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Choristoneura fumiferana caterpillar
Scientific classification
Kingdom:
Animalia
Phylum:
Arthropoda
Class:
Insecta
Order:
Lepidoptera
Family:
Tortricidae
Genus:
Choristoneura
Species:
C. fumiferana
Binomial name
Choristoneura fumiferana
(Clemens, 1865)[1]
Synonyms
  • Tortrix fumiferana Clemens, 1865
  • Tortrix nigrida Beutenmuller, 1892
  • Tortrix nigridia Robinson, 1869

Choristoneura fumiferana, the eastern spruce budworm, is a species of moth of the Tortricidae family. It is also commonly referred to as the spruce budworm.[2] It is one of the most destructive native insects in the northern spruce and fir forests of the eastern United States and Canada with the widest range of all the budworm species.[3] Eastern spruce budworm populations oscillate widely, exhibiting extremely high densities during outbreaks.[4] According to one common theory, popularized in the 1970s, periodic outbreaks of the spruce budworm are a part of the natural cycle of events associated with the maturing of balsam fir. The catastrophe theory of budworm outbreaks holds that particularly major infestations occur every 40–60 years, as the result of a cusp-catastrophe event, whereby populations jump suddenly from endemic to epidemic levels. An alternative theory holds that outbreaks are the result of spatially synchronized population oscillations that are caused by delayed density-dependent feedback (from various mortality agents) which are synchronized via a process of entrainment.

The first recorded outbreak of the spruce budworm in the United States occurred in Maine about 1807. Another outbreak followed in 1878. Since 1909 there have been waves of budworm outbreaks throughout the eastern United States and Canada. The states most often affected are Maine, New Hampshire, New York, Michigan, Minnesota, and Wisconsin. These outbreaks have resulted in the loss of millions of cords of spruce and fir. In 20th-century eastern Canada, the major outbreaks occurred in the periods circa 1910–20, c. 1940–50, and c. 1970–80. These outbreaks impacted, respectively, 10, 25, and 57 million ha of forest. Longer-term tree-ring studies suggest that spruce budworm outbreaks have been recurring every three decades or so since the 16th century. Paleoecological studies suggest the spruce budworm has been breaking out in eastern North America for thousands of years.[5]

Taxonomy

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Clemens originally named the spruce budworm, C. fumiferana, in 1865, which was recognized as a Nearctic representative of the genus Choristoneura Lederer.[6] At this time, the name applied to populations in a variety of geographic regions and biotopes. The C. pinus, a distinct form of the Choristoneura, was later established as a separate species. However, a large group of this genus in the western part of North America remained taxonomically undefined as the "western complex"[7] until T.N. Freeman established several new species in 1967.[8] Field collections of late instar larvae of Choristoneura populations were taken from a range of localities in a wide arc, from the Atlantic seaboard along the edge of the Laurentian Shield to the Mackenzie River area near the Arctic Ocean. From these collections, only points east of the Rocky Mountain foothills yielded C. fumiferana.[9] The 2-year-cycle budworm C. biennis Freeman occurs only in the subalpine forest region,[10][11] with alpine fir and interior spruce as hosts. Budworm populations from Rocky Mountain regions south of the area of introgressive hybridization of spruce differ from C. biennis.[9] Other budworms are of little or no consequence with respect to spruces.

Geographic range

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The range of the C. fumiferana is the largest of all budworms and coincides with the range of its hosts: fir and spruce trees in eastern North America, primarily in Canada.[12][4] It includes the Boreal forest as well as the Great Lakes-St. Lawrence, Northern, and Acadian forest regions.[2] This range extends westward to Alaska.[13]

Habitat

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The spruce budworm is commonly found in boreal and sub-boreal forest regions, specifically those that consist of spruce and fir forests.[3]

Food resources

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Caterpillars

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Host plant preferences

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A host plant of the spruce budworm, Abies balsamea (balsam fir)

The main hosts of the eastern spruce budworm in eastern North America are balsam fir, white spruce, and black spruce,[14][15] but the larvae feed almost exclusively on current-year needles of balsam fir and white spruce.[16] In massive outbreaks, populations of the insect can become so high that the larvae will feed on old foliage as well.[17]

Traditionally, the eastern spruce budworm prefers balsam fir over white spruce.[18][19] However, a study showed contradicting evidence. In this study, Bichon sampled spruce budworm populations on branches from the upper mid-crowns of dominant or co-dominant balsam fir and white spruce. This was done at 20 randomly selected points in the Black Sturgeon Lake area near Thunder Bay, Ontario. The number of late-instar larvae captured in water traps was recorded throughout the dispersal period of the late instar larvae. The data indicated that white spruce canopies contained 2 to 3 times more spruce budworm than balsam fir canopies. A similar pattern was found in the the understory. Water traps under white spruce trees captured more than 3 times as many larvae as did those under balsam fir trees for most of the dispersal period.[19]

Impact on host plants

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Needles on a white spruce tree

Balsam fir is the most susceptible host to outbreaks of the spruce budworm; annual defoliation of current-year growth for 5 to 8 years will kill the host tree.[17] Defoliation by the spruce budworm is most clearly reflected in the fir's radial growth. The population of mature balsam fir in a forest is greatly reduced by the combined factors of its shorter lifespan and the great vulnerability to lethal budworm attacks.[20][21][22] The dietary preference for balsam fir over white spruce has the potential to alter the structure and composition of spruce-fir forests. Similarly, the next-generation stand of trees are influenced by the late instar larvae that disperse to the understory of the forest and feed on the regeneration of plants.[19] During a budworm outbreak in Quebec in 1957, balsam fir mortality greater than 75% occurred in stands in which no mortality was reported among the small component of white spruce.[23]

However, while balsam fir is the preferred host, severe outbreaks have occurred among white spruce stands in the Prairie Provinces and Northwest Territories containing little or no balsam fir.[18] The white spruce is less susceptible to budworm attack but can experience extreme defoliation during severe outbreaks.[24] Young white spruce and black spruce trees that had been transplanted to cleared areas became infested with dozens of late-stage larvae during severe outbreaks in north-central Ontario.[25] Mortality among white spruce also occurred in northwestern Ontario and the Algoma District of Ontario, as well as in certain areas of New Brunswick.[26]

Significant damage is also caused to subalpine fir.[27] Red spruce, in its limited distribution, is also attacked, as is tamarack.[28]

Food shortage

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Food shortages can occur in budworm populations if the budworm kills a significant amount of trees in the stand. When food becomes depleted, the larvae feed on old foliage, which will result in slowed development and reduced fecundity in the female moths. However, food shortages generally do not lead to larval mortality.[29]

Parental care

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Choristoneura fumiferana eggs

Oviposition

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Female moths lay one brood per season. Eggs are laid over several days in around 19 eggs per mass in 2 to 4 rows on conifer foliage, preferably balsam fir and spruce. Generally, females can lay 100 to 300 eggs in a lifetime but average approximately 200 eggs, which hatch in 10 days.[30][29]

In Ontario, the spruce budworm oviposits on needles of host trees in late June or early July. Large numbers of egg masses are deposited on the peripheral shoots of the crown. The number of eggs per egg mass varies from 1 to about 60, but commonly averages 20.[2]

Host plant learning and selection for egg laying

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C. fumiferana females are univoltine and must make careful decisions about oviposition sites. Selection is based on chemical cues, shape, and structure of the cuticular wax on the site. Studies have shown that sensilla important in detecting this information may be located on the moth's legs. When evaluating the host plant, the moth drums its forelegs against the surface and likely scratches the leaf with its tarsal claws, which releases compounds detected by chemoreceptors. Unsuccessfully mated and virgin females are less adept at probing oviposition sites due to unactivated sensilla.[31]

Life history

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Egg

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Eggs are a light green in color and laid in several overlapping rows within masses on the host plant.[13][32] They hatch 8–12 days after they are laid.[33]

Caterpillar

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After dispersal, first-instar caterpillars create hibernacula and molt to the second instar without feeding. It then overwinters as second-instar larvae.[33] The second-instar larvae emerge in early May and disperse to feed on seed, pollen cones, and needles at host trees. In June and July, larvae in third to sixth instars feed on current-year shoots then old foliage after the shoots are depleted. 90% of a larva's food consumption occurs after the sixth instar.[29]

Young caterpillars are a cream color when they hatch. Late instar larvae have dark brown heads and prothoracic shields and are 3 cm long when fully developed. Their bodies are also dark brown but have light spots on the back.[2][32]

 
Choristoneura fumiferana adult and pupa

Pupa

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The pupae are formed in early July on foliage in the forests. C. fumiferana are sex-dimorphic, but both sexes of pupae are initially light green then later range in color from black to a reddish-brown. They are approximately 1.2 to 1.5 mm long.[2][13][32]

Adult

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The moths will emerge from the pupae within 8–12 days, or from mid-June to mid-July. Adult spruce budworm are medium-sized, only 1.5 cm in length, and are dichromatic, exhibiting gray and rust colors.[3] The wings have silvery patches and are 21 mm to 30 mm in wingspan.[13] Peak activity occurs during the later afternoon and early evening.[32] After emerging, the adults will mate and lay eggs in July or August.[13][33]

Migration

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Local or regional dispersal

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After the eggs hatch, the first-instar caterpillars will disperse from the oviposition site throughout the tree or stand using silk strands. They are sometimes carried further by the wind. In early May, the second-instar larvae emerge and disperse to host trees. The majority of larval mortality occurs during fall and spring dispersal.[29]

The spruce budworm moths are strong fliers and disperse in exodus in the evening. They can fly over 100 meters high before going to a new site, which is sometimes 450 kilometers away, but typically only 50 to 100 kilometers downwind. After depositing some eggs at the first dispersion site, female moths may emigrate and lay eggs at multiple sites. Factors controlling budworm flight during dispersal include meteorological conditions and temperature. Moths will not disperse when the temperature is below 14°C or above 30°C. When the temperature drops below 14°C mid-flight, the moth will fold its wings and descend from the sky.[29]

Whole scale migration over long distances

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Long distance migration of the spruce budworm does occur as they can disperse distances ranging from 20 to 450 kilometers. In northern Minnesota, spruce budworm moths emigrate to the east lakeshore of Lake Superior in Ontario, Canada, because of seasonal changes. Dispersal is influenced heavily by temperature as low temperatures can slow down both take off and arrival. Other factors include dispersal direction, precipitation, altitude, and wind flow. It is likely that mass exoduses of the C. fumiferana over long distances is a result of food shortage in the local area.[34]

Enemies

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Predators

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Insectivorous birds are a common and major predator of the C. fumiferana, mainly preying on the larvae and pupae. Examples of species include sparrows, thrushes, and overstory warblers. Bird distribution will change to reflect budworm density in the forests.[29] In 1989, a study found that the highest populations of C. fumiferana larvae and pupae occur in June and July. This coincides with the period when some species of birds require maximum food to feed their young. As a result, predation by birds helps control the growth of budworm predation.[12]

Other major predators include various invertebrates, primarily spiders.[29]

Parasites

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Spruce budworm larvae are attacked by parasitoids from the Hymenoptera and Diptera orders, which include common wasps such as the Apanteles fumiferanae and Glypta fumiferanae. First- and second-instar larvae are parasitized by these two species in the summer. When they are in their fourth or higher instars the next summer, the larvae are killed by the newly emerged wasps. Other species of parasitic wasps (e.g. Meteorus trachynotus) will attack the larvae when they are in their third to fourth instars, emerging during the sixth instar or from the pupae.[29]

About 90 parasitoids have been collected from spruce budworm in eastern North America. In 1996, Henry found the suite of parasitoids collected from spruce budworm in isolated white spruce plantations of southern Ontario differed from the usual suite of parasitoids found in the boreal forest.[35]

Mating

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Female/male interaction

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Pheromones

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As with other species in the Choristoneura genus, spruce budworm females produce sex pheromones to attract males as potential mates and enhance their base level of sexual activity. C. fumiferana emit aldehydes, using a 95:5 mix of E- and Z11-tetradecenals (E/Z11-14Ald) while some other species of Choristoneura emit acetates and alcohols. The pheromone is made with palmitate using β-oxidation and Δ11-desaturation and stored as unsaturated E/Z11-14Ac.[4]

Male size is an important factor in reproductive success, but male C. fumiferana also emit a pheromone that helps attract females. This pheromone becomes available through larval and adult feeding.[36]

Mate choice

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Females exhibit selective mate choice as they show more parental investment. Pheromones allow females to recognize and assess males as mates. Male C. fumiferana prefer to mate with virgin females.[4]

Copulation

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Female C. fumiferana start accepting males for copulation early in the day, and a good number of females are active by sunset. Before attempting to mate, the male will spread its abdominal hairs and fan its wings as either the wing glands or the hairs have a scent that females respond to. The moths perform end-to-end mating with attached genitalia. Males will mate guard through prolonged copulation with the female.[4] Mating lasts around 3 hours. Increased mating times are correlated with increased production of fertile eggs. When mating is interrupted, the C. fumiferana female may oviposit infertile eggs or resume mating with other males.[37] Consecutive matings in male C. fumiferana lead to an overall decline in male reproductive performance: decreased spermatophore mass, increased mating time, and a smaller amount of sperm produced.[38]

Nuptial gifts

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Upon copulation, males transfer a spermatophore containing its ejaculate to the female, which functions as a nuptial gift. This gift is an important display of male investment because females may only have a few mature eggs to be fertilized upon emergence from the pupae. Male larval nutrition influences the quality, size, and weight of the spermatophore. During outbreak periods when food is scarcer, this is important because larvae will feed on old foliage and receive less nutrition. Males that feed on young foliage have been found to grow bigger, produce larger spermatophores, and often have more success in attracting a female.[36]

Physiology

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Thermoregulation

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Weather and variances in temperature can influence the larval development of the spruce budworm. During the cold winters, the larvae overwinter in their hibernaculae in true diapause until they can resume growth in the springtime. When the weather is warm in late fall and early spring, the budworm may metabolize at a higher rate, which depletes its finite food resources while in the hibernaculae. Harsher winters are associated with declines in population, even reaching 49% mortality. This is either due to the frigid temperatures or cumulative effect of the cold over time. Frost can be deadly to these early-instar larvae. Warm spring temperatures may have multiple effects. After emergence, it may prompt more dispersal which increases mortality, but this is hard to determine. It is more likely to help development and increase survival. Overall, cold, wet temperature may be detrimental during this larval period while hot and dry summer weather is most favorable.[33]

Favorable weather plays a more important role than dispersal for the outbreak of spruce budworms within forests.[33]

Diapause

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During diapause, the C. fumiferana larvae have low metabolic activity and stalled developmental growth. After the first instar, they enter diapause and overwinter. Spruce budworms may overwinter twice, and thus enter diapause twice, when they are on a two-year life cycle. This can occur in the spruce-basalm forests of central and southern British Columbia and of the Rocky Mountains. Larvae have been observed to end the first diapause in the summer and develop slowly until they enter diapause as fourth-instar larvae. They then emerge the following spring and develop into adults by late July. Factors determining this second diapause include food and altitude. Two-year life cycles typically occur in regions with low average daily temperatures and short frost-free seasons. In general, diapause is environmentally determined.[39]

Microbiome

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The midgut microbiota of the spruce budworm larvae is primarily composed of Proteobacteria, mainly from the genus Pseudonomas. Two specific species from this genus are P. fluorescens and P. paea. Enterococcus and Staphylococcus bacteria were found in lower abundance as well.[40]

Diet plays a role in influencing the gut microbiome. One study found possible negative consequences of ingesting balsam fir as it may release juices that adversely affect the midgut microbiota.[40]

Outbreaks

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Evidence

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Example of a cross section that shows tree radial-growth

Balsam fir can provide evidence of outbreaks with its radial-growth data. However, it generally cannot be used to obtain information on outbreaks more than 75 years previously.[24]

White spruce is also particularly useful for providing evidence of past outbreaks of spruce budworm through radial-growth data. They can provide excellent records as long as 200, and sometimes 300, years.[24] Although the white spruce is more resistant to budworm attack than balsam fir, heavy defoliation can occur in severe outbreaks, which results in reduction of radial growth.[41] In lesser outbreaks, radial growth is moderately reduced, which often makes it difficult to distinguish from random or weather-related fluctuations. Comparisons between radial growth in host trees with that of non-host trees (especially white and red pines) are used to detect the budworm effect.

Occurrences

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Spruce budworm outbreaks usually first appear in localized areas before spreading to immense territories.[42] Population explosions can be astonishingly rapid. For example, in the Kedgwick Lake area of Quebec, egg sampling in summer 1959 had indicated that budworm populations would be low in 1960, but a much higher than expected population developed in response to favorable weather and food conditions. Such situations are unlikely to recur frequently, but it is common for populations of larvae to be spread through wind dispersal. Unfavorable weather in the spring can strongly influence both budworm and host development.[43][44]

Massive outbreaks of spruce budworm occur irregularly throughout the range, but populations of this insect can remain at an endemic level for long periods.[41] In 1943, a continuing outbreak in Ontario and western Quebec was causing heavy mortality, particularly in stands of balsam fir.[45] Half of the 25 million cords (90,615,000 m3) of balsam fir standing in 1931 were estimated to have died or been injured beyond recovery, while millions of cords of white spruce were also probably killed. Atwood noted the increased difficulty of logging in budworm-affected stands as well as the increased risk of fire. Past outbreaks, instead of affecting the whole area subject to budworm infestation, have occurred in separate regions.[46] Within affected regions, epidemics did not recur regularly. In the lower St. Lawrence and Gaspé regions, for instance, radial-growth studies of balsam fir and white spruce confirmed outbreaks known to have taken place in the lower St. Lawrence in 1878 and 1912.[47] The Gaspé area had been thought to have escaped those outbreaks, but Blais found clear evidence that the 1912 outbreak had covered more than 2 million ha in that region.

Further evidence obtained by Blais in 1965[48] from determinations of radial growth on basal disks of balsam fir, white spruce, and black spruce (susceptible species), and non-susceptible white pine in the Laurentide Park, Quebec, led him to conclude that outbreaks had occurred about 1704, 1748, 1808, 1834, 1910, and 1947. The more recent outbreaks seemed to have been more severe than earlier ones, possibly, he suggested, due to an increase in numbers of highly susceptible balsam fir and a decrease in numbers of less susceptible white spruce following harvesting operations.[26]

Evidence of a budworm attack in the Lake Nipigon region of Ontario contemporaneously with the 1704 outbreak in Quebec’s Laurentide Park was adduced by Turner,[49] based on the pattern of radial growth in a single 300-year-old white spruce that showed a characteristic budworm suppression pattern beginning in 1702 and lasting for 10 years.[24] Intensive searches failed to find other white spruce of similar age.

Interactions with humans

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Pest of forests

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The eastern spruce budworm Choristoneura fumiferana has been called “the most destructive forest insect in North America."[50] Massive budworm epidemics erupt periodically in spruce–fir forests in northern and eastern Canada. Populations of spruce budworm vary in density over several orders of magnitude. Recorded densities in the boreal forest range from less than 0.01[51] to more than 100 larvae per 45 cm branch tip.[35]

Damage to trees in forests can begin even before the buds have flushed. Early instar larvae mine and kill these buds. Late instar larvae are voracious and wasteful feeders, chewing off needles at their bases. In heavy infestations, old foliage is also eaten. Increment loss, tree deformity, and tree mortality follow several years of heavy infestation.[52][53]

Defoliation of trees reduces their photosynthetic capacity and therefore curtails growth. In conifers, reduction in radial growth does not normally coincide with the first year of defoliation. For instance, the ring width of white spruce defoliation by the European spruce sawfly (Gilpinia hercyniae Htg.) showed reduced growth throughout the stem beginning in the year after defoliation.[54] One preliminary study showed that, during the first 3 or 4 years, repeated severe defoliation of white spruce by the spruce budworm was not reflected in reduced radial growth at breast height.[55] However, in the Lac Seul infestation in northwestern Ontario, apparent radial growth suppression at breast height in white spruce first occurred in the 2nd year of severe defoliation in 2 plots and in the 3rd year in 1 plot.[16]

Control

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Airplane spraying pesticide to control spruce budworm populations

Pest management implies some manipulation of the environment to adversely affect an organism that is using it in a way that is incompatible with our own use, in this case the C. fumiferana. The manipulation is effected through cultural practice, or by the introduction of a regulatory agent such as a predator or an insecticide. In regard to massive outbreaks, the use of insecticide is a primary practical method of crop protection.

If the program of spraying against budworm had not been carried out, forest production in central New Brunswick would have been reduced to 20% of normal, with a loss of some 2400 man-years of employment annually. The cost of the program, $11,600,000 for 1952 to 1958 and $10,200,000 for 1960 to 1967, was but a small fraction of the value of the resource saved.[56]

Pesticide

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In New Brunswick, over 3,600,000 ha were sprayed at least once between 1952 and 1967. Most of the sprayed forests were still “in good condition” in 1968. Although a scattering of dead trees occurred throughout the region, in no case did mortality destroy a major operating unit or disrupt a long-term management plan. In contrast, mortality exceeded 65% in 2 unsprayed check areas, each 155 km2.[56]

Biological control

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Chemical controls are controversial because of the short-term protection and need for multiple applications. As a result, research has been done on alternative biological controls using natural predators. A 1989 study found that, during outbreaks, woodland birds cannot effectively control the damage caused by budworms because their food requirements are exceeded. However, birds are important in controlling budworms and lessening damage caused by defoliation when budworm populations are less than outbreak levels.[12]

In 1986, Smith et al. investigated the effectiveness of inundated releases of Trichogramma minutum Ril., a species of parasitic wasp, for biological control of Choristoneura fumiferana in the Canadian boreal forest between 1982–83. The most significant factors affecting the level of egg parasitism were the time of release, parasite density, and local weather. The food supply of adult female parasites, vertical location of the host egg-mass in the stand, intensity of solar radiation, and density of the host were less important. Parasitism of eggs was similar on white spruce and balsam fir. Parasites reared at different temperatures and on different host eggs differed in biological characteristics, with undetermined effects on the success of field releases. Geographical strains of Trichogramma minutum were not considered as important as rearing conditions in subsequent releases because of the high degree of individual variation within each strain.[57]

https://naldc.nal.usda.gov/download/CAT86864305/PDF [58]

https://books.google.com/books?id=C1nSBwAAQBAJ&pg=PA432#v=onepage&q&f=false (forestry//pest control) [59]

References

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  1. ^ tortricidae.com
  2. ^ a b c d e Sanders, C.J. 1991. "Biology of North American spruce budworms". p. 579–520 in van der Geest, L.P.S.; Evenhuis, H.H. (Eds.). Tortricid Pests, their Biology, Natural Enemies and Control. Elsevier Science, Amsterdam [Dordrecht], The Netherlands.
  3. ^ a b c "Out Of Print : Biosystematic Studies of Conifer-Feeding Choristoneura (Lepidoptera Tortricidae) in the Western United States : Edited by Jerry A. Powell - University of California Press". www.ucpress.edu. Retrieved 2017-10-23.
  4. ^ a b c d e Allison, Jeremy D.; Carde, Ring T. (2016-10-25). Pheromone Communication in Moths: Evolution, Behavior, and Application. Univ of California Press. ISBN 9780520964433.
  5. ^ MacLean, David A. (1984). "Effects of Spruce Budworm Outbreaks on the Productivity and Stability of Balsam Fir Forests". The Forestry Chronicle. 60 (5): 273–279. doi:10.5558/tfc60273-5.
  6. ^ Freeman, T.N. 1947. A new generic assignment for Archips fumiferana (Clemens), the spruce budworm. Can. Entomol. 79:21.
  7. ^ Freeman, T.N. 1953. The spruce budworm Choristoneura fumiferana (Clem.) and an allied new species on pine (Lepidoptera: Tortricidae). Can. Entomol. 85:121–127.
  8. ^ Freeman, T.N. 1967. On coniferophagous species of Choristoneura (Lepidoptera: Tortricidae) in North America. I. Some new forms of Choristoneura allied to C. fumiferana. Can. Entomol. 99:449–455.
  9. ^ a b Stehr, G.W. 1967. "On coniferophagous species of Choristoneura (Lepidoptera: Tortricidae) in North America. II. Geographic distribution in accordance with forest regions." Can. Entomol. 99:456–463.
  10. ^ Rowe, J.S. 1959. Forest regions of Canada. Ottawa, Dept. Northern Affairs & National Resources, Forestry Branch. 71 p.
  11. ^ Halliday, W.E.D. 1937. A forest classification for Canada. Can. Dep. Mines and Resources, Dominion For. Serv., Ottawa ON, Bull. 89. 50 p.
  12. ^ a b c Crawford, Hewlette S.; Jennings, Daniel T. (1989). "Predation by Birds on Spruce Budworm Choristoneura Fumiferana: Functional, Numerical, and Total Responses". Ecology. 70 (1): 152–163. doi:10.2307/1938422. JSTOR 1938422.
  13. ^ a b c d e "Forest Pest Fact Sheet" (PDF). Saskatchewan Ministry of Environment.
  14. ^ Swaine, J.M.; Craighead, F.C.; Bailey, J.W. 1924. Studies on the spruce budworm Cacoecia fumiferana Clem. Can. Dep. Agric., Ottawa ON, Tech. Bull. 37 (N.S.).
  15. ^ Balch, R.E.; Webb, F.E.; Morris, R.F. 1954. Results of spraying against spruce budworm in New Brunswick. Can. Dep. Agric., For. Biol. Div., Ottawa ON, Bi-mo. Progr. Rep. 10(1).
  16. ^ a b Blais, J.R. 1958a. Effects of defoliation by spruce budworm (Choristoneura fumiferana (Clem.) on radial growth at breast height of balsam fir (Abies balsamea [L.] Mill.) and white spruce (Picea glauca [Moench] Voss). For. Chron. 34:39–47.
  17. ^ a b Belyea, R.M. 1952. Death and deterioration of balsam fir weakened by spruce budworm defoliation in Ontario. J. For. 50:729–738.
  18. ^ a b Ives, W.G.H.; Wong, H.R. 1988. Tree and shrub insects of the prairie provinces. Gov’t Can., Can. For. Serv., Edmonton AB, Inf. Rep. NOR-X-292. 327 p.[Coates et al. 1994]
  19. ^ a b c Bichon, R. 1995. Canopy population and late instar dispersal of eastern spruce budworm: balsam fir versus white spruce. p. 25 in Carroll, A.L. and Raske, A.G. (Ed./Comp.). Proc. Eastern Spruce Budworm Research Conference, St. John’s NL, April 1994.
  20. ^ Blais, J.R. 1958b. The vulnerability of balsam fir to spruce budworm attack in northwestern Ontario, with special reference to the physiological age of the tree. For. Chron. 34(4):405–422.
  21. ^ Blais, J.R. 1981b. Mortality of balsam fir and white spruce following a spruce budworm outbreak in the Ottawa River watershed in Quebec. Can. J. For. Res. 11(3):620–629.
  22. ^ Blais, J.R.; Archambault, L. 1982. Rating vulnerability of balsam fir to spruce budworm attack in Quebec. Can. For. Serv., Ste.-Foy QC, Inf. Rep. LAU-X-51. 19 p.
  23. ^ Blais, J.R.; Martineau, R. 1960. A recent spruce budworm outbreak in the lower St. Lawrence and Gaspé Peninsula with reference to aerial spraying operations. For. Chron. 36(3):209–224.
  24. ^ a b c d Blais, J.R. 1962. Collection and analysis of radial-growth data from trees for evidence of past spruce budworm outbreaks. For. Chron. 38(4):474–484.
  25. ^ Sutton, R.F. 1982. Plantation establishment in the boreal forest: planting season extension. Can. Dep. Environ., Can. For. Serv., Sault Ste. Marie ON, Inf. Rep. O-X-344. 129 p.
  26. ^ a b Blais, J.R. 1976. Preliminary observations on the vulnerability of white spruce to spruce budworm defoliation in western Quebec. Environ. Can., Can. For. Serv., Ottawa ON, Bi-mo. Res. Notes 32(2):10–11.
  27. ^ Harvey, G.T. 1985. The taxonomy of the coniferophagous Choristoneura (Lepidoptera: Tortricidae): a review. p. 16–48 in Sanders C.J., Stark, R.W., Mullins, E.J.; Murphy, J. (Eds.). Recent Advances in Spruce Budworms Research. CANUSA Spruce Budworms Research Symp. Proc., Bangor ME, Sept. 1984. Can For. Serv./USDA For. Serv., Ottawa ON.
  28. ^ Sippell, W.L. 1983. A review of the spruce budworm and its outbreak history. p. 17–25 in Sanders, C.J.; Carrow, J.R. (Eds.). The spruce budworm problem in Ontario – real or imaginary? Can.–Ont. Joint For. Res. Committee Sympos., Timmins ON, Sept. 1982. COJFRC Sympos. Proc. O-P-11.
  29. ^ a b c d e f g h Royama, T. (1984). "Population Dynamics of the Spruce Budworm Choristoneura fumiferana" (PDF). Ecological Monographs. 54 (4): 429–462. doi:10.2307/1942595. JSTOR 1942595.
  30. ^ McKnight, Melvin E.; Rocky Mountain Forest and Range Experiment Station (Fort Collins, Colo ) (1968). A literature review of the spruce, western, and 2-year-cycle budworms : Choristoneura fumiferana, C. occidentalis, and C. biennis (Lepidoptera: Tortricidae). National Agricultural Library U. S. Department of Agriculture. Fort Collins, Colo. : Rocky Mountain Forest and Range Experiment Station, Forest Service, U.S. Dept. of Agriculture.
  31. ^ Wallace, E. K.; Albert, P. J.; McNeil, J. N. (2004-03-01). "Oviposition Behavior of the Eastern Spruce Budworm Choristoneura fumiferana (Clemens) (Lepidoptera: Tortricidae)". Journal of Insect Behavior. 17 (2): 145–154. doi:10.1023/B:JOIR.0000028565.41613.1a. ISSN 0892-7553. S2CID 26997125.
  32. ^ a b c d Holsten, Ed. "Spruce Budworm" (PDF). U.S. Forest Service.
  33. ^ a b c d e Ives, W.G.H. (1974). "Weather and Outbreaks of the Spruce Budworm, Choristoneura fumiferana (Lepidoptera: Tortricidae)" (PDF). Canada Forestry Service, Department of the Environment.
  34. ^ Sturtevant, Brian R. (2012). "Long-distance dispersal of spruce budworm (Choristoneura fumiferana Clemens) in Minnesota (USA) and Ontario (Canada) via the atmospheric pathway" (PDF). Agricultural and Forest Meteorology. 168: 186–200. doi:10.1016/j.agrformet.2012.09.008.
  35. ^ a b Henry, B.S. 1996. Spruce budworm parasitoid investigations in southern Ontario white spruce plantations. MSc thesis, Univ. Guelph, Guelph ON. 187 p.
  36. ^ a b Delisle, J.; Hardy, M. (1997-08-01). "Male larval nutrition influences the reproductive success of both sexes of the Spruce Budworm, Choristoneura fumiferana (Lepidoptera: Tortricidae)". Functional Ecology. 11 (4): 451–463. doi:10.1046/j.1365-2435.1997.00114.x. ISSN 1365-2435.
  37. ^ Delisle, Johanne; Simard, Jocelyne (2002-02-01). "Factors involved in the post-copulatory neural inhibition of pheromone production in Choristoneura fumiferana and C. rosaceana females". Journal of Insect Physiology. 48 (2): 181–188. doi:10.1016/S0022-1910(01)00162-7. PMID 12770117.
  38. ^ Marcotte, Mireille; Delisle, Johanne; McNeil, Jeremy N. (2005-05-01). "Impact of male mating history on the temporal sperm dynamics of Choristoneura rosaceana and C. fumiferana females". Journal of Insect Physiology. 51 (5): 537–544. doi:10.1016/j.jinsphys.2004.12.009. PMID 15894000.
  39. ^ Campbell, Douglas Kennedy (1953). Ecological factors influencing diapause in the spruce budworm, Choristoneura fumiferana (Clem.). (Tortricidae) (Thesis). University of British Columbia.
  40. ^ a b Landry, Mathieu; Comeau, André M.; Derome, Nicolas; Cusson, Michel; Levesque, Roger C. (2015-12-04). "Composition of the Spruce Budworm (Choristoneura fumiferana) Midgut Microbiota as Affected by Rearing Conditions". PLOS ONE. 10 (12): e0144077. doi:10.1371/journal.pone.0144077. ISSN 1932-6203. PMC 4670206. PMID 26636571.
  41. ^ a b Blais, J.R. 1985. The ecology of the eastern spruce budworm: a review and discussion. p. 49–59 in Sanders C.J.; Stark, R.W.; Mullins, E.J.; Murphy, J. (Eds.). Recent Advances in Spruce Budworms Research. CANUSA Spruce Budworms Research Symp. Proc., Bangor ME, Sept. 1984. Can For. Serv./USDA For. Serv., Ottawa ON.
  42. ^ Blais, J.R. 1961b. Aerial application of insecticides and the suppression of incipient budworm outbreaks. For. Chron. 37(3):203–210.
  43. ^ Blais, J.R. 1981a. Effects of late spring frosts in 1980 on spruce budworm and its host trees in the Laurentian Park region of Quebec. Can. For. Serv., Ottawa, ON. Res. Notes 1(3):16–17.
  44. ^ Luciuk, G.S. 1984. Effect of climatic factors on post-diapause emergence and survival of spruce budworm larvae (Lepidoptera: Tortricidae). Can. Entomol. 116:1077–1083.
  45. ^ Atwood, C.E. 1945. The status of the spruce budworm in Ontario and western Quebec. Entomol. Soc. Ont., 74th Ann. Rep.:52–54.
  46. ^ Blais, J.R. 1968. Regional variation in susceptibility of eastern North American forests to budworm attack based on history of outbreaks. For. Chron. 44(3):17–23 [reprint, separate pagination].
  47. ^ Blais, J.R. 1961a. Spruce budworm outbreaks in the lower St. Lawrence and Gaspé regions. For. Chron. 37(3):192–202.
  48. ^ Blais, J.R. 1965. Spruce budworm outbreaks in the past three centuries in the Laurentide Park, Quebec. For. Sci. 11(2):130–138.
  49. ^ Turner, K.B. 1952. The relation of mortality of balsam fir caused by the spruce budworm to forest composition in the Algoma forest of Ontario. Can. Dep. Agric., Ottawa ON, Publ. 875. 107 p.
  50. ^ Rose, A.H.; Lindquist, O.H. 1985. Insects of eastern spruces, fir and, hemlock, revised edition. Gov’t Can., Can. For. Serv., Ottawa, For. Tech. Rep. 23. 159 p. (cited in Coates et al. 1994, cited orig ed 1977)
  51. ^ Miller, C.A.; Renault, T.R. 1976. Incidence of parasitoids attacking endemic spruce budworm (Lepidoptera: Tortricidae) populations in New Brunswick. Can. Ent. 108:1045–1052.
  52. ^ Blais, J.R. 1980. Condition du sapin et de l’épineete blanche dans la région du parc des Laurentides en 1979 face à l’épidémic de al tordeuse et prévision des peretes. Can. ^^^, Laurentian For. Res. Centre, Ste.-Foy QC, Inf. Rep. LAU-X-43. 16 p.
  53. ^ Brown, R.G. 1971. Spruce budworm in British Columbia. Can. Dep. Environ., Can. For. Serv., Victoria BC, For. Insect & Disease Survey, Pest Leaflet 31. 4 p.
  54. ^ Reeks, W.A.; Barter, G.W. 1951. Growth reduction and mortality of spruce caused by the European spruce sawfly Gilpinia hercyniae (Hymenoptera: Diprionidae). For. Chron. 27(2):140–156.
  55. ^ Blais, J.R. 1954. The recurrence of spruce budworm infestations in the past century in the Lac Seul area of northwestern Ontario. Ecology 35:62–71.
  56. ^ a b MacDonald, D.R. 1968. Management of spruce budworm populations. For. Chron. 44(3):33–36 (separate pagination).
  57. ^ Smith, S.M.; Hubbes, M.; Carrow, J.R. 1986. Factors affecting inundative releases of Trichogramma minutum Ril. against the spruce budworm. J. Appl. Entomol. 101(1):29–39.
  58. ^ "Predators of the Spruce Budworm". Spruce Budworms Handbook. November 1985.
  59. ^ Hummel, Hans E.; Miller, Thomas A. (2012-12-06). Techniques in Pheromone Research. Springer Science & Business Media. ISBN 9781461252207.
 
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