bid Je EASTERN FOREST PESEGIS - U.S. DEPARTMENT OF AGRICULTUREe FOREST SERVICE MISCELLANEOUS PUBLICATION NO. 1175 i / +? & ee 4 Tet) A a! Historic, archived document Do not assume content reflects current scientific knowledge, policies, or practices. 4D-B Reokplate 2063) NATIONAL qOomMHOPHHPmdH4 LIBRARY DC BRANCH WHITEFORD L. BAKER PRINCIPAL ENTOMOLOGIST, RETIRED FOREST INSECT RESEARCH BRANCH FOREST INSECT AND DISEASE RESEARCH DIVISION FOREST SERVICE EASTERN oe INSECTS U.S. DEPARTMENT OF AGRICULTUREe FOREST SERVICE MISCELLANEOUS PUBLICATION NO. 1175 FEBRUARY 1972 THIS PUBLICATION SUPERSEDES ‘INSECT ENEMIES OF THE EASTERN FORESTS,"’ MISCELLANEOUS PUBLICATION NO. 657 For sale by the Superintendent of Documents, U.S. Government Printing Office Washington, D.C. 20402—Price $5 ACKNOWLEDGMENTS The author gratefully acknowledges the invaluable assistance of many of his colleagues in the Forest Insect Branch of the USDA Forest Service in the preparation of this publication. He is also greatly indebted to the following individuals for their helpful reviews of different sections of it: Dr. A. E. Brower, Maine Forest Service; Dr. R. L. Giese, Purdue University; Dr. D. M. Benjamin, University of Wisconsin; Dr. R. F. Anderson, Duke University; Dr. Jack L. Krall, State University of New York College of Forestry at Syracuse; Dr. R. T. Franklin, University of Georgia; Dr. C. E. Atwood, University of Toronto, Canada; Dr. J. A. Slater, University of Connecticut; Dr. John A. Davidson, Dr. T. L. Bissell, and Dr. F. E. Wood, University of Maryland; Dr. D. L. Collins and Dr J. A. Wilcox, New York State Museum and Science Service, Albany, New York. Finally, he wishes to make acknowledgement to the Connecticut Agricultural Experi- ment Station, Illinois Natural History Survey, and Duke School of Forestry for the loan of many photographs for illustrations. LIBRARY OF CONGRESS CATALOG NO. 76—607316 | CONTENTS HAA ETEO GLUNC EL O10 arene ear nee et UL ee ee ean tuicss erst Imseetswand elated Oreanisms 2. ee. mee @laccs#Hexanoda—=INSsectsy ee ee re GlacscseGrustacea——WiOOdNCe ee ee ! Class Diplopoda——Miallipedes: 23.) ded , Class-Chilopoda=—Centipedes)) 24.72 isso Sine 3 Class Arachnida—Spiders, mites, ticks, scorpions, ete. ....... Order vwAraneida=—Splders)..- 2 eee & Order-Acarina—-Mites-and! ticks 25. 3.2.2 ne Order ScorpionideAa—ScorpioMs oie... ene nee: Order Pseudoscorpoinidae—F alse scorpions ......................... Order Phalangida—Daddy-long-legs 0... ae Phylum? Mollusea=_Ship worms =< 3.60. ee Honest MinSeCi sin tise Mee. Rete We me ed Oe ern ee | ? Borest insect causedlosses 2 ee py Cae MOrest IMSeCClISUEVEYS. |. ee oe Ed ile | Forest insect control... APN eget ECL ee aw Ne oa oy atetsely INaturaleconerolin Scrat Fi tte Seed Bee as AMC CMC OMER Ole Met anes eee rs Ns ee Sivacultumalscontrol et ee uy Physical and mechanical methods of control... Reoulatory control 20s: ee | Biolosicalecontrolo =e ee Cy, Se a ee Chemicalecontroles 396 ee ope Other approaches to control =e. ) teerated=controle as hee hs ae Practical keys to the orders, families, and genera of forest Imsectssoasedv on types of Injury 72 2 RAMA ya VISIONS Ole KOY. ie ee Se : important orders of forest insects. 3... Order Anoplura—sSuckineg lice 20d Order Mallophaga—Chewing Vice 00... icc Order Siphonoptera—Fleas ea, Order rhysanura—bristietails Order Collembola—Sprinetails ©... ecccccccecceenseueee ee Ordercchysanoptera——Eehrips (0 Se ee Order Psocoptera—Book lice and psocids ......................... aie Ordersneuroptera i 6.2 re OO GS Order Ephemeroptera—Mayflies 00... ccc. nae ace Order Plecoptera—Stonefhies oi... ccsssesesssssceeeee Nes Order Odonata—Dragonflies and damselflies ...................... 7 Order-lsoptera—— Termites 2 ee Order Orthoptera—Cockroaches, grasshoppers and allies Order Hemiptera—True bugs i ceccccccccccccecsessssseeneeee | Order Homoptera—Aphids, scales, mealybugs, etc. ._. Order Coleoptera—Beetles .cscccecccetecsessesecssscstssstsrtestieneace Order Lepidoptera—Butterflies, moths, skippers... OrdernoDiptera=—Mlies ota ee : OndersryMeNOPCerar. oe ee cone eae nies imsectseand. Tree: Diseases: 5 nc sea cee HP OR A LUC sO AUCC her ah ed ie eee eeu NN Os ei Mie ye indexatosiisects: by- Host: Plants... oe mMsecteinGdexis sen. wer We Aonsierh Sips say i nae OMAP PWNNH INTRODUCTION Interest in the protection of the Nation’s forests from insects has grown considerably in recent years. This has come about largely because of increased awareness of the destructive capaci- ties of insects and the heavy toll they take of our dwindling sup- plies of commercial timber. Interest has been further heightened by the fact that more and more people have come to realize that much of the damage caused by insects need not necessarily hap- pen—that given adequate knowledge of the habits and behavior of injurious insects, it should be possible to either prevent or reduce most of it. Increased interest in the protection of our forests from insect- caused losses has resulted in increased research to develop cheaper, safer, and more effective methods of control. Much prog- ress has been made in recent years, especially since World War II, in studies of the biology and ecology of many important species, leading to new or improved control methods. Much new informa- tion has also been obtained on many other species of potential pests. The results of these investigations appear in many publica- tions, some of limited circulation and more or less inaccessible to the general public. It is the purpose of this publication, which supersedes U.S. Department of Agriculture Miscellaneous Publication 657 (167),! to review the literature on eastern forest insects which has been published since 1940, the cutoff date for nearly all of the informa- tion contained in M.P. 657. Insects discussed are those which occur either entirely in portions of the United States lying east of the 100th meridian or which occur in both the eastern and western halves of the country.2 The major portion of the publication is devoted to the identification, distribution, host relationships, and life histories of insects occurring in eastern forests. This publication includes not only new information obtained since 1940, but also much of the still pertinent information ob- tained earlier and reported in M.P. 657. The common names of insects preceding the scientific names are approved (85); the common names following the scientific names have not been approved. ‘Italic numbers in parentheses refer to Literature Cited, p. 503. 2A companion volume covering western forest insects is also available. if INSECTS AND RELATED ORGANISMS Insects belong to the phylum Arthropoda, one of the major groups of the animal kingdom. In the hierarchy of animal phyla it stands near the top, far removed from the simplest, one-celled organisms in the phylum Protozoa. The phylum also contains many other well-known forms such as crawfish, shrimp, milli- pedes, centipedes, spiders, and mites. Members of the phylum are distinguished by having the body composed of a series of more or less similar rings or segments joined together and in having some of these segments bear jointed legs. In certain forms, the segmen- tations of the body may be obscure and not evident from cursory examination. In most instances this is due to a secondary modifi- cation of form, a result of adaptation to special modes of life (152). Insects comprise the most abundant and important group of arthropods, but many other members of the phylum are also com- mon and often important. Many of the latter are harmful, either to trees and other vegetation or to wildlife and man. Many are so small they are seldom seen, although enormously abundant; others, larger ones, are easily seen. Some of the latter are also many-legged and wormlike and bear little or no resemblance to insects; others are often mistakenly identified as insects. The arthropods discussed here belong to the Classes Hexapoda (In- sects) ; Crustacea (crawfish, shrimp, crabs) ; Diplopoda (milli- pedes) ; Chilopoda (centipedes) ; and Arachnida (spiders, mites, and scorpions). Mention is also made of shipworms which belong to the phylum Mollusca. Class HEXAPODA Insects An insect is an air-breathing arthropod with a distinct head, thorax, and abdomen. It has one pair of antennae, three pairs of legs, and usually one or two pairs of wings in the adult state. The majority of species are terrestrial and are found in an almost endless variety of microhabitats on the land. Many other species spend parts of their lives in water. The majority of insects hatch into wormlike larvae which grow by periodically shedding the outer skin, finally transforming into an inactive pupal stage from which the adult emerges. This sort of development is known as complete metamorphosis. The imma- ture stages of others are very similar in appearance to the adults and are known as nymphs. Members of the latter group are said to have simple or incomplete metamorphosis. Approximately 900,000 species of insects have been described. This represents 80 to 90 percent of all the known kinds of animals. The actual number of insect species, however, is believed to be much larger and to run into the millions (628). Countless numbers feed on plants of all kinds, attacking all parts from the roots in the ground to the flowers and seeds in the tops. Thousands of others feed on other insects or other animals, including man. 2 Fortunately for man and his interests, the majority of insects are either innocuous or beneficial. The remainder, unfortunately, include some of his most important enemies—not only do they feed on him and other animals and often transmit deadly or debil- itating disease organisms, but they also devour his crops and decimate his forests. Because of their abundance, their fantastic reproductive powers, and their remarkable capacities for adapting to changing conditions, they present a continuing challenge to man in his efforts to limit their numbers to tolerable levels. Several general references to insects are available for consulta- tion: Leonard (454), Brimley (101), Essig (232), Comstock (152), Imms (391), Matheson (510), Brues, Melander and Car- penter (114), Ross (624), and Borror and DeLong (90). Class CRUSTACEA Wood Lice Crustaceans are aquatic organisms, mostly marine. They occur throughout the world, and several species attack the wood of most species of trees when they are placed in salt water. The surface of heavily infested wood may be so completely honey-combed that it resembles a sponge. When this damaged wood is removed by wave action, deeper layers of uninfested wood are exposed. They, in turn, are attacked and the process of destruction is repeated. Continuous infestation may result in the loss of the outer 1 inch of wood per year, Infested pilings often have an hour-glass shape as a result of the erosion of infested portions between low- and high-tide marks. Heaviest attacks occur between mean tide level and low tide, but serious damage sometimes occurs at water depths of 40 to 70 feet or more (9). Limnoria ignorum (Rathke), commonly called the wood louse, is one of the most destructive species. It has seven pairs of legs, sharp claws for holding onto the wood, and a pair of toothed mandibles for boring into it. Full-grown specimens are 3 to 6 mm. long and resemble sowbugs. This species occurs in clear salt water only and spreads slowly, usually in infested driftwood. Members of the genus Sphaeroma are beetle-like in appearance and are up to 12 mm. long. They occur in both salt and fresh water and may be found in such places as crevices, empty barnacle Shells, and in burrows made by molluscan borers. They also dam- age pilings, usually between tide marks but sometimes all the way down to the mud line. Damage is usually less severe than that caused by Limnoria, however, even though the burrows are some- what wider and penetrate to depths of 3 or 4 inches. The genus Chelura contains the largest of the wood-boring crustaceans. None of these initiate attacks on wood, but they do invade and enlarge burrows made by shipworms. C. terebrans is a well-known species along the Atlantic Coast. Methods for protecting timbers from wood-boring crustaceans are the same as those used against molluscan borers. Class DIPLOPODA Millipedes Millipedes are slow-moving, elongate, worm-like organisms, usually with 30 or more pairs of legs. They are usually found under bark, stones, old boards, or in damp rubbish. Their food consists of decaying vegetable matter. The adult has two body regions: (1) the head, which bears a pair of short antennae, usually seven- segmented; and (2) the rest of the body, which consists of a large number of similar cylindrical segments. The first four or five body segments are not fused and each bears a single pair of legs. The remaining segments are fused into ring-like joints, each of which bears two pairs of legs. Spirobolus marginatus Say, one of the larger species, is dark brown, narrowly ringed with red, and about 100 mm. long. Millipedes sometimes become very abundant. At such times they may invade camps, old buildings, and residences in large numbers. Many species emit a fluid with a cyanide-like odor through open- ings along the sides of the body. Removal of moisture and of accumulations of vegetable matter from infested areas should be helpful in their control. Williams and Hefner (768) discuss many of the species occurring in eastern United States. Class CHILOPODA Centipedes Centipedes are worm-like animals, with elongate, flattened seg- mented bodies. They have 15 or more pairs of strong legs, one pair per segment. The antennae have 14 or more segments, and the appendages of the first body segment behind the head are clawlike and function as poison jaws. The last two pairs of legs at the posterior of the body are directed backward. Centipedes are usu- ally found under bark, in rotting logs, or under stones or boards. They are swift runners and feed on various small animals such as snails, insects, and spiders. All species possess poison jaws with which to paralyze their prey. They will also bite man. The largest centipedes belong to the family Scolopendridae, some of which may be more than one foot long. The largest species found in the United States, however, is only 125 mm. long. Mem- bers of this family are also the most venomous of all centipedes. The bite of the largest ones are not only quite painful but also are occasionally fatal (90). The larger and more dangerous species are southern in distribution; those occurring in the North are usually too small to be harmful to man. Bailey (16) discussed the centipedes of New York. The removal of debris used as hiding places is helpful in centi- pede control. 4 Class ARACHNIDA Spiders, ticks, mites, scorpions, etc. The class Arachnida is a large group of air-breathing arthro- pods in which the body is usually comprised of two regions: (1) the cephalothorax, and (2) the abdomen. They generally have six pairs of appendages (the chelicera, pedialps, and four pairs of legs) but are without antennae. Order ARANEIDA Spiders Spiders are found almost everywhere, both indoors and out- doors, and are so familiar as to need no description (153). Ob- jects of fear and revulsion to many people, their presence in large numbers in and around places of habitation or other areas fre- quented by people, is often considered intolerable. Fortunately, the majority of species pose no hazard to man, even though all have venom glands. Actually, they generally are more beneficial than harmful since their food consists mainly of insects and other small organisms. A few species, however, are poisonous to man and should be avoided (14). The black widow spider, Latrodectus mactans (Fab.), is prob- ably the most poisonous spider in the United States. Its bite is described as being extremely painful throughout all the muscles of the body, and it occasionally results in death. The black widow occurs from southern Canada southward through the United States, Mexico, Central America, and deep into South America. In the Eastern States it is most common in the South, but also occurs as far north as Maine. Black widows are usually found in such places as garages, sheds, outdoor toilets, under rocks and old boards, and in hollow logs or animal burrows. The female is shining jet black and bears an hour glass-like red mark on the underside of the abdomen. The body of a full-grown specimen is about 12 mm. long exclusive of the long legs. Males are much smaller and are seldom seen. Loxosceles reclusa Gertsch and Muliak, the brown recluse spider, is also quite poisonous to man, its bite producing a condition known as “North American Loxoscelism.” Adults are about 9 mm. long, have long legs, and vary from light fawn to dark brown. A distinguishing mark is a dark fiddle-shaped band on the anterior portion of the carapace, which narrows to a thin center line and extends almost to the abdomen. It is only within recent years that this species has been recognized as poisonous to man. It has been recorded from several Midwestern and Southern States—Okla- homa, Arkansas, Kansas, Texas, Louisiana, Mississippi, Alabama, and Tennessee. It may be found in almost any situation where protection, food, and dryness are adequate, but it probably occurs most commonly inside buildings. Its web is medium-sized and irregular, with a maze of threads extending in all directions with- out definite pattern or plan (354). It is usually impractical or impossible to eliminate spiders com- pletely. Populations can be reduced, however, by the removal of favorite breeding places. Order ACARINA Mites and ticks The order Acarina contains a large number of important pests of plants and man and animals. The majority are extremely small and seldom seen; others, such as the ticks, are large enough to be seen with the naked eye. Members of this order differ from other Arachinids in having the mouth parts more or less distinctly set off from the rest of the body on a false head and in never having the body so divided that a distinct cephalothorax and abdomen are clearly recognizable (18). MITES.—Numerous species of mites feed on and weaken or kill a wide variety of valuable plants, including trees. Many others attack man and various other forms of animal life, often causing extreme irritation, and sometimes illness and death. A consider- able number are either parasitic or predaceous on various species of destructive insects and harmful species of their own kind. Many others feed on dead materials of all kinds on the forest floor. The family Tetranychidae (480, 281) contains a large number of species commonly known as spider mites, many of which are important pests of trees and shrubs. These mites vary in color from yellowish, greenish, orangish, and reddish to red, and all are less than 1 mm. long. Infested leaf surfaces are usually covered with a fine netting of silk and spotted with tiny spherical eggs or broken egg shells. Heavily infested foliage may be dis- colored, disfigured, or killed. The spruce spider mite, Oligonychus ununguis (Jacobi), feeds on a number of conifers, especially spruce, cedar, and some of the pines and is widely distributed in the United States. Infested trees may become brownish-gray and appear unhealthy, or they may be completely defoliated. Outbreaks over large forested areas have been recorded. Periods of drought appear to be most favor- able for pepulation build-ups. Outbreaks have also occurred fol- lowing widespread spraying with DDT (403). Young nursery stock and recently planted trees are especially subject to serious injury. Oligonychus milleri (McG.) feeds on pines throughout the South and north to Pennsylvania and the Lake States. Out- breaks covering millions of acres have been recorded during recent years from North Carolina to Florida, in northern Louisi- ana and southern Arkansas, and in Mississippi and Texas. Young, Spee sown, even-aged stands appear to be susceptible to severe attack. Other important species in the genus Oligonychus include: (1) O. bicolor (Banks)—long recognized as a pest of oaks, especially shade oaks and sometimes injures beech; (2) the southern red mite, O. ilicis (McG.)—damages azalea and camellia; (8) O. aceris (Shimer)—sometimes a serious pest of maples; (4) O. letch- wortht Reeves—occasionally seriously injures hop hornbeam; (5) O. newcomert McG.—often seriously infests shadbush; (6) O. cunliffei P. & B.—feeds on longleaf pine in Florida; (7) O. bou- dreauxt P. & B.—feeds on cypress in the South; and (8) O. Bans P. & B.—feeds on oaks from Washington, D. C. to North arolina. 6 The carmine spider mite, Tetranychus cinnabarinus (Bois.), is a common and widely distributed species that feeds on a great many species of plants, trees, and ornamentals. Several genera- tions are produced during the summer months, often giving rise to tremendous populations. Heavily infested plants may be en- tirely defoliated, especially during hot, dry weather. T. ellipticus Garm. is often abundant on honey locust in the Midwest. T. homorus P. & B. feeds on hickory and ash in North Carolina; T. magnoliae Boud. occurs on magnolia and yellow poplar in Louisiana; the four-spotted spider mite, 7. canadensis (McG.), feeds on elm, basswood, horse chestnut, osage orange, and poplar throughout eastern United States and southern Canada; and the Schoene spider mite, 7. schoenet McG., infests elm and black locust throughout eastern United States. The genus Hotetranychus also contains a number of common and frequently important species. E. populi (Koch) and E. wel- dont (Ewing) are found on poplars and willows; E. hicoriae (McG.) occurs on pecan, hickory, horse chestnut, and various oaks; and E.. matthyssei Reeves attacks elm in New York. Heavy infestations may cause severe browning and cupping of the under- sides of leaves. EF. querci Reeves has caused severe browning of pin oaks in New York. Platytetranychus multidigituli (Ewing) feeds on the leaves of honey locust, causing them to turn yellow, and P. thujae (McG.) attacks arborvitae, juniper, and cypress. Eurytetranychus buxi (Garman) is a serious pest of European boxwood. The leaves of infested plants become bronzed, then wither and sometimes fall prematurely. The family Eriophyidae contains a number of tree-infesting species (414). Many produce open pouch-like or blister-like galls on the twigs and leaves of their hosts. Some cause a rusting of infested leaves, and certain others feed on buds. A few of the more common and important tree-infesting species are discussed here. The maple bladder-gall mite, Vasates quadripedes (Shimer), is a common species. It ranges in length from about 1/20 to 1/5 of a mm. and feeds on the under-surface of silver maple leaves, caus- ing the formation of pouch-like or bladder-like galls up to 3 mm. in diameter (fig. 1). At first, these galls are light colored or yellowish green. Later, they are reddish to almost black and look for all the world like miniature green peppers standing on stalks above the leaf surface. Heavily infested leaves are often distorted. The related species, V. aceris-crummena Riley, produces slender, fusiform, or spindle-shaped galls about 5 mm. long on the upper surfaces of silver and sugar maple leaves. A few of the other eriophyids infesting trees and some of their hosts are as follows: Eriophyes fraxiniflora Felt—feeds in the staminate flowers of ash. Infested clusters become deformed and remain on the tree as green masses until fall. The pear leaf blister mite, EZ. pyri (Pagen)—an introduced pest of pear and apple, has also been recorded on mountain ash and shadbush. It is sometimes abundant enough on mountain ash to cause noticeable injury. E. parapopuli (K.)—stunts the growth of poplar by producing woody galls around the buds. EH. caulis Keifer—causes large, de- forming, hairy growths on the petioles of black walnut leaves. The 7 F-506694 FIGURE 1.—Galls of the maple bladder-gall mite, Vasates quad- ripedes, on leaf of maple. pine bud mite, Phytoptus pini Nal.—causes the yellowing and dropping of pine needles. Aceria phloceoptes (Nal.)—deforms fruit spurs and produces woody galls on plum. Nalepella tsugi- foliae Keifer—has been reported damaging hemlock in nurseries in New York. Trisetaceus cupressi (K.)—attacks southern red cedars, causing distortion and deformation of young trees. Mites of the family Sarcoptidae are skin parasites of warm blooded animals. The itch mite, Sarcoptes scabet (DeG.), is a well- known species. It attacks man and causes severe itching as it bur- rows into the skin. The family Trombiculidae contains the notorious red bugs or chiggers. The common chigger in eastern United States is the first instar larva of the species, Eutrombicula alfreddugesi (Ouder- mans). In its later stages, it feeds on other insects, snakes, birds, lizards, and rodents. When it attaches itself to the skin of man and insects, it inserts its mouth parts to feed, causing intense itching and sores. Heavy attacks may cause fever, and secondary infections may occur. Chiggers are often abundant in the forests of the Central and Southern States and along the Atlantic Sea- board north to New Jersey. Many other species of mites occur in association with bark beetles,? and some are known to be parasitic. So far, very little information is available on their effectiveness in natural con- trol of the beetles. In some instances, it may be substantial. TICKS.—Ticks are all parasitic, chiefly on mammals, birds and reptiles. All American species have a number of features in com- mon, such as large size, a piercing hypostome with recurved teeth, and chelicera with lateral teeth on the movable digits. Some ticks are mostly covered by a hard dorsal plate called the scutum; in others this hard plate is absent. * Unpublished manuscript by J. C. Moser and L. M. Roton. Mites asso- ciated with southern pine bark beetles in Allen Parish, La. 8 The American dog tick, Dermacentor variabilis (Say), occurs throughout eastern United States, but is most abundant in coastal areas and in the Mississippi River Valley. The larvae and nymphs feed largely on rodents; the adults feed on dogs, horses, hogs, cattle, and many species of wild animals. Man also may be bitten, but he is not a preferred host (477). Unfed adults are brown, variously marked with white, and about 5 mm. long. Engorged females are bluish gray and sometimes reach a length of 12 mm. Females lay eggs in various places but never on the host; the young seek out their host after hatching. Heaviest infestations are usually found on vegetation along game trails, paths, and roadways. Adults are most abundant during spring and early summer in the North. After August they are usually very scarce. In the South, they occur throughout the year. This species trans- mits Rocky Mountain spotted fever and tularemia, both serious diseases of man. It also transmits anaplamosis, a disease of cattle. The black-legged tick, Ixodes scapularis Say, occurs along the Atlantic Coast. The larvae and nymphs feed on rodents and rep- tiles, and the adults feed on deer, cattle, sheep, dogs, and other large animals. People are also bitten. This species has long mouth parts and inflicts a very painful bite. Infestations are usually found along game trails, paths, and roadways where the ticks wait on vegetation for people or animals to come by. Adults are most prevalent during fall and early winter. This species trans- mits anaplamosis to cattle and piroplasmosis to dogs (726). Order SCORPIONIDEA Scorpions Scorpions are fairly common in eastern United States, espe- cially in the South. However, because they are active only at night and usually remain hidden during the day, they are seldom seen. Indoors, they usually hide in such places as closets, attics, folded blankets, shoes, and papers. Scorpions vary considerably in size, ranging from about 14 to 714 inches in length. The abdomen is divided into a large anterior portion of seven segments and a long, narrow tail-like posterior portion of five segments. The latter ends in a vesicle which bears a poisonous sting. When a scorpion runs, it holds it large claw-like pedialps forward, and the posterior end, bearing the sting, is usually curved upward. Scorpions are capable of inflicting painful and sometimes fatal stings. Very young and very old people appear to be the most vulnerable. Scorpions’ food consists of a wide variety of animal life including other scorpions, spiders, flies, beetles, cockroaches, grasshoppers, crickets, termites, centipedes, and earthworms. A common species in many parts of eastern United States is Centu- roides vittatus (Say), the so-called striped scorpion. This is a fairly small species, being only about 58 to 60 mm. long. Its sting results in a sharp pain which usually lasts about 15 to 20 minutes. Stings inflicted from late March to early May, however, may re- main painful for several hours (15). Scorpions may be trapped during dry seasons by spreading wet burlap bags on the ground in infested areas. Order PSEUDOSCORPIONIDAE False scorpions False scorpions bear a striking resemblance to their larger rel- atives, the true scorpions, but differ in having wider, shorter abdomens and in not having terminal poison glands. They are seldom more than 5 mm. long. Pseudoscorpions may be found in a wide variety of places—in soil cover, under bark, under the wings of beetles, on the bodies of birds and in their nests, in buildings, and in chicken houses and beehives. Their food consists of mites, ants, and various other insects. They have also been reported as biting man but without inflicting appreciable injury. One species, Chelifer cancroides (Linn.), is frequently found in association with man. Adults are about 2.5 to 3 mm. long (860). Order PHALANGIDA Daddy-long-legs Daddy-long-legs are somewhat similar in appearance to spiders but differ in having small, compact, nearly globular bodies and extremely long legs. They also are rather slow in movement, usu- ally appearing to totter about, and they occur commonly in most parts of the United States. Their food consists chiefly of plant juices or dead insects. Some apparently feed on living insects. When crushed, their bodies give off a disagreeable odor. None are harmful to man. Phylum MOLLUSCA Shipworms Wood submerged in salt water is attacked by several species of bivalve mollusks, commonly known as shipworms. Damage to pilings is often severe, especially along the Gulf Coast and along the Atlantic Coast south of the Chesapeake Bay. Boats are also damaged occasionally. These organisms are discussed briefly be- cause the damage they cause is similar to and often confused with that caused by wood-boring insects. The genera Teredo and Bankia contain the so-called shipworms. Their bodies are long and soft. They are armed with small, chisel- like shells at the anterior end and there are two siphon tubes at the posterior end. They are free-swimmers in the early larval stage, and during this period the body is protected by a bivalve shell. Free-swimming larvae seek out wood and attach themselves to it near the mud line. Then they bore into the wood leaving very small openings to the outside. Once inside they develop rapidly, enlarging and lengthening their tunnels as they grow. During this period the shell, which is no longer needed for protection, is used as a boring tool. As they develop, shipworms secrete a calcareous material with which they line their tunnels. The openings made by the young larvae are never enlarged. As a result, the only external signs of infestation of a piece of heavily damaged wood are tiny holes in its surface. 10 Because a single piling may contain several thousand ship- worms, it may be literally honeycombed (fig. 2). In such situa- tions, tunnels may be no more than 14, of an inch in diameter and only a few inches long. Under the most favorable conditions, how- ever, the tunnels may reach a diameter of 1 inch and a length of 4 feet. The genus Martesia also contains a number of destructive species. They differ from the shipworms in being clam-like. The young are also free-swimmers and seek out and attack submerged wood, making small, inconspicuous entrance holes. Once inside the wood, they grow until they are about 25 mm. in diameter and 60 mm. long. As they grow, they enlarge their cavities to accomo- date their bodies. Members of this genus are found along the shores of the Gulf of Mexico. Damage to pilings by shipworms can be prevented by impreg- nation of the wood with a suitable preservative. Coal tar 1 creosote is recommended for treating waterfront timbers of Douglas-fir and southern pine. Copper naphthenate is usually used for the protection of wood in boats. Coatings of paint and metal are also effective as long as they remain intact. F-519930 FIGURE 2.—Cross-section of a piece of timber riddled with tunnels made by a molluscan shipworm of the genus Bankza. 11 FOREST INSECTS Insects are by far the most numerous of all the forms of animal life inhabiting the forest. They are remarkably well adapted to their surroundings and occupy an incredibly wide variety of eco- logical niches. They serve many functions in the economy of the forest and are as essential a part of the complex association of organisms comprising it as are the trees themselves (412). While the majority of species are either beneficial or innocuous, many species are exceedingly injurious. Beneficial forest insects are represented by a great many species, some of which are enormously abundant. Some feed on forest debris and aid in its deterioration; others feed on organic matter in the duff and soil and contribute to improvements in soil fertility. Some contribute to stand improvement by attacking and killing decadent, diseased, or overmature trees and making way for younger growing stock. Many others are parasites or preda- tors of destructive species of insects. Harmful forest insects are those that are responsible for eco- nomic loss. They include (1) species that damage or destroy the flowers and seeds of trees and which are particularly important pests in seed orchards and seed production areas; (2) species that stunt, deform, or kill young trees by damaging or destroying the terminals, laterals, or roots of reproduction and in plantations; (3) species that cause loss of vitality, growth reduction, and often the death of trees by eating the foliage; and (4) species that feed under the bark or in the wood of living trees and girdle and kill them or riddle them with tunnels are important pests in the forest. These are not all: Numerous others that bore into and damage or destroy green logs, storm-felled timber, green-sawn and seasoned lumber, rustic construction, poles, posts, crossties, mine props, and all manner of finished products from flooring to furniture are highly destructive. Most of our forest insects are native to the continent and are usually distributed throughout the ranges of their hosts. Some are destructive at normal population levels, but the majority normally occur in such low numbers as to be of little or no consequence. A few of the latter, however, are capable of great and rapid in- creases in numbers when favorable environmental conditions prevail. Eastern forests are also inhabited by many species of intro- duced insects, a few of which are widely distributed and extremely destructive. These include the gypsy moth, European pine shoot moth, balsam woolly aphid, European pine sawfly, and the smaller European elm bark beetle. Many species of natural enemies of several introduced pests have also been imported and established in eastern forests. Conditions conducive to forest insect outbreaks are only partly understood. It appears though that outbreaks are most likely to occur (1) in pure stands rather than in stands of mixed composi- tion, (2) in overmature rather than immature stands, and (3) in 12 ner | | plantations rather than natural stands. They may also develop in stands weakened or decimated by hailstorms, flood, wind, drought, tree diseases, fire, or defoliation or during logging opera- tions. Any time a breakdown occurs in the effectiveness of natural control factors, or when changes occur in the genetic composition of populations, or in the age, composition, and density of stands, outbreaks are likely to occur. Forest insect outbreaks vary greatly in frequency, size, and duration. Fortunately, the majority are small and short-lived, and usually consist of only one or a few “spots” in a stand or region. Unfortunately, some may expand until they encompass hundreds of thousands of acres and last for many years before subsiding. From 1957 to 1966, a total of 154 different species were recorded in out- break status in eastern forests.4 The following general discussions on forest insects are avail- able for reference: Anderson (9); Doane, et al (196); Graham, K. (302); Graham and Knight (309) ; Thatcher (710) ; Beal and Massey (41); Beal, et al (40); Becker (50); Houser (381); Kotinsky (437); MacAloney and Ewan (472); MacAloney and Schmiege (473); and Shenefelt and Benjamin (644). Forest Insect Caused Losses Insects are among the most destructive agents affecting forest and shade trees. During 1952 (considered an average year), they killed an estimated 1 billion cubic feet of young, growing trees and 5 billion board feet of older, more mature trees of sawtimber size. In addition, they were responsible for a loss in growth of 1.8 billion cubic feet in the young, growing stock and 8.6 billion board feet in surviving sawtimber trees (729). The.losses in sawtimber alone were enough to build 114 million homes. Losses incurred during epidemics are sometimes much heavier. Additional losses of a considerable but unknown amount are caused by insects that bore into the wood of living trees or dead and fallen timber. Insects are not only responsible for the killing of valuable trees and the loss of growth or recoverable volumes from surviving damaged trees, for the weakening or destruction of wood products of all kinds, but also for serious losses of other kinds, both tangible and intangible. Management plans are often upset and fire hazards increased; watersheds and wildlife habitats are im- paired or destroyed; water in streams and lakes is polluted; the incidence and severity of floods are increased; and the attractive- ness of parks and other recreational areas is reduced or destroyed. Heavy investments in tree improvement programs are also jeopar- dized or upset by the destruction of seeds and cones or valuable seed trees in seed orchards; stand composition is often changed, leading to the displacement of valuable tree species by others of lesser value; and innumerable shade and ornamental trees around homes, along roadsides, or along the streets of towns and cities are killed or their attractiveness greatly reduced or destroyed. *Forest Insect Conditions Annual Reports, 1957-1966 inclusive, USDA Forest Service. 13 Forest Insect Surveys It has long been recognized that successful control of forest insect outbreaks depends not so much on the control method used as upon a knowledge of the insect situation on immediate, sur- rounding areas. When an outbreak is discovered, it needs to be known whether it is increasing or decreasing. It is also impor- tant to locate the center of greatest concentration and to deter- mine the direction of spread (169). When an outbreak occurs, it is also important to know the value of the resources at stake and the status of natural control factors, before decisions to apply control are made. Of like importance is the possession of a general knowledge of insect conditions throughout a timber type or region. This is helpful in developing plans for the detection of outbreaks in their early stages, a time when they may be sup- pressed most easily and economically and before heavy losses are incurred. Similarly, it is helpful to have a continuing record of the presence and abundance of the less spectacular, non-outbreak types of insects, to determine if, when, and where their numbers or damage are reaching economic levels of concern. Where inten- Sive management of the forest for timber or other objectives is being practiced, it is also important to have up-to-date informa- tion on all destructive pests to allow for their early control where needed. Such knowledge as described above is sought or acquired through surveys. Forest insect surveys of one sort or another have been made in the United States since the early days of this century (88), but prior to the passage of the Forest Pest Control Act in 1947, they were usually conducted on a more or less unorganized basis. Pas- sage of the Act made it possible for the first time to conduct surveys on an organized, systematic basis on forest lands of all ownerships. In part, the Act authorized the Secretary of Agri- culture, either directly or in cooperation with other Departments of the Federal Government, with states and other public agencies, and with private organizations and individuals, to conduct surveys to detect and appraise insect infestations before they develop to outbreak proportions; to appraise their potential destructiveness ; and to determine the needs for their control. Forest insect surveys are also conducted in Canada. There, the aim is not only to detect and appraise infestations but also to obtain information on the distribution, biology, and cycles of abundance of insect species for taxonomic and other purposes (481). Basically, forest insect surveys are of two kinds, detection and evaluation, and they may be conducted separately or at the same time. Detection surveys, as the term applies, are primarily for the purpose of discovering threatening infestations. Evaluation sur- veys are usually far more intensive and complex, being concerned with such factors as the intensity and trends of pest populations, the identification and evaluation of natural control factors, the size and boundaries of infestations, the value of the resources at stake, the possibilities of economic loss and an estimate of its magnitude if suppressive measures are not taken. Many methods and techniques are employed in conducting sur- veys, the choice depending on many factors, such as the insect 14 species, its life history and habits, the nature of the damage it causes, the forest type and terrain, the size and accessibility of the area, a working knowledge of natural control factors affecting it, and the availability of trained personnel and funds. Aircraft are widely used in detection surveys and to a lesser extent in evaluation surveys. Conditions may be recorded by trained observers riding with the pilot (3, 339, 341) ; or by aerial photography (745, 2, 338, 340, 746, 142). Unfortunately, evidence of infestation by many insect species is difficult or impossible to detect from the air. Where these insects are concerned, the only recourse is to use ground survey methods. To the extent that it is possible to use them, aerial surveys are far less time consuming and costly than comparable ground surveys. Ground surveys are not only required to detect infestations of many species but are essential for evaluation purposes. In most cases, they are highly complex and require the services of highly trained personnel. Ground surveys for evaluation purposes pre- sent many different sampling problems, such as when, where, and how to sample in order to obtain needed information within desired confidence limits. The choice of procedure is governed largely by the insect species and the intensity and size of the infestation. In addition to insect population density and size, data also may be collected to identify and record the abundance of natural control factors. In all cases information is sought and analyzed to determine two things: what likely will happen if no action is taken to suppress the infestation, and what might be expected to happen if suppressive measures are applied. Much progress has been made in recent years in reducing the time and cost of conducting surveys, particularly through the use of sequential sampling techniques. These techniques provide for flexibility in sample size in contrast to conventional techniques which usually specify a fixed number of sampling units to be examined. Units chosen at random from a sample are examined in sequence until the sample falls into one or more classes dis- tinguished by specified limits (743). Sampling plans have been published for several important forest insect pests (158, 157, 393, 894, 542, 612, 692). Forest Insect Control The impact of naturally occurring adverse environmental fac- tors on forest insects is so great that the majority of species never occur in sufficient numbers to constitute an economic hazard. Even those insects that become sufficiently abundant at times to be considered ‘“‘pests” are also subject to control by these factors, though usually to a lesser degree and frequency. Depending on the insect and the value of the forest resources affected, a given de- gree of natural control may be economically effective. When natural control factors fail to hold populations to eco- nomically tolerable levels, it may be necessary to apply arti- ficial controls. Depending on the insect and its biology and eco- logical relationships, a wide variety of materials and methods are available for suppressing populations. These may be applied directly against the insect to interfere with its growth or repro- 15 duction, or to kill it; or they may be applied to the environment to render it less favorable for the insect either through alteration in food supply, in microclimatic factors, or in the abundance and effectiveness of natural enemies. The choice of materials or methods in artificial control de- pends on several things: whether the insect is a native or intro- duced species; the factors known or thought to be responsible for its abundance; the need for quick and effective reductions in its numbers; and cost. If a native species is involved, the aim usually is not to eradicate it, but rather to reduce and maintain its num- bers to a tolerable level; if it is an introduced pest, the aim may be to eradicate it or to slow down or prevent its spread. Artificial control methods designed to suppress existing out- breaks, usually have short-term effects only; those that are used for the prevention of outbreaks may be long lasting. Control costs vary considerably, depending on the insect and its habits, the methods and materials used, and the size and accessibility of in- fected stands. It may be limited to only a few dollars per acre where infested stands are treated with aerial applications or insecticides or it may cost several dollars per tree when treat- ments are made to individual trees. Occasionally, control costs may be retrieved through the salvage and sale of infested timber. Some types of control may be used with complete safety; others, in which hazardous materials are involved, must be used with great care. NATURAL CONTROL Natural control results when naturally occurring adverse en- vironmental factors prevent insect populations from reaching or exceeding harmful proportions. It may be effected by a single factor, such as abnormally low winter temperatures, or by several factors working in combination; it never ceases to function en- tirely, but its impact may fluctuate greatly from place to place and time to time (9, 302, 309). PHYSICAL FACTORS.—Temperature is one of the most im- portant physical factors affecting forest insects. It not only sets limits to their distribution but also often profoundly affects their abundance. The optimum temperature for many eastern species appears to lie between 75° and 80° F. As temperatures depart from this range, in either direction, activity gradually declines and eventually ceases. When they climb to 120° or drop to around 0° or lower, death results. Rapid changes in temperatures, such as occur in the fall and spring, also may cause mortality even though absolute lethal temperatures are not reached. Insects react in many ways to escape the rigors of adverse temperatures. During the summer, leaf-feeding larvae may move from the upper to lower surfaces of leaves, or from the periphery of the crowns to the shaded interior to escape excessive heat. Adults find relief from heat by moving into the interior of stands, to the shaded portions of trunks, or to the interior of crowns. Dur- ing cooler than normal days, they may seek out individual, exposed trees, the sunny side of trunks, or trees along the edges of stands. To escape the effects of winter cold, a species may utilize areas in 16 which to hibernate either in the egg, larval, pupal, or adult stage where the likelihood of lethal temperatures occurring are greatly lessened. Because of physiological changes which occur in the dor- mant state, many northern species are able to survive tempera- tures well below 0°. Southern species are much less likely to Survive exposure to such temperatures. Outbreaks of leaf eating insects may be suppressed by late spring frosts which kill the young, tender foliage which the young larvae depend on for food. Late springs may result in greatly delayed emergence from hibernation and cool summers may result in a slow-down in the rate of larval development. Prolonged de- velopmental periods add up to an extended period of exposure to parasites, predators, and disease pathogens, which may lead to unusually heavy losses. The number of generations produced per year is related to photoperiod and the length of the season of biologically effective temperatures. In the South, a species may produce five or more generations per year; whereas in the North, it may produce only one. Outbreaks of such a species often appear to develop with explosive suddenness in the South. In the North, it may require several years for an equivalent outbreak to occur. Insect populations are also affected by atmospheric moisture and by moisture conditions in host trees and in the soil. For example, various species of wood borers, such as powder-post beetles, breed successfully only in very dry wood; whereas others, such as the ambrosia beetles, require wood with a much higher moisture content. Damage to black locust by the locust borer and to pines by various species of bark beetles may be greatly intensi- fied during or following periods of drought. A considerable degree of control also may be effected by other adverse weather conditions. For example, heavy, beating rains may dislodge and destroy large numbers of larvae that feed on the foliage of trees; moist weather may result in the development of disease epizootics and the decimation of insect populations. HOST FACTORS.—Many species of forest insects feed on only one species of tree. Some of the most serious bark beetle pests. belong to this group. Many species of destructive wood borers also confine their attacks to a single species or to closely related species. In contrast, numerous other species feed on several to a great many tree species, often in different families. Many leaf eating species belong to this group. The females of some insects deposit their eggs in all manner of places; others deposit them on host trees only. This often leads to heavy losses among newly- hatched larvae, especially where acceptable food is not readily available. Infestations of a single-host species that develop in weak or decadent trees may disappear or be greatly reduced when the ratio of these trees to healthy vigorous trees drops below a critical level in a stand. Populations of multiple-host species, many of which attack trees in all stages of health or vigor, may be held to low levels in mixed stands which contain a low ratio of preferred to non-preferred host species. BIOTIC FACTORS—Parasites, predators, and pathogenic micro-organisms play important roles in the natural control of insects. Their effects may not always be evident, but they always bring some degree of pressure to bear on their hosts, and it is 17 often severe. Occasionally, as when a virus epizootic develops, the results may be catastrophic. Operating singly or in combination, biotic factors may limit the duration and magnitude of an outbreak, prolong the intervals between outbreaks, or prevent outbreaks entirely. A large number of these control agents have been col- lected and identified in the forests of eastern America, and new ones are being added to the list each year. Insect control by biotic factors has several advantages not offered by many of the other approaches to control now available. Where these factors are well established they usually are self- perpetuating, barring natural catastrophies or unwise interference by man; they adjust to changes in the size of host populations; and they operate with practically no adverse side effects. The majority of the parasites and predators of insects are other insects. Many thousands of species belonging to well over 200 families in 15 orders are known to be either parasitic or pre- daceous; many of these attack forest insects. The majority of parasitic forms belong to only a few families in the orders Hy- menoptera and Diptera. Important predators are found in several families of the orders Coleoptera, Diptera, Neuroptera, Hemip- tera, and Hymenoptera. Parasitic and predaceous insects differ widely in habits and behavior. A parasite usually requires only one host in which to complete its development; a predator usually requires several to many hosts for its development. A parasite usually does not kill its host until it has completed its own development; a predator usually kills its host as soon as it is encountered. Host selection by parasites is a function of the egg-laying female adult only; whereas each individual predator must search out hosts in all of the feeding stages. Forest insects are also fed upon by many other forms of animal life, principally spiders, mites, birds, and many mammals. Birds, especially woodpeckers, are sometimes effective in suppressing outbreaks. Many other species of birds are also thought to play important roles in control (284, 535). Small mammals such as shrews are often effective in controlling species that spend parts of their lives on the ground. The literature contains many references to the role of parasites and predators in insect control. A good introduction to the subject is found in publications by DeBach (187), Sweetman (701), Clausen (144), Balch (25), Turnbull and Chant (722), Thompson (714), and Burkner (118). Many species of forest insects are also subject to a consider- able degree of control by pathogenic micro-organisms. Some of the latter, especially the viruses, frequently occur in the form of epizootics and decimate or eliminate outbreaks over large areas. Notable examples are (1) a polyhedrosis virus disease which has played a leading role in the control of gypsy moth outbreaks in the Northeast for many years, and (2) a disease of the same type which caused the collapse of an outbreak of the European spruce sawfly over a region of several thousand square miles in eastern Canada and the Northeastern States during the late 1930’s. Well over 1100 different kinds of micro-organisms, most of which are pathogenic, have been found associated with insects. 18 This total includes 90 species and varieties of bacteria, 260 species of viruses and rickettsia, 460 species of fungi, 255 species of proto- zoa, and 100 species of nematodes (557). Generally speaking, they gain entry into the insect either by being ingested with food, through wounds or other damaged areas in the integument, or through the integument or trachea. Most of them rely on wind, rain, streams, healthy or contaminated insects, small mammals, or birds for dispersal throughout an insect infestation. Spread is occasionally so rapid that all of the insects in an infestation may appear to be dying at the same time. Many species of forest insects are particularly susceptible to viruses of the nuclear-polyhedrosis type. Once inside the host these viruses enter the cell nuclei, replicate, and become encapsu- lated in many-sided, rodlike crystals, known as polyhedra. In- vaded cells are soon destroyed, the polyhedra are then released in the body cavity, and the host dies. Diseased larvae usually become sluggish, cease feeding, and in some instances move upward in the trees. After death they may be seen hanging by their forelegs, with the body darkened, decomposed, and liquefied. Eventually they completely disintegrate and dry up on the trees. Some of the more important eastern forest insects, in addition to the gypsy moth and European spruce sawfly, that are subject to polyhedrosis virus diseases are eastern tent and forest tent caterpillars, fall webworm, linden looper, white-marked tussock moth, winter moth, European pine sawfly, red-headed pine sawfly, jack-pine sawfly, Virginia pine sawfly, and Neodiprion excitans. Forest insects are also affected by several other kinds of viruses—cytoplasmic polyhedrosis, granulosis, polymorphic inclu- sion, and non-inclusion. Generally speaking, these viruses appear to be less effective and less specific in control than those of the nuclear-polyhedrosis type. For further information on viruses the reader is referred to Bergold (61), Bird (67), Hughes (389), Martignoni and Langston (501), and Steinhaus (690). Several species of bacteria produce so-called milky diseases in the insect host, the best known being the milky disease of Japa-. nese bettle larvae (212). The larvae of many closely related species of beetles are also affected by this disease. Scores of species of Lepidoptera and apparently several species of Hymen- optera, Coleoptera, Diptera, and Orthoptera are susceptible to diseases caused by various crystalliferous bacteria, the best known of which are several varieties of Bacillus thuringrensis (G3), 332). Some species of fungi occasionally cause significant reductions in insect populations. Aphids are particularly susceptible to at- tack by species of Entomophora (=Empusa). The species, E. megasperma, was credited with causing a high degree of control of the forest tent caterpillar in Ontario from 1949 to 1952. An- other species, Beawveria bassiana, reportedly killed over 90 per- cent of the larvae of the smaller European elm bark beetle in a number of infested elm trees in Connecticut (195). Many species of pathogenic Protozoa are also associated with forest insects. Generally speaking, they prolong the length of the larval stage and reduce the fecundity of surviving adults. tg Numerous species of nematodes may be found in the gut, the hemocoel, or in particular organs such as the Malpighian tubules of insects. Some of these kill the host when they emerge; some cause death by initiating the action of lethal microbial disease agents; and some cause injury but not death. Certain bark beetle- infesting species riddle the intestines and gonads of their hosts, block the ducts, and cause the ovaries to shrivel. This may lead to a marked reduction in egg production by infested female beetles and a sharp decline in beetle populations (508). Welch (753) reviewed the literature on the subject. APPLIED CONTROL Applied control consists of the regulation by man of insect activities, distribution, and abundance through the use of prac- tices designed to enhance, supplement, or serve as substitutes for natural control. The action taken may be either direct or indirect; i.e., 1t may be directed either against the insect itself to suppress currently destructive populations or toward the alteration of en- vironmental conditions in such a way that destructive populations cannot develop. Whatever the objective, the aim is to use the cheapest, safest, and most economical methods available. SILVICULTURAL CONTROL Insect population density is influenced by the composition and condition of forest stands. Because of this, it is sometimes possible to create unfavorable conditions through the application of care- fully designed cultural or management practices. Efforts directed toward this end are commonly called silvicultural control. Possibilities of silvicultural control occur during the establish- ment and throughout the lives of stands, by selecting the more resistant tree species for planting, by putting them on sites best suited for them, or by controlling their composition and density. Stand conditions may be created or modified as needed by thin- nings or cuttings. Pure stands may be broken up into mixtures of age-classes in small units, with no two contiguous units of the same age-class. Mixed stands may be broken up by cutting in small groups to maintain and promote diversification in species composition and density. Overmature trees may be removed from stands and the stands harvested as soon as they mature. High- Ae trees may be removed in sanitation-salvage cuttings (413, 631). For further discussions of silvicultural control, see Keen (412), Graham and Knight (309), and Prebble (605). PHYSICAL AND MECHANICAL METHODS OF CONTROL Many forest, shade tree, plantation, and wood products insect pests are amenable to control by physical or mechanical methods. The method chosen is dictated by many factors, such as the habits and behavior of the insect pest involved, the location and value of the trees or products attacked, and cost. 20 Trap trees and trap logs are sometimes effective in the control of bark beetles (552). Bands of tanglefoot or similar materials may be placed around the trunks of shade trees to prevent larvae or wingless female adults of several species, such as the fall cankerworm, from ascending the trees to feed or oviposit. Young, newly-planted shade trees may be protected from borers of various kinds by enclosing the trunks in wrapping paper. Bag- worms on ornamental trees may be controlled by handpicking. Subterranean termites can be kept out of structures by capping foundations with a 4-inch layer of high grade concrete or with properly applied metal shields, by keeping untreated wood from contact with the ground, by using solid foundation masonry, and by providing good ventilation between the ground and timbers. The logging and milling of infested timber and destruction of the slabs containing the broods is often effective in preventing bark beetle outbreaks, but this may be feasible only where the trees are of merchantable size, are accessible, and when they can be harvested promptly. Bark beetle broods in or under the bark may also be disposed of by the storage of infested logs in water ; by peeling infested logs and burning the bark; by sawing infested trees into short lengths and burning them; by peeling the bark of infested trees and exposing the brood to desiccation and to natural enemies such as ants, birds, and rodents; or by felling infested trees in a north-south direction in the open where the bark is exposed to heat from direct exposure in the sun. Ambrosia beetle damage to summer cut logs can be reduced or prevented by the quick removal of the logs from the woods, by quickly manufacturing them or storing them in ponds, by quickly drying the lumber cut from them, and by the removal of the bark from rough-hewn pieces. Ips bark beetle populations which develop in slash following cutting operations can be reduced by limiting small scale cuttings to the fall and winter months, or by continuing large scale cut- tings throughout the summer months. In situations where it is necessary to cut on a small seale or discontinuously during the summer, control may be obtained by piling and burning the slash before the beetles complete their development in it. The gathering and burning of severed branches late in the fall or in the winter or early spring when the eggs and grubs are in the twigs is an effective method of controlling twig girdling species. Wood-borer damage to field-piled pulpwood in the Lake States has been reduced by piling the wood in the shade or by placing it in standard compact piles. Lyctus powder-post beetle damage can be reduced by the long storage of susceptible sapwood in water or by steaming it at high temperatures. Bark-beetle damage to bark- covered poles and slabs used in rustic construction can be reduced or prevented by cutting the material during the fall and winter and then seasoning it off the ground and under cover. Damage to young pines by the European pine shoot moth in the Lake States can be reduced by removing the lower limbs. This forces the over- wintering stages of the insect into buds on the upper branches above the snow line where they are killed by lethal low tempera- tures during the winter. 21 REGULATORY CONTROL Regulatory control is aimed at the prevention of entry and es- tablishment of foreign plant and animal pests, or at the suppres- sion, containment, or eradication of such pests as may have become established in limited areas. This form of control became possible with the passage of the Federal Insect Pest Act in 1905 which enabled the Federal Government to regulate the importa- tion and interstate movement of articles that might spread insect pests. It was reinforced in 1912 by passage of the Plant Quaran- tine Act, which authorized the Secretary of Agriculture to enforce necessary regulations to protect the agricultural economy of the United States by preventing the introduction of insects and plant diseases, and by passage of the McNary-McSweeney Act in 1928, which established a federal policy regarding the use of legislative means for combatting forest insects and diseases. Then, in 1947, passage of the Forest Pest Control Act provided authority for the United States Government to act alone or in cooperation with states, territories, or private timber owners to control destructive forest insects or diseases. Prior to the passage and enforcement of quarantine laws, many species of forest, shade tree, and ornamental insects, several of which are highly destructive, gained entry into Eastern United States. Since then the rate of entry of additional species has been drastically reduced. The following is a list of species known to have been introduced into Eastern United States. Order and Species Country of origin Principal food plant Orthoptera Gryllotalpa gryllotalpa (L.) Europe Nursery stock Hemiptera Stephanitis rhododendri Harv. Europe Rhododendron Isoptera Coptotermes formosanus Shiraki Far East Wood products Homoptera Adelges abietis L. Europe Spruce piceae (Ratz.) Europe True firs strobilobius Kalt. Europe Larch Asterolecanium variolosum (Ratz.) Europe Oak Cryptococcus fagi (Baer) Europe Beech Gossyparia spuria (Mod.) Europe Elm Matsucoccus resinosae (B. & G.) Red Pine Pealius azaleae (B. & M.) Asia Azalea Phenacoccus acericola King Europe Sugar maple Pineus strobi (Htg.) Europe Pine Pseudococcus comstocki (Kuwani) Far East Deciduous trees Quadraspidiotus perniciosus (Comst.) China Deciduous trees Coleoptera Amphimallon majalis (Raz.) Europe Various plants Anobium punctatum (DeG.) Europe Wood products Anomala orientalis Waterhouse Chlorophorus annularis (F.) Philippines Japan, India Nursery stock Stored bamboo Chrysomela interrupta F. Europe Willow, poplar crotchi Brown Europe Willow, poplar Cryptorhynchus lapathi (1L.) Europe Poplar Crytepistomus castaneus (Roelofs) Japan Oak Heterobostrychus aequalis (Waterh.) Far East Oak & mahog- any boards Hylotrupes bajulus (L.) Europe Seasoned conif- 22 erous wood Order and Species Maladera castanea (Arrow) Minthea rugicollis (Walk.) Nacerdes melanura (L.) Phyllobius oblongus (L.) Plagiodera versicolora (Laich.) Polydrusus impressifrons Gyll. Popillia japonica Newm. Pseudocneorhinus bifasciatus (Roelofs) Pyrrhalta luteola (Mueller) Scolytus multistriatus Marsh. Thylacites incanus (L.) Xestobium rufovillosum Zengophora scutellaris Suffr. Lepidoptera Aegeria apiformis (Clerck) Anthophila pariana Clerck Archips rosanus (L.) Chrysoclista linneella (Clerck) Cnidocampa flavescens (Wlk.) Coleophora laricella (Hbn.) fuscedinella (Zell.) limosipennella (Dup.) Dichomeris marginellus (D & S.) Dioryctria abietella (D. & 8S.) Epinotia nanana (Treit.) Gracillaria syringella (F.) Homadula anisocentra Merrick Nepticula sericopeza Zell. Nygmia phaeorrhoea (Don.) Orgyia antiqua (L.) Phalonia rutilana (Hbn.) Porthetria dispar (L.) Rhyacionia buoliana (Schiff. ) Samia cynthia (Drury) Spilonota ocellana (D. & S.) Stilpnotia salicis (L.) Zeiraphera ratzeburgiana (Ratz.) Zeuzera pyrina (L.) Diptera Monarthropalpus bux. (Lab.) Oligotrophus betulae ( Winn.) Rhabdophaga salicis (Schr.) Hymenoptera Acantholyda erythrocephala (L.) Caliroa cerasi (L.) Diprion frutetorum (F.) hercyniae (Htg.) similis (Htg.) Fenusa dohrnii (Tisch.) pusilla (Lep.) ulmi (Sund.) Hemichroa crocea (Fourcroy) Heterarthrus nemoratus (Fallen) Neodiprion sertifer (Geoff. ) Pristiphora erichsonu (Htg.) geniculata (Htg.) Sirex juvencus (L.) Solenopsis saevissima richteri Forel Trichiocampus viminalis (Fall.) Country of origin Orient Antilles (7?) Europe Europe Europe, Japan Europe Japan Japan Europe Europe Europe Europe Europe Europe Europe Europe Europe Asia Europe, Japan 9 Europe Europe Europe Europe Europe 9 Europe Europe Europe Europe Europe Europe Asia Europe Europe Europe Europe Europe Europe Europe Europe, Japan Europe Europe Europe Europe Europe Europe Europe Europe Europe Europe Eurasia Europe Europe South America Europe Principal food plant Deciduous trees Oak flooring Wooden wharves Deciduous trees Willow Poplar Wide variety of plants Ornamentals Elm Elm Pine Wood products Poplar Poplar Apple, thorn Deciduous trees, privet Linden Norway maple Larch Birch Elm Juniper Pines Spruce Lilac Mimosa, honeylocust Norway maple Apple, pear Deciduous trees Juniper Oak, etc. Pines Ailanthus, cherry Apple, oak Poplar, willow Spruce Elm, maple Boxwood Birch Willow Pine Cherry, shadbush Pine Spruce Pine Alder Birch Elm Alder Birch Pine Larch Mountain ash Pine, fir, spruce General feeder Poplar 23 BIOLOGICAL CONTROL Biological control is possible because of the existence in nature of a continuing interplay between the abundance of insects and their natural enemies, and because many of the latter are subject to manipulation one way or another. Traditionally, it has con- sisted of the use of parasites, predators, and disease pathogens to hold populations in check, but within recent years the concept has been broadened to include various other biotic methods for reduc- ing and/or maintaining insect populations at tolerable levels. So far, almost all biological control efforts against forest insects have been confined to the use of parasites, predators, and pathogens. Generally speaking, biological control efforts against forest in- sects have been limited to (1) the importation and establishment of foreign parasites and predators of introduced pests; (2) the transfer of parasites, predators, and disease pathogens from one region to another within the country; (8) the augmentation of established parasite and predator populations with fie!d-collected or laboratory-reared individuals; and (4) the use of microbial sprays to control outbreaks. The majority of importations of parasites and predators were made prior to World War II, with emphasis on enemies of the gypsy moth, brown-tail moth, satin moth (387, 124), European pine shoot moth, European pine sawfly, European spruce sawfly, balsam woolly aphid, and larch casebearer. Since World War II, importations have been limited mostly to enemies of the balsam woolly aphid and the smaller European elm bark beetle. Alto- gether, a total of 156 species of parasites and predators had been imported and liberated against 59 species of introduced and native pests by 1960. Of these, a total of 44 were successfully established (205). Since the early 1930’s, the Canadian govern- ment has also imported large numbers of many species of para- sites and predators against a number of pests, many of which also occur in the United States (484). Some of these have spread into adjoining areas of the United States. Large numbers of others have been shipped to this country and liberated in infested stands. A polyhedrosis virus disease of the gypsy moth accidentally introduced into the United States in the early 1900’s has since played an important role in the control of outbreaks of its host. Like others of its kind, this virus is most effective in dense popu- lations and is almost unnoticeable in light infestations. Limited field trials have indicated that direct spraying of the virus in water formulations has considerable promise for direct control. Applications of polyhedrosis virus sprays have been used to suppress populations of the European pine sawfly (66), the Vir- ginia pine sawfly (485), and the Swaine jack pine sawfly (654). Virus epizootics have been initiated in populations of the forest tent caterpillar by disseminating the virus during one generation (685). Viruses are usually applied as sprays, but they may also be applied as dusts if first incorporated with powder. Sprays may be applied by hand-operated sprayers, mist blowers, or aircraft. Progress has been made in the control of a number of lepidop- terous defoliators with Bacillus thuringiensis. Aerial applications 24 re caused some mortality of the gypsy moth but the results were inconclusive. Higher mortalities of two species of loopers (EHran- mis tiliaria and Phigalia titea), which also were present in the sprayed areas, were recorded. CHEMICAL CONTROL The use of chemicals to suppress forest insect populations is a method of last resort. It is the policy to use them only when other forms of control, either natural or artificial, fail or threaten to fail in the prevention or control of destructive populations. Depending on the situation, chemicals may be applied to a single tree or to forested areas covering thousands of acres or square miles. The aim, therefore, is usually limited to the suppression of injurious populations to tolerable levels. Many different types of equipment and techniques are available for applying insecticides (601). Aerial applications are made by fixed-wing aircraft (fig. 3) or helicopters to large areas (29, 214, 57, and 392). Individual trees, small groups of trees, and seed orchard trees (fig. 4) may be treated by ground equipment such as mist blowers (602) or by knapsack sprayers. Large individual trees may be treated by mist blowers and by hydraulic sprayers. Logs are treated by power sprayers. Fogging machines are sometimes used around resorts and campgrounds. Chemicals may be introduced into the tissues of living trees for bark beetle control (171, 52, and 762). Systemic insecticides may be applied by trunk implantation or injection, by banding or spraying of the circumference of the trunk, by spraying the foliage, by treating the soil around the base of trees, or by dipping cuttings prior to plantine= (570-587-199, 515, 36, and 447). The effectiveness of chemicals in suppressing many forest insect populations has been amply demonstrated during the past 25 years er 3 Rah F-482299 FicgurRE 3.—Airplane spraying for spruce budworm control 25 F-517833 FIGURE 4.—Mist blower applying insecticide to pine trees in a seed orchard. —a period during which a large number of new insecticides and methods of application have come into extensive use, and during which outbreaks covering hundreds of thousands of acres of forest have been suppressed. As effective as insecticidal control has been, however, it has not proved to be an unmixed blessing. It has given rise to many complex problems associated with known or suspected adverse side effects caused by some of the more com- monly used chemicals. This stems from the fact that these chemi- cals, like most other chemicals used as insecticides, are non-specific and can be expected to be harmful to at least some other exposed animal species. The problem is compounded in that some chemical insecticides are very persistent, that all of the material applied in a given environment may not remain in that environment and that free-ranging animals cannot be excluded from sprayed areas. Public awareness of known and possible hazards associated with the use of these chemicals in insect control projects, therefore, has given rise to a considerable degree of concern over their con- tinued widespread use. Efforts are unceasing to discover and develop new and safer insecticides and to determine the danger points of insecticidal accumulations in the tissues of various forms of wildlife, as a basis for preventing undesirable damage to the biota. Application techniques and equipment are being refined in order to provide better control of the placement of insecticides in the environment and to further lessen the dangers of undesirable side effects. Studies are being made to improve sampling and biological evalu- ation techniques as a basis for improving the timing of application and to insure that insecticides are applied only when and where they are needed. The rapid changes occurring in the development and use of insecticides in forest insect control make it inadvisable to include 26 control recommendations in this publication. If you are going to use pesticides, remember: Because some States have restrictions on the use of certain pesticides, check your State and local regula- tions. Also, because registrations of pesticides are under constant review by the U. S. Department of Agriculture, consult your county agricultural agent or State Extension specialist. For fur- ther information on chemical control, in addition to U. S. Depart- ment of Agriculture Handbook No. 331, many publications are available. The following are of particular interest: Billings (65), Brown (109), Brown (110), Gorham (301), Hickey (350), Hoff- man, et al. (363), Hoffman and Merkel (362), Hoffman and Linduska (361), National Academy of Science (555, 556), Whit- ten (761), and Rudd and Genelly (625). OTHER APPROACHES TO CONTROL Many conventional methods of suppressing forest insect popu- lations are very effective, but they are all found wanting in many important respects. Insecticides are often entirely effective, but they usually cannot be applied to large areas without endangering other forms of animal life. Furthermore, they usually do not hold pest populations to subeconomic levels for long, nor do they reduce the vulnerability of stands to future outbreaks. Most forms of biological control cannot be depended upon to suppress an out- break before unacceptable damage has been incurred. They are also incapable of preventing outbreaks, although they may reduce their frequency of occurrence and their magnitude, intensity, and duration. Because of these deficiencies, as well as those of other current methods of control, intensive research is underway to develop new or improved methods which may be used as comple- ments, supplements, or substitutes for them. Sexual sterilization is receiving much current attention be- cause of its potential use as a new method of control. The effec- tiveness of releasing males sterilized by gamma radiation was- established in the mid-1950’s when they were used to eradicate the screw-worm from the West Indian island of Curacao and from the southeastern portions of its range in the United States. Knipling discussed the principal of sexual sterilization in several papers (425, 428, 426, 429, 427). Several authors reported the research that led to the method and its use against the screw-worm (456, 457, 129, 180, 131). Some progress has also been reported in the sterilization cf a few important forest insects by gamma radia- tion (300, 401). Further research must be conducted before the possibilities of using the sterile male release technique for forest insect control can be determined. Chemically produced sterility also offers promise in control. The appropriate chemicals are called chemosterilants because of their capacity to deprive insects of the ability to reproduce (89). Most of the chemosterilants that offer promise for practical con- trol are mutagenic and can be used only in ways that will avoid all contact between them and non-target animals (557). Chemo- sterilants may be administered with the insect’s food or by apply- ing them to surfaces to which the insects are attracted. Those mixed with food appear to produce maximum effectiveness and minimum hazard. So far, none are available for use in forest insect control. 27 Insect attractants are being given increased research atten- tion to improve or reduce the cost of surveys and to open up hew opportunities in integrated control of forest insects. Some of these materials are powerful enough to lure insects over consider- able distances. Attractants of many kinds are being studied, but those consisting of natural chemicals produced by host plants or the insects themselves are receiving the most attention. tion (665, 666, 667). INTEGRATED CONTROL Integrated control is defined as a pest Management system that in the context of the associated environment and the population dynamics of the pest species, utilizes all suitable techniques and methods in as compatible manner as possible and maintains the pest populations at levels below that causing economic injury. In forest insect control, this would seem to encompass many of the methods discussed in preceding sections on applied control. 28 Most of the important pest species in eastern forests lend them- selves to some form and degree of integrated control. The long life of the forest crop and the fact that many species of commer- cially valuable trees can withstand some degree of infestation without serious damage provides the opportunity in the majority of cases to utilize different methods of control. Since the early days of this century, considerable emphasis has been placed on the importation and augmentation of natural ene- mies of many species of introduced pests. In many cases, the rate of dispersal of these imported enemies has been speeded up by the liberation of colonies in many parts of infested areas. The build-up in numbers after successful establishment of several species has also been speeded up by the liberation of large num- bers of field-collected or laboratory-reared individuals. The presence and abundance of natural enemies is taken into consideration in deciding whether to suppress an outbreak and in planning how to accomplish it. For example, the sudden ap- pearance of a virus disease in heavily infested stands usually por- tends the imminent collapse of the outbreak. Therefore, when evidence of this disease is encountered during surveys, it is often decided to withhold other methods of control, such as the appli- cation of insecticide. Observation of abnormally high percentages of natural control provided by insect parasites and predators may lead to a similar decision. In other situations where insecticidal control is deemed necessary, it is often possible to limit spraying to designated portions of infested areas because of the abundance of natural enemies in other portions (423). Knowledge of the population dynamics of a pest species pro- vides opportunities for various other means of preventing or reducing losses caused by it, thereby obviating the need for di- rect, suppressive measures to control outbreaks. Depending on the situation, outbreaks of certain leaf-feeding insects may be prevented or minimized by modifying the composition and den- sity of susceptible stands. It is often possible to prevent or sup- press outbreaks of some bark beetles by the removal of infested slash or the salvage of infested trees before the emergence of beetle broods from the bark. The utilization of mature trees growing on poor sites before they begin to deteriorate and become attractive to borers, such as the bronze birch borer, is a recommended con- trol practice. The avoidance of unfavorable sites in planting pro- grams is recommended for preventing damage by certain species (318). Adherence to good construction methods in the building of structures obviates the need for chemical control of termites later on (630). The destruction of elm material suitable for breed- ing by the smaller European elm bark beetle reduces the need for the use of insecticides in Dutch elm disease control (763). Some of the new approaches to biological control, many of which are yet to be perfected, may be expected to provide addi- tional opportunities for the integrated approach to control in the next few years. For a discussion of the integrated control concept, see Stern et al. (691). Comprehensive treatments of insect-pest control management and control has also been pub- lished (557, 416). 29 Practical Keys to the Orders and Families of Forest Insects, Based on Types of Injury The following keys are designed for the use of those unfamiliar with the orders, families, and genera of insects. The insects are first separated into primary divisions according to the portions of trees attacked, the size of the trees, and the timber products infested. These main divisions are in turn subdivided to other groups or subdivisions. PRIMARY DIVISIONS OF KEY Te Insects injurious to seeds, seedlings, young plantations, and small reproduction. A. To seeds, cones, and fruits. B. To seedlings and small reproduction. II. Insects injurious to large reproduction, forest trees, and shade trees. A. Acarina (red spiders). B. Defoliators, leaf miners, etc. C. Twig and tip damage, etc. D. Borers in wood and bark. E. Galls, swellings, etc. F. Sucking Insects. III. Insects injurious to forest products. A. Defects in green timber. B. Insects in round logs. C. Insects in lumber. D. Insects in material in ground. E. Defects in wood in salt and brackish water—marine borers. DIVISION I INSECTS INJURIOUS TO SEEDS, SEEDLINGS, YOUNG PLANTATIONS, AND SMALL REPRODUCTION This group includes the insects that attack the fruit and seeds of forest trees, also young seedlings in the nursery, plantation, or forest. Insects attacking seedlings more than 4 or 5 years old and somewhat shrubby and woody are discussed under Division II. A. Insects Attacking Seeds, Cones, and Fruits 1. Larvae without well-developed head capsule; maggot-like: With a sclerotized structure like a breastbone near an- terior end; in seeds of fir, cypress, birch, and fruit of chokecherry Diptera, Cecidomyiidae Without breastbone; mouth parts well developed; in fruits of cherry, apple, plum, hawthorn; in berries of dogwood, holly, and others; and in walnut husks Diptera, Tephritidae Larvae with distinct head capsule . 2 30 2. Larvae active; body extended; abdominal prolegs present Larvae less active; no abdominal prolegs; body curved .... 3. In the shucks of pecans, hickories, and walnuts and in ACOLMS +e Lepidoptera, Blastobasidae, Olethreutidae TRC ONCS Bes oars 8 SON) a lat Tt Lepidoptera, Phycitidae In fruits of wild cranberries and blueberries... Lepidoptera, Phycitidae 4. In acorns, walnuts, chestnuts, hickory nuts, and filberts.... imnvlesuminouseseeds: 2. 228 Coleoptera, Bruchidae COMES) ee ek ere aA) ee cole lien 1 wae en ree 5. First abdominal spiracle vestigal; body spindle-shaped Hymenoptera, Cynipidae First abdominal spiracle normal; body curved like a closed ingen tee! Coleoptera, Curculionidae 6. Cones abnormal and dropping prematurely Coleoptera, Scolytidae Cones maturing; damage to seeds alone Warvaevlegless: ....5.2..c hadi... Hymenoptera, Chalcididae Larvae with true legs ............000... Coleoptera, Anobiidae B. Insects Attacking Seedlings and Small Reproduction a Plants cut off near ground line or stems lacerated and GINTIVClCO shee orn Fo, meet Named ree ee eke Plants wilting or fading, easily plucked from ground be- cause of severed stem or roots below ground... | Gall-like swellings Onethe Stems. Oe es Oe eae Bark gnawed in patches along the stem of conifers... | Foliage off-color, yellowish or rusty, and often covered with very fine cobweb-like threads or matting Tetranychididae Roots showing small cottony or globular objects at time of CRANSMIAMCINO 210 Fee cae Homoptera, Aphididae Leaves or cotyledons cut off and carried away; Southern SENECA aRe oT Hymenoptera, Formicidae Other types of damage. See Division II. 8. Small, tender plants: Small, maggotlike larvae causing injury Diptera, Muscidae Large, smooth, dark-colored caterpillars present Lepidoptera, Phalaenidae Larger plants, hardwoods, with woody part tunneled: Tunnels longitudinal ................. Coleoptera, Cerambycidae Tunnels across the grain, wood stained Coleoptera, Scolytidae Tunnels irregular, chiefly underground .................. lsoptera 9. Curved, grublike larvae in the soil Coleoptera, Scarabaeidae Elongate, cylindrical, hard-shelled larvae Coleoptera, Elateridae Small, molelike tunnels usually near the surface of the SOU ee .. Orthoptera, Gryllotalpinae 10 Jit 31 10. Bark swollen and gnarled at or just below ground line Lepidoptera, Phycitidae pouthern: States he... we Homoptera, Fulgoridae Northern States .......... ncaa Hymenoptera, Formicidae 11. Northern, Southern, and Lake States Coleoptera, Curculionidae More southern and western States and Lake States Orthoptera, Acrididae DIVISION II INSECTS INJURIOUS TO LARGE LIVING TREES AND TO SMALL TREES MORE THAN 4 OR 5 FEET TALL This group includes insects and related organisms which com- monly attack living forest and shade trees other than those that attack fruit and seeds or that attack small plants not more than 4 or 5 years old. Insects responsible for damage to wood products, many of which primarily inhabit dead or dying trees or which attack logs, lumber, and other wood products are discussed under Division ITI. Injury consisting of discolored, yellowish, rusty, or mottled foliage covered with fine cobweblike threads or matting Tetranychidae A Injury consisting of defoliation, leaf rolling, leaf tying, leaf and petiole mining, or bast or epidermis miners on green- barked ‘Stems. oes a eo es B Injury occurring on new growth, twigs, branches, or small trees, consisting of mining, pruning, withering, or flagging OC Injury caused by larvae or beetles boring in the bark, under the bark, orci the wood" 2.9 fee ee eee D Injury consisting of a gall or swelling on stem, branch, or 11-5) aaa aemnnrTOne Ss muUnnUTNS Son oh ERD Sinemmact GV NA Mer CCT NAT iy ec E Injury caused by sucking insects feeding on leaves, twigs, or bark surfaces, usually the softer tissues of the plant ............. F B. Defoliation and Other Injury 1. injury esrused-by beetles’ sc.) nn tk hoe Ce eee 2 Injury*caused-by larvae. 8 ee Gea ee eee 4 Injury caused by other forms or insect not present ....... wrID 2. Adults and larvae associated on the leaves Coleoptera, Chrysomelidae Adults’ only’ present... ee ee eee 3 3. Beetles usually found feeding at night Coleoptera, Scarabaeidae Small, bright-colored, jumping beetles, Flea beetles, Coleoptera, Chrysomelidae Dull black, purplish, or gray, soft-bodied beetles, Blister Weetles i set OEE oy A ee Coleoptera, Meloidae Small snout beetles _..... Coleoptera, Curculionidae 32 4, Prolegs, usually two or five pairs os Lepidoptera Prolegs, usually six or more pairs—or none Hymenoptera, Tenthredinidae Prolegs inconspicuous; leaf- or bast-mining forms 5 5. Circular holes cut in the leaves Hymenoptera, Megachilidae Leaves rolled into a small, compact bundle Coleoptera, Curculionidae Grasshoppers associated with injury Orthoptera, Acrididae Walkingsticks associated with injury Orthoptera, Phasmatidae C. Twig Pruning and Other Injury 6. Injured portion hollowed or mined; injury caused by larvae or bark beetles, which are usually present ff Injury caused by external feeding or ovipositing, which removes a portion of the bark or causes a definite mechanical injury or a resin-infiltrated scar ........ 13 Cottony-masses on tips of twigs concealing the insects ; conifers: .).= _Homoptera, Coccidae, Phylloxeridae 7. Injury on two or more whorls of the terminal of conifers; inactive, curved larvae under bark or in pupal cells in WOOC ew ers | cen sree Coleoptera, Curculionidae Twigs or brances of hardwoods or conifers containing bark beetles or powder-post beetles or a cylindrical shotlike hole, usually darkly stained, directly entering injured portion Coleoptera, BUR Bostrichidae In ysOUuneRWISG 4 eee) es ae 8 8. Twigs not mined below fading portion .__. 9 Twigs mined far below fading portion, ‘tunnel often ex- tending to the ground ..... Coleoptera, Cerambycidae rea ONCE Seater ee ea ene ee LO UAC OOGSS mite (tote) ss onal sooth Srey ial 10. Larvae with prolegs; often pitch masses at point of INJURY. = Lepidoptera, Olethreutidae Larvae without conspicuous pr olegs; usually a spine on lastseement! 2125 26.23. Hymenoptera, Tenthredinidae 11. Larvae with well-developed prolegs; usually colored; usually in more tender parts of twigs Lepidoptera, Olethreutidae, Aegeridae, Cossidae Larvae with under- peve oped prolegs in pees portions OMFtWIGS eS LN ence geome ys 12. Elongate, flat larvae; ‘mines filled Coleoptera, Buprestidae Cylindrical larvae; mines open Coleoptera, Cerambycidae > There seems to be no simple and practical method of separating the leaf miners of the four orders that have species with this habit. Those found in conifers are probably either Lepidoptera or Hymenoptera; those on hardwoods may be Lepidoptera or Hymenoptera, or of the families Curcu- lionidae, Chrysomelidae, or Buprestidae of the Coleoptera; or they may be Diptera of the families Agromyzidae or Cecidomyiidae. 33 13. Obvious scar and pitching of wood at base of injury or 14. 15. 16. U7. 18. Ig 34 along twigs; conifers Scale bodies present on twig Homoptera, Margarodidae Scale bodies absent .................. Coleoptera, Cerambycidae Numerous phloem scars on twigs; spittle masses may be’ present #02". 0) anes ae Homoptera, Cercopidae (Hail injury is similar except that the scars are al- ways on top side of branch) Twigs slit with a lacerated wound at base of injury or at point of breaking Homoptera, Cicadidae, Membracidae Orthoptera, Gryllidae D. Borers in Wood and Bark Borers in the phloem and outer corky bark of living trees rarely scarring the: wood 444 6 ee Borers in callous tissue around wounds On various hardwoods ........ Coleoptera, Curculionidae On maplesa:treer oti sees Lepidoptera, Aegeriidae Oni coniters7: es 25 Lepidoptera, Aegeridae, Phycitidae Borers in the dead wood beneath fire scars, turpentined faces, blazes, cavities, and similar wounds .................... Borers under the bark or in the wood (other than be- neath scars or catfaces) of living trees 0... Bark beetles associated with their larvae under the bark Coleoptera, Scolytidae Root borers or mining at base of tree White, unpigmented larvae Coleoptera, Cerambycidae Highly pigmented larvae Hymenoptera, Tenthredinidae Serpentine mines just under the epidermis of chestnut and oak _.. Lepidoptera, Nepticulidae Ambrosia beetles; wood stained around holes Coleoptera, Scolytidae Platypodidae White, fleshy, cylindrical larvae in hardwoods Coleoptera, Cerambycidae, Brentidae White, fleshy, flat-headed larvae in turpentined faces in fire scars on conifers | Coleoptera, Buprestidae Larvae with heavy, chitinous armature on last segment; chestnut, oak, maple ... Coleoptera Larval mines extended under the bark and also deep into the wood in later stages Larval mines entirely under the bark or only in wood of current annual ring Pitch exuding from larval mines; larvae with prolegs present; conifers Lepidoptera, No pitch, but often water and frass exuding Head of larvae globular, protuberant Head of larvae somewhat flattened and embedded in prothorax Coleoptera, Cerambycidae 15 16 ey 22 18 21 i 20 20. 21. 22. 23. 24, 25. 26. ale Prolegs absent; last segment often heavily armed Coleoptera, Tenebrionidae Prolegs absent; larvae curved, grublike; in willow, pop- larvandwpalmettoy. 2.2... Coleoptera, Curculionidae Prolegs present; last segment not heavily armed Lepidoptera, Hepialidae, Aegeriidae Larvae depressed, flat-headed or pestle-shaped Coleoptera, Buprestidae Larvae curved, grublike ............ Coleoptera, Curculionidae Larvae slender; thoracic segments not noticeably en- larged; cause pitch flecks in wood, birch, ete. Diptera, Agromyzidae Larvae with prolegs; poplar, willow, alder, ash, persim- MOM Aare Neer os Lepidoptera, Hepialidae, Aegeriidae Larvae without prolegs Inghardwoodsies<5 2405.2. Coleoptera, Cerambycidae In conifers; associated with pitch mass Coleoptera, Curculionidae, Scolytidae EB. Galls § Galls of more or less open, exposed, simple structure, or, when enclosed, the insects maintain permanent open- ings, or the gall is dehiscent to permit the escape of rarely, several insects to a cavity; occasionally a per- manent opening is maintained by the feeding larva. Mites present having 2 pairs of legs; galls of various shapes but always provided with an opening to the exterior and lined on the inside with hairy or fuzzy POMC INSGe ee ee he Se EN. ci Brag ee A cnn ee hee Acarina Galls otherwise ......... Satie Bir ane Siow ath de leanne es 7 | Insects=not.fitted. for JUMPING ...8..60.8 ban Insects with hind legs developed for jumping Homoptera, Psyllidae Leaf galls on hardwoods, chiefly elm, poplar, hickory, ash, sumac, and witch-hazel Homoptera, Aphididae Conelike galls on tips of spruce twigs Homoptera, Chermidae Pitlike galls on twigs of hard pines Homoptera, Margarodidae Pitlike galls on twigs of white oak Homoptera, Asterolecanidae Galls inhabited by larvae with a well-developed head capsule ..... NaC e ee hae eee ae eee a ae ne Larvae without well-developed head capsule, maggot- like; white to yellowish or reddish in color: 24 27 25 26 28 Salt seems impossible to devise a key that will separate all the varied types of galls into family or order groups. On the other hand, many groups are fairly true to type, and if considered with the larvae or other stages of the insect inhabiting them, you can make a fairly workable distinction. 30 28. 29. 30. ol. 32. 33. 36 Larvae with a distinct structure like a breastbone near Anterior End eee Diptera, Cecidomyiidae Larvae without breastbone; mouth parts well de- veloped? 11.2. 2 See eee cs mees Diptera, Berouiyzide Larvae legless or with only minute legs 0.0... Legs well developed, also prolegs present 0... Woody galls containing plain evidences of mining ac- tivity of the larvae; larvae with a well-developed head capsule and mandibles Coleoptera, Buprestidae, Cerambycidae, Curculionidae Larval mines not obvious; white larvae, curved or grub- like in form, legless, and with distinct head capsule, each contained in a specialized cell Hymenoptera, Cynipidae, Chalcididae On, willow. 26-2 Hymenoptera, Tenthredinidae On locust, poplar, maple... Lepidoptera, Olethreutidae F. Sucking Insects Injury or insects present on leaves ..... Injury primarily confined to twigs ... i Injury primarily confined to branches and main stem __ Leaves off-color, yellowish or spotted from feeding punc- tures of active, jumping insects: Homoptera, Cicadellidae Hemiptera, Tingidae Leaves bearing galls or abnormal spots: On Nackberty- 2) Sane Homoptera, Phyllidae On elm, poplar, willow, witch-hazel, hickory, oak, chestnut, etc. Homoptera, Aphididae, Phylloxeridae On: conifers2542 54 eae Homoptera, Phylloxeridae Exposed insects on the leaves: Sealelike, gall-like, or soft grublike insects covered with wax in the form of powder or tufts Homoptera, Coccidae Fringed, scalelike immature forms associated on the leaves with white 4-winged flies Homoptera, Aleyrodidae Soft-bodied insects with long conspicuous antennae Homoptera, Aphididae Insects surrounded by a conspicuous frothy mass of spittle; ends of branches and trees slowly dying in severe infestations; pines ......... Homoptera, Cercopidae Injury consisting of ragged slits in the twigs, often breaking at incision; the tips of the branches hanging with withered leaves; hardwoods Homoptera, Cicadidae Homoptera, Membracidae Injury consisting of gall-like or gouty swellings on limbs ANG CWilLeiSrOl tlie ee. ee Homoptera, Chermidae Tips of hard pines flagged (needles yellowing’) ; scales embedded in pits in bark Homoptera, Coccidae 29 30 32 33 34 Branches and twigs infested with scalelike, gall-like or soft-bodied insects covered with waxy powder or tufts; twigs often dying... Homoptera, Coccidae Tips of branches swollen forming pineapplelike galls; COMIMETS te ee. Homoptera, Phylloxeridae Tips of new growth withering, infested with numerous soft-bodied insects with prominent antennae Homoptera, Aphididae 34. Fir trees unhealthy and dying; trunks infested with masses of soft-bodied insects appearing as a whitish WOO RMN Re ee Homoptera, Chermidae Beech trees unhealthy and slowly dying, with dead areas of bark on stems covered with whitish masses of soft- bodiedinsects = Homoptera, Margarodidae Trees infested with scalelike, gall-like, or soft grublike insects, and covered with wax in the form of powder ORL UES Heres Fear oo is Homoptera, Coccidae DIVISION III INSECTS INJURIOUS TO FOREST PRODUCTS This group includes insects causing the type of injury seen in the handling of forest products, i.e., logs and lumber, poles, posts, piling, and manufactured materials, as handles, gun stocks, stored wood, and wood in buildings. Certain types of damage found in green logs or freshly sawed lumber are the result of insects bor- ing in the phloem or wood of the living tree. These are also treated here for convenience. They are usually distinguishable by the more or less stained condition of the surrounding wood, pitch infiltration, or the presence of scar (callous) tissue. Defects occuring in the wood of green logs or lumber, re- vealed as the logs are sawed, usually as darkly stained, pitch-infiltrated wood, or scar (callous) tissue Injury occuring to material having the bark present (lumber excepted), such as round logs after the trees are felled and left either in the woods or at the mill, or logs utilized for LUStiG work, ete; 0s. Injury to freshly sawed lumber, seasoned lumber, stored and manufactured materials, or wood in buildings Injury to materials in contact with the ground, such as cross ties, posts, poles: foundation materials, piling above water, Cl Cer ‘ A. Defects in Green Timber 1. In hardwoods MS COMITECTS inet 3 | 2. Holes small, ‘‘pinholes,”’ 14 inch or less in cross section; circular, open 1.€., never filled with boring dust Holes larger, “grub holes,” up to “4 inch in diameter, usually oval in cross section, usually open, not filled with boring dust 37 38 Pith flecks in wood, birch, maple, etc. Diptera, Agromyzidae Pinholes, about 1, inch in size, of uniform diameter throughout, wood stained in streaks, in oaks and yeilow PODIAL: cn eNVRee eee ee ee Coleoptera, Scolytidae Holes tapering, several sizes grouped together and origin- ating in a wound: Holes up to 14 inch in diameter, in chestnut and chinaguapin = ene Coleoptera, Lymexylidae Holes up to 144 inch in diameter, in oak and other WO OGS in. retain eee ee ee Coleoptera, Brentidae Variable-sized holes grouped and radiating from wounds or cavities Coleoptera, Cerambycidae, Tenebrionidae, Brentidae Large grub holes, up to 1 inch in diameter, usually ap- pearing singly and not associated with wounds Invhickonyeie a Se ee Coleoptera, Cerambycidae, Lepidoptera, Cossidae In poplar and cottonwood Coleoptera, Cerambycidae, Lepidoptera, Cossidae, Aegeriidae In maple Coleoptera, Cerambycidae, Tenebrionidae, Lepidoptera, Cossidae, Aegeriidae Invashist s