Comparison of moth communities following clear-cutting and wildfire disturbance in the southern boreal forest

Nocturnal macrolepidopteran fauna (moths) of the southern boreal forest of Ontario, Canada, were compared between forests clear-cut or burned by wildfire approximately 5. years previously to assess whether their assemblages differed following disturbance. Moths were light-trapped for 27. days during...

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Autor principal: Chaundy-Smart, R.F.C
Otros Autores: Smith, S.M, Malcolm, J.R, Bellocq, M.I
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Publicado: 2012
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100 1 |a Chaundy-Smart, R.F.C. 
245 1 0 |a Comparison of moth communities following clear-cutting and wildfire disturbance in the southern boreal forest 
260 |c 2012 
270 1 0 |m Smith, S.M.; Faculty of Forestry, University of Toronto, 33 Willcocks St., Toronto, ON, M5S 3B3, Canada; email: s.smith.a@utoronto.ca 
506 |2 openaire  |e Política editorial 
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520 3 |a Nocturnal macrolepidopteran fauna (moths) of the southern boreal forest of Ontario, Canada, were compared between forests clear-cut or burned by wildfire approximately 5. years previously to assess whether their assemblages differed following disturbance. Moths were light-trapped for 27. days during the summer in three burned and three clear-cut sites that had been formerly mature mixed jack pine (Pinus banksiana) forest. The dominant species varied throughout the summer (Protorthodes oviduca dominated in June, Orthodes cynica in July and Idia americalis in August), but they were similar between disturbance types. Diversity indices were similar although ordinations showed significant differences between the two disturbance types. Nine species were more significantly abundant in burn than clear-cut sites (Callopistra cordata, Cyclophora pendulinaria, Gluphisia septentrionis, Hyppa nr. xylinoides, Nemoria rubrifrontaria, Semiothisa neptaria, Spiramater lutra, and Tacparia detersata), whereas the converse was true for three species (Acronicta innotata, Phyllodesma Americana, and Euxoa comosa). Vegetation composition, disturbance age, percentage of jack pine pre-disturbance, and amount of downed woody debris and snags were the most important environmental correlates of moth community composition. Our study supports that of previous work on the effects of forest disturbance and biodiversity suggesting that clear-cutting may emulate wildfire for some organisms, but not for others. Thus, forest managers must consider multiple aspects of forest structure in attempting to use clear-cuts to mimic fire. © 2011 Elsevier B.V.  |l eng 
536 |a Detalles de la financiación: University of Toronto, UofT 
536 |a Detalles de la financiación: Ministry of Natural Resources 
536 |a Detalles de la financiación: We thank D. Lafontaine (noctuids and other families) and K. Bolte (geometrids) of the Canadian National Collection, Ottawa for providing species verification and retaining voucher specimens. Also, thanks to T. Carleton (Forestry, University of Toronto) for statistical help and T. Scarr (Ontario Ministry of Natural Resources) for financial support. We would also like to thank S. Baker and an anonymous reviewer for their comments on an earlier version of the manuscript. Appendix A 
593 |a Faculty of Forestry, University of Toronto, 33 Willcocks St., Toronto, ON, M5S 3B3, Canada 
593 |a Departamento de Ecología, Genética y Evolución, FCEN - Universidad de Buenos Aires, CONICET, Ciudad Universitaria, Pab 2, piso 4, 1426 Buenos Aires, Argentina 
690 1 0 |a BOREAL FOREST 
690 1 0 |a CLEAR-CUTTING 
690 1 0 |a DISTURBANCE 
690 1 0 |a JACK PINE 
690 1 0 |a MOTHS 
690 1 0 |a WILDFIRE 
690 1 0 |a BOREAL FORESTS 
690 1 0 |a CLEAR-CUTTING 
690 1 0 |a DISTURBANCE 
690 1 0 |a JACK PINE 
690 1 0 |a MOTHS 
690 1 0 |a WILDFIRE 
690 1 0 |a BIODIVERSITY 
690 1 0 |a DEBRIS 
690 1 0 |a FIRES 
690 1 0 |a VEGETATION 
690 1 0 |a FORESTRY 
690 1 0 |a ABUNDANCE 
690 1 0 |a BOREAL FOREST 
690 1 0 |a CLEARCUTTING 
690 1 0 |a COMMUNITY COMPOSITION 
690 1 0 |a COMPARATIVE STUDY 
690 1 0 |a CONIFEROUS FOREST 
690 1 0 |a DIVERSITY INDEX 
690 1 0 |a ENVIRONMENTAL DISTURBANCE 
690 1 0 |a MOTH 
690 1 0 |a SNAG 
690 1 0 |a WILDFIRE 
690 1 0 |a WOODY DEBRIS 
690 1 0 |a ONTARIO [CANADA] 
690 1 0 |a ACRONICTA INNOTATA 
690 1 0 |a CYCLOPHORA PENDULINARIA 
690 1 0 |a EUXOA 
690 1 0 |a GLUPHISIA SEPTENTRIONIS 
690 1 0 |a HYPPA 
690 1 0 |a LEPIDOPTERA 
690 1 0 |a LUTRA 
690 1 0 |a MACROLEPIDOPTERA 
690 1 0 |a NEMORIA RUBRIFRONTARIA 
690 1 0 |a ORTHODES CYNICA 
690 1 0 |a PINUS BANKSIANA 
690 1 0 |a PROTORTHODES OVIDUCA 
690 1 0 |a SEMIOTHISA NEPTARIA 
650 1 7 |2 spines  |a CANADA 
651 4 |a IDIA AMERICALIS 
651 4 |a PHYLLODESMA AMERICANA 
700 1 |a Smith, S.M. 
700 1 |a Malcolm, J.R. 
700 1 |a Bellocq, M.I. 
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