How do landscape composition and configuration, organic farming and fallow strips affect the diversity of bees, wasps and their parasitoids?

1. Habitat destruction and increasing land use intensity result in habitat loss, fragmentation and degradation, and subsequently in the loss of species diversity. The fact that these factors are often highly confounded makes disentangling their effects extremely difficult, if not impossible, and their relative impact on species loss is mostly speculative. 2. In a two-year study, we analysed the relative importance of changed landscape composition (increased areas of cropped habitats), reduced habitat connectivity and reduced habitat quality on nest colonization of cavity-nesting bees, wasps and their parasitoids. We selected 23 pairs of conventional and organic wheat fields in the centre of landscape circles (500 m radius) differing in edge densities (landscape configuration) and % non-crop habitats (landscape composition). Standardized trap nests were established in the field centres and in neighbouring permanent fallow strips (making a total of 92 nesting sites). 3. Factors at all three scales affected nest colonization. While bees were enhanced by high proportions of non-crop habitat in the landscape, wasps profited from high edge densities, supporting our hypothesis that wasps are enhanced by connecting corridors. Colonization of herbivore-predating wasps was lower in field centres than in fallow strips for conventional sites, but not for organic sites, indicating a fallow-like connectivity value of organic fields. The relative importance of habitat type and farming system varied among functional groups suggesting that their perception of crop-non-crop boundaries or the availability of their food resources differed. 4. Local and landscape effects on parasitoids were mainly mediated by their hosts. Parasitism rates were marginally affected by local factors. A specialist parasitoid was more sensitive to high land use intensity than its host, whereas generalist parasitoids were less sensitive. 5. We conclude that the conversion of cropland into non-crop habitat may not be a sufficiently successful strategy to enhance wasps or other species that suffer more from isolation than from habitat loss. Interestingly, habitat connectivity appeared to be enhanced by both higher edge densities and by organic field management. Thus, we conclude that high proportions of conventionally managed and large crop fields threaten pollination and biological control services at a landscape scale.

[1]  Teja Tscharntke,et al.  Habitat modification alters the structure of tropical host–parasitoid food webs , 2007, Nature.

[2]  T. O. Crist,et al.  Direct and indirect effects of habitat area and matrix composition on species interactions among flower-visiting insects , 2007 .

[3]  Carsten Thies,et al.  Differential effects of landscape and management on diversity and density of ground-dwelling farmland spiders , 2005 .

[4]  Lenore Fahrig,et al.  Relative Effects of Habitat Loss and Fragmentation on Population Extinction , 1997 .

[5]  Sharon K. Collinge,et al.  Ecological consequences of habitat fragmentation: implications for landscape architecture and planning , 1996 .

[6]  Tobias Purtauf,et al.  Alpha and beta diversity of arthropods and plants in organically and conventionally managed wheat fields , 2007 .

[7]  T. Tscharntke,et al.  Habitat Fragmentation, Species Loss, and Biological Control , 1994, Science.

[8]  Achim Gathmann,et al.  Foraging ranges of solitary bees , 2002 .

[9]  D. Macdonald,et al.  A comparison of butterfly populations on organically and conventionally managed farmland , 2007 .

[10]  K. Vernes,et al.  Effects of landscape composition and configuration on northern flying squirrels in a forest mosaic , 2009 .

[11]  J. Roland,et al.  Insect parasitoid species respond to forest structure at different spatial scales , 1997, Nature.

[12]  Maj Rundlöf,et al.  Interacting effects of farming practice and landscape context on bumble bees , 2008 .

[13]  Kevin McGarigal,et al.  Hierarchical, Multi-scale decomposition of species-environment relationships , 2002, Landscape Ecology.

[14]  D. Bates,et al.  Mixed-Effects Models in S and S-PLUS , 2001 .

[15]  I. Steffan‐Dewenter Landscape context affects trap‐nesting bees, wasps, and their natural enemies , 2002 .

[16]  T. Tscharntke,et al.  Grass strip corridors in agricultural landscapes enhance nest-site colonization by solitary wasps. , 2009, Ecological applications : a publication of the Ecological Society of America.

[17]  Kevin McGarigal,et al.  COMPARATIVE EVALUATION OF EXPERIMENTAL APPROACHES TO THE STUDY OF HABITAT FRAGMENTATION EFFECTS , 2002 .

[18]  R. Holt,et al.  A Survey and Overview of Habitat Fragmentation Experiments , 2000 .

[19]  J. Tewksbury,et al.  LOW-QUALITY HABITAT CORRIDORS AS MOVEMENT CONDUITS FOR TWO BUTTERFLY SPECIES , 2005 .

[20]  James T. Cronin,et al.  THE MATRIX ENHANCES THE EFFECTIVENESS OF CORRIDORS AND STEPPING STONES , 2004 .

[21]  A. Klein,et al.  Foraging trip duration and density of megachilid bees, eumenid wasps and pompilid wasps in tropical agroforestry systems , 2004 .

[22]  S. Corbet,et al.  Forage for bumble bees and honey bees in farmland: a case study. , 1991 .

[23]  Teja Tscharntke,et al.  The effects of landscape complexity on arable weed species diversity in organic and conventional farming , 2005 .

[24]  D. Levey,et al.  Habitat corridors function as both drift fences and movement conduits for dispersing flies , 2005, Oecologia.

[25]  A. Klein,et al.  Rain forest promotes trophic interactions and diversity of trap-nesting Hymenoptera in adjacent agroforestry. , 2006, The Journal of animal ecology.

[26]  L. Fahrig Effects of Habitat Fragmentation on Biodiversity , 2003 .

[27]  A. B. Hald,et al.  Conservation value of the herbaceous vegetation in hedgerows – does organic farming make a difference? , 2004 .

[28]  J. Bengtsson,et al.  The effects of organic agriculture on biodiversity and abundance: a meta‐analysis , 2005 .

[29]  T. Tscharntke,et al.  Plant-insect interactions in fragmented landscapes. , 2004, Annual review of entomology.

[30]  Emilio M. Bruna,et al.  Habitat fragmentation and large‐scale conservation: what do we know for sure? , 1999 .

[31]  Y. Clough,et al.  Spider diversity in cereal fields: comparing factors at local, landscape and regional scales , 2005 .

[32]  Lenore Fahrig,et al.  INDEPENDENT EFFECTS OF FOREST COVER AND FRAGMENTATION ON THE DISTRIBUTION OF FOREST BREEDING BIRDS , 1999 .

[33]  T. Sparks,et al.  Effectiveness of new agri-environment schemes in providing foraging resources for bumblebees in intensively farmed landscapes , 2006 .

[34]  Carsten Thies,et al.  REVIEWS AND SYNTHESES Landscape perspectives on agricultural intensification and biodiversity - ecosystem service management , 2005 .

[35]  T. Tscharntke,et al.  Agricultural landscapes with organic crops support higher pollinator diversity , 2008 .

[36]  Neal M. Williams,et al.  The area requirements of an ecosystem service: crop pollination by native bee communities in California , 2004 .

[37]  Teja Tscharntke,et al.  Diversity of flower-visiting bees in cereal fields: effects of farming system, landscape composition and regional context , 2006 .

[38]  Erik Öckinger,et al.  Do corridors promote dispersal in grassland butterflies and other insects? , 2007, Landscape Ecology.

[39]  M. Rundlöf,et al.  The effect of organic farming on butterfly diversity depends on landscape context , 2006 .

[40]  B. Schmid,et al.  Interaction diversity within quantified insect food webs in restored and adjacent intensively managed meadows. , 2007, The Journal of animal ecology.

[41]  Nick M. Haddad,et al.  CORRIDOR AND DISTANCE EFFECTS ON INTERPATCH MOVEMENTS: A LANDSCAPE EXPERIMENT WITH BUTTERFLIES , 1999 .

[42]  I. Steffan‐Dewenter,et al.  Do resources or natural enemies drive bee population dynamics in fragmented habitats? , 2008, Ecology.

[43]  D. Landis,et al.  Habitat management to conserve natural enemies of arthropod pests in agriculture. , 2000, Annual review of entomology.

[44]  T. Sparks,et al.  Providing foraging resources for bumblebees in intensively farmed landscapes , 2005 .

[45]  E. Marshall,et al.  Field margins in northern Europe: their functions and interactions with agriculture , 2002 .

[46]  J. Tiainen,et al.  Habitat quality of field margins in a Finnish farmland area for bumblebees (Hymenoptera: Bombus and Psithyrus) , 2002 .

[47]  Neo D. Martinez,et al.  TROPHIC RANK AND THE SPECIES-AREA RELATIONSHIP , 1999 .

[48]  T. Tscharntke,et al.  Bioindication using trap‐nesting bees and wasps and their natural enemies: community structure and interactions , 1998 .

[49]  Jeremy D. Wilson,et al.  Does organic farming benefit biodiversity , 2005 .