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Quelle est la contribution des milieux semi-naturels - Les thèses en ...

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Annexesedges, some possibly live in this habitat. Indeed, it is thought that European woodlots and for<strong>est</strong>s havebecome much d<strong>en</strong>ser with an increasingly closed canopy during the 20 th c<strong>en</strong>tury, due to a decrease inwild ungu<strong>la</strong>te popu<strong>la</strong>tions and abandonm<strong>en</strong>t of anc<strong>est</strong>ral practices such as pasture and coppicing infavour of ev<strong>en</strong>-aged stands (Rackham et al., 1998; Vera, 2000). Sparse for<strong>est</strong> stands are rare at th<strong>est</strong>udy site, and woodlot edges could be surrogate habitats for species preferring for<strong>est</strong>s with an op<strong>en</strong>canopy, as is the case for some relic species of ground beetles in sparse stands of trees in C<strong>en</strong>tralEurope (Spitzer et al., 2008).The date of the most rec<strong>en</strong>t logging operation had no effect on any parameter characterizing thespecies assemb<strong>la</strong>ge of ground beetles within the woodlot (total d<strong>en</strong>sity, number of species per trap,d<strong>en</strong>sity of particu<strong>la</strong>r groups of species with respect to their common habitat). This was quite surprisingsince the soil structure of rec<strong>en</strong>tly logged zones is disturbed and the vegetation structure is alsodiffer<strong>en</strong>t, which may affect the assemb<strong>la</strong>ge of overwintering beetles (D<strong>en</strong>nis et al., 1994; Pywell et al.,2005). In addition, a former study showed that differ<strong>en</strong>t species assemb<strong>la</strong>ges of active ground beetlesoccurred in young stands compared to old stands of trees, with an additional influ<strong>en</strong>ce of<strong>en</strong>vironm<strong>en</strong>tal conditions linked to for<strong>est</strong> managem<strong>en</strong>t (du Bus de Warnaffe & Dufrêne, 2004). In thepres<strong>en</strong>t study, we only noted a tr<strong>en</strong>d to a higher d<strong>en</strong>sity of op<strong>en</strong> habitat species overwintering in zoneslogged betwe<strong>en</strong> 2000 and 2003, but too few traps were p<strong>la</strong>ced in these zones to determine whether thistr<strong>en</strong>d was statistically significant. Thus it is likely that the effect of managem<strong>en</strong>t on ground beetles inthe case of coppicing with standards is much more transi<strong>en</strong>t than that associated with the logging ofev<strong>en</strong>-aged stands (du Bus de Warnaffe & Dufrêne, 2004; Niemelä et al., 1996) since the canopy andundergrowth rapidly develop and shade the for<strong>est</strong> floor.It is noteworthy that all the edges of the woodlot did not have the same assemb<strong>la</strong>ge of overwinteringspecies. Some species were associated with particu<strong>la</strong>r edges, which could be the consequ<strong>en</strong>ce of theori<strong>en</strong>tation of edges, their adjac<strong>en</strong>t habitat or their vegetation structure, as shown for hedges (D<strong>en</strong>nis etal., 1994).Most of the species <strong>des</strong>cribed in this study are pot<strong>en</strong>tial or confirmed biocontrol ag<strong>en</strong>ts. Species<strong>des</strong>cribed here as woody habitat species are reported to eat <strong>la</strong>rge preys such as slugs (Asteraki, 1993)and many g<strong>en</strong>eralist and op<strong>en</strong> habitat species also eat agricultural p<strong>est</strong>s. For instance, Anchom<strong>en</strong>usdorsalis, Demetrias atricapillus and Trechus quadristriatus, all of which overwintered in the edges ofthe woodlot studied, are predators of aphids (Sotherton, 1984; Sunder<strong>la</strong>nd, 2002).A better knowledge of the factors determining the distribution of these species would <strong>en</strong>able ownersand farmers to manage woodlot edges so as to increase overwintering of op<strong>en</strong> habitat species at theselocations and thus favour their action as biocontrol ag<strong>en</strong>ts in adjac<strong>en</strong>t fields. Woodlot edges and other<strong>semi</strong>-natural habitats provide suitable overwintering refuges for differ<strong>en</strong>t kinds of natural predators ofagricultural p<strong>est</strong>s. Indeed, woodlot edges may not be the most important overwintering habitat forpredators (Sotherton, 1984) but could nonetheless provide shelter for particu<strong>la</strong>r species due to themore buffered conditions there than in other <strong>semi</strong>-natural habitats and this needs to be inv<strong>est</strong>igated.Acknowledgem<strong>en</strong>tsWe sincerely thank M. Gou<strong>la</strong>rd for his advice on sample stratification, S. Ladet for help with GIS, M.Redon for help in the field, C. Pelosi and reviewers for useful comm<strong>en</strong>ts on the manuscript and D.Goodfellow for improving the English. We thank colleagues of UMR Dynafor for their technica<strong>la</strong>ssistance during the setting of the traps. We also gratefully acknowledge the <strong>la</strong>nd owners whoallowed us to install emerg<strong>en</strong>ce traps in their woodlot. This study was funded by the joint Midi-Pyr<strong>en</strong>ees-Aquitaine Regions’ program “For<strong>est</strong> Biodiversity Dynamics under Global Change” and theANR-Biodiversity “BiodivAgriM” program. Anthony Roume’s fellowship was granted by the Fr<strong>en</strong>chministry of Research and Universities.175

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