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Landscapes Forest and Global Change - ESA - Escola Superior ...

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A. Ouin et al. 2010. Do wooded elements in agricultural l<strong>and</strong>scape contribute to biological control in crops<br />

726<br />

hoverfly abundance (eggs+larvae) in wheat fields between the wooded <strong>and</strong> non wooded<br />

l<strong>and</strong>scapes. Compared with poorly wooded l<strong>and</strong>scapes, l<strong>and</strong>scapes with 27% of wood l<strong>and</strong>cover<br />

seemed to shelter higher hoverfly abundance during one of the key-periods for the aphid<br />

population dynamics (early spring), thus providing them with higher potential regulation<br />

capabilities. Afterwards, the difference between hoverfly population abundances decreased<br />

during the season (Figure 1).<br />

Density of overwintering ground beetles in a woodlot<br />

We collected a total of 2014 ground beetles during the whole trapping period, belonging to 48<br />

species. The total density of emerging ground beetles was four to five times higherin edges than<br />

in the inner areas of the woodlot <strong>and</strong> the mean number of species per trap was three times<br />

higher in edges than in the inner areas. Open habitats species overwintered only in the edges <strong>and</strong><br />

not in the inner areas while the two other groups of species overwintered in all the woodlot but<br />

with a marked preference for the edges (Figure 2).<br />

4. Discussion<br />

Our results show that woodlot edges are favourable for insect biodiversity in agricultural<br />

l<strong>and</strong>scapes, by (i) favouring abundances of aphidophagous hoverflies in early spring in fields,<br />

<strong>and</strong> (ii) sheltering both high species richness <strong>and</strong> abundances of ground beetles. Positive<br />

influence of woodlot edges on these insect populations seems to occur mainly during the winter<br />

period, probably by offering local environmental conditions favourable to their overwintering.<br />

Identifying such l<strong>and</strong>scape elements which favour overwintering of beneficial insects is of a<br />

particularly interest from the agronomic point of view of biological control of pests, for which<br />

early arrival of a natural enemy is required in spring (Honek, 1983; Tenhumberg & Poehling,<br />

1995; Corbett in Pickett & Bugg, 1998). Aphidophagous hoverflies distribution <strong>and</strong> abundance<br />

prove to be dependent both on l<strong>and</strong>scape parameters (Molthan, 1990), peculiar to forests <strong>and</strong><br />

crop mosaic respectively, which act at different periods through the year <strong>and</strong> sometimes with a<br />

lasting effect. Indeed south forest edges proved to be important l<strong>and</strong>scape elements for the<br />

overwintering of adult females of the beneficial aphidophagous hoverfly Episyrphus balteatus,<br />

particularly when spatially coupled with grassl<strong>and</strong>s <strong>and</strong> fallows rich in floral resources<br />

(Arrignon et al., 2007). As for north forest edges, they also proved to enhance populations of<br />

adult E. balteatus emerging in spring since they are preferential overwintering sites for the<br />

larvae, probably because of higher density of aphid populations in the fall (Sarthou et al., 2005).<br />

For ground beetles, forest edges appeared as a major reservoir of specific diversity (numerous<br />

species <strong>and</strong> their individuals) potentially able to control some pest species in the nearby crop<br />

fields, even the forest species, which are the biggest ones <strong>and</strong> are reported to prey on slugs<br />

(Kromp, 1999; Symondson et al., 2002). Moreover, woodlot edges sheltered ground beetles<br />

species whose adults live <strong>and</strong> exert beneficial influence in crops but are not usually found in<br />

wooded habitats. The impacts of edge management on these populations <strong>and</strong> their ability to<br />

move from forest to crop have to be investigated in the future. These results offer new insights<br />

for pest regulation through l<strong>and</strong>scape management, particularly by pointing the forest edges as<br />

other important l<strong>and</strong>scape elements to add to well-known set-asides <strong>and</strong> hedges in the design of<br />

semi-natural element network in agricultural l<strong>and</strong>scapes (Russel, 1989; L<strong>and</strong>is et al., 2000; Gurr<br />

et al., 2004). Undoubtedly, this 'l<strong>and</strong>scaping' management of agroecosystems will benefit from a<br />

better ecological services-based knowledge of other l<strong>and</strong>scape elements (natural grassl<strong>and</strong>s,<br />

fallows, ditch edges…) at different spatial scales, <strong>and</strong> a better integration of this knowledge in<br />

crop management.<br />

<strong>Forest</strong> <strong>L<strong>and</strong>scapes</strong> <strong>and</strong> <strong>Global</strong> <strong>Change</strong>-New Frontiers in Management, Conservation <strong>and</strong> Restoration. Proceedings of the IUFRO L<strong>and</strong>scape Ecology<br />

Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.)<br />

2010, Instituto Politécnico de Bragança, Bragança, Portugal.

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