Predation by Carpenter Ants: a Deterrent to the Spread of Cinnabar Moth

Total Page:16

File Type:pdf, Size:1020Kb

Predation by Carpenter Ants: a Deterrent to the Spread of Cinnabar Moth J . E1'T()\I(11. S()C lil( l T COI.lI \IIlI.\ 73 (19761. D,·:(' :3 1. 1976 7 Literature Cited Il odl·k. I. 197:L Hi olog.v of Coccin ellid ae. Junk. The Hague. 260 p. Kapur. A.D. 1942. Bionomics of some Coccinellidae, predaceous on a phids and coccids in North India. lnd. J. Entomol. 4: 49-56. Kulman. H. :V1. 197 1. Parasitism of Anatis quindeei l11J)unl'tal a bv lIom alol)·lw.; krminalis. Ann. Entomol. Soc. Amer. 641 11:953-54. Leonard . 'VI. D. 193:1. A braconid parasit e of a Coccinelli d new in Puerto Hie o. ,J. F:con . 1·: n LO mol. :!1i:294 "Iiller. n. L . and W . L. Thompson. 1926. Life histories of Lady-beetle predaLOr s of the citrus iJphid. FloridiJ Entomol. 111: 40-46.57-:19. Miller. R. L. and W. L. Thompson. 1927. Life histories of Lady-beetle predators of t he citrus aphid. Florida Entomol. II : 1-18. \lueslwck. C. F. W .. K. V. Krombein and H. K. Townes. 19:) 1. Hvmenoptera of America "Iorlh of Mexico. U.S.D.A. agr. Monograph 2. 1~ 20 p. Peck. O. 1963. A catalogue of the Nearctic Chalcid oidae (I nsecta: H"menopteriJ I. Can. ~ : nt oll1o l. Suppl. 30. 1092 p. PREDATION BY CARPENTER ANTS: A DETERRENT TO THE SPREAD OF CINNABAR MOTH JUDITH H. MYERS AND BARBARA J. CAMPBELL Institute of Animal Resource Ecology and Department of Plant Science University of British Colu mbia. Vancouver ABSTRACT Cinnabar moth, an introduced biological cont rol agent for tansy ragwort. suffers heavy predation by carpenter ants in recently logged areas of Oregon. We suggest that t his mortality factor wi ll reduce the spread of Cin­ nabar moth, t hus preventing it from attacking a major seed source of tansy ragwort and reducing its potential as a biological control agent. Single larvae escape predation by ants more often than those in groups which suggests that carpenter ant predation may select for larval dispersal. The Cinnabar moth, Tyria jacobaeae L. alienus. a predaceous ant. Further studies of 1Arctiidae). has been widely spread from its Lasius predation led Van der Meijden (1973) to native E urope because of its potential as a conclu de that this ant may limi t Ci nnabar biological control agent against the weed Tansy numbers in some sand dune areas of t he Neth­ ragwort, Senecio jacobaea L. The success of erlands. these in troductions has ranged from "never The following observations on predation by seen again" to "abundant and thriving" a fter ants were made as a by-product of experiments 15 years. At Abbotsford, B.C. the failure of the designed to investigate larval dispersal in the first releases was attributed to heavy predation Ci nnabar moth. by ground beetles 1Wilkinson , 1965). In the Gippsland vicinity of Victoria, Australia a Study Area and Methods mecopteran, Harpobittacus nigriceps. heavily The study was carried out in Linn County , predated a newly introduced Cinnabar popula­ Oregon which lies between t he western slope of tion and a nuclear polyhedral virus assured the t he Cascade Mountains and the eastern edge of failure of the attempted in troduction (Borne­ the Will amette Va lley. Larvae were collected missza, 1966). The causes for the lack of from the Silbernagel population which was success of other introductions are not known studied by Isaacson 11973). and were trans­ (Hawkes. 1968, Harris et al. 1975, fsaacson ported to an area about 10 miles to the south on 1973). Neal Creek Road. This area was logged within Van der Meijden (197 1) records an almost the last 10 years so that stumps and fallen logs perfect correlation between the log % mortality were abundant on the steep hillsides. Tansy of Cinnabar larvae and log density of Lasius ragwort is a common component of t he herb- 8 J. ENT()\IOL Soc BIUT CO!'U\1IlIA 73 (19761. DF:c 31. 1976 TABLE 1. Survival after 2 days of 3rd and 4th instar Cinn'abar larvae introduced to tansy ragwort plants in groups of approximately 20 individuals. Percent Survival 0-10% 11 -25% 40% 65% 80-90% Frequency 8 ::l 2 1 3 Total Survival = 98/ 329=30% aceous vegetation which has invaded this area, Results and moth populations occur sporadically along The disappearance rate of larvae from tansy the road. ragwort plants was exceedingly high (Table 11. We chose the particular site for the study Observations revealed that the reason for this because while abundant, large ragwort plants disappearance was the activity of carpenter occurred there, Cinnabar moth larvae were ants, Camponotlls sp., which nested in sur- lacking. We placed third and fourth instar rounding stumps. Ants were seen to attack and larvae on plants in groups of approximately 20 carry off the Cinnabar moth caterpillars but individuals, and recorded their movement from to verify t hat t he high rate of disappearance the central plant to surrounding plants. was due to ant predation we set up groups of TABLE 2. A comparison of Cinnabar larval survival on tansy ragwort plants to which ants had access and those which were ant-free. Larvae placed on plants in groups of 10. Plants Without Ants Plants With Ants Original Number 49 40 Number After 2 Days 43 9 Percent Survival 86 23 larvae on plants with the base coated with Discussion "stickum" which prevented ants from crawling The relationship of the carpenter ant to the onto the plants. The comparative rates of dis­ Cinnabar larvae is an interesting one. The appearance of larvae on ant-free plants and Cinnabar larvae feed preferent ially at the tops those to which ants had access are compared in of the plants on the flower buds. Their feeding Table 2. activity re leases sap a nd t he carpe n ter a nLs will feed beside the caterpillars taking t he sap We observed that those Cinnabar larvae from the freshly cut surface. The t wo species which dispersed from the original plant had have been observed to coexist in this way. better short term survival than those which re- However, suddenly an ant may attack a cater- mained behind (Table 31. The effect of group pillar. The usual result is that the caterpillar size was further tested by comparing the sur- falls from the plant, sometimes taking its vival of single larvae to those in groups of 10. attacker with it . If other ants are nearby t hey While the survival of these individual larvae too will join in the attack. On one occasion wa s net as high as that of the natural dis- eight larvae lived two days on a plant that was persers (Table 3), it was almost double that of occasionally visited by ants. Suddenly t he larvae in groups of 10 (Table 2) ave! a 2 day attack began, and within one hour only t hree observation period. remained the others having been carried off TABLE :3. Survival after 2 days of Cinnabar larvae which dispersed nat uraliy from original tansy ragwort plants or were placed individually on plants. Larvae Larvae Placed Dispersed On Individual Naturally Plants Original Number 10 31 Number After 2 Days 9 13 Percent Survival 90 42 ,1. E:->Tm l{l l.. Soc Burr C() 1.II ~ IH 1.· \ 73 (1976). DI':C 3 1. 1976 9 by the carpenter ants. a situation in which dispersal of Cinnabar Tansy ragwort is common in Oregon on the larvae could be at a strong selective advantage. extensively logged slopes of the Cascades and The general interpretation has been that in of the Coastal mountains to the West. Although areas of high predation. survival of dispersing in many areas Cinnabar moths have become larvae will be low (Green. 1974). However. a l­ established (Nagel and Isaacson. 1974) the though larvae are exposed to predation while presence of carpenter ants in this environment traversing from one plant to another. aban­ will undoubtedly influence the success of the donment of the usual clumped distribution of natural spread of the moth to tansy ragwort Cinnabar moth larvae might make the areas. This wi ll interfere with the attempt to difference between success and failure of estab­ destroy t he source for tansy ragwort seed li shment. If there is a genetic component to which these areas provide. dispersal one might predict strong selection for Predation by carpenter ants gives rise to dispersal in these areas. References Bornemissza. G. F . 1966. An attempt to control ragwort in Australia with the Cinnabar Moth. Callimorpha jacobaeae (L.) (Arctiidae: Lepidoptera). Australian J. of Zoology 14 : 201-243. Green. W. Q. 1974. An antagoni stic insect/host-plant system: The problem of persistence. Ph.D. t hesis. University of British Columbia. Hawkes. R. B. 1968. The Cinnabar moth, Tyria jacobaeae. for control of tansy ragwort. J. econ. Ent.61:499-501. Harris, P .. A. T. S. Wilkinson. M. E. Neary . L. S. Thompson, and D. Finnamore. 1975. Establish­ ment in Canada of the Cinnabar Moth. Tyria jacobaeal' (Lepidoptera: Arctiidae) for con­ t rolling t he weed Se nec io jaco baea. Can. E nt. 107 :913-9 17. Isaacson, D. L. 1973. A life table for the Cinnabar Moth, Tyria jacobaeae. in Oregon. Entomophaga 18: 29 1-303. Nagel. W . D. and D. L. Isaacson. 1974. Tyria jacobaeae and tansy ragwort in Western Oregon. J. econ. Ent. 67: 494-496. Van der Meijden. E. 1971. Sl' necio and Tyria (Callimorpha) in a Dutch dune area. A study on an interaction between a monophagous consumer and its host plant.
Recommended publications
  • Effect of Diet on Larval Development, Adult Emergence and Fecundity of the Cinnabar Moth, Tyria Jacobaeae (L.) (Lepidoptera: Arctiidae)
    AN ABSTRACT OF THE THESIS OF Sharon Diane Rose for the degree of Master of Science in Entomology presented on January 1978 Title: Effect of Diet on Larval Development, Adult Emergence and Fecundity of the Cinnabar Moth, Tyria jacobaeae (L.) (Lepidoptera: Arctiidae) Abstract approved: Redacted for privacy Dr. N. H. Anderson The cinnabar moth, Tyria jacobaeae (L.), is a biological control agent introduced in Oregon against the weed tansyragwort, Senecio jacobaea L. Goals of this research were: to determine if there exists significant variation in progeny of different cinnabar moth egg masses; to determine if (and how) rearing on different ragwort diets affects larval growth and subsequent adult emergence and fecundity;to investigate adult mating behavior; and to refine rearing techniques. Tansy ragwort diets used in this research include: leaves from first-year rosettes, leaves from second-year flowering plants, leaves from shade-grown plants, floral parts, and a mixture of the four preceeding diets. All larvae were reared in a growth chamber with photoperiod 12/12 and temperature 23.9° C. Mating pairs and ovipositing females were housed at photoperiod 14/10 and thermoperiod 23.90/100 C. Female and male pupae reared on the floral diet are significantly larger than those reared on the shade-leaf diet. Adults reared on the floral diet emerge significantly later than those rearedon the other four diets. Female moths reared on the floral, mixture and second-year leaf diets lay significantly more eggs than those rearedon the shade- leaf diet. Ranking diets by decreasing fecundity yields: floral, second-year leaves, mixture, first-year leaves, and shade-grown leaves.
    [Show full text]
  • Feeding, Colonization and Impact of the Cinnabar Moth, Tyria Jacobaeae
    AN ABSTRACT OF THE THESIS OF Jonathan W. Diehl for the degree of Master of Science in Entomology presented on May 20, 1988. Title: Feeding, Colonization and Impact of the Cinnabar Moth Tyria jacobaeae, on Senecio triangularisa Novel, Native Host Plant Abstract Redacted for privacy approved: Peter B. McEvoy I conducted field and laboratory studies to determine the impact of the cinnabar moth, Tvria jacobaeae L., on the native perennial herb, Senecio triangularis Hook. The cinnabar moth was introduced into Oregon in 1960 to control the noxious weed Senecio iacobaea L. and is now well established on both the native plant and the weed in Oregon. My objectives were to determine the suitability of S. triangularis as a diet for the cinnabar moth, to estimate the frequency with which the moths colonize the native plant in the field, and to estimate the impact of larval feeding on the plant's survivorship and reproduction. Larvae successfully completed development on S. triangularis, but development time was longer, growth was slower, and pupae were lighter compared to performance on S. iacobaea. Cinnabar moth colonization and feeding damage were concentrated at one of the four study sites observed. Cinnabar moth defoliation results in a 3.9% reduction in seed viability and is inversely related to damage to seeds by native insects. I conclude that cinnabar moths commonly discover this native plant in the field, can establish and develop on it, and cause a small reduction in plant reproductive success. Feeding, Colonization and Impact of the Cinnabar Moth, Tvria iacobaeae, on Senecio triangularis, a Novel, Native Host Plant by Jonathan W.
    [Show full text]
  • Habitat and Corridor Function of Rights- Of-Way Marcel P. Huijser & Anthony
    233 CHAPTER 11: HABITAT AND CORRIDOR FUNCTION OF RIGHTS- OF-WAY MARCEL P. HUIJSER & ANTHONY P. CLEVENGER Western Transportation Institute – Montana State University, PO Box 174250, Bozeman, MT 59717-4250, USA. 1. Introduction Roads, railroads and traffic can negatively affect plants, animals and other species groups (see reviews in Forman & Alexander 1998; Spellerberg 1998; van der Grift 1999). Transportation induced habitat loss, habitat fragmentation, reduced habitat quality and increased animal mortality can lead to serious problems for certain species or species groups, especially if they also suffer from other human-related disturbances such as large scale intensive agriculture and urban sprawl (Mader 1984; Ewing et al. 2005). Some species may even face local or regional extinction. However, other species or species groups can benefit from the presence of transportation infrastructure. Depending on the species and the surrounding landscape, the right-of-way can provide an important habitat or their only remaining functional habitat in the surrounding area. Rights-of-way may also serve as corridors between key habitat patches. The habitat and corridor function of rights-of-way can help improve the population viability of meta-populations of certain species in fragmented landscapes. This chapter aims to illustrate the habitat and corridor function of rights-of-way. While our focus is on roads, we include some examples of ecological benefits of railroads and railroad rights-of-way. For this chapter we define the term “right-of-way” as the area between the edge of the road surface, which is usually asphalt, concrete or gravel, and the edge of the area that is not owned or managed by the transportation agency.
    [Show full text]
  • Non-Native Plants and Wildlife in the Intermountain West
    Wildlife Society Bulletin; DOI: 10.1002/wsb.306 Invasive Plants and Wildlife Habitat Non-Native Plants and Wildlife in the Intermountain West ANDREA R. LITT,1 Department of Ecology, Montana State University, P.O. Box 173460, Bozeman, MT 59717, USA DEAN E. PEARSON, Rocky Mountain Research Station, 800 E Beckwith Avenue, Missoula, MT 59801, USA; and Division of Biological Sciences, University of Montana, Missoula, MT 59812, USA ABSTRACT Non-native plant invasions can change communities and ecosystems by altering the structure and composition of native vegetation. Changes in native plant communities caused by non-native plants can influence native wildlife species in diverse ways, but the outcomes and underlying mechanisms are poorly understood. Here, we review and synthesize current information for the Intermountain West of the United States, to develop a general mechanistic understanding of how invasions by non-native plants affect wildlife, and we identify important information gaps. In this region, most species of recognized conservation and management concern are non-native forbs (e.g., leafy spurge [Euphorbia esula], spotted knapweed [Centaurea stoebe]), although non-native grasses (e.g., cheatgrass [Bromus tectorum], medusahead [Taeniatherum caput- medusae]) also have greatly altered vegetation communities. These invasions by non-native plants affect native fauna through both trophic and non-trophic (habitat) pathways and via both direct and indirect effects. The degree to which these invasions affect wildlife depends largely on the degree to which non-native plants alter form and function of native vegetation communities. Reciprocally, native animals can influence distribution and abundance of non-native plants by facilitating or inhibiting invasions through herbivory, seed predation, seed dispersal, soil disturbance, and pollination.
    [Show full text]
  • And the Ragwort Flea Beetle (Longitarsus Jacobaeae) on Ragwort (Senecio Jacobaea)
    -44-sratit-E-irr :44U:::;4.4% Journal of Applied Ecology Combining the cinnabar moth (Tyriajacobaeae) and the 1992, 29, ragwort flea beetle (Longitarsus jacobaeae) for control 589-596 of ragwort (Seneciojacobaea): an experimental analysis R.R. JAMES, P.B. McEVOY and C.S. COX Department of Entomology, Oregon State University, Corvallis, Oregon 97331-2907, USA Summary A field experiment tested the independent and combined effects of the cinnabar moth (Tvria jacobaeae) and the ragwort flea beetle (Longitarsus jacobaeae) on ragwort (Senecio jacobaea). These insect herbivores feed on different stages of the host-plant and at different times of the year and were introduced to North America as biological control agents. Flea beetles alone were found to reduce vegetative ragwort densities b y 95%, and flower production by 39%, as compared to plants in control plots. Damage by cinnabar moths was simulated by removing all leaves and capitula from generative plants, but plants were able to regenerate some of the foliage and flowers. The treatment ultimately reduced capitulum production by 77% and the number of achenes per capitulum by 15%. Flea beetle damage was found to reduce the ability of flowering plants to compensate for defoliation and defloration to the extent that capitulum production was reduced by 98% and no viable achenes were produced. 3. These findings support the strategy of introducing complementary enemies which attack different stages and at different times, thereby reducing the number of invulnerable life stage and temporal refuges for the host. Key-words: biological control, weeds, insects, single vs. multiple enemy introductions. Journal of Applied Ecology (1992) 29, 589-596 and after the introduction of biological control agents Introduction (Dodd 1940; Huffaker Kennett 1959; Hawkes In the practice of biological control, several different Johnson 1978; Cullen 1978; McEvoy 1985).
    [Show full text]
  • Lepidoptera: Arctiidae), and Potential for Biological Control of Senecio Madagascariensis (Asteraceae) M
    J. Appl. Entomol. Host range of Secusio extensa (Lepidoptera: Arctiidae), and potential for biological control of Senecio madagascariensis (Asteraceae) M. M. Ramadan1, K. T. Murai1 & T. Johnson2 1 State of Hawaii Department of Agriculture, Plant Pest Control Branch, Honolulu, Hawaii, USA 2 Institute of Pacific Islands Forestry, Pacific Southwest Research Station, USDA Forest Service, Volcano, Hawaii, USA Keywords Abstract Host range, Secusio extensa, Senecio madagascariensis Secusio extensa (Lepidoptera: Arctiidae) was evaluated as a potential bio- logical control agent for Madagascar fireweed, Senecio madagascariensis Correspondence (Asteraceae), which has invaded over 400 000 acres of rangeland in the Mohsen M. Ramadan (corresponding author), Hawaiian Islands and is toxic to cattle and horses. The moth was intro- State of Hawaii Department of Agriculture, duced from southeastern Madagascar into containment facilities in Plant Pest Control Branch, 1428 South King Hawaii, and host specificity tests were conducted on 71 endemic and Street, Honolulu, Hawaii 96814, USA. E-mail: [email protected] naturalized species (52 genera) in 12 tribes of Asteraceae and 17 species of non-Asteraceae including six native shrubs and trees considered key Received: September 15, 2009; accepted: components of Hawaiian ecosystems. No-choice feeding tests indicated April 6, 2010. that plant species of the tribe Senecioneae were suitable hosts with first instars completing development to adult stage on S. madagascariensis doi: 10.1111/j.1439-0418.2010.01536.x (78.3%), Delairea odorata (66.1%), Senecio vulgaris (57.1%), Crassoceph- alum crepidioides (41.2%), and at significantly lower rates on Emilia fos- bergii (1.8%) and Erechtites hieracifolia (1.3%). A low rate of complete larval development also was observed on sunflower, Helianthus annuus (11.6%), in the tribe Heliantheae.
    [Show full text]
  • Classical Biological Control of Invasive Legacy Crop Pests: New Technologies Offer Opportunities to Revisit Old Pest Problems in Perennial Tree Crops
    Insects 2015, 6, 13-37; doi:10.3390/insects6010013 OPEN ACCESS insects ISSN 2075-4450 www.mdpi.com/journal/insects/ Review Classical Biological Control of Invasive Legacy Crop Pests: New Technologies Offer Opportunities to Revisit Old Pest Problems in Perennial Tree Crops Mark S. Hoddle 1,†,*, Keith Warner 2,†, John Steggall 3,† and Karen M. Jetter 4,† 1 Department of Entomology, University of California, Riverside, CA 92521, USA 2 Center for Science, Technology, and Society, Santa Clara University, CA 95053, USA; E-Mail: [email protected] 3 California Department of Food and Agriculture, Sacramento, CA 95814, USA; E-Mail: [email protected] 4 UC Agricultural Issues Center, University of California, Davis, CA 95616, USA; E-Mail: [email protected] † These authors contributed equally to this work. * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel.: +1-951-827-4714; Fax: +1-951-827-3086. Academic Editor: Michael J. Stout Received: 11 November 2014 / Accepted: 13 December 2014 / Published: 23 December 2014 Abstract: Advances in scientific disciplines that support classical biological control have provided “new tools” that could have important applications for biocontrol programs for some long-established invasive arthropod pests. We suggest that these previously unavailable tools should be used in biological control programs targeting “legacy pests”, even if they have been targets of previously unsuccessful biocontrol projects. Examples of “new tools” include molecular analyses to verify species identities and likely geographic area of origin, climate matching and ecological niche modeling, preservation of natural enemy genetic diversity in quarantine, the use of theory from invasion biology to maximize establishment likelihoods for natural enemies, and improved understanding of the interactions between natural enemy and target pest microbiomes.
    [Show full text]
  • Chapter 12. Biocontrol Arthropods: New Denizens of Canada's
    291 Chapter 12 Biocontrol Arthropods: New Denizens of Canada’s Grassland Agroecosystems Rosemarie De Clerck-Floate and Héctor Cárcamo Agriculture and Agri-Food Canada, Lethbridge Research Centre 5403 - 1 Avenue South, P.O. Box 3000 Lethbridge, Alberta, Canada T1J 4B1 Abstract. Canada’s grassland ecosystems have undergone major changes since the arrival of European agriculture, ranging from near-complete replacement of native biodiversity with annual crops to the effects of overgrazing by cattle on remnant native grasslands. The majority of the “agroecosystems” that have replaced the historical native grasslands now encompass completely new associations of plants and arthropods in what is typically a mix of introduced and native species. Some of these species are pests of crops and pastures and were accidentally introduced. Other species are natural enemies of these pests and were deliberately introduced as classical biological control (biocontrol) agents to control these pests. To control weeds, 76 arthropod species have been released against 24 target species in Canada since 1951, all of which also have been released in western Canada. Of these released species, 53 (70%) have become established, with 18 estimated to be reducing target weed populations. The biocontrol programs for leafy spurge in the prairie provinces and knapweeds in British Columbia have been the largest, each responsible for the establishment of 10 new arthropod species on rangelands. This chapter summarizes the ecological highlights of these programs and those for miscellaneous weeds. Compared with weed biocontrol on rangelands, classical biocontrol of arthropod crop pests by using arthropods lags far behind, mostly because of a preference to manage crop pests with chemicals.
    [Show full text]
  • By the Cinnabar Moth, Tyria Jacobaeae (CL) (Lepidoptera: Arctiidae), in the Northern Rocky Mountains
    Biological control of tansy ragwort (Senecio jacobaeae, L.) by the cinnabar moth, Tyria jacobaeae (CL) (Lepidoptera: Arctiidae), in the northern Rocky Mountains G.P. Markin1 and J.L. Littlefield2 Summary The control of tansy ragwort on the coast of western North America is a major success story for weed biological control. However, tansy ragwort is still expanding into the colder interior regions of the Pacific Northwest of the United States where previous efforts to establish the same complex of agents have failed. We have successfully established one of the agents, the cinnabar moth, Tyria jacobaeae L., on a major new tansy ragwort infestation in the mountains of northwestern Montana. The cinnabar moth is still expanding its range, but in the areas where first released, it has given excellent control, having eliminated tansy ragwort as a visible component in the forest ecosystem while not impacting native Senecio species. Although establishment in other areas has been slower, we predict that we will eventually control tansy ragwort over most of its range in the northern Rocky Mountains of the United States. Keywords: tansy ragwort, Senecio jacobaea, cinnabar moth, Tyria jacobaeae. Introduction Mountains into eastern Oregon, Washington and north- ern Idaho. In the Pacific Northwest corner of the United States, In 1994, a wild fire burned 6100 ha of fir and pine tansy ragwort, Senecio jacobaea L., (Asteraceae), an forests in a mountainous area straddling the boundary introduced European forb, is an invasive weed in pas- between Lincoln and Flathead Counties in northwestern tures, native meadows and open forests (Coombs et al., Montana. Tansy ragwort was probably already present, 1991, 1999).
    [Show full text]
  • From Plant Exploitation to Mutualism
    From Plant Exploitation to Mutualism. Chapter 3 François Lieutier, Kalina Bermudez-Torres, James Cook, Marion O. Harris, Luc Legal, Aurélien Sallé, Bertrand Schatz, David Giron To cite this version: François Lieutier, Kalina Bermudez-Torres, James Cook, Marion O. Harris, Luc Legal, et al.. From Plant Exploitation to Mutualism. Chapter 3. Nicolas Sauvion, Denis Thiéry, Paul-André Calatayud. Insect-Plant Interactions in a Crop Protection Perspective, 81, 2017, Advances in Botanical Research, 978-0-12-803318-0. hal-02318872 HAL Id: hal-02318872 https://hal.archives-ouvertes.fr/hal-02318872 Submitted on 1 May 2020 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. VOLUME EIGHTY ONE ADVANCES IN BOTANICAL RESEARCH Insect-Plant Interactions in a Crop Protection Perspective Volume Editor NICOLAS SAUVION INRA,UMR BGPI 0385 (INRA-CIRAD-SupAgro), Montpellier, France DENIS THIERY INRA, UMR SAVE 1065, Bordeaux Sciences Agro, Centre INRA de recherches de Bordeaux- Aquitaine, Institut des Sciences de la Vigne et du Vin, Villenave d’Ornon, France PAUL-ANDRE CALATAYUD IRD UMR EGCE (Evolution, Génome, Comportement, Ecologie), CNRS-IRD-Univ. Paris-Sud, IDEEV, Université Paris-Saclay, Gif-sur-Yvette, France; IRD c/o ICIPE, Nairobi, Kenya Academic Press is an imprint of Elsevier 125 London Wall, London EC2Y 5AS, United Kingdom The Boulevard, Langford Lane, Kidlington, Oxford OX5 1GB, United Kingdom 50 Hampshire Street, 5th Floor, Cambridge, MA 02139, United States 525 B Street, Suite 1800, San Diego, CA 92101-4495, United States First edition 2017 Copyright Ó 2017 Elsevier Ltd.
    [Show full text]
  • Systematic List of the Noctuoidea of Europe (Notodontidae, Nolidae, Arctiidae, Lymantriidae, Erebidae, Micronoctuidae, and Noctuidae)
    Esperiana Buchreihe zur Entomologie Bd. 11: 93-205 Schwanfeld, 29. Juni 2005 ISBN 3-938249-01-3 Systematic List of the Noctuoidea of Europe (Notodontidae, Nolidae, Arctiidae, Lymantriidae, Erebidae, Micronoctuidae, and Noctuidae) Michael FIBIGER and Hermann H. HACKER Superfamily NOCTUOIDEA LATREILLE, 1809 Remarks to Classification In the European List of Noctuidae (FIBIGER and HACKER, 1991) we refrained from writing a justification for subdividing the family into subfamilies and tribes. Our understanding of the classification of the family has progressed since then, but only to some extent therefore several paraphyletic or even polyphyletic groupings still remain in the Noctuidae (s.l.) and in the other families dealt with here. Most of the tribes listed here are monophyletic and we believe that most of them will stand the test of time. In groups where research is lasting, we refer to the latest knowledge available. For example the family Noctuidae has now been divided into three families, the Noctuidae, Micronoctuidae and Erebidae, these corresponding roughly to the groups previously called “quadrifid“ and “trifid“ noctuids. Ongoing research, however, suggests that the arctiid clade might be derived from within the Erebidae (WELLER and MITCHELL, pers. com.). Other important results have been published in the last 13 years, some of which are: KITCHING and RAWLINS (in KRISTENSEN, 1998); KITCHING and YELA (1999); SPEIDEL, FÄNGER and NAUMANN (1996); SPEIDEL and NAUMANN (1996); POOLE (1995, and his catalogue from 1989); the North American Moths of North America (MONA) book series: LAFONTAINE and POOLE (1991), POOLE (1995), LAFONTAINE (1998, 2004); BECK (1996, 1999, 2000); the volumes of the book series Noctuidae Europaeae (1990-2003); and many papers in Esperiana.
    [Show full text]
  • Butterflies and Moths of Pacific Northwest Forests and Woodlands: Rare, Endangered, and Management- Sensitive Species
    he Forest Health Technology Enterprise Team (FHTET) was created in 1995 by the Deputy Chief for State and Private TForestry, USDA Forest Service, to develop and deliver technologies to protect and improve the health of American forests. This book was published by FHTET as part of the technology transfer series. http://www.fs.fed.us/foresthealth/technology/ United States Depart- US Forest US Forest Service ment of Agriculture Service Forest Health Technology Enterprise Team Cover design Chuck Benedict. Photo, Taylor’s Checkerspot, Euphydryas editha taylori. Photo by Dana Ross. See page 38. For copies of this publication, contact: Dr. Jeffrey C. Miller Richard Reardon Oregon State University FHTET, USDA Forest Service Department of Rangeland Ecology 180 Canfield Street and Management Morgantown, WV 26505 202 Strand Agriculture Hall 304-285-1566 Corvallis, Washington, USA [email protected] 97331-2218 FAX 541-737-0504 Phone 541-737-5508 [email protected] The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, sex, religion, age, disability, political beliefs, sexual orientation, or marital or family status. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program informa- tion (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at 202-720-2600 (voice and TDD). To file a complaint of discrimination, write USDA, Director, Office of Civil Rights, Room 326-W, Whitten Building, 1400 Inde- pendence Avenue, SW, Washington, D.C. 20250-9410 or call 202-720-5964 (voice and TDD).
    [Show full text]