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CIRCULAR No. 464 MARCH 1938 


UNITED STATES DEPARTMENT OF AGRICULTURE 
WASHINGTON, D.C. 


THE GYPSY AND BROWN-TAIL MOTHS AND THEIR 
CONTROL’ 


By A. F. Buresss, principal entomologist, Division of Gypsy Moth and Brown-Tail 
Moth Control, and W. L. Baker, assistant entomologist, Division of Forest Insect 
Investigations, Bureau of Entomology and Plant Quarantine 


CONTENTS 
: Page Page 
RhewypsSyeMoOpnes === eee ee ee oe 1 | The brown-tail moth—Continued. 

History of the pest in the United States____ 1 INative:ecnemies 222 sa een eee see 33 
Conditions of infestation in New England.. 5 Introduced parasites and other enemies_____ 33 
IP ORIS COT Yee ee eee eee se 6 | Effect of low temperatures__-_---_.----______ 33 
Injury caused by the gypsy moth__________ 8 Methodsiof control at eat eae set eo es 33 

WOOGRD aN USE ee en ee es ga 9 Recent Controle lontsess eee 3 

Wieansiotspread =.) ee itia Leeehie 13 | Organization and status of work against the 

HnecholiGlimates———=— = SP 14 gypsy moth and the brown-tail moth________ 34 
INGLIVOlCNeMieS © acs en eer eo on ye ee ee 15 VA TING os oe ae oe ra Re ee tee 34 
Introduced parasites and other enemies______ 15 INeweklampshires]: Gas sae eee eta 35 
@ontrolemet hogs asses ee ee ae 16 GTI TG xe a eee ee 35 
Recent control work in New England and iViassachusetis=eae = sas 2 hee eee eee ee 35 
ING wry ork woodlands: =-25 2-225 2. 23 IRhodewslandis=== 2 ee eee 36 
Record of clean-up of outlying colonies______ 23 Connechicu te. eras a eee ee eee 36 
Extermination project in New Jersey______-_ 25 ING WSY(Or Koka eee eet eae pons Se 2 ay tens 3 36 
Extermination project in Pennsylvania_____ 28 IN CAS CTSC Vissi Sate 8 a le oe 36 
HHetbrowal-vallomno thee ete See ee eee EEE 29 IRennSylvariiaeee eee. eee eee eek eee 36 
History of the pest in the United States____ 29 Mominioniok@anaday _-—- = i eee 36 
STOUR ISL OG Vee oe ee ee Oe eee 31 United States Department of Agriculture... 37 
Hoodsplants aaa ee eee eee Per ee 31 Cooperative: workers oh ss setae Seas ees 37 


Injury caused by the brown-tail moth______ 32 


THE GYPSY MOTH 
HISTORY OF THE PEST IN THE UNITED STATES 


In 1869 a number of egg clusters of the gypsy moth (Porthetria 
dispar Li.) were brought from France to Medford, Mass., by a French 
mathematician and astronomer, who had the idea that he could cross 
this insect with silkworm moths and thus develop a hardy race of 
silk-producing insects. In the course of his rearing experiments some 
of the eggs were accidentally lost or some of the caterpillars escaped, 
and he made at that time public acknowledgment of this fact, evidently 
appreciating the danger. 

The insect increased slowly at first. After 10 years it seemed to 
have been noticed by local residents but was believed to be some 
native caterpillar. Not until the summer of 1889, or 20 years after 
its introduction, did this insect become so abundant and destructive 
as to bring it into general public notice. At that time fruit and 
shade trees were completely defoliated, and the caterpillars, swarming 


1This circular supersedes Farmers’ Bulletin 1623, The Gipsy Moth and the Brown-Tail Moth. 
35349°—38——1 1 


2 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


into the houses, became a very grave nuisance. The situation was 
so serious that the State of Massachusetts appropriated funds and 
delegated to the State Department of Agriculture the task of exter- 
minating this pest. 

The infested area then covered about 359 square miles, and trees 
in many towns around Boston were completely defoliated each season 
fora number of years. As the work continued, more effective methods 
of treatment were developed and better results were obtained; conse- 
quently, during the summers of 1898 and 1899 little defoliation could 
be found in the entire area and few specimens of the moth were located 
throughout the residential sections. Careful examination indicated 
that the insect had been exterminated in some of the towns bordering 
the originally infested area. In February 1900 the legislature ordered 
the work discontinued because of the popular belief that the danger 
had passed, in spite of the advice of experts that the insect had not 
been stamped out. 

During the next 5 years the insect increased enormously. Many of 
the towns and cities in the old infested area were overrun with cater- 
pillars, which completely defoliated trees in many of the residential 
sections, and thousands of acres of woodland were stripped of leaves 
during the summer. The situation became so serious and intolerable 
that in 1905 the State resumed control work. In the meantime the 
insect had spread far beyond the original limits of infestation, more 
than 2,224 square miles being involved in Massachusetts as well as 
many isolated areas in Maine, New Hampshire, and Rhode Island. 

In 1906 an appropriation was made by Congress, and the Secretary 
of Agriculture was authorized to take all possible measures, in coopera- 
tion with the States concerned, to prevent the spread of this pest. 
The insect had increased to such enormous numbers and had spread 
so rapidly that the utmost efforts of the Federal and State forces 
were only able to apply relief measures in the badly infested residential 
sections and slightly retard the continued spread of the pest. Efforts 
were made to prevent the shipment of the insect to uninfested localities 
by inspecting products that were likely to carry it. This phase of 
the work was greatly strengthened as a result of the enactment of 
the plant quarantine law by Congress on August 20, 1912. Since 
October of that year shipments from the infested district have been 
regulated by Federal quarantine. 

On account of the continued spread and increasing damage caused 
by this insect, efforts were constantly being made to develop better 
means of control. The process of manufacturing lead arsenate, which 
was first made and used on the gypsy moth work in 1893, was im- 
proved so that the cost of production was reduced and the product 
could be more effectively applied. Spraying machinery and equip- 
ment were developed to a high point of efficiency. The details of 
field management were constantly improved, following experimental 
work in carrying on field operations, in order that the greatest possible 
volume of effective work could be done with the funds available. 

In spite of the efforts that were made by the Federal Government 
and all the States concerned, the insect continued to spread. By 
1914 it had covered the southern half of New Hampshire and extended 
as far east as Bangor, Maine. On the west it had crossed the Con- 
necticut River in Massachusetts and into Vermont. Rhode Island 
and towns in eastern Connecticut were found to be infested. 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 3 


During the war period conditions were unfavorable for preventing 
spread. The loss of efficient personnel and the constant turn-over of 
men, together with extraordinary increase in costs, made progress 
difficult. By the fall of 1922 scattered colonies were found farther 
west in Vermont, Massachusetts, and Connecticut, and in New York 
State near the Massachusetts State line. There was every indication 
of the continued spread of the insect unless more intensive work 
was done. 

To meet this serious situation a conference was held in the office 
of the commissioner of farms and markets in Albany, November 26, 
1922, which was attended by representatives from all the infested 
States, the Dominion of Canada, and the United States Department 
of Agriculture.? The entire subject of the prevention of spread of 
the gypsy moth and its control was discussed, and a resolution was 
adopted urging that sufficient funds be obtained from the States 
interested and the Federal Government to continue and strengthen 
control methods in the infested area, to do necessary scouting for the 
discovery and destruction of border infestations, to determine the 
location of the most practical place for a control zone, to take necessary 
steps to make control therein effective, and to destroy all infestations 
in and west of said zone. 

To carry out this project, in April 1923 the State of New York 
appropriated $150,000 to be administered by the Department of 
Conservation. Federal funds were also provided for the fiscal year 
beginning July 1, 1923, to bring about effective cooperation. 

The plan finally adopted, by the Federal and State authorities, was 

to locate a zone where clean-up operations to prevent westward 
spread of this pest would be centered. This barrier zone embraced 
an area of about 9,000 square miles east of the Hudson River extend- 
ing from Long Island Sound (excluding Westchester County, N. Y.) 
to the Canadian border, a distance of more than 250 miles, and rang- 
ing in width from 25 to 30 miles (fig. 1). This is the shortest and 
most feasible area in the United States that could be selected to pre- 
vent Nation-wide spread of the insect. The territory east of this 
zone was to be treated by the States concerned as far as their funds 
would permit, and their work was to be supplemented by liberation 
of imported parasites and other natural enemies of the insect by the 
Bureau of Entomology. Work in the New York portion of the area 
was to be financed by the State, with such assistance as could be given 
by the Bureau after covering the eastern part of the zone in western 
Vermont, Massachusetts, and Connecticut. 
_ While much of the extremely rugged country in the Adirondacks 
in northern New York and the Green Mountains in Vermont was 
avoided, as well as the Catskills and some of the rougher country 
west of the Connecticut River in Connecticut, there are areas in this 
zone, embracing the Berkshire Hills in western Massachusetts and 
some of the territory directly south and southwest of them in Con- 
necticut and New York, where the terrain is extremely difficult. 

In 1924, owing to the number of infestations found in Massa- 
chusetts and Vermont, and the discovery of a colony at Henrysburg, 
Quebec, by the inspection force of the Dominion entomologist of 
Canada, the quarantine line was moved westward from the eastern 


2 FELT, E. P., and others. THE GYPSY MOTH, AN IMMINENT MENACE TO THE FOREST AND SHADE TREES 
OF THE STATE OF NEW YORK. N. Y. State Dept. Farms and Markets Agr. Bull. 148, 58 pp., illus. 1922. 


4 CIRCULAR 464, U. 5. DEPARTMENT OF AGRICULTURE 


boundary of the zone to embrace the entire State of Vermont and 
additional towns in northwestern Connecticut. A foreign quaran- 
tine regulating the movement of Christmas trees was made effective 
covering the southern tier of towns in the Province of Quebec. In 
1926, owing to the effectiveness of the clean-up work in the zone and 
the fact that scouting west of the zone showed no infestation, the 
area under quarantine lying in the zone was eliminated from quaran- 
tine. The Canadian quarantine was withdrawn July 1, 1928. 


LEGEND 


AREA QUARANTINED FOR GYPSY MOTH 1934. 

DELIMITS AREA QUARANTINED FOR BROWN-TAIL MOTH 1934. 
E35 sarrier Zone. 

AREA REMOVED FROM BARRIER ZONE 1934. 

PENN, GYPSY MOTH INFESTED AREA. 


ISOLATED GYPSY MOTH 
INFESTATIONS IN NJ. AND N.Y. 


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FIGURE 1.—Barrier zone and status of the gypsy moth and brown-tail moth control areas at the end of 1934. 


Later in 1928 more infestations were found in the Massachusetts 
and northern Connecticut portions of the barrier zone than during 
the previous fiscal year. This made the problem far more difficult 
and emphasized the necessity of carrying on work in the territory 
east of the zone to facilitate eradication in the zone itself. Since 
there was also an increase in infestation directly east of the zone, 
7 towns in Vermont, 12 in Massachusetts, and 31 in Connecticut, 
embracing an area of 1,581 square miles, were reclassified from the 
lightly infested: to the generally infested area. 


- 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL oO 


Scouting during the latter half of 1929 and the first half of 1930 
showed a further increase in the number of infestations in the barrier 
zone, and Congress made additional funds available for clean-up 
work. No provision was made, however, for examination of terri- 
tory immediately east of the zone to check the increase there. The 
infestations located in 1929 and 1930 were new ones, as most of those 
previously discovered had been cleaned up. 

In 1933, after the passage of the National Industrial Recovery Act, 
funds were made available and extensive scouting and clean-up work 
was undertaken between the barrier zone and the Connecticut River. 
This was extended very materially by personnel from certain Civilian 
Conservation Corps camps, which were supervised by the gypsy moth 
organization of the Bureau of Entomology and Plant Quarantine 
through cooperative arrangements with the Forest Service of the 
United States Department of Agriculture, the State forest services, 
and the United States Department of the Interior. 

The prompt elimination of a few sporadic colonies that had been 
found just beyond the zone, together with the suitability of the area 
in the zone for effective clean-up, offers conclusive proof of the feas- 
ibility of checking westward spread. 

In 1934 a change in quarantine was made by transferring from the 
lightly to the generally infested area 74 towns in Maine, 5 in New 
Hampshire, 2 in Vermont, and 3 in Connecticut. In northern Ver- 
mont 39 towns were dropped from quarantine. The barrier zone 
line in northeastern New York was relocated on the New York- 
Vermont State line, thus eliminating 807 square miles, and a strip of 
towns in Vermont adjoining the barrier zone on the east, aggregating 
604 square miles, was added to the zone. 

Since July 1935 emergency funds have been made available for 
gypsy moth work, and more scouting and clean-up work has been 
carried on than heretofore. This has suppressed the insect in many 
isolated colonies and improved the condition in the barrier zone and 
the area adjoining it to the east. 


CONDITIONS OF INFESTATION IN NEW ENGLAND 


From the beginning of its gypsy moth work the Bureau of Ento- 
mology obtained general records of the density of local and general 
infestations in the territory not covered by the Bureau. Since 1911, 
however, counts of egg clusters have been taken annually from a 
series of woodland plots in the eastern portion of the infested area. 
They are summarized as follows: 


Egg clusters 


Egg clusters 


per acre Year per acre 
“ar LS Sa A gt a a A era 431) | Oe ee Ronn nee ee est FF ST 110 
Ps LASS 3? SESS * ieee oe ee PEPE Les J HR Gal: VOR TOSI fete lit 50 
Lis 3 Geek See Oa es eC BYon pale) agile Deke ee ee oe ee ee 61 
Lee eS Sa oe a ee STR 2 ee ees 127 
Lie 22k toa a es AAO OMe ee ge 303 
Te De 2 ee eh NR a i ipl Sel ha eee ee tee Cte 722 
Va wee eee Br TAN PAN OS! 2 407 
LS iets Se i ry ee Be j4 PeC ayy AUS). ce ee 66 
LSU oS ee EM Ses el pe ee SS Sk ey 42 
i AD aR aed Scat Tee a a Fee eats Ro tile Oil Ne Si 112 
LSet | Ue ils oe eG eS Dots | LO ae ene CVC set 344 
Hera pen mene ty); rl) _phiechogh cen 402 | 1934 181 


6 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


As the habits and the variable mortality of the gypsy moth and its 
food-plant limitations cause wide differences in its abundance in 
various parts of the infested area, it has seemed that the damage done 
and the possibilities of greatest "future injury could be gaged most 
accurately by determining the defoliation caused by the species over 
the area as a whole. The total acreage showing from 25- to 100-per- 
cent defoliation each year beginning in 1924, when defoliation was less 
than in any previous year, is as follows: 


Year Acres defoliated | Year Acres defoliated 
19242 Lioisa8 On iS EN S25MOS1. Oe wee I ee erie 204, 720 


FIGURE 2.—Life stages of the gypsy moth: A, Female moth; B and F, pupae; C, larvae or caterpillars; 
D, male moth; E, egg mass. All about three-fourths natural size. 


The danger of reinfestation of the barrier zone depends largely on 
the severity of infestation east of the zone. In the last 3 years the 
areas of defoliation were smaller in eastern Massachusetts and certain 
sections of southeastern New Hampshire, which comprise most of the 
older infested territory. In the same years heavy defoliation was 
noted much farther west in Massachusetts, and in 1934 and 1935 
extensive areas of complete defoliation occurred in the Connecticut 
River Valley and the adjoining territory about 20 miles from the zone. 


LIFE HISTORY 


The gypsy moth passes through four stages—the egg, the larva or 
caterpillar, the pupa, and the adult or moth (fig. 2). There is one 
generation a year. The times of the year when the different forms 
may be found in the field are shown in figure 3. 


( 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 7 


THE EGGS 


The female gypsy moth lays from 100 to 800 eggs in a cluster, 
depending on her size. The average number per cluster is approx- 
imately 400. In light infestations where the food supply is plentiful 
clusters are larger than the average, and in heavy infestations where 
the food supply becomes limited during the late larval stages they 
are smaller. Each cluster is covered with buff-colored hairs from 
the body of the female, which no doubt serve as a protection for the 
eggs during the long interval between oviposition and hatching. 

Most of the egg clusters are laid in July and hatch the following 
spring. The hatching date varies from about May 1 in southern 
New England to May 25 in the extreme northern part. The date 
of oviposition bears no relation to the date of hatching, as eggs laid 
in mid-August may hatch at the same time as those laid early in July 
under the same envi- 
ronmental conditions. 
Eggs deposited in warm 
locations, as on the 
southern exposure of 
buildings, may hatch 
several days earlier than 
others laid in cool and 
moist locations. 

The gypsy moth egg 
must be exposed to a 
chillng temperature 
before it will hatch. 
Just what this temper- 
ature is is unknown. 
Eges that have under- 
gone this conditioning 
process will hatch in 
midwinter in a warm 
building. 

The female moth de- ; 
posits her ego clusters FIGURE ee ees Seat ene ner stages of the 
on the trunks of trees, 
on the underside of limbs, under loose bark, in cavities in the trunks 
or branches, and sometimes on leaves, on ground debris, under stones, 
and in stone walls. When infested trees are found along stone walls, 
a large proportion of the eggs are often laid in the wall; but where 
the ground is free of stones or debris, a large proportion of clusters 
will be found on the tree trunks. 


THE LARVAE 


The newly hatched larvae begin immediately to search for palatable 
food. In pure stands of favored food this is a simple matter, but as 
the proportion of favored food in the stand decreases the problem 
becomes more acute. There is no evidence that such larvae can pick 
out a favored tree from an unfavored one without examining the 
foliage. They find the food through random movement. The 
normal mortality of first-stage larvae is very high. Newly hatched 
larvae can ordinarily live only about a week without feeding. The 


re) CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


absence of water becomes less of a problem as the larvae increase 
in size, probably because of the decrease in the ratio between evapo- 
rative surface and body volume. 

First-instar larvae move very slowly. They are active only when 
the temperature is above 60° F. and are more active when the temper- 
ature is 70° or higher. 

Gypsy moth larvae that are to become male moths molt five times, 
and those that are to be females molt six times. The full-grown 
larva is from 1% to 2% inches long. The head has yellow markings; 
the body is ale or ‘sooty colored, hairy, and on the dorsum is a 
double row of five pairs of blue spots followed by a double row of six 
pairs of red spots. As the larvae grow, the quantity of foliage eaten 
per day increases tremendously. Approximately 75 percent of all 
the foliage eaten by larvae having five instars is eaten in the fifth 
or last instar, and approximately 65 percent of the foliage eaten by 
larvae living through six instars 1s consumed in the last instar. Con- 
trol measures against larvae should therefore be applied as soon as 
possible after the eggs hatch, to protect the foliage from the later 


instars. 
THE PUPAE 


When full grown, the larvae shed their skins and transform to 
chestnut-brown pupae bearing tufts of yellow hairs. After about 10 
days in this stage the adult moths emerge. 


THE ADULTS 


The male gypsy moth is dark brown with black wing markings, 
and is a strong flier. The males usually emerge earlier than the 
females, and fly near the ground, in a characteristic zigzag manner, 
in search of female moths. 

The female moth is nearly white, with black wing markings, and 
is much larger than the male. Because of the weight of their bodies, 
the females are incapable of flight, and are usually found beside their 
empty pupal cases. Here they deposit their eggs, and once this 
function has been performed they die. Oviposition begins within a 
day or two after the female emerges from the pupa. The moths do 


not feed. 
INJURY CAUSED BY THE GYPSY MOTH 


It is impossible to state with precision the loss to New England 
forests due to the ravages of the gypsy moth. The best information 
compiled from data extending over a long period of years indicates 
losses of many millions of dollars in tree growth. These losses have 
been due not only to the direct or indirect killing of the trees but 
also to the retardation of growth through defoliation. Although far 
less spectacular than the immediate killing of trees, the second type 
of loss is more to be feared, for tens of thousands of trees are so 
affected for every one killed. Most conifers, notably hemlock and 
white pine, are killed by a single complete defoliation. Most rapid- 
growing deciduous trees put out a new crop of foliage the same season 
in which stripping occurs; they are therefore without foliage but a 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 9 


short interval during the growing season, but retardation of growth 
aud less wood result. 

Trees that are weakened by defoliation are susceptible to secondary 
injuries by fungi and bark borers. From 1912 to 1915 heavy mor- 
tality was noted among oaks that had been defoliated by the gypsy 
moth, and this was followed by an outbreak of the two-lined chestnut 
borer (Agrilus bilineatus Weber), whose larvae fed beneath the bark 
of the weakened trees. During recent years this beetle has not caused 
noticeable damage, but such a condition might recur without warning. 

The importance of tree growth in aiding retention of moisture in 
the soil and preventing erosion, particularly in rugged country, is 
well recognized. Defoliation encourages evaporation of moisture 
from the soil during the most critical growing period in the summer, 
renders such areas more susceptible to forest fires, and undoubtedly 
diminishes the flow of small streams, some of which furnish the water 
supply for reservoirs maintained for commercial or city use. The 
money value of these losses cannot be readily computed. 

Defoliated or dying trees along roadsides and streets in residential 
areas are objectionable, and the removal of trees from such locations 
is a distinct loss to the community and the publicin general. Recrea- 
tional areas are being used to a greater extent each year, and here 
the value of trees far outweighs the commercial value of the timber. 
Ragged foliage and denuded trees, accompanied by crawling cater- 
pillars, are avoided by the public. Trees in such locations have more 
of a struggle for existence than trees that grow in natural environ- 
ment without interference by man, and they therefore require added 
protection. The increased interest in natural playground develop- 
ment in New England and New York State seems to warrant more 
than ordinary expenditures to preserve the trees for their esthetic 
value alone. 

Figures 4, 5, and 6 illustrate the results of gypsy moth feeding in 
various types of stands. 

FOOD PLANTS 


Unlike many leaf-eating insects, which confine their feeding to a 
single species or group of plants, the gypsy moth is a general feeder 
on trees and shrubs. In fact, in heavy infestations few species of 
trees are ignored, especially by the larger larvae, and when food is 
scarce grass and cultivated crops are sometimes eaten. 

A study of the food plants of the gypsy moth in 1913 ® revealed 
distinct differences in the preferences of the very small and the larger 
larvae. The food plants were grouped in four classes, which are 
given herewith, with a few changes that subsequent observations have 
justified. This classification can be used as a basis for thinning to 
eliminate the most favored species and retain and encourage the more 
valuable and resistant species. It will be noted that class 2 includes 
most of the conifers, which suffer severely if grown in association with 
more favored species. Unfortunately, the infested region abounds 
in class 1 trees either in solid stands or in more or less diluted mixtures. 


ie MOSHER, F.H. FOOD PLANTS OF THE GIPSY MOTHIN AMERICA. U.S. Dept. Agr. Bull. 250, 39 pp., illus. 
1915. 


35349°—38——2 


CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


10 


illed by the gypsy moth. 


ted and k 


la 


defoli 


ith favored food trees, 


ture Ww 


1X 


inm 


ine growing i 


FIGURE 4.— White p 


ted by the gypsy moth. 


la 


Oak trees defoli 


RE 5. 


FIGU 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL Lit. 


FIGURE 6.—Hemlock growing in mixture with favored species defoliated and killed by the gypsy moth at 
Orange, Mass., in 1934. 


12 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


Cuass 1.—Species that are favored food for the gypsy moth larvae 


Alder, speckled Oak, rock chestnut 

Apple Oak, bear 

Aspen, American ~ Oak, bur 

Aspen, large-toothed Oak, pin 

Balm-of-Gilead Oak, post 

Birch, gray Oak, red 

Birch, paper Oak, scarlet 

Birch, red Oak, shingle 

Blueberry (Vaccinium angustifolium) Oak, swamp white 

Boxelder Oak, white 

Gum, red Poplar, Lombardy 

Hawthorn Rose, pasture 

Hazelnut Serviceberry 

Hazelnut, beaked Spruce, blue? 

Larch, American Sumac, mountain 

Larch, European Sumac, scarlet 

Linden, American Sumac, staghorn 

Linden, European Willow, glaucous 

Mountain-ash Willow, sandbar 

Oak, black Willow, white 

Oak, dwarf chestnut Witch-hazel 

Cuiass 2.—Species that are favored food for the gypsy moth after the earlier larval 
stages 

Beech, American (1)4 Pine, western white 

Cedar, red (4) Pine, white 

Chestnut Plum, beach 

Hemlock Spruce, black 

Pine, jack Spruce, Norway 

Pine, pitch Spruce, red 

Pine, red - Spruce, white 


Pine, Scotch 


Cuiass 3.—Species that are not favored but upon which a small proportion of the 
gypsy moth larvae may develop 


Barberry, European Elm, slippery 
Bayberry Gum, black 
Birch, black Hickory, bitternut 
Birch, yellow Hickory, mockernut 
Blueberry, low Hickory, pignut 
Blueberry, tall Hickory, shagbark 
Butternut (4) i hie Hophornbeam 
Cedar, southern white (4) Hornbeam, American 
Cherry, sweet Maple, Norway 
Cherry, wild black Maple, red 
Cherry, wild red - Maple, silver 
Chokeberry Maple, sugar 
Chokecherry Pear 
Cottonwood ; Poplar, silver. 
Cranberry, American Sassafras 
Elm, American Sweetfern 
Elm, European Sweetgale 
4 Numbers in parentheses refer to the original classification of plants that have been reclassified. Blue (fea 
spruce has been subsequently added. bi 


GYPSY AND BROWN-TAIL 


MOTHS AND THEIR CONTROL 


Cuass 4.—Species that are wnfavored food for gypsy moth larvae 


Arborvitae 
Arrowwood 
Arrowwood, maple-leaved 
Ash, black 

Ash, blue 

Ash, red 

Ash, white 

Azalea, white and flame 
Balsam, fir 
Blackberry, high 
Blueflag, larger 
Catalpa, hardy 
Cornus 

Cranberry tree 
Currant, red 
Cypress, bald 
Dangleberry 

Dock, narrow 
Dogwood, flowering 
Elder, American 
Eubotrys, swamp 
Feverbush F 
Grape 

Greenbrier 
Hackberry 
Hardhack, pink 
Hardhack, white 
Holly, American 
Honeylocust 
Honeysuckle, bush 


Huckleberry, highbush 
Inkberry 

Juniper, common 
Kentucky coffeetree 
Lambkill (sheep laurel) 
Locust, black 
Maple, mountain 
Maple, striped 
Mountain-laurel 
Mulberry, red 
Mulberry, white 
Osage-orange 

Osier, red 
Pepperbush 
Persimmon 
Poison-ivy 

Privet 

Raspberry 
Sarsaparilla 
Skunkeabbage 
Spicebush 
Sweetbrier 

Sweet pepperbush 
Sycamore 

Tea, Appalachian 
Tuliptree 

Viburnum, sweet 
Walnut, black 
Willow, bay-leaved 
Winterberry, smooth 


13 


MEANS OF SPREAD 


Egg clusters of the gypsy moth deposited on trees, lumber, stone, 
and other products that are likely to be shipped may be carried long 
distances and cause new colonies of the insect to be established. The 
only way to prevent spread of this kind is to inspect such products and 
treat any clusters found on them before they are shipped. 

Larvae of the gypsy moth may be carried on such moving objects 
as trains and automobiles. Horse-drawn vehicles and freshets may 
also transport them for limited distances, and egg clusters on debris 
may be carried by high water. The danger of such spread is depend- 
ent upon the extent of infestation along railroads, highways, and 
streams. | : 

It is probable that the principal agent in the spread of the gypsy 
moth is the wind. The chief trend of spread of the insect, since its 
introduction into New England, has been to the north and northeast, 
which is the general direction of prevailing surface winds after the 
hatching season. 

Since the newly hatched larvae are abundantly supplied with hairs, 
they are easily carried by the wind. Probably few larvae are ever 
blown loose from their supports by the wind. An enormous number, 
however, spin down from tree tops when disturbed and are intercepted 
by air currents; the strand of silk is broken and they are whirled away 
with this silk attached to their bodies. Spinning larvae normally 
sever the strand of silk by biting only when they come to rest upon 
some object; they seldom do this while hanging free. The distance 
that a larva may be carried aloft by currents of air depends to some 


14 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


extent upon the length of silk attached to its body. Larvae have 
been captured onscreens more than 20 miles from the nearest known 
infestation, and one larva has been taken on a screen attached to an 
airplane at a height of about 1,800 or 1,900 feet above the ground 
(2,000 feet above sea level). The height to which they may be carried 
varies from day to day and may greatly exceed 2,000 feet. Once lar- 
vae have reached such heights, they may encounter cross currents of 
air and be blown in the direction opposite to which surface winds are 
blowing. 

Transportation of larvae by the wind is, however, less serious than 
it would appear. The farther the larvae are carried the more widely 
they are separated and the less chance they have of falling close 
enough together to establish infestations. ‘There must be a large 
number of such larvae present to offset natural mortality. Millions 
of larvae, however, may be blown out of an infestation, fall nearby, 
and succeed in spreading the infestation short distances. That 
undoubtedly is why the infestation in New England has progressed 
only a few miles per year. Were it not for the tremendous natural 
mortality of larvae, the insect would have become established in new 
localities far more rapidly than it has. For this reason special efforts 
are made to destroy egg clusters before hatching, particularly those 
that are in exposed or wind-swept locations. 

Wind spread takes place primarily on hot days when convection 
currents from the heated surface of the ground are prevalent. The 
appearance of cumulus clouds signifies the existence of convection 
currents and the days when danger of wind spread is greatest. 


EFFECT OF CLIMATE 


The effect of climate, in all its phases, upon the gypsy moth has 
never been fully investigated, and is therefore little understood. The 
effect of extremely low temperatures upon overwintering eggs has 
received more study than any other single factor. It has been deter- 
mined that all egg clusters are killed when exposed to a temperature 
of —25° F. and that some eggs are killed at —15°. 

In the field, however, temperatures fluctuate greatly within very 
short distances. For instance, a temperature of —25° F. at a weather 
station in a town or city does not necessarily mean that such a tem- 
perature is common to the entire town. For this reason it has been 
impossible to estimate accurately just what was happening to gypsy 
moth eggs in towns from which temperature records were available. 

Winter temperature is an important factor in gypsy moth abund- 
ance in most of New England. In some winters the temperature 
does not get low enough to be fatal, but in other years mortality 
from this cause is heavy. In northern Maine, northern New:iHamp- 
shire, and most of Vermont except the Champlain and Connecticut 
River Valleys, minimum winter temperatures are low enough to kill 
ege clusters that are not protected by snow, ice, or otherwise, and in 
most of these areas infestations have become established slowly and. 
the increase of the species has been retarded. 

Late frosts in the spring sometimes cause severe damage to foliage, 
and this usually results in heavy mortality of the small larvae. This 
is most likely to occur locally, but was noticeable in many sections 
of the infested areas during the spring of 1936. Frequently there is 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 15 


also a considerable mortality of newly hatched larvae during long 
periods of rainy weather accompanied by low temperatures. 

Evaporation is another climatic factor that is known to influence 
caterpillar activity. Feeding is noticeably greater when evaporation 
is high, the loss of water from the caterpillar’s body probably acting 
as the stimulus. This may account for the more rapid feeding in the 
upper part of the crown than in the lower part. Such feeding serves 
to open the crown canopy, admitting more light, raising the tempera- 
ture, permitting a freer circulation of air, and increasing the evapora- 
tion rate below. Thus the entire crown becomes more and more 
susceptible to rapid feeding. Young larvae seem to be attracted and 
older larvae repelled by strong light. 


NATIVE ENEMIES 


No insect enemies of the gypsy moth native to New England cause 
any noticeable reduction in its numbers. This is shown by the fact 
that from 1900 to 1905, when no systematic effort was made to sup- 
press the insect, alarming i injury resulted, and native insect enemies 
did not increase to any marked degree. ‘The same is true of native 
insect-eating birds. While they undoubtedly feed to seme extent on 
gypsy moth caterpillars, there is no record of their being able to control 
the insect. The “wilt,” a disease that attacks and kills the cater- 
pillars and pupae, has probably occurred in this country for many 
years. During some seasons it kills an enormous number of the 
caterpillars and is often an important factor in reducing the infesta- 
tion locally. As a rule this disease is more common in heavy infesta- 
tions, although many caterpillars have been killed by it when the 
infestation has been relatively light. 


INTRODUCED PARASITES AND OTHER ENEMIES 


In 1905 the State of Massachusetts, in cooperation with the Bureau 
of Entomology, began to introduce parasites and other natural enemies 
of the gypsy moth from its native home in Europe and Japan. Since 
that time a large quantity of parasitized material has been received, 
and as a result some important natural enemies have become estab- 
lished in this country and are assisting in the control of the pest. 
The enemies which have become established, and which destroy the 
largest number of gypsy moth caterpillars and pupae, are the beetle 
Calosoma sycophanta L.; two species of parasitic flies, Sturmia scutellata 
R. D. and Compsilura concinnata Meig., one of which attacks the 
caterpillars of the brown-tail moth as well as those of many native 
insects; and a small wasplike fly, Apanteles melanoscelus Ratz. Two 
tiny important parasites of gypsy moth eggs have also been estab- 
lished, one, Oencyrtus kuvanae How., having been introduced from 
Japan and the other, Anastatus disparis Ruschka, from Europe and 
Japan. Two other introduced parasites, Hyposoter disparis Vier. 
and Phorocera agilis R. D., are established in this country, but they 
have not increased sufficiently to be important factors in gypsy 
moth control. 

The work of the natural enemies of the gypsy moth has greatly 
reduced the numbers of the insect. In some sections the reduction 
has been greater than in others, and their effectiveness has also varied 
from year to year. 


16 CIRCULAR 464, U. 8S. DEPARTMENT OF AGRICULTURE 


Since 1911 annual examinations have been made at observation 
points scattered over the infested area to determine the intensity of 
the infestation and the percentage of eggs, larvae, and pupae killed 
by introduced natural enemies. These points were located in York 
County in southwestern Maine; in Strafford, Merrimac, Hillsboro, 
and Rockingham Counties in southeastern New Hampshire; and in 
Essex, Middlesex, Worcester, Norfolk, and Plymouth Counties in 
eastern Massachusetts. The results indicated a rapid building up 
of the natural enemies, with an increasing percentage of the eggs, 
larvae, and pupae being destroyed, until 1923. In the meantime the 
intensity of the gypsy moth infestation, which had already reached 
a high level in 1912, remained high until 1921, when it declined 
rapidly until 1924. Since then there have been fluctuations in both 
the intensity of the infestation and the percentage of moths destroyed, 
but since the natural enemies have become thoroughly established 
the infestation has not reached the high level attained in the earlier 
years in some portions of the area. To evaluate correctly the benefit 
derived from parasites and natural enemies, other factors, including 
climatic conditions, must be taken into consideration. Without 
doubt, however, these beneficial insects have played a useful role 
with other control agencies in decreasing damage by this pest. 


CONTROL METHODS 


GENERAL METHODS 


A number of standard methods are in use for controlling the gypsy 
moth. They may be applied singly or in combination, depending on 
the tree growth, the density of infestation, and other local conditions. 
The essential information concerning each method is given in the 
following paragraphs, but each owner or operator should select the 
procedure that will give the best results when applied to his particular 
problem. 

USE OF GYPSY MOTH CREOSOTE 


The application of gypsy moth creosote with a brush will destroy 
ege clusters without removing them from the trees or objects on which 
they are deposited. This work can be done between the first of 
August and the time of hatching in the spring, which is about the 
first of May. ‘Treatment can be given most satisfactorily when there 
is no snow on the ground. 

Gypsy moth creosote is on sale in the infested area and is a low- 
grade coal-tar creosote which has been impregnated with sufficient 
coal-tar pitch to discolor the egg masses and thus indicate those that 
have been treated. A satisfactory grade can be bought in quantity 
under the following specifications: 


Specificporayity sea) - ee) ees ie 4. . ie ae Beets 0.990—-1.025 at 15.5° C. 
ParSaC Gs es Se ere ee 10 to 15 percent. 
Coaletar iby drocarponses 2 =. sang ee 80 to 85 percent. 
Water-anotrmoresuhan 2eee ie: 2h) - Se ee eee 2 percent. 

Flasht point = Preheat s genie iiiei tet |. 5 ee OR eee 70°—75° C. 


No separation of naphthalene at 0° C. - 
Initial boiling point, 170°—180° C.; 95 percent over at 

285°—295° C. 

In addition, not less than 6.5 percent nor more than 8.5 percent by 
weight of coal-tar pitch shall be added to the creosote furnished under 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 17 


this specification, in order that the finished product shall bave a color 
suitable for the proper staining of gypsy moth egg masses. This 
material must remain fluid and workable at subzero temperatures. 


USE OF BURLAP BANDS 


Gypsy moth caterpillars usually seek shelter during hot, sunny 
days, and if a band of burlap is attached to a tree (fig. 7) large numbers 


FIGURE 7.—Burlap band on tree showing caterpillars beneath. 


of them will crawl beneath it, where they may be crushed each day. 
A strip of burlap about 8 inches wide is placed loosely around the tree 
trunk, and a piece of twine is passed around the center and_tied to 
hold it in place. The top part of the burlap is then folded down to 
make a double shelter beneath it. 

This method requires considerable hand labor, but is effective in 
many places. If brown-tail moth caterpillars are present on the 

35349 °-—38——_3 


18 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


trees, burlap should not be ap- 
plied until after June 15, when 
most of these caterpillars have 
pupated. Otherwise they may 
form their cocoons beneath it, 
and the workmen may be poi- 
soned by the poisonous hairs 
that accumulate there. 


USE OF STICKY BANDS 


Bands of sticky tree-banding 
material, which may be obtained 
on the market, may be used on 
tree trunks (fig. 8) after the bark 
has been scraped so that the 
material can be applied evenly 
in a thin layer with a paddle. 
These bands prevent caterpillars 
from ascending the trees, and if 
proper treatment of egg clusters 
has reduced the number of lar- 
vae sufficiently, this is a very 
effective measure. Further- 
more, as the caterpillars are 
usually massed in large numbers 
beneath the bands, conditions 
are favorable for wilt disease to 
develop, and the caterpillars 
often die in large numbers from 
this disease and from starva- 
tion. Every week or 10 days 
during the caterpillar season a 
comb or similar implement 
should be run over the band to 
keep the surface from harden- 
ing and to bring up fresh, sticky 
material from the part near the 
bark. This material is expen- 
sive, and considerable labor is 
required to prepare the trees 
and apply and tend the bands. 
In some locations, particularly 
where there has been a heavy 
deposit of egg clusters on debris 
on the ground or in stone walls, 


FIGURE Sea imunk below its use is advisable. 


USE OF GYPSY MOTH TREE-BANDING MATERIAL 


A black greasy substance called “gypsy moth tree-banding material” 
is sometimes used to prevent caterpillars from crawling up the trunks 
of trees. It is similar to the product known as ‘‘Raupenleim” that 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 19 


has been used in German forests for many years. It has to be applied 
with a special gun in a thick narrow band encircling the tree trunk. 
At the present time it is not manufactured in this country, but infor- 
mation concerning its preparation and use can be sopalicdl by the 
Greenfield, Mass., office of the Bureau of Entomology and Plant 
Quarantine. 

SPRAYING 


The most effective spray material is lead arsenate. To make it 
adhere firmly to the foliage 4 fluid ounces of fish oil or raw linseed oil 
should be placed in the spray tank for each pound of lead arsenate. 
The oil should be added after the poison is well mixed with water in the 
tank, and while the whole is being agitated. Agitation should be con- 
tinued while the spray is being applied. The best grade of fish oil, 
known as ‘light pressed,’’ should be used. Five pounds of lead 
arsenate to each 100 gallons of spray is required to kill larvae that are 
half grown. A slight reduction in dosage may be made for the smaller 
larvae. In areas where there is mixed growth it is impractical to 
begin the spraying until the trees that produce foliage the latest—and 
they are usually the oaks—are ready for treatment. Under such 
circumstances larvae are found in several stages of development, and 
use of the stronger dosage may obviate the necessity of respraying. 
Many investigations are being carried on to develop low-priced non- 
arsenical insecticides which will not be harmful to man or domestic 
animals. Improvements along this lme would be most useful for 
gypsy moth spraying operations. 

Warning.—Lead arsenate is a stomach poison and is toxic to animal 
life. Itis unsafe to allow animals to graze underneath trees that have 
been recently sprayed. When fish oil is used as an adhesive, the 
spray will disfigure paint on buildings or vehicles unless it is removed 
with clear water before it has an opportunity to dry. Water may be 
provided by a low-pressure pump or from a hydrant. Fruit trees 
should not be sprayed with lead arsenate after the fruit is half grown, 
as it is difficult to remove the residue. 


CLEAN-UP AND THINNING WORK 


In many areas satisfactory control work cannot be attempted with- 
out the removal, and usually the burning, of infested rubbish and 
worthless trees. This should be done in such a way as to improve the 
property. Woodland areas may be thinned to advantage by removing 
trees that are favored as food by the gypsy moth caterpillars and 
encouraging the growth of better species of the less favored classes. 
When it is necessary to remove dead or useless wood in trees, the best 
practice of pruning and tree care should be employed. 


EQUIPMENT 


In creosoting work a brush with a round handle, which can be fitted 
with a cork stopper into a can containing creosote, is useful for treating 
ege clusters within easy reach. Those higher up can be treated w ith 
brushes that are attached at an angle to the tip of bamboo poles ranging 
from 8 to 18 feet in length. Axes, saws, and bark knives for marking 
trees are also necessary. 


20 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


For applying burlap ee ds knives should be supplied for cutting the 
burlap and the twine and destroying the caterpillars. For applying 
sticky bands, knives or steel brushes should be used to destroy the 
caterpillars, and tree scrapers will be required to smooth the rough 
bark before the bands are applied. 

The most expensive item in gypsy moth work is the spraying ma- 
chinery and the equipment necessary to operate it. If orchard trees 
or low growth is to be treated, an orchard sprayer equipped with one or 
more lines of hose and with nozzles of the vermorel or bordeaux type 
will be satisfactory. The object of treatment is, of course, to cover all 
the foliage evenly with a thin deposit of spray. The higher the trees 
the more difficult it is to apply the material without waste. When 
large shade, park, or woodland trees are to be treated, high-powered 
spraying apparatus and use of the solid-stream type of treatment will 
enable the work to be done rapidly. For best results the machine 
should be equipped with hose 1 inch in diameter, and a nozzle pressure 
of 300 pounds per square inch should be maintained. The speed of 
the pump must be regulated according to the aperture of the nozzle. 
Since the quantity of Jiquid passing through increases with the diame- 
ter of the tip, the pump pressure has to be stepped up to furnish the 
300-pound nozzle pressure necessary to break up the spray. As hose 
lines are lengthened or the elevation of the nozzle above the spraying 
machine increases, there is a loss of pressure at the nozzle due to the 
friction in the hose and the additional height to which the spray 
material must be forced. The pump should be of the triplex type, 

capable of delivering at least 35 gallons of liquid per minute for a short 
spray line. A spray tank of 300 gallons’ capacity is commonly used, 
and the tank and suction line should be provided with strainers to 
keep out foreign matter, which will either injure the pump or clog the 
nozzle. 

One-inch hose capable of withstandmg a working pressure of 600 
pounds is satisfactory for most park and shade-tree work, where ex- 
tremely long lines of hose are not required, or where isolated areas 
are to be treated and the equipment has to be moved frequently. On 
larger and more extensive areas, or where a water supply is some 
distance away, a higher-powered machine and hose that will withstand 
a working pressure of 1,000 pounds per square inch are necessary 
(fig. 9). To perform a maximum amount of work the sprayer should 
be set at the water supply. If the machine is equipped with an 
auxiliary pump for drafting water to supply the tank, and the tank 
is divided, one section can be filled while the other is being emptied 
as the spraying operation proceeds, and continuous spraying will 
result. With equipment of this type and on areas where there are 
slight elevations, 4,000 to 5,000 feet of hose can be laid to reach 
outlying areas. 

In the intensive work that is being carried on by the Bureau of 
Entomology and Plant Quarantine in some of the outlying areas 
longer hose lines are necessary, and on account of higher elevations 
the sprayer and the hose are required to pass a performance test of 
1,500 pounds’ working pressure. “As much as 12,000 feet of hose has 
been used on work of this type. Sprayers are constructed either with 
a power take-off or as individual units, so that they can be transferred 
to a truck and moved to points where they are needed in the field. 
With this type of machinery and the proper diameter of tip on the 


a 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 21 


nozzle, it is possible to spray thoroughly trees from 60 to 100 feet 
high. By using the same type of machine under reduced pressure 
and attaching to the nozzle a device known as a spreader, low growth 
may be treated rapidly and satisfactorily. 

Tests have been made during several seasons with airships, both 
heavier-than-air and dirigible types, to determine whether infested 
woodland areas could be dusted satisfactorily and economically. 
This method has not proved entirely satisfactory up to the present 
time. _ During the past year spraying with an autogiro has been tried, 
and the results have been more promising. This method has not yet 
been perfected sufficiently, however, to warrant its general adoption 
for woodland spraying, although for applying dust insecticides on 
certain low-growing crops it has given excellent results in some sections 
of the country. 

METHODS TO BE APPLIED IN ORCHARDS 


Of the fruit trees, apple trees are the most likely to be infested 
with this insect, and some injury to peach trees has been noted. 


FIGURE 9.—High-power truck sprayer. 


Apple orchards that are sprayed with lead arsenate for the control of 
other insects are protected from the gypsy moth. If systematic care 
or spraying of the orchard is not the practice, a program consisting of 
the removal of deadwood and defective trees, treatment of egg clus- 
ters, and spraying with lead arsenate and fish oil shortly after the 
blossoms fall should be put into operation. Orchards that are in 
close proximity to infested woodlands are sometimes severely damaged 
as a result of dispersion of small caterpillars by the wind or migration 
of the larger ones. ‘This can be prevented for the most part by proper 
care of the surrounding woodland. 


PROTECTION OF SHADE, ORNAMENTAL, AND ROADSIDE TREES 


Protection of shade, ornamental, and roadside trees is vital to the 
communities and rural districts in which they grow, as they increase 
property values. In most thickly settled communities, when street 
planting has been done in recent years, maple, elm, and other varie- 
ties that are not favored by the gypsy "moth have been planted, but 


22 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


in many areas poplar, linden, willow, and, to a less extent, some of 
the oaks have been used. In the rural sections there has been rela- 
tively little roadside planting, and most of the shade trees are seedlings 
or have developed from sprouts from trees that have previously been 
cut. On private grounds there is a wide range of species, both native 
and exotic, and on such properties there are frequently many trees 
that are suspectible to gypsy moth attack. 

To obtain information as to the species that are growing on trunk- 
line roads, in the summer of 1936 a hurried survey was made on one 
of the principal State roads from the New York State line through 
central Massachusetts, swinging southeast, and extending diagonally 
through Barnstable County to Orleans on Cape Cod. The route 
covered 260 miles of road, 48 miles of which was classified as city 
and 212 as rural. The tree growth for 50 feet on each side of the 
road was noted, because trees growing within these strips will even- 
tually furnish shade for the highway. As a result of this survey 38.5 
percent of the trees were rated as favored species, 27 percent were 
conifers and beech, which are highly favored during certain stages of 
the insect’s development, 26.5 percent were far less favored but occa- 
sionally defoliated, and 8 percent were in the unfavored group. 
About 51 miles of this road was open country with no trees, and there 
were additional areas where trees had been cut and were being replaced 
by sprout growth. These sprout, or brush, areas were about 50 per- 
cent favored food. The species growing in the wooded areas adjoin- 
ing these strips along the highway, and in the forest areas that were 
more remote, varied greatly in different localities, but it is estimated 
that more than half the tree growth was of favored species. 

A survey of this type does not show what conditions exist in sec- 
tions north or south of the road that was selected or on rural or unim- 
proved roads. A larger percentage of favored food plants might be 
expected southward toward Long Island Sound, and of less favored 
ones in southern Vermont, New Hampshire, and Maine. ‘The 
information obtained, however, indicates the necessity of protecting 
roadside trees from the oypsy moth. Officials in charge of tree pro- 
tection could well afford to have maps indicating the growth along the 
streets under their control as a basis for planning for protection or 
replacement of the most desirable species. An endeavor should be 
made to remove as much of the favored growth as possible and to 
encourage the growth of nonfavored trees. When it is impractical to 
do this, treatment should be applied for the protection of the favored 
species. Where solid woodland adjoining the road is heavily infested 
with the gypsy moth, roadside trees will be denuded by migrating 
caterpillars. In such cases protective work should be done to prevent 
defoliation, and the methods that can be most economically employed 
should be put into practice in an area adjoining the trees along the 
roadway. The size of this area will depend upon the severity of the 
infestation. 

THE WOODLAND PROBLEM 7 

In the barrier zone and the adjoining areas, as well as in isolated 
infestations beyond the zone, intensive methods must be applied to 
curtail the infestation, not only for the benefit of the locality where it 
exists, but to prevent the spread of the pest beyond the known 
infested area. This makes necessary the use of a combination of the 
methods that can be most cheaply applied. 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 22 


In the generally infested area it is impracticable to apply such 
intensive methods to large woodlands unless the property is of special 
esthetic value or to protect other areas that have been intensively 
treated. On account of the low value of most of the forest growth, 
some relief can be obtained by the adoption of a thinning program 
based on the removal of the most favored food trees in order that the 
food of the insect may be reduced. This work, together with the 
encouragement of the growth of nonfavored species, will assist in 
preventing damage by this insect. It can be done by the owner 
himself if he makes proper selection of the trees to be removed. 
Obviously the best silvicultural practice should be followed in such 
selective thinning (figs. 10 and 11). In pure or nearly pure stands of 
favored trees clean cutting and the planting of unfavored species is 
the best method of building up a resistant stand even though the cost 
is considerable, but there are many areas scattered through the 
infested territory where clean cutting is not necessary to improve 
the stand. 

The same principles of thinning, aimed at the creation of more 
resistant growth, can be applied by owners even if their property is 
not infested, as this will reduce the opportunity for establishment of 
this pest. In young plantations of white pine or other conifers favored 
species should be removed, and if there are adjoining areas of favored 
erowth as many of such species as possible should be removed to 
prevent the insect from migrating into the plantations. 


RECENT CONTROL WORK IN NEW ENGLAND AND NEW YORK 
WOODLANDS 


In both the barrier zone and the outlying infested areas intensive 
work is being done, most of it in woodland, to exterminate the insect 
and to prevent westward spread. In the zone itself such treatment has 
eliminated the insect in many localities in Vermont, Massachusetts, 
and New York. Isolated colonies are now (1937) being treated in 
southwestern Massachusetts and northwestern Connecticut, and in a 
few towns in the southern part of New York State. On Long Island 
and in the Borough of the Bronx in New York City the infestation 
has been greatly reduced. In 1936 a colony was found in Shawangunk, 
west of the Hudson River, and intensive treatment is being applied 
in this locality. 

Between the barrier zone and the Connecticut River isolated colonies 
have been found, especially in the territory nearest the river in 
Vermont and over a wider area in Massachusetts and Connecticut. 
Work similar to that in the barrier zone is being carried on here, the 
number of infestations is being reduced, and infestations have been 
exterminated. 


RECORD OF CLEAN-UP OF OUTLYING COLONIES 


A few colonies of the gypsy moth have been discovered at points 
quite distant from the generally infested New England region, 
notably at Geneva, N. Y., in 1912; at Cleveland, Ohio, in 1914; at 
North Castle, Westchester County, N. Y., in 1914; at Rutherford, 
N.J., in 1914: and at Greenport, near the eastern end of Long Island, 
in 1921. In practically all these cases the Federal Government was 
assisted by the States involved in ferreting out the limits of the 


AGRICULTURE 


DEPARTMENT OF 


= 
Ne) 


CIRCULAR 464, U. 


24 


FIGURE 10.—Mixed stand of hardwoods and conifers before thinning. 


Here white 


ed from danger. 


as been rele 


—Same woodland shown in peure 10 after favored food trees had been removed. 
pine as 


FIGURE 11 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 25 


colonies and applying intensive clean-up measures, and in every case 


the colonies have been exterminated. 


Since 1921 several other small, scattered infestations have been 
found on Long Island (fig. 12), and clean-up work here was undertaken 


by the New York Department of 
Conservation. Owing to its geo- 
graphical location and the general 
trend of spread of the insect away 
from rather than to this island, 
sufficient field work should furnish 
ample protection from this pest. 


EXTERMINATION PROJECT IN 
NEW JERSEY 


In July 1920 a State inspector 
found the gypsy moth on a large 
estate near Somerville, N. J. When 
discovered, the infestation centered 
in a large plantation of blue spruce 
trees, several acres of which were 
defoliated. There were dead trees 
in the worst-infested portion of the 
plantation, with indications that 
they had been killed by complete 
defoliation (fig. 13). 

The trees in this plantation had 
been imported from the Nether- 
lands about 10 years before, and 


the infestation came with the shipment. 


FIGURE 12.—Locations, outside of the large New 


Jersey and Pennsylvania infestations and the 
barrier zone, where the gypsy moth has been 
exterminated: 1, Cleveland (Bratenahl), Ohio; 
2, Loretto, Pa.; 3, Geneva, N. Y.; 4, Schenec- 
tady, N. Y.; 5, North Castle and Garrison, 
N. Y.; 6, Brooklyn, Roslyn, Kew Gardens, 
Patchogue, Shelter Island, and Greenport on 
Long Island, N. Y.; 7, Deal Beach, Wyckoff, 
South Orange, Scotch Plains, Paterson, Madi- 
son, Glen Rock, Elizabeth, and Rutherford, 
N.J.; 8, Henrysburg, Quebec. 


This was prior to the en. 


actment of the Plant Quarantine Act, and emphasizes the pressing 
need for precautionary measures to keep out dangerous pests. 


FIGURE 13.—Blue spruce defoliated and killed by the gypsy moth. 


26 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


Scouting during the fall of 1920 and the spring of 1921, financed 
by the State of New Jersey and the Federal Government, revealed 
infestations of this insect in scattered localities over an area of more 
than 400 square miles surrounding Somerville (fig. 14). 


FIGURE 14.—Area in New Jersey infested by the gypsy moth in 1921. Dots indicate location of colonies 
within the infested area, and dots enclosed in circles indicate isolated colonies. 


Previous successes in cleaning up local infestations led to the 
adoption of a cooperative plan to clean up this large, newly discovered 
infestation. State and Federal funds were appropriated, and the 
work was organized under the direction of the field office for gypsy 
moth control of the Bureau of Entomology. When the limits of 
infestation had been determined, the area was placed under State 
quarantine, which required as a condition of movement the certifica- 
tion of freedom from infestation of all products likely to carry any 
stage of the gypsy moth. Thorough inspection, which permitted 
certification, was made in cooperation with the Federal Government and 
by Federal inspectors. The area under regulation has been gradually 
reduced as a result of the clean-up work, and in 1932 Federal opera- 
tions were stopped and all inspection requirements were withdrawn. 

As soon as active work was under way in New Jersey, it was learned 
that trees had been shipped from the estate on which the insect was 
first discovered, and that the danger of its establishment in many 


Q) 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL D7 


localities was very great. Fortunately, a record of all these ship- 
ments was available. It was found that 261 shipments had been sent 
to the District of Columbia and the following States: Connecticut, 
Delaware, Florida, Illinois, Indiana, Kentucky, Maryland, Minnesota, 
Missouri, New York, North Carolina, Ohio, Pennsylvania, Virginia, 
and Wisconsin. ‘These shipments were traced and the planted stock 
was inspected by State or Federal officials. In addition, 318 ship- 
ments that had been distributed in New Jersey were followed up 
the same way. 

As a result of this work small infestations were found at Loretto, 
Pa.; Garrison, Roslyn, and Kew Gardens, N. Y.; and Deal Beach, 
Wyckoff, South Orange, Scotch Plains, Paterson, Madison, Glen 
Rock, and Elizabeth, N. J. These small infestations were cleaned up 
the following year, and repeated scouting has failed to indicate the 
presence of the pest. 

In the meantime the center of the infested area was receiving in- 
tensive treatment, including spraying, and an enormous number of 
ego clusters were destroyed. It is significant that no trees in New 
Jersey have suffered from gypsy moth feeding since that time. During 
the next 4 years scouting and clean-up operations were continued 
throughout the known infested area, particular attention being paid 
to extensive woodlands north of Somerville, known as the Watchung 
Ridge. These areas were heavily wooded and were difficult and 
expensive to work. 

Since 1925 the gypsy moth has been steadily reduced in numbers. 
The scouting and clean-up work covered over 2,369 square miles, 
although the towns in which colonies were found were in an area of 
924 square miles. Federal operations were discontinued in 1932, 
as no infestations had been discovered since 1929. Since 1932 the 
State force has been making inspections in many localities and has 
uncovered a few small infestations along the northern border of the 
old infested area. ‘These have been treated by the Federal Govern- 
ment in cooperation with the State. Although a large amount of 
intensive work has been done, no infestation has been found during 
the past 2 years. 

Table 1 shows the number of townships in the barrier zone, New 
York, and New Jersey where the gypsy moth has been eradicated and 
the number of infestations that have been cleaned up. It indicates the 
protection that has been afforded to other sections of the United States. 


TaBLE 1.—Townships in the barrier zone, New York, and New Jersey, where 
gypsy moth infestations have been eradicated, with the number of infestations 
cleaned up, fiscal years 1920-19385 


Infestations Infestations 
Infested Infested = 
State A extermi- State extermi- 
townships ata d townships mated 
In barrier zone: Number Number South and west of barrier 
Connecticut_________- 20 92 zone: Number Number 
Massachusetts_______- 27 362 New Jersey__.___-___- 38 878 
ING Wa VOnKe ee 24 75 ING winViOE kee 17 567 
WeLmMonte eee ese 18 78 
a Mo tales. Sates re 55 1, 445 
MRotaltaee Boe = 89 607 
——_ | ———— Grand total_______- 144 2, 052 


28 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


EXTERMINATION PROJECT IN PENNSYLVANIA 


Late in July 1932 a serious infestation was discovered near Pitts- 
ton, Luzerne County, Pa., through the location of male moths by 
a biology student. A survey was made and scattered infestations 
were found over a wide area. An eradication program was adopted 
under the supervision of the officials of the Federal Bureau of Ento- 


NEW YORK 


™ wa ci 
; eo 


FISCAL YEAR 


i935 GYPSY MOTH PROJECT 


NORTHEASTERN PENNSYLVANIA 
———=_ DELIMITS KNOWN AREA OF GYPSY MOTH 
INFESTATION= APPROXIMATELY 410 SQUARE MILES 


J 
=> 1} 
WiLKES}BaRRE® 


ono ' NEW JERSEY 


e INFESTATION 


HARRISBURG 


© ISOLATED INFESTATION ez, 


MARYLAND 


Mmm PENNSYLVANIA QUARANTINE — SEPTEMBER I, 1934 
APPROXIMATELY 880 SQUARE MILES 


FIGURE 15.—Gypsy moth infestation in northeastern Pennsylvania in 1935. 


mology in cooperation with the Pennsylvania Department of Agricul- 
ture and Department of Forests and Waters, and an office was estab- 
lished in Wilkes-Barre. From the fall of 1932 to the spring of 1933 
over 1,200 acres of tree growth were thinned and cleared of brush and 
worthless and dead trees in the worst infested portion of the area. 
During the same period about 2 million egg clusters were destroyed 
by creosoting. In the summer of 1933, 3,200 acres of woodland and 
thousands of trees in residential sections and open country were 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 29 


sprayed. A larger area was thinned and cleaned during the fall and 
winter. 

The work has been intensified and expanded since that time, and 
there has been a marked decrease in the number of egg clusters treated 
each year. Some new infested points have been found, and they have 
been promptly treated. No defoliation has been noted since the 
first summer. The infested areas and some of the surrounding town- 
ships have been placed under a State quarantine, and movement of 
materials likely to carry the insect is not permitted until they have 
been inspected and certified by officials from the Wilkes-Barre office. 

The area infested in 1935 is shown in figure 15. The present 
infested area aggregates 680 square miles, and additional areas sur- 
rounding it totaling 320 square miles are covered by the quarantine 
and inspection regulations. This includes Coolbaugh and Foster, 
which were added in 1936. 

Substantial progress has been made on this project in Pennsylvania, 
and excellent cooperation has been received from the State. The 
territory is located in the heart of the anthracite district, and much 
of the country is wooded and mountainous, and therefore difficult 
to work. Part of this area is in the valley of the Susquehanna and 
Lackawanna Rivers, and some infestations have been found in the 
Pocono Mountain range. This infestation is located the farthest 
west of any in the United States, and the importance of reducing the 
abundance of the insect and bringing about its final extermination can- 
not be overestimated. If the work is not continued aggressively, 
the insect might spread rapidly to surrounding territory and to other 
States where it is not now known to exist. 


THE BROWN-TAIL MOTH 
HISTORY OF THE PEST IN THE UNITED STATES 


The brown-tail moth (Nygmia phaeorrhoea Don.) was first found in 
the United States in Somerville, Mass., in the summer of 1897, and 
was undoubtedly introduced several seasons previous to that time on 
imported nursery stock. The insect increased enormously, and as the 
caterpillars were fond of the foliage of fruit and ornamental trees and 
shrubs, they became an unbearable nuisance, particularly in residential 
sections. Not only was complete defoliation common early in the 
summer, but as the hairs from the caterpillars caused serious poisoning 
to human beings the presence of this pest became a veritable scourge 
in densely populated areas. The insect extended its range very 
rapidly, because the moths of both sexes fly freely. This species 
occurs in many parts of Europe and is frequently very injurious. 

The State of Massachusetts applied suppressive measures from the 
winter of 1897 until February 1900, when it discontinued the work 
along with that of the gypsy moth. By 1905 the brown-tail moth was 
extremely abundant in eastern Massachusetts. It was also present 
in enormous numbers in Rhode Island, southern New Hampshire, 
and southwestern Maine. Not only did fruit and shade trees suffer 
defoliation, but large areas of oak woodland, particularly sprout 
erowth, were completely defoliated. 


30 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


The insect continued to spread until 1915, when most of the area 
east of the Connecticut River, with the exception of a portion of 
northern New Hampshire and Maine, was heavily infested. Some 
infestation also existed in Vermont and west of the Connecticut River 


TJodener. pipe: : 


FIGURE 16.—Life stages of the brown-tail moth: A, Winter nest; B, male pupa; C, female pupa; D, cocoon 
in leaves; H, young caterpillars on leaf; F, full-grown caterpillar; G, female depositing eggs on a leaf, and 
egg mass also on leaf; H, egg mass removed from leaf and with some of the eggs exposed; J, male moth; 
J, female moth. All about three-fourths natural size. 


in Massachusetts and Connecticut. Suppressive work carried on 
by the States and the Federal Government kept the residential 
sections fairly free from this pest. 

The area now infested by the brown-tail moth is shown in figure 1, 
and is much less extensive than formerly. Low winter temperatures, 


Oi 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 31 


particularly in the northern part of the territory, coupled with the 
work of natural enemies and disease and the continuous repressive 
measures used in the residential sections, have caused a remarkable 
decrease in the abundance of this pest. The insect has been found 
in Nova Scotia and New Brunswick, but has not been reported from 
there in excessive numbers for several years. 

This pest can easily be shipped on woody plants, but general spread 
in this manner has been prevented by the strict enforcement of 
inspection and quarantine regulations. 


LIFE HISTORY 


The different stages in the development of the brown-tail moth are 


shown in figure 16. 
THE EGGS 


The female moth deposits a small cluster of from 200 to 400 eggs 
on the underside of a leaf. They are usually laid in July, and are 
covered with brown hairs from the body of the female. Hatching 


begins about August 15. 
THE LARVAE 


The newly hatched larvae, or caterpillars, feed on the epidermis of 
the leaf. After molting once or twice they construct a winter web. 
This is made by drawing together several terminal leaves and fasten- 
ing them with silk which they secrete. The larvae from one or more 
ege clusters live and feed in common, and as cold weather approaches 
they retire to the web, in which they remain during the winter. In 
the spring, as soon as the buds begin to develop, the larvae leave the 
web and feed upon the bud scales and small leaflets. As they increase 
in size they consume most of the foliage. They become full grown 
late in June. 

The full-grown larva, which is hairy, is about 14 inches long. The 
head is light brown. The body is dark brown to almost black, with 
a broken white line on each side and two conspicuous reddish spots 
on the dorsum near the posterior end. 


THE PUPAE 


After the caterpillars have finished feeding, they spin loose silken 
cocoons in which to pupate. These cocoons may be constructed sep- 
arately, or large numbers may be spun in a single mass. Sometimes 
leaves are drawn together as shelters; in other cases the cocoons are 
attached to trees or other objects. About 2 weeks is spent in the 
pupal stage. 

THE ADULTS 

Emergence of the moths usually begins the first week in July. 
The adult is pure white, except for the tip of the abdomen, which is 
covered with brown hairs. The body of the female is much larger 
than that of the male. These moths are attracted to strong light, 
and as they fly at night they are often seen around electric lights in 
cities and towns during the first half of July. 


FOOD PLANTS 


The caterpillars of the brown-tail moth feed on the leaves of apple, 
pear, cherry, oak, and willow, and they are sometimes found in con- 
siderable numbers on other common deciduous trees and shrubs. 


32 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


They never attack conifers and are seldom found on hickory, ash, or 
other trees. 

Oak foliage is one of the favored foods of the brown-tail moth cat- 
erpillars in Europe and was severely injured in New England for a 
number of years after this insect became established there. It has not 
suffered in this way in recent years except in Maine and New Hamp- 
shire in 1933, when the insect was unusually abundant, and then some 
webs were found on oak trees and the caterpillars caused considerable 
defoliation locally. 


INJURY CAUSED BY THE BROWN-TAIL MOTH 


The principal injury caused by the brown-tail moth is due to the 
feeding of the larvae in the spring. ‘The caterpillars are often numer- 


FIGURE 17.—Apple trees defoliated by the brown-tail motn. Note the hibernating webs on the twigs. 


ous enough to devour the leaves as fast as the trees are able to develop 
them. As the webs are made on the terminals, the growth of the 
trees is often severely checked. In severe infestations trees may be 
completely stripped (fig. 17), but as the larvae grow rapidly during 
the first part of June there is usually an opportunity for the trees to 
produce new leaves before midsummer. The larvae hatch in August 
and frequently skeletonize the leaves, but this does not damage the 
trees seriously, as the growing period for the season is nearly over. 
The bodies of the caterpillars are provided with poisonous hairs. 
A microscopic examination of these hairs shows that the edges are 
barbed in such a way as to cause intense irritation when they come in 
contact with the human skin. They are also hollow and contain a 
substance which acts on the blood corpuscles. Poisoning and irrita- 
tion caused by this insect are accompanied by external swelling, and is 
known as the brown-tail rash. Persons differ in their susceptibility 
to this poison, but many cases are reported each year in the infested 
area. Many camps and summer cottages cannot be occupied with 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 30 


any comfort during the early summer if the caterpillars are abundant. 
If clothing is hung on the line near badly infested trees, the hairs 
frequently find lodgment and are brought into the houses, with 
consequent poisoning of the inhabitants. 


NATIVE ENEMIES 


One of the important native enemies of the brown-tail moth is a 
fungus disease (Hntomophthora aulicae Reich.) which attacks the 
caterpillars. It was first reported in this country by Roland Thaxter 
in 1888. Like all diseases of this nature, the benefit derived from it 
is regulated largely by weather conditions. This fungus sometimes 
works to a slight degree on the small caterpillars in the fall, and is 
found occasionally in the winter webs. As a rule, however, the 
greatest mortality of caterpillars takes place in the spring, when they 
are nearly full grown, and the pupae may, under the most favorable 
conditions, be almost completely exterminated. 

Native parasites and predacious insects have done little to check 
the increase of the brown-tail moth. 


INTRODUCED PARASITES AND OTHER ENEMIES 


Compsilura concinnata Meig., one of the species introduced as an 
enemy of the gypsy moth, attacks the caterpillars of the brown-tail 
moth freely, while two others, Apanteles lacteicolor Vier. and Sturmia 
midicola Towns., that were introduced from Europe at about the 
same time are also important enemies of the insect. Other imported 
enemies, Carcelia laxifrons Vill., Meteorus versicolor Wesm., and 
Eupteromalus nidulans Foerst., that have become established help to 
reduce the numbers of the moth but are not usually of great importance. 


EFFECT OF LOW TEMPERATURES 


Extremely low temperatures in the winter often prove fatal to a 
large proportion of the small caterpillars in the webs. When unpro- 
tected by snow or other covering, they are usually killed by tempera- 
tures below —25° F. 


METHODS OF CONTROL 


The brown-tail moth can be controlled by cutting off the winter 
webs and burning them before the caterpillars begin to emerge in 
April. These webs should be destroyed by fire, for if they are simply 
cut from the trees and left on the ground, the caterpillars will emerge 
and no benefit will result from the work that has been done. 

In orchards it is sometimes inadvisable to cut the winter webs, for 
where an infestation is heavy the cutting is likely to leave poorly 
shaped trees. Spraying in the spring is not a satisfactory remedy 
unless the infestation is very light, because large numbers of cater- 
pillars do not allow the tree to put out sufficient foliage to hold the 
spray material. 

An effective method in orchards is to spray the trees before the 
middle of August, using 3 pounds of powdered lead arsenate to 100 
gallons of water. Before doing so the orchardist should determine 
to what extent the trees are infested with egg masses of the brown- 
tail moth. In spraying fruit trees, particularly early fall varieties, 


34 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


caution should be used to avoid excessive spray residues. The 
foliage should be treated, particularly the terminal shoots, and care 
should be taken not to cover the fruit. Late fall or winter varieties 
of fruit may be sprayed with lead arsenate in August, and although 
an occasional spot may be found on the fruit at the time of picking, 
no injury will result from it. Where only a few choice fruit trees 
are sprayed, it is practicable to wipe the fruit before packing it for sale. 

The damage caused by the brown-tail moth is ordinarily not so 
severe as that due to the gypsy moth, because the brown-tail moth 
does not have so wide a range of food plants and, since most of the 
feeding is done early in the season, the trees have an opportunity 
to recover before midsummer. In the territory where both insects 
exist the caterpillars of the gypsy moth supplement the feeding done 
by those of the brown-tail moth, and the injury is therefore greatly 
increased. 

Thorough destruction of the webs in residential sections and in 
orchards has materially reduced the infestation in such places. Elim- 
ination of worthless apple and wild cherry trees would help greatly 
in reducing the pest. 


RECENT CONTROL EFFORTS 


In the winter of 1933-34 an extensive Civil Works Administration 
brown-tail-moth project was carried on, under the direction of the 
Bureau of Entomology in cooperation with the New England States, 
in which almost 24 million webs were cut and burned. Although 
the insect was much less abundant the following summer, during the 
winter of 1934-35 almost 2 million webs were cut and destroyed by 
State officials using local or State funds. The following winter a 
Works Progress Administration project was conducted by the Bureau 
in cooperation with the States, and more than 4% million webs were 
destroyed. The work was continued during the winter of 1936-37, 
and up to the end of March more than 2% million webs had been 
cut and destroyed. 

The destruction of such large numbers of winter webs has resulted 
in a decided decrease in infestation over much of the infested area. 
Prior to the C. W. A. work heavy defoliation was common in many 
parts of this area. During the past summer little defoliation was 
found. ‘Towns have been found in all the infested States where no 
infestation could be located, and it should be possible to reduce the 
affected territory materially if the work is continued. 


ORGANIZATION AND STATUS OF WORK AGAINST THE 
GYPSY MOTH AND THE BROWN-TAIL MOTH 


Each State infested with the gypsy moth and the brown-tail moth 
is carrying on control work, and many of the towns and cities are 
similarly engaged. The Dominion of Canada and several of the 
Provinces have also taken up control and eradication work. 


MAINE 


In Maine the work is in charge of the commissioner of agriculture, 
who has authority to appoint assistants to supervise the operations. 
In the southwestern part of the State the gypsy moth infestation is 


>| = 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 35 


general and, in places, severe; the northern part of the insect’s range 
is only lightly infested. The severity of infestation increased in 1932 
and 1933, and many heavily infested sections have been found since 
that time. Several small infestations were found in the eastern 
part of Washington County in 1936. The brown-tail moth was 
very abundant in the southwestern part of Maine from 1931 to 1933, 
but the wholesale cutting of the webs has greatly reduced the in- 
festation. Over 12,000 square miles in the State are infested with 
the gypsy moth, and about 7,000 with the brown-tail moth. The 
latter has been spreading to new territory since 1931. 


NEW HAMPSHIRE 


The moth work in New Hampshire is in charge of the State ento- 
mologist. Over 8,000 square miles are infested with the gypsy moth 
and about 5,000 square miles with the brown-tail moth. Most of 
the territory from Lake Winnipesaukee south to the Massachusetts 
line has suffered severe and repeated defoliation from the gypsy 
moth. The territory directly north and northeast of the lake has 
also had considerable defoliation. The same areas were heavily 
infested with the brown-tail moth from 1931 to 1933. Since that 
time the infestation has been greatly reduced by control work, and 
also, in some sections, by winter mortality of the larvae. 


VERMONT 


In Vermont the moth work is in charge of the commissioner of 
agriculture, who appoints an entomologist to carry on the field work. 
After intensive scouting for the gypsy moth in the winter of 1933-34, 
the area under quarantine was reduced from about 6,000 to 4,500 
square miles. The heaviest infestations are located along the Con- 
necticut River. Only a few brown-tail moth infestations have been 
found in Vermont in recent years. A survey along the eastern border 
of the State in 1933 and 1934 indicated a number of scattered in- 
festations, and this area was placed under quarantine. As a result 
of work done since that time no infestation by this insect has been 
found during the last 2 years. 


MASSACHUSETTS 


The commissioner of conservation has charge of the moth work in 
Massachusetts. Each infested town is required by law to select a 
local superintendent, whose appointment must be approved by the 
commissioner. Owners are required by law to keep their property 
free from these pests, but cannot be compelled to expend for this 
puruose more than $5 per year on each $1,000 assessed valuation. 

owns and cities must provide for proper treatment of the street 
trees and those in parks and on public grounds. After the amounts 
fixed by law are expended, financial aid may be supplied by the 
State. The gypsy moth at present (1937) occurs in every town in 
the State east of Berkshire County. It has increased in abundance 
over much of the infested area during the last 3 years, especially in 
the towns directly east of the Connecticut River. The area infested 
by the brown-tail moth is a little over 4,500 square miles. 


36 CIRCULAR 464, U. S. DEPARTMENT OF AGRICULTURE 


RHODE ISLAND 


In Rhode Island the commissioner of agriculture has charge of the 
moth work, which is done under the supervision of the State ento- 
mologist. The gypsy moth occurs in all towns in the State. Since 
1931 the infestation has increased rapidly, and in 1934 much defolia- 
tion was noted. The conditions approximate those which the State 
of Massachusetts has encountered for many years. No brown-tail 
moth infestation had been found for a number of years prior to 1936, 
when a few webs were found in two towns in the eastern part of the 


State. 
CONNECTICUT 


In Connecticut the work is in charge of the State entomologist. 
The brown-tail moth has not been found in this State for several 
years. The area infested by the gypsy moth is now about 3,000 
square miles. During the past 3 years the infestation has increased 
noticeably in some localities in the eastern part of the State. 


NEW YORK 


In New York State the work is supervised by the Department of 
Conservation, which is cooperating with the Federal Bureau of Ento- 
mology and Plant Quarantine in the New York section of the barrier 
zone. <A few scattered infestations in eastern New York and on Long 
Island, including New York City, and a newly discovered infestation 
at Shawangunk, west of the barrier zone, are being treated by the 
State. During the past 2 years a special survey of the entire State 
has been made, but no additional infestations have been found. 


NEW JERSEY 


In New Jersey the State work is under the control of the State 
Department of Agriculture. The funds appropriated have been 
used in conjunction with Federal funds, and the work is supervised 
by the Bureau of Entomology and Plant Quarantine. No infesta- 
tion has been found for 2 years. 


PENNSYLVANIA 


In Pennsylvania the work is carried on under the direct supervision 
of the Bureau of Entomology and Plant Quarantine of the United 
States Department of Agriculture, with the cooperation of the Penn- 
sylvania Department of Agriculture and Department of Forests and 
Waters. Progress has been made in the eradication work conducted 
in this State. 

DOMINION OF CANADA 


Scouting for the gypsy moth and the brown-tail moth in Canada is 
conducted by the Division of Foreign Pests Suppression of the office 
of the Government entomologist. Cooperation with the provincial 
governments of New Brunswick, Nova Scotia, and Quebec has been 
maintained. The gypsy moth colony found at Henrysburg, Quebec, 
has been exterminated through the efforts of the Dominion and pro- 
vincial officials. Late in 1936 a few gypsy moth egg clusters were 
found in and around St. Stephen, New Brunswick, and extensive 
scouting and clean-up work has been done. 


GYPSY AND BROWN-TAIL MOTHS AND THEIR CONTROL 37 


UNITED STATES DEPARTMENT OF AGRICULTURE 


The gypsy moth project has been conducted by the Bureau of 
Entomology for many years. On July 1, 1928, the quarantine and 
control work was transferred to the Plant Quarantine and Control 
Administration, which later became the Bureau of Plant Quarantine, 
and the research work was assigned to the Division of Forest Insects 
of the Bureau of Entomology. On January 1, 1934, the quarantine 
work was transferred to another section of the Bureau, and on July 1, 
1934, the two bureaus became the Bureau of Entomology and Plant 
Quarantine. 

For a number of years it was believed to be impossible to restrict 
the spread of the brown-tail moth on account of the heavy migration 
of the adults. Owing, however, to the effectiveness of parasites 
introduced by the Bureau, to winter conditions unfavorable to the 
insect, and in some sections to the effectiveness of a fungus disease 
that attacks the caterpillars, in addition to a large amount of hand 
suppression work, not only was spread prevented but marked reduc- 
tion in the infested area recorded. 

A large amount of experimental work has been done to devise 
better methods of controlling these insects. Natural enemies have 
been introduced from Europe, northern Africa, and Japan and colo- 
nized throughout most of the infested area. Specialists have spent 
considerable time studying the insects in their native homes and col- 
lecting parasites for shipment to this country. 

The entire area known to be infested by either of these insects is 
under quarantine, and shipments of nursery stock, lumber, cordwood, 
and other forest products, including Christmas trees and greenery 
and stone and quarry products, are not permitted to leave the terri- 
tory unless they are inspected and accompanied by a certificate 
stating that they are free from infestation. 

The results of the work in the barrier zone in preventing spread 
and the cleaning up of isolated infestations have justified the efforts 
expended and have protected the United States at large from infesta- 
tions and resultant damage from these pests. 


COOPERATIVE WORK 


Since the gypsy moth and brown-tail moth work was begun by the 
Bureau of Entomology, more or less work has been done in coopera- 
tion with the States concerned. The general plan of field work in 
New England is for the States to manage the clean-up east of the 
barrier zone while the Federal forces work in the zone and cooperate 
in making the entire work effective. 

In New York the work in the barrier zone is handled in cooperation 
with the State authorities. 

In New Jersey and Pennsylvania close cooperation has been main- 
tained with the State departments. 

During the past 3 years the work has been extended and intensified 
through cooperation with the N. R. A., W. P. A., and C. C. C., and 
recently cooperation has been established with the Northeastern 
Forest Experiment Station of the Forest Service for the purpose of 
utilizing the latest silvicultural methods in connection with the control 
work in forests. 


ORGANIZATION OF THE UNITED STATES DEPARTMENT OF AGRICULTURE 
WHEN THIS PUBLICATION WAS LAST PRINTED 


Secretary of Agniculiine=== sae. | Henry A. WALLACE. { 
Under Secretary = ae ee Pee M. L. Wiuson. 

Assisiant SeChela ites 455 ee oe eg Harry L. Brown. 

Director of Hatension, Work a= 2. ae ae C. W. WARBURTON. 

Director ofpliinance: 22 a ae W. A. Jump. 

Director, of Informations =.= see es M. 8S. EISENHOWER. 
Darectorsofeeersonnela =o == Cee W. W. STOCKBERGER. 

Direction OfeiteSear Chia see eee © eee James T. JARDINE. 

SolieuOp eo eee: - eee Mastin G. WHITE. 

Agriculiural Adjustment Administration ____- H. R. Totuny, Administrator. 
Bureau of Agricultural Economics________-_- A. G. Buack, Chief. 
Bureau of Agricultural Engineering________- S. H. McCrory, Chief. 

BUrean Of; ANUMGLLngUstin) =e eee JoHn R. MouueEr, Chief. 

Bureau of Biological Survey_——-.__--_=--__- Ira N. GABRIELSON, Chief. 
Bureau of Chemistry and Soils____________- Henry G. Kniaut, Chief. 
Commodity Exchange Administration________ J. W. T. Duveu, Chief. 

Bureau of, Dainyslndusicy 2 oe O. E. ReeEp, Chief. 

Bureau of Entomology and Plant Quarantine. Liz A. Strrone, Chief. 

Office of Experiment Stations______-_-__---- JAMES T. JARDINE, Chief. 
Farmisecumty Administration. =— 2 =e =e W. W. ALEXANDER, Administrator. 
Food and Drug Administration_____--_---_-~- WatrerR G. CAMPBELL, Chief. 
THiOnestySerutce 2 Nas Nn eee ee! 82 ee FERDINAND A. Siucox, Chief. 
Bureau Of MAomeseConomicss2 = se ee LovutsE STANLEY, Chief. 

YA OG ah 0 se ore eae ese at er ee a So 28s CLARIBEL R. Barnett, Librarian. 
BUneaw Of lant ANdUSiiy = 2 =a eee EK. C. AucHTER, Chief. 

Bureau, eublic oad seen! ee = eee Tuomas H. MacDona.tp, Chief. 
Soil Conservation Service___-_ ~~ exit: eee H. H. Bennett, Chief. 

Weather Buncat= 525 es sss 1 ee Wiuuis R. Greae, Chief. 


This circular is a contribution from 


Bureau of Entomology and Plant Quarantine. LeE A. Srrone, Chief. 
Division of Gypsy Moth and Brown-Tail A. F. Buresss, Principal Entomol- 


Moth Control. ogist, in charge. 
Division of Forest Insect Investigations__ F. C. CRAIGHEAD, Principal En- 
tomologist, in charge. ) 
38 qi 


U.S. GOVERNMENT PRINTING OFFICE: 1938 


For sale by the Superintendent of Documents, Washington, D.C. - - - - Price 10 cents