 
ROSACEAE 9 
84.Pyrus malus 
FAGACEAE 
85.Quercus gambelii 20,37 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 323 
8 g § 8 
“alt oe] ele le ies = 
c| 9 > a} £ ® o |na £ = 
o| <x ® bod 6 a r= ie oe | 
< | 21 & 5 = & 
0 ® o © 
uJ Bey ” = 
86.Quercus pungens 7,36 
1,7,9,15 
ANACARDIACEAE 5.33 18,19,22 7 
87.Rhus aromatica : 24,27, 
31,35,36 
POLYGONACEAE 1,7,9,12, 
: 5,8,34 15,18,19 
hymenosepalus e452,57 
725 
SALICACEAE body 
89 Salix irrorata paint 
CHENOPODIACEAE 37 
90.Salsola kali 
Sacrobatus 20 
vermiculatus 
{ASTERACEAE 24 
92.Senecio douglasii 
7 
bod 
paint 
CRUCIFERAE 7,25 
94 Stanleyella wrightii 
ASTERACEAE 9.37 
95.Tagetes micrantha : 
96. Taraxacum A vei 
officinale 
97.Tetradymia 18 
canescens 
98.Thelesperma = re 18,32, 
megapotamicum aa 37 
99. Thelesperma 9 
subnudum a4 
TYPHACEAE 7 
100.7ypha angustifolia 
1101.Ustilago zeae bee 
y 
(fungus) paint 
ERICACEA 
{102.Vaccinium 9 
humifusu 


324 HART and COX Vol. 20, No. 2 


Eastern Keres 
Hopi 
Navajo 
Papago 
Pima 
Southern Tiwa 
Tewa 
Western 
Apache 
Western Keres 
Zuni 


AMPELIDACEAE 
103. Vitis arizonica 


2 fon) 
58 | Jemez (Towa) 
we 


'104.Xanthium body 
paint 


commune 
105.Xanthoparmelia 
en 18,32 
lichen) 
LILIACEAE 
106. Yucca glauca 18,32 
GRAMINEAE 
107.Zea mays 5,34 
(cultivated) 
ASTERACEAE i 
|108.Zinnia grandiflora 


* Ref f ific citati f each plant d diff t tribes. See literature cited for full 
citation. 

1. Amsden 31. Vestal 1940 
2. Bell rie icp 1937 32. Vestal 1952 
3. Carter 1945 33. White 1945 
4. rete and Underhill 1953 iti 
5. Colton 1965 
6 


74 
; Cook "1930 36. Wyman and Harris 1951 
7. Dennis 1939 37. Young 1940 
8. Dunmire < Tierney 1995 
9. Elmore 194. 
10. Fewkes 186 
11. Ford 1968 


12. Franciscan Fathers 1910 
sa 

16. Jones 1931 

17. J 

20. pet and Lacy 1989 


25. Robbins, Harrington and Freire-Marreco 1916 
26. Russel 1908 
27. Sauer 1950 
28. Standley 1911 
. Stevenson 1915 
30. Swank 1932 


Winter 2000 JOURNAL OF ETHNOBIOLOGY 


sist: 2. ¥ a|$ = =} bab 512 ial f-~ 
lalalzielg lala eal = a sla als 
o 5 0}/° < FS re) a\= 
ol Fs ro) o 
=) —= 2 
~ 3 ef me] a maa} | fein} | | 64 
~ } ok ab 5 
= ) ial pa 6 
= are 7 
_ ae 8 
= } ‘ale ard (gag pre 9 
_ al 10 
= =| ad 11 
= = —_ 12 
ab ( = ab] ad 13 
> 68 ad) 14 
~ 69 ol tal ; 
a ) a lati oul 4 
wade 
= ey ee 72 = 3 
= 73 ah 
=| 74 = ) 
oath ae 7: aa oh ablabl lad) 
‘a r —_=! 4 
ie s =| =a} =a} oa) = } 
a 3 rs | 
_ ] a 
Be ) = =| =! ally ab) 
2 a Be ar eg are 
n 4 alt) 
a 3 —_ ] 
ee q call ) 
ee ) art 
= a ai =k =| } 
oath 3 Ss 
= ) «hl 
—_ ) baad 
a alt 
al J Ss } 
ali } =| } 
an q _ 40 
p< coe 4 
= os 4 
ab) F a 43 
a ee 3 = é 
a i 4 é 
_ 100 - y. 
= 102 - 48 
aii 103 ~ 49 
cai 104 50 
lk 105 al é 
4 Ge 22 
107 53 
ale 108 u 


APPENDIX 2.—Data matrix for cladistic analysis. Characters are represented by 
individual plant species as numbered in Appendix 1. A blank cell denotes plant not 
used by tribe, a “1” denotes plant used. 


325 


NOTICE TO woe 53 00298 2038 
The Journal of Ethnobiology’s revised “Guidelines for Authors” appears in volume 19, 9, number two | 
(winter 1999). If you need a copy of these Guidelines you may request a copy from the Editor. 
Careful scrutiny of recent issues of the Journal should provide appropriate stylistic models for any 
manuscript you may wish to submit. 


Th bmitti f ideration for publication in the Journal should send three 
hard copies and o one copy on a te density 3.5" pe arse in IBM-compatible or Apple format with 
original camera-ready figures. Manuscripts submitted in inappropriate style and format will be 
returned. 


Manuscripts should be sent to: 
WILLIAM BALEE 
Editor, Journal of Ethnobiology 
Department of Anthropology 
Tulane University 
New Orleans, LA 70118 USA 
(wbalee@tulane.edu) 


BOOK REVIEWS 
We welcome suggestions on books to review or actual reviews from readers of the Journal. If you 
submit a book review for consideration please send two hard copies and one on diskette. Send 
suggestions, comments, or reviews to: 
MICHAEL K. STEINBERG 
Book Review Editor, Journal of Us 
Department of Geography- opology 
University of Southern ihe 
Gorham, ME 04038 
(mstein@usm.maine.edu) 


SUBSCRIPTIONS 
Subscriptions to the vet i Ethnobiology should be addressed to Virginia Popper, UCLA Institute 
of Archae eology, Box 951510, Fowler A-210, Los Angeles, CA 90095-1510 USA (Email: 


ada, and Mexico, $35 
HACE Heo Shas eal eC pas t for Mexico, for whic 


vpopper@ucla.edu). Subscription sia are win v4 institutional nape nit in the U.S., Canada 
ana 


and Mexico, $90 for instituti 
or students el } 
subscriptions are $25; individual best from Kicica, Asia, Avaivalis, and Europe are $45. For 
postage outside of the USA, Canada, or Mexico, add $10. Make checks payable to the Jour nal of 
Ethnobiology. Defective or lost copies will be replaced if a written request is received within one year 
of issue. For information on back issues contact Cecil Brown, Department of Anthropology, 
Northern Illinois University, DeKalb, IL 60115 USA, (815) 753-0246. For further details on subscrip- 
tions and the Society of Ethnobiology in general, consult http:/ /www.ethnobiology.org. 


CONTENTS 


ETHNOBIOTICA iv 


MAYA KNOWLEDGE AND “SCIENCE WARS” 
Anderson 129 


EASTERN SUMBANESE BIRD CLASSIFICATION 
Forth 161 


KNOWING, GATHERING AND EATING: KNOWLEDGE AND ATTITUDES 
ABOUT WILD FOOD IN AN ISAN VILLAGE IN NORTHEASTERN 
THAILAND 

Somnasang & Moreno-Black in7 


THE JAGUARS OF ALTAR Q, COPAN, HONDURAS: FAUNAL ANALYSIS, 
ARCHAEOLOGY, AND ECOLOGY 
Ballinger & Stomper 223 


PERCEPTION AND MANAGEMENT OF CASSAVA (MANIHOT ESCULENTA 
CRANTZ) DIVERSITY AMONG MAKUSHI AMERINDIANS OF GUYANA 
Elias et al. 239 


THE HISTORICAL ECOLOGY OF SOUTHEASTERN LONGLEAF PINE AND 
ITS SOUTHERNMOST EXPRESSION 
Walker 269 


A CLADISTIC APPROACH TO COMPARATIVE ETHNOBOTANY 
Hart & Cox 303 


BOOK REVIEWS 159, 193, 217, 237, 266, 300