Linking Macrodetritivore Distribution to Desiccation Resistance in Small Forest Fragments Embedded in Agricultural Landscapes in Europe
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Landscape Ecol https://doi.org/10.1007/s10980-017-0607-7 RESEARCH ARTICLE Linking macrodetritivore distribution to desiccation resistance in small forest fragments embedded in agricultural landscapes in Europe Pallieter De Smedt . Lander Baeten . Willem Proesmans . Matty P. Berg . Jo¨rg Brunet . Sara A. O. Cousins . Guillaume Decocq . Marc Deconchat . Martin Diekmann . Emilie Gallet-Moron . Brice Giffard . Jaan Liira . Ludmilla Martin . Astra Ooms . Alicia Valde´s . Monika Wulf . Martin Hermy . Dries Bonte . Kris Verheyen Received: 9 May 2017 / Accepted: 21 December 2017 Ó Springer Science+Business Media B.V., part of Springer Nature 2017 Abstract resistance) to gain mechanistic insights of the putative Purpose Most of the agricultural landscape in drivers. Europe, and elsewhere, consists of mosaics with Methods Macrodetritivores were sampled in forest scattered fragments of semi-natural habitat like small edges-centres of 224 European forest fragments across forest fragments. Mutual interactions between forest 14 landscapes opposing in land use intensity. We used fragments and agricultural areas influence ecosystem a multilevel analysis of variance to assess the relative processes such as nutrient cycling, a process strongly contribution of different spatial scales in explaining mediated by the macrodetritivore community, which activity-density and Shannon-diversity of woodlice is however, poorly studied. We investigated macrode- and millipedes, together with a model-based analysis tritivore distribution patterns at local and landscape- of the multivariate activity-density data testing the level and used a key functional trait (desiccation effect on species composition. Secondly, we tested if desiccation resistance of macrodetritivores varied across communities at different spatial scales using Data accessibility All data is available in the smallFOREST linear mixed effect models. geodatabase. Access to this database can be achieved after Results Forest edge-centre and landscape use inten- contacting the smallFOREST geodatabase management committee (http://www.u-picardie.fr/smallforest/uk/). sity determined activity-density and community com- position of macrodetritivores in forest fragments, Electronic supplementary material The online version of while fragment characteristics like size and continuity this article (https://doi.org/10.1007/s10980-017-0607-7) con- were relatively unimportant. Forest edges and higher tains supplementary material, which is available to authorized users. P. De Smedt (&) Á L. Baeten Á W. Proesmans Á M. P. Berg K. Verheyen Groningen Institute for Evolutionary Life Sciences, Forest & Nature Lab, Ghent University, University of Groningen, PO Box 11103, Geraardsbergsesteenweg 267, 9090 Melle-Gontrode, 9700 CC Groningen, The Netherlands Belgium e-mail: [email protected] J. Brunet Swedish University of Agricultural Sciences, Southern M. P. Berg Á A. Ooms Swedish Forest Research Centre, Box 49, Department of Ecological Science/Animal Ecology, SE-230 53 Alnarp, Sweden Faculty of Earth and Life Sciences, Vrije Universiteit Amsterdam, De Boelelaan 1085, 1081 HV Amsterdam, The Netherlands 123 Landscape Ecol intensity landscapes supported higher activity-density implications on, respectively, tree and crop growth. A of macrodetritivores and determined species compo- fast recycling of nutrients is facilitated by a quick sition. Forest edges sustained woodlouse communities breakdown of litter and enhances plant growth dominated by more drought tolerant species. (Belovsky and Slade 2000) a process that is strongly Conclusions Landscape use intensity and forest mediated by soil invertebrate communities (de Vries edges are main drivers in macrodetritivore distribution et al. 2013). in forest fragments with desiccation resistance a good In forests, macro-arthropod detritivores are predictor of macrodetritivore distribution. Key func- amongst the largest representatives of this soil inver- tional traits can help us to predict changes in tebrate community. They fragment dead organic community structure in changing landscapes. material on the forest floor (Anderson 1988; Grelle et al. 2000) and their activity significantly increases Keywords Forest edges Á Landscape use intensity Á nitrogen mineralisation (David 2014). Woodlice and Litter dwelling soil fauna Á Millipedes Á Nutrient millipedes are important taxa in this context, as they cycling Á Woodlice are amongst the most important litter dwelling macrodetritivores, at least in terms of their biomass (Jeffery et al. 2010), but poorly studied in a landscape context (David and Handa 2010). These taxa can be Introduction extremely abundant and perform a critical first step in the breakdown of organic matter in almost every Currently, a large share of the European landscapes terrestrial ecosystem (Ha¨ttenschwiler et al. 2005). The consists of small forest fragments embedded in an distribution of woodlouse and millipede communities agricultural matrix varying in landscape use intensity varies at different spatial scales. Landscape charac- (Honnay et al. 2005). The often sharp boundaries teristics like land cover heterogeneity or land use between small forest fragments and agricultural fields intensity affect woodlouse and millipede distribution causes mutual influences on communities and ecosys- (Dauber et al. 2005;Ba´ldi 2008). Their distribution tems, like spill-over effects of organisms and nutrients patterns vary, within landscapes, between forest altering ecosystem processes (for an overview see e.g., fragments differing in size, age or dominating tree Tscharntke et al. (2012)). Litter breakdown is an species (Dekoninck et al. 2005; Topp et al. 2006; important ecosystem process in both small forest Tajovsky´ et al. 2012; De Smedt et al. 2016). Within fragments and agricultural landscapes, cause of its forest fragments, there are large differences in S. A. O. Cousins J. Liira Biogeography and Geomatics, Department of Physical Institute of Ecology and Earth Sciences, University of Geography, Stockholm University, SE-106 91 Stockholm, Tartu, Lai 40, EE-51005 Tartu, Estonia Sweden A. Valde´s G. Decocq Á E. Gallet-Moron Á L. Martin Á A. Valde´s Department of Ecology, Environment and Plant Sciences, Jules Verne University of Picardie, UR Ecologie Et Stockholm University, Svante Arrhenius Va¨g20A, Dynamique Des Syste`mes Anthropise´s (EDYSAN, FRE SE-106 91 Stockholm, Sweden 3498 CNRS), 1 Rue Des Louvels, 80037 Amiens Cedex 1, France M. Wulf Institute of Land Use Systems, Leibniz-ZALF (E.V.), M. Deconchat Eberswalder Strasse 84, D-15374 Mu¨ncheberg, Germany UMR 1201 Dynafor, Inra, Chemin de Borde Rouge, CS 52627, F-31326 Castanet Tolosan, France M. Hermy Division of Forest, Nature and Landscape, University of M. Diekmann Leuven, Celestijnenlaan 200E, B-3001 Louvain, Belgium Institute of Ecology, FB02, University of Bremen, Leobener Str, D-28359 Bremen, Germany D. Bonte Terrestrial Ecology Unit (TEREC), Dept. Biology, Ghent B. Giffard University, K.L. Ledeganckstraat 35, 9000 Ghent, Bordeaux Sciences Agro, University of Bordeaux, 1 Belgium Cours Du Ge´ne´ral de Gaulle, 33170 Gradignan, France 123 Landscape Ecol macrodetritivore distribution between forest edges and Accordingly, besides describing community pat- forest interiors (Riutta et al. 2012; Bogyo´ et al. 2015; terns across different spatial scales, we want to De Smedt et al. 2016). These environmental aspects understand macrodetritivore patterns in small forest affect distribution patterns at different spatial scales, fragments using community weighted desiccation but it is unclear whether local or regional drivers resistance of the species. Significant trait-patterns predominate (Wolters 2001; Dauber et al. 2005; David could therefore indicate drivers of macrodetritivore and Handa 2010; Martins da Silva et al. 2015). biodiversity in these landscapes and give insights Therefore, we studied distribution of macrodetriti- about the potential effects on ecosystem functioning. vores at three diverse spatial scales focussing on some We intend to investigate the following hypotheses important drivers acting at these scales based on the (1) macrodetritivore distribution differs at different abovementioned references: (1) landscape scale, com- spatial scales across Europe; (i) between landscapes, paring forest fragments that occur in landscapes (ii) forest fragments and (iii) locations within forest differing in land use intensity; (2) fragment scale, fragments; (2) community weighted mean macrode- comparing forest fragments with different size and tritivore desiccation resistance, which will help us to continuity; and (3) within-fragment scale comparing understand how the environment at different spatial forest edges and interiors within the same forest scales influences community structure. fragment. Besides describing the observed patterns of macrodetritivore distribution, we want to understand Methods the underlying mechanisms. An analysis of the differences in functional traits across spatial scales Study area and selected forest fragments provides a valuable way forward, as functional traits are being widely used in ecology to study the causes The study was carried out in seven regions across the and potential ecosystem consequences of changes in temperate forest biome of Western Europe, along a communities (McGill et al. 2006; Suding et al. 2006). latitudinal gradient spanning more than 2000 km These causes and consequences could be explained (Fig. 1a). In every region, we selected two through the functional