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US  ISSN  0006-9698 


Cambridge,  Mass.  3 June  2015  Number  545 


EFFECTS  OF  ECTOPARASITISM  ON  BEHAVIORAL  THERMOREGULATION  IN 
THE  TROPICAL  LIZARDS  ANOLIS  CYBOTES  (SQUAMATA:  DACTYLOIDAE)  AND 

ANOL1S  ARMOURI  (SQUAMATA:  DACTYLOIDAE) 

Asa  E.  Conover,12  Ellee  G.  Cook,1 2 3  Katherine  E.  Boronow,4-5  and  Martha  M.  Munoz6 


Abstract.  A febrile  response,  or  a raised  body  temperature  in  response  to  infection,  has  been  widely  documented  in 
various  species  of  reptiles  in  laboratory  trials.  However,  whether  and  how  behavioral  fever  is  achieved  in  nature  remains  almost 
entirely  unknown.  Here,  we  examine  whether  two  species  of  lizard  in  the  cybotoid  clade  of  Hispaniolan  trunk-ground  anoles 
( Anolis  cybotes  and  Anolis  armouri ) change  their  basking  behavior  in  response  to  infestation  by  the  chigger  mite,  Eutrombicula 
alfreddugesi.  We  examined  body  temperature  and  basking  behavior  in  wild  populations  of  A.  cybotes  and  A.  armouri  from  four 
localities  that  spanned  a 2,000-m  elevational  transect  in  the  Sierra  de  Baoruco,  Dominican  Republic.  Although  basking  rate 
increased  with  elevation,  we  found  that  it  did  not  correlate  with  mite  load.  Body  temperature  was  also  unrelated  to  parasite 
load.  Thus,  we  found  that  E.  alfreddugesi  infestation  did  not  induce  behavioral  fever  in  these  anoles.  We  found  a strong 
altitudinal  pattern  in  chigger  infestations:  Infestations  levels  were  highest  in  lizards  from  mid-elevation  and  dropped 
dramatically  at  low  and  high  elevation  (particularly  in  the  latter).  We  discuss  possible  mechanisms  for  this  altitudinal  pattern  in 
chigger  infestation  and  discuss  the  relationship  between  infection  and  behavioral  thermoregulation  in  lizards. 

Key  words:  behavioral  fever;  parasitism;  lizard;  chigger  mites;  behavioral  thermoregulation;  anole 


1 Stuyvesant  High  School,  New  York,  New  York,  10282, 
USA. 

2 Department  of  Biological  Sciences,  University  of 
Southern  California,  Los  Angeles,  California  90089, 
U.S.A.;  e-mail:  aeconove@usc.edu 

' Division  of  Biological  Sciences,  University  of  Missouri, 
Columbia,  Columbia,  Missouri  65211,  U.S.A.;  e-mail: 
egcrg7@mail.missouri.edu 

4 Department  of  Organismic  and  Evolutionary  Biology, 
Harvard  University,  Cambridge,  Massachusetts  02138, 
U.S.A.;  e-mail:  kboronow@fas.harvard.edu 

5 Museum  of  Comparative  Zoology,  Harvard  Universi- 
ty, Cambridge,  Massachusetts  02138,  LJ.S.A. 

6 Ecology,  Evolution,  and  Genetics,  Australian  National 
University,  Acton,  Australian  Capital  Territory,  Aus- 
tralia 0200;  e-mail:  martha.munoz@anu.edu.au. 


INTRODUCTION 

Many  lizards  respond  to  pathogen  in- 
fection through  a febrile  response,  or 
a marked  increase  in  body  temperature, 
which  is  proposed  to  enhance  the  inflamma- 
tory reaction  (Vaughn  et  al.,  1974;  Bernheim 
and  Kluger,  1976;  Bernheim  et  al.,  1978). 
Unlike  endothermic  animals  such  as  birds 
and  mammals,  ectotherms  rely  heavily  on 
thermoregulation  to  induce  heightened  body 
temperatures  (Huey,  1982;  Angilletta,  2009). 
Laboratory  studies  on  lizards  (Bernheim  and 


© The  President  and  Fellows  of  Harvard  College  2015. 


BREVIORA 


No.  545 


? 


Kluger,  1976;  Muchlinski  et  al,  1989;  Ortega 
et  al. , 1991;  Ramos  et  al .,  1993;  Scholnick 
et  al.,  2010),  crocodilians  (Lang,  1987; 
Merchant  et  al,  2007),  turtles  (Monagas 
and  Gatten,  1983;  Amoral  et  al,  2002),  and 
snakes  (Burns  et  al,  1996)  have  found  that 
individuals  injected  with  bacteria  exhibit 
elevated  set-point  body  temperatures,  mean- 
ing that  they  attain  warmer  temperatures 
than  uninfected  individuals  when  placed  in 
a temperature  gradient  and  allowed  to 
choose  where  to  sit. 

The  laboratory  studies  discussed  above 
suggest  that  behavioral  thermoregulation 
mechanistically  underlies  fever,  but  this 
remains  unconfirmed  in  wild  populations  of 
naturally  infected  lizards.  In  a semi-natural 
experiment,  Muchlinski  et  al  (1989)  found 
that,  when  injected  with  Aeromonas  bacteria, 
free-ranging  chuckwallas  ( Sauromalus  obe- 
sus)  exhibit  heightened  body  temperatures, 
supporting  the  hypothesis  that  shifts  in 
basking  behavior  are  important  for  inducing 
fever.  Malvin  and  Kluger  (1979)  found  that 
iguanas  do  not  increase  their  internal  heat 
production  to  raise  their  core  temperature 
during  infection,  further  supporting  the  idea 
that  extrinsic  behavioral  shifts  are  critical  to 
achieving  fever  in  lizards. 

Here  we  tested  whether  infestations  by 
chigger  mites  induced  behavioral  fever  in 
anoles  from  the  Dominican  Republic.  Ecto- 
parasites such  as  chigger  mites  are  known  to 
affect  lizard  metabolism  negatively  (Booth 
et  al,  1993)  and  induce  immune  responses  by 
skin  inflammation  (Goldberg  and  Bursey, 
1991).  Previous  studies  in  lizards  have  found 
that  ectoparasite  infestation  is  associated 
with  reduced  body  condition  (Dunlap  and 
Mathies,  1993;  Klukowski  and  Nelson,  2001; 
Cook  et  al,  2013),  and  reduced  sprint  speed 
(Main  and  Bull,  2000).  In  a previous  study 
of  Anolis  brevirostris,  an  anole  from  the 
Caribbean  island  of  Hispaniola,  Cook  et  al 
(2013)  found  that  individuals  with  greater 


infestations  of  the  chigger  Eutrombicula 
alfreddugesi  exhibited  poorer  body  condi- 
tion, had  duller  colored  dewlaps  (extensible 
throat  fans),  and  displayed  less  frequently 
than  individuals  with  lower  parasite  loads. 
Fence  lizards  with  malaria  also  exhibit 
shifts  in  coloration  (Ressel  and  Schall, 
1989)  and  reduced  body  condition  (Dunlap 
and  Mathies,  1993),  suggesting  that  ectopar- 
asites have  negative  effects  on  their  lizard 
hosts,  either  through  the  effects  of  the 
parasites  themselves  or  through  pathogens 
transmitted  by  the  chiggers.  Given  the 
negative  effects  of  chiggers,  it  is  possible  that 
lizards  respond  to  infestation  by  these  para- 
sites through  behavioral  fever;  by  increasing 
their  core  temperature  through  increased 
basking,  lizards  may  combat  pathogens 
transmitted  by  the  chiggers  or  cause  the 
mites  to  drop  off.  The  relationship  between 
basking  behavior  and  parasite  infestation 
may  further  vary  with  altitude:  In  a study  of 
three  Hispaniolan  anoles  ( Anolis  coelestinus, 
Anolis  cybotes,  and  Anolis  olssoni ),  Zippel  et  al. 
(1996)  found  that  chigger  infestation  levels 
increased  dramatically  with  elevation.  Given 
that  basking  frequency  also  tends  to  increase 
with  elevation  in  some  anoles  from  Hispaniola 
(Hertz  and  Huey,  1981;  Munoz  etal.,  2014),  the 
use  of  behavioral  fever  may  be  expected  also  to 
vary  across  altitude. 

The  goal  of  this  study  was  to  assess  whether 
chigger  infestations  induce  behavioral  fever  in 
wild  populations  of  two  species  of  Anolis 
lizards  ( Anolis  armouri  and  A.  cybotes)  from 
the  Dominican  Republic,  Hispaniola,  arrayed 
across  a 2,000-m  elevational  gradient.  Specif- 
ically, we  tested  three  hypotheses:  (1)  chigger 
infestation  reduces  lizard  body  condition;  (2) 
lizards  with  greater  parasite  loads  also  have 
higher  core  body  temperatures  (i.e.,  exhibit 
a fever)  and  bask  more  than  less  infested 
lizards;  (3)  behavioral  fever  should  be  most 
pronounced  at  high  elevation,  where  chigger 
infestations  and  basking  rates  are  highest. 


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BEHAVIORAL  FEVER  IN  TWO  SPECIES  OF  ANOLE 


3 


Table  1.  Summary  Data  are  Given  for  Each  Population  for  Study  Sites  in  the  Southwestern  Region  of  the 

Dominican  Republic. 


Los  Patos 

Guayuyal 

Polo 

Zapoten 

Coordinates 

17°  57'  36"N, 

18°  3'  36"N, 

18°  10'  12"N, 

18°  18'  0''N, 

71°  11'  24"W 

71°  8'  24"W 

71°  15'  0''W 

71°  42'  0"W 

Elevation  (m) 

13 

727 

1,236 

2,020 

Mean  annual  temperature  (°C)a 

26.0 

22.4 

23.5 

13.9 

Sample  size 

18 

18 

20 

22 

Prevalence6 

100 

100 

100 

78.3 

Infestation  intensity11 

29.4  ± 4.3 

99.4  ± 18.4 

108.4  ± 19.1 

15.2  ± 4.4 

Infestation  ranged 

4—78 

18-354 

12-274 

0-75 

Observation  time  (min)e 

58.2 

57.7 

59.1 

57.2 

Basking  ratef 

14.6  ± 1.0 

44.4  ± 1.9 

70.1  ± 2.1 

90.3  ± 1.0 

Body  temperature  (°C)s 

30.9  ± 0.3 

27.8  ± 1.7 

26.7  ± 2.5 

28.2  ± 2.3 

aMean  annual  temperature  was  extracted  from  the  WorldClim  database  (Hijmans  et  al.,  2005). 

bPercentage  of  individuals  with  at  least  one  mite. 

cMean  number  of  mites  per  individual  (±  1 SEM). 

dRange  of  infestation  intensities  for  a population. 

cMean  behavioral  observation  time. 

‘Percentage  of  time  lizards  were  observed  basking  (±  1 SEM). 

^Temperature  ± 1 SEM. 


METHODS  AND  MATERIALS 

We  conducted  our  study  on  the  two 
cybotoid  anoles,  A.  cybotes  and  A.  armour i, 
in  June  and  July  2012  in  the  Dominican 
Republic.  The  term  “cybotoid”  refers  to  the 
clade  of  anoles  containing  the  widespread 
species  A.  cybotes  and  its  relatives  from  the 
Caribbean  island  of  Hispaniola  (Glor  et  al , 
2003).  Though  A.  armouri  shares  many  over- 
lapping morphological  features  with  A.  cybotes 
(Schwartz,  1989),  this  high-elevation  specialist 
is  considered  a separate  species  (Glor  et  al., 
2003;  Wollenberg  et  al.,  2013).  Within  the 
adaptive  radiation  of  Caribbean  anoles,  the 
cybotoids  all  belong  to  the  same  “ecomorph” 
or  habitat  specialist  category,  meaning  that 
they  overlap  substantially  in  behavioral,  eco- 
logical, and  morphological  characteristics 
(Losos,  2009).  Specifically,  the  cybotoids  are 
“trunk-ground”  anoles;  as  such,  they  perch 
close  to  the  ground,  especially  on  tree  trunks, 
have  stocky  builds  with  long  hindlimbs,  and 


forage  actively  on  the  ground  (Schwartz,  1989; 
Glor  et  al.,  2003;  Losos,  2009). 

We  worked  at  four  different  localities  ranging 
between  13  and  2,020  m in  the  Sierra  de 
Baoruco  in  the  southwestern  region  of  the 
Dominican  Republic  (Table  1;  Fig.  2).  Study 
sites  were  located  at  Los  Patos  (13  m above  sea 
level  [masl];  17°  57'  36"N,  71°  11'  24"W), 
Guayuyal  (727  masl;  18°  3'  36"N,  71°  8' 
24"W),  Polo  (1,236  masl;  18°  10'  12"N,  71° 
15'  0"W),  and  Zapoten  (2,020  masl,  18°  18' 
0"N,  71°  42'  0"W).  Anolis  cybotes  is  found  at 
the  three  low-elevation  sites  (Los  Patos, 
Guayuyal,  and  Polo),  where  it  occupies  mesic, 
semi-disturbed  habitats,  especially  near  agricul- 
tural sites  (plantain,  coconut,  and  coffee  planta- 
tions). The  high-elevation  specialist  A.  armouri 
is  found  in  Zapoten.  At  this  montane  locality 
the  habitat  is  composed  of  monodominant  pine 
forest  and  open  fields  with  rocky  outcrops. 

Eutrombiculid  mites  are  known  to  parasitize 
anoles  from  low-  to  mid-elevation  (~  520  masl) 
on  Hispaniola  (Zippel  et  al.,  1996).  These 


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BREVIORA 


No.  545 


Figure  1.  A male  Anolis  cybotes  infested  with 
Eutrombicula  alfreddugesi  mites  on  its  dewlap 
(throat  fan). 


small,  orange-colored  mites  are  most  com- 
monly found  in  densely  vegetated  areas  with 
high  humidity  and  moderate  ambient  temper- 
ature (Clopton  and  Gold,  1993;  Bulte  et  al. , 
2009).  The  larvae  attach  to  anoles  through 
direct  contact  and  typically  cluster  in  skin 
folds,  especially  behind  the  front  and  back 
limb  joints  and  on  the  dewlap,  an  extensible 
throat  fan  used  extensively  in  Anolis  commu- 
nication (Fig.  1).  Mites  can  cause  lesions, 
blood  loss,  and  skin  inflammation  in  lizards 
(Goldberg  and  Bursey,  1991;  Goldberg  and 
Flolshuh,  1992)  and  can  transmit  pathogens. 
In  Asia,  chigger  mites  are  known  to  transmit 
scrub  typhus  (Traub  and  Wisseman,  1974), 
and,  more  generally,  mites  might  be  vectors  for 
bloodbome  parasites  known  as  haemogregar- 
ines,  which  are  known  to  reduce  burst  speed  in 
lizards  (Oppliger  et  al,  1996;  Garrido  and 
Perez-Mellado,  2014). 

Following  Rand  (1962),  we  found  focal 
lizards  through  slow,  random  sweeps  through 
the  habitat  over  the  course  of  2-3  days  per  site 


during  all  weather  conditions  except  rain.  All 
observations  were  made  on  undisturbed, 
naturally  behaving  adult  male  animals  fol- 
lowing the  methods  of  Johnson  et  al.  (2010). 
We  performed  behavioral  observations  either 
by  watching  lizards  with  binoculars  and 
manually  transcribing  observations  or  with 
video  recordings  (Sony  HDR-XR500V  cam- 
era, set  in  standard  definition),  which  we 
subsequently  scored.  Observations  lasted 
from  30  to  60  min  ( X = 57  min)  per  lizard. 

During  each  behavioral  observation  peri- 
od we  recorded  the  amount  of  time  the  lizard 
spent  under  different  basking  conditions.  We 
recorded  each  lizard’s  basking  status,  which 
refers  to  how  it  was  exploiting  weather 
conditions,  following  Munoz  et  al.  (2014). 
During  each  observation  period  we  recorded 
the  weather  conditions  as  sunny,  partly 
sunny,  or  overcast.  Under  sunny  or  partly 
sunny  conditions  lizards  could  be  scored  as 
perching  in  the  sun,  in  the  partial  sun,  or  in 
the  full  shade.  Under  overcast  conditions 
lizards  could  only  be  in  the  shade  (i.e.,  there 
was  no  basking  choice),  and  these  observa- 
tions were  discarded  from  further  analysis. 
At  the  end  of  the  observation,  the  relative 
amount  of  time  each  lizard  spent  basking 
was  calculated  as  the  total  time  spent  either 
in  the  full  or  partial  sun  divided  by  the  length 
of  the  total  observation. 

At  the  conclusion  of  each  observation  we 
attempted  to  catch  the  lizard  to  obtain  infor- 
mation on  body  temperature,  body  condition, 
and  parasite  infestation.  We  noosed  lizards 
using  a dental  floss  noose  tied  to  the  end  of 
a 10-  12-foot  (3-3.7  m)  telescopic  panfish 
pole  (Cabela’s  Incorporated,  Sidney,  Ne- 
braska). Immediately  after  capture,  we  mea- 
sured the  core  temperature  of  the  lizard  by 
inserting  a thermocouple  (type  T,  copper- 
constantan;  Omega  Engineering)  approxi- 
mately 1 cm  into  the  lizard’s  cloaca.  The 
thermocouple  was  attached  to  a handheld 


2015 


BEHAVIORAL  FEVER  IN  TWO  SPECIES  OF  ANOLE 


5 


Figure  2.  Images  showing  the  four  localities  where  this  study  was  conducted:  A.  Los  Patos  (13  m elevation); 
B.  Guayuyal  (727  m);  C,  Polo  (1,236  m);  and  D,  Zapoten  (2,020  m). 


6 


BREVIORA 


No.  545 


reader  (model  HH603A;  Omega  Engineering), 
which  gave  temperature  measurements  to  the 
nearest  0.1  °C. 

For  each  lizard  captured  we  also  measured 
body  mass  to  the  nearest  0.1  g,  using  a spring 
scale,  and  body  size  as  snout-vent  length 
(SVL),  the  distance  from  the  tip  of  the  snout 
to  the  anterior  edge  of  the  cloaca,  using  digital 
calipers  (Mitutoyo),  which  gave  length  mea- 
surements to  the  nearest  0.01  mm.  We  then 
counted  the  total  number  of  ectoparasites  on 
each  anole  using  a handheld  loupe.  We 
sampled  individuals  only  once  and  released 
them  at  the  site  of  capture  within  48  hours. 

For  each  population,  we  calculated  preva- 
lence, which  refers  to  the  proportion  of 
individuals  in  a population  that  had  at  least 
one  mite.  Following  Margolis  et  al.  (1982),  we 
measured  infestation  intensity  as  the  number 
of  mites  per  lizard.  We  estimated  body 
condition  as  the  residuals  of  body  mass 
regressed  against  SVL  (Schulte-Hostedde 
et  al.,  2005).  Before  statistical  analyses,  we 
log-transformed  all  continuous  variables  and 
arcsine  square  root-transformed  the  propor- 
tional variable  (basking  rate).  Given  that 
infestation  intensity  correlated  strongly  with 
body  size  (Pearson’s  r — 0.441,  d.f.  = 16,  p < 
0.001),  we  used  the  residuals  of  infestation 
intensity  regressed  against  SVL  as  our  mea- 
sure of  parasite  load  in  our  examinations  of 
correlation  with  body  temperature  and  bask- 
ing rate.  We  assessed  the  Pearson  correlation 
between  variables,  and  used  the  Bonferroni 
correction  to  correct  for  multiple  tests.  None 
of  the  relationships  were  changed  when  we 
compared  body  temperature  and  basking  rate 
to  infestation  intensity,  rather  than  parasite 
load.  We  compared  body  temperature  among 
populations  using  the  Mann-Whitney  U test. 

RESULTS 

Prevalence  was  extremely  high  across 
localities:  73  of  the  78  lizards  examined  were 


infested  with  E.  alfreddugesi  mites,  and  100% 
of  lizards  from  the  three  lower  elevation  sites 
were  infested  (Table  1).  Prevalence  was 
slightly  lower  in  Zapoten,  where  21.7%  of 
lizards  captured  had  no  parasites,  and  most 
individuals  had  fewer  than  20  mites  (Fig.  3). 
On  average  lizards  harbored  61.7  mites,  and 
infestation  intensity  ranged  from  0 to  354 
mites  (Table  1).  Despite  high  numbers  of 
ectoparasites,  we  found  no  significant  rela- 
tionships between  infestation  intensity  and 
lizard  body  condition  (Table  2). 

Basking  behavior  differed  among  localities 
(Table  1):  The  proportion  of  time  lizards 
spent  basking  increased  with  elevation  from 
14.6%  in  Los  Patos  (13  m)  to  90.1%  in 
Zapoten  (2,020  m).  Mean  body  temperature 
ranged  from  26.7°C  (Polo)  to  30.9°C  (Los 
Patos)  (Table  1)  and  was  significantly  higher 
in  Los  Patos  relative  to  the  other  populations 
(Mann-Whitney  U test;  all  p < 0.01). 
However,  basking  rate  and  parasite  load 
were  not  strongly  correlated  (Table  2).  Sim- 
ilarly, we  found  no  significant  relationships 
between  body  temperature  and  parasite  load 
(Table  2). 

DISCUSSION 

Behavioral  fever  is  one  way  that  ectother- 
mic  animals  might  be  able  to  respond  to 
parasite  infestation.  However,  we  found  that 
basking  frequency  and  body  temperature 
were  not  correlated  with  parasite  load 
(Table  2),  indicating  that  A.  cybotes  and  A. 
armouri  did  not  exhibit  a febrile  response  to 
chigger  infestation.  One  possible  explana- 
tion is  that  anoles  do  not  exhibit  behavioral 
fevers.  Muchlinski  et  al.  (1995)  found  that 
Anolis  eqaestris  injected  with  bacteria  did 
not  exhibit  elevated  core  temperatures 
compared  with  uninfected  individuals.  In 
another  study,  Anolis  carolinensis  that  were 
injected  with  bacterial  lipopolysaccharide 
exhibited  a hypothermic  response  (i.e.,  cooler, 


Count 


2015 


BEHAVIORAL  FEVER  IN  TWO  SPECIES  OF  ANOLE 


7 


CN 

o 

— 

CN  - 
O - 

^ — 
CN  - 
O - 


CO 

o 


J=L 


_Dn 


h n 


Los  Patos 


Guayuyal 




n 


r 

0 


100 


200 


300 


400 


Number  of  Ectoparasites 

Figure  3.  Histogram  showing  infestation  intensity  frequency  in  each  of  the  populations  sampled. 


Table  2.  Results  for  Correlation  Tests  Examining  Relationships  Between  (A)  Body  Condition,  (B)  Basking 
Rate,  and  (C)  Body  Temperature  and  Parasite  Load.  Pearson’s  r and  P Values  are  Given  for  Each  Test, 

and  Sample  Size  is  Given  in  Parentheses. 


r 

P 

A.  Body  condition  ~ infestation  intensitya 

Los  Patos  (18) 

-0.161 

0.525 

Guayuyal  (18) 

0.326 

0.187 

Polo  (20) 

0.231 

0.328 

Zapoten  (22) 

-0.319 

0.148 

B.  Basking  rate  ~ parasite  loadb 

Los  Patos 

0.262 

0.293 

Guayuyal 

-0.399 

0.101 

Polo 

-0.129 

0.599 

Zapoten 

0.033 

0.896 

C.  Body  temperature  ~ parasite  load 

Los  Patos 

-0.080 

0.753 

Guayuyal 

-0.489 

0.040 

Polo 

-0.219 

0.353 

Zapoten 

0.036 

0.875 

“Residuals  of  body  mass/SVL  and  the  number  of  ectoparasites  (infestation  intensity).  SVL  refers  to  the  body  size  of 
the  lizard,  measured  as  the  distance  from  the  tip  of  the  snout  to  the  cloaca  (snout-vent  length). 
b(Time  spent  basking)/(total  observation  length)  and  parasite  load  (residuals  of  infestation  intensity  ~ SVL). 


8 


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No.  545 


rather  than  warmer,  body  temperatures) 
when  placed  in  a temperature  gradient  and 
allowed  to  choose  where  to  sit  (Merchant 
et  al.,  2008).  Looking  more  broadly,  whereas 
many  studies  have  observed  a febrile 
response  to  infection  in  lizards  (e.g.,  Bernheim 
and  Kluger,  1976;  Muchlinski  et  al,  1989; 
Ortega  et  al.,  1991;  Ramos  et  al,  1993), 
others  have  failed  to  detect  a pattern 
(Laburn  et  al.,  1981;  Mitchell  et  al.,  1990) 
or  have  found  that  individuals  can  vary  in 
whether  or  not  fever  is  induced  (Bernheim 
and  Kluger,  1976). 

Behavioral  fever  might  not  be  prevalent  in 
lizards  because  the  costs  associated  with 
fever  are  too  high  to  induce  them  in  nature. 
Almost  all  studies  examining  febrile  re- 
sponses in  lizards  were  conducted  using 
laboratory  heat  gradients,  where  all  other 
ecological  variables  besides  infection  are  held 
constant.  Given  that  extra  time  spent  ther- 
moregulating imposes  a cost  to  other  activ- 
ities, such  as  foraging,  predator  avoidance, 
and  reproduction  (e.g.,  Huey,  1974;  Grant 
and  Dunham,  1988;  Adolph  and  Porter, 
1993),  it  is  possible  that  selection  does  not 
favor  fevers  in  nature.  It  is  also  possible  that 
the  chigger  mites  can  withstand  more  heat 
than  A.  cy botes  and  A.  armouri.  Tropical 
lizards  such  as  anoles  tend  to  exhibit  low 
body  temperatures  and  heat  tolerances  rela- 
tive to  other  lizard  species  (discussed  in 
Sunday  et  al,  2010;  Araujo  et  al,  2013);  it 
is  possible  that  a febrile  response  is  not 
effective  for  lizards  with  low  heat  tolerances, 
such  as  these  species  (critical  thermal  maxi- 
mum: ~ 38-40°C;  Munoz  et  al,  2014), 
although  it  may  be  possible  and  advanta- 
geous in  more  heat  tolerant  species. 

It  is  also  possible  that  mite  infestations  do 
not  negatively  affect  lizards  enough  to  induce 
fever  in  A.  cy  botes  and  A.  armouri.  Although 
some  studies  have  found  negative  correla- 
tions between  chigger  infestation  and  lizard 
body  condition  (Dunlap  and  Mathies,  1993; 


Klukowski  and  Nelson,  2001;  Cook  et  al, 
2013),  we  did  not  observe  any  correlation 
between  body  condition  and  chigger  infesta- 
tion (Table  2).  Similarly,  other  studies  have 
found  no  effect  of  E.  alfreddugesi  infestation 
on  lizard  health  (Garcia-De  La  Pena  et  al, 
2004,  2010;  Schlaepfer,  2006;  Rocha  et  al, 
2008),  and  others  have  found  positive 
correlations  (Amo  et  al,  2005),  suggesting 
that  the  health  effects  of  mite  infestation  may 
vary  among  taxa.  This  variable  response  in 
host  health  is  not  limited  to  chiggers:  Even 
when  infected  with  malaria,  some  anole 
species  exhibit  negative  effects,  whereas 
others  do  not  (Schall,  1992;  Schall  and 
Pearson,  2000).  These  findings  underscore 
that  a more  comprehensive  understanding  of 
how  ectoparasites  (and  the  pathogens  they 
may  transmit)  affect  lizard  health  is  neces- 
sary for  determining  whether  behavioral 
fever  should  occur. 

More  broadly,  it  is  still  not  fully  un- 
derstood how  ectoparasite  infestation  should 
affect  lizard  body  condition.  For  example, 
the  detrimental  effects  of  ectoparasites  can 
be  inferred  from  both  negative  correlations 
between  body  condition  and  mite  loads 
(Dunlap  and  Mathies,  1993;  Klukowski  and 
Nelson,  2001;  Cook  et  al,  2013)  and  from 
positive  correlations  (e.g.,  Amo  et  al,  2005). 
In  the  former,  the  reduced  body  condition  of 
infested  lizards  can  suggest  that  the  ectopar- 
asites reduce  health  and  immunity,  as  evident 
in  the  reduced  body  condition,  and  in  the 
latter  it  is  thought  that  parasites  reduce 
survival  and  so  only  the  individuals  with 
best  body  condition  can  survive  (Amo  et  al, 
2005).  Furthermore,  even  when  negative 
correlations  between  body  condition  and 
parasite  load  are  detected,  they  may  not  be 
driven  by  the  parasites  inducing  lizards  to 
lose  mass.  Klukowski  and  Nelson  (2001) 
found  that  body  condition  was  reduced  in 
infested  lizards  because  high  mite  loads 
appeared  to  prevent  lizards  from  gaining 


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BEHAVIORAL  FEVER  IN  TWO  SPECIES  OF  ANOLE 


9 


mass.  In  short,  a deeper  understanding  of 
how  ectoparasites  and  their  associated 
bloodborne  pathogens  influence  host  health 
will  vastly  improve  our  predictions  for  how 
behavioral  fever  should  occur,  if  at  all. 

Although  basking  rate  was  uncorrelated 
with  parasite  load,  the  use  of  sun  and  shade 
varied  considerably  across  elevation.  Whereas 
lizards  near  sea  level  spent  only  a small  fraction 
of  their  time  perching  in  the  sun,  those  found  at 
high  elevation  (Zapoten)  were  almost  invari- 
ably observed  basking  (Table  1),  a result  that 
aligns  with  findings  from  previous  studies  on 
these  species  (Hertz  and  Huey,  1981;  Munoz 
et  al. , 2014).  Prevalence  was  also  considerably 
lower  at  Zapoten,  and  most  lizards  harbored 
fewer  than  20  parasites  (Fig.  3).  If  increased 
basking  frequency  were  associated  with  warm- 
er core  temperatures  in  Zapoten,  then  it  could 
be  possible  that  fever  in  A.  armouri  reduced 
ectoparasite  levels.  However,  this  is  unlikely 
because  mean  body  temperature  was  signifi- 
cantly lower  in  Zapoten  ( X — 28.2°C)  than  in 
Los  Patos  ( X = 30.9°C),  suggesting  that  even 
though  they  bask  continually,  lizards  in  high- 
elevation  populations  might  not  always  be  able 
to  attain  body  temperatures  comparable  to 
their  low-elevation  counterparts,  let  alone 
behaviorally  induce  a fever. 

The  markedly  low  levels  of  infestation 
intensity  observed  in  A.  armouri  from  Zapo- 
ten appear  to  conflict  with  previous  findings 
on  A.  cybotes  by  Zippel  et  al  (1996),  who 
found  that  intensity  increased  with  elevation. 
Both  their  study  and  ours  were  conducted  in 
the  Sierra  de  Baoruco  mountain  chain  in  the 
western  Dominican  Republic.  However, 
Zippel  and  colleagues  did  not  sample  A. 
cybotes  lizards  above  520  m,  and  our  transect 
extended  to  2,020  m.  Consistent  with  Zippel 
et  al.  (1996),  we  found  that  mite  infestation 
increased  from  sea  level  to  mid-elevation,  as 
intensities  were  particularly  high  in  the  mid- 
elevation populations  at  Guayuyal  (727  m) 
and  Polo  (1,236  m),  where  up  to  354  and  274 


ectoparasites  were  observed  on  a single  lizard, 
respectively  (Table  1;  Fig.  3).  The  inlestation 
levels  in  Guayuyal  and  Polo  are  among  the 
highest  recorded  for  mites  on  other  species  of 
lizards  (Amo  et  al. , 2005;  Rocha  et  al. , 2008; 
Garcia-De  La  Pena  et  al .,  2010;  Delfino  et  al., 
2011;  Ramirez-Morales  et  al.,  2012;  Cook 
et  al.  ,2013,  but  see  Garcia-De  La  Pena,  2011), 
as  well  as  for  lizards  with  other  types  of 
ectoparasites  such  as  ticks  (e.g.,  Ixodes  ricinus 
[Acari:  Ixodidae]:  Amore  et  al,  2007;  Gryc- 
zynska-Siemi^tkowska  et  al.,  2007;  Stuart- 
Fox  et  al.,  2009;  Gomes  et  al,  2013). 

Why  do  intensities  drop  so  dramatically  in 
Zapoten?  Habitat  preference  by  E.  alfreddugesi 
may  explain  particularly  low  infestation  levels 
observed  at  high  elevation.  Previous  work  has 
shown  that  chigger  mites  tend  to  prefer  mesic 
habitats  with  low-incident  sunlight  and  mod- 
erate temperatures  (Clopton  and  Gold,  1993; 
Schlaepfer  and  Gavin,  2001)  and  that  parasite 
intensity  is  typically  higher  in  forest  interiors 
than  in  forest  edges  (Bulte  et  al,  2009;  Rubio 
and  Simonetti,  2009).  At  elevations  above 
approximately  1,800  m in  Hispaniola,  anoles 
tend  to  cluster  in  forest  clearings  and  rocky 
outcrops,  presumably  to  access  open  basking 
sites  in  this  colder  environment,  where  tem- 
peratures can  reach  near  freezing  throughout 
the  year  (Hertz  and  Huey,  1981;  Munoz  et  al, 
2014).  Even  contiguous  forest  tends  to  be  more 
open  than  at  low  elevation  because  the  pine 
forest  lacks  the  closed  canopy  characteristic  of 
the  broadleaf  forest  at  lower  elevations  (Fig.  2) 
(Martin  et  al.,  2011).  Thus,  open  habitat  and 
cold  temperatures  may  prevent  E.  alfreddugesi 
from  reaching  densities  comparable  to  those 
observed  at  lower  elevations. 

Although  behavioral  fever  is  likely  a key 
response  to  infection  in  lizards,  we  still  know 
little  of  how  it  occurs  in  nature.  In  the  case  of 
A.  cybotes  and  A.  armouri,  we  did  not  find 
evidence  that  lizards  respond  to  ectoparasite 
infestation  through  behavioral  fever.  It  is 
not  fully  known  how  these  (and  other) 


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No.  545 


ectoparasites  influence  their  lizard  hosts  and 
what  pathogens  they  transmit  (Amo 
et  al.,  2005;  Garrido  and  Perez-Mellado, 
2014).  A more  detailed  understanding  of 
how  ectoparasites  and  bloodborne  patho- 
gens influence  lizard  health  and  how  path- 
ogen and  host  temperature  tolerances  differ 
will  lead  to  more  detailed  hypotheses  about 
the  conditions  under  which  we  expect  lizards 
to  exhibit  behavioral  fever. 

ACKNOWLEDGMENTS 

We  thank  I.  Shields  for  assistance  in  the 
field,  the  Ministerio  de  Medio  Ambiente  y 
Recursos  Naturales  and  the  Museo  Nacional 
de  Historia  Natural  for  granting  our  research 
permit  requests,  and  J.  Gastel,  J.  Losos,  and 
M.  Johnson  for  helpful  comments  on  this 
manuscript.  We  thank  two  anonymous  re- 
viewers, who  greatly  improved  this  manu- 
script. This  study  was  conducted  in  accordance 
with  the  Institutional  Animal  Care  and  Use 
Committee  at  Harvard  University  under  pro- 
tocol 26-11.  This  project  was  completed  by 
Conover  in  partial  fulfillment  for  the  Intel 
Science  Talent  Search  through  Stuyvesant 
High  School.  Support  for  this  work  came  from 
a David  Rockefeller  Center  for  Latin  Ameri- 
can Studies  Research  Grant;  a Ken  Miyata 
Award  from  the  Museum  of  Comparative 
Zoology;  a Sigma  Xi  Grant-In-Aid  Award  to 
M.M.M.;  and  a Beckman  Scholar  Award  from 
the  Arnold  and  Mabel  Beckman  Foundation, 
Sigma  Xi  Grant-In-Aid,  and  Explorer’s  Club 
Youth  Activity  Fund  Grant  to  E.G.C.  This 
material  is  based  on  work  supported  by 
National  Science  Foundation  Graduate  Re- 
search Fellowships  to  K.E.B.  and  M.M.M. 

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