Configurational landscape heterogeneity shapes functional community composition of grassland butterflies
Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. W...
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Published in | The Journal of applied ecology Vol. 52; no. 2; pp. 505 - 513 |
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Main Authors | , , , , , , , , , , |
Format | Journal Article |
Language | English |
Published |
Oxford
Blackwell Scientific Publications
01.04.2015
John Wiley & Sons Ltd Blackwell Publishing Ltd |
Subjects | |
Online Access | Get full text |
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Abstract | Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land‐use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency. As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency. The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land‐use intensity on larval‐feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities. Synthesis and applications. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. |
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AbstractList | Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition.
We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land‐use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency.
As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency.
The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land‐use intensity on larval‐feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities.
Synthesis and applications
. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the
EU
2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes.
We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the
EU
2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land‐use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency. As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency. The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land‐use intensity on larval‐feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities. Synthesis and applications. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land-use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency. As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency. The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land-use intensity on larval-feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250-1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land‐use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency. As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency. The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land‐use intensity on larval‐feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities. Synthesis and applications. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition.We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land-use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency.As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency.The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land-use intensity on larval-feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities.Synthesis and applications. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250-1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250-1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. Summary Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomic and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land‐use intensity on butterfly taxonomic diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency. As expected, compositional heterogeneity had strong positive effects on taxonomic diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency. The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land‐use intensity on larval‐feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities. Synthesis and applications. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. We show that landscapes with high compositional heterogeneity support communities with greater taxonomic diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250–1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. 1. Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii) configurational heterogeneity (number, size and arrangement of habitat patches), both with different ecological implications for community composition. 2. We examined how independent gradients of compositional and configurational landscape heterogeneity, at eight spatial scales, shape taxonomie and functional composition of butterfly communities in 91 managed grasslands across Germany. We used landscape metrics that were calculated from functional maps based on habitat preferences of individual species during different life stages. The relative effects of compositional and configurational landscape heterogeneity were compared with those of local land-use intensity on butterfly taxonomie diversity, community composition and functional diversity of traits related to body size, feeding breadth and migratory tendency. 3. As expected, compositional heterogeneity had strong positive effects on taxonomie diversity, while configurational heterogeneity had strong positive effects on trait dominance within the community. When landscapes had smaller mean patch size and greater boundary area, communities were dominated by species with more specialized larval feeding, decreased forewing length and limited migratory tendency. 4. The positive effects of increased configurational landscape heterogeneity outweighed the negative effects of local land-use intensity on larval-feeding specialization, at all spatial scales, highlighting its importance for specialists of all dispersal capabilities. 5. Synthesis and applications. We show that landscapes with high compositional heterogeneity support communities with greater taxonomie diversity, while landscapes with high configurational heterogeneity support communities that include vulnerable species (feeding specialists with larger body size, sedentary nature and more negatively affected by local management intensity). A decline in functional community composition can lead to functional homogenization, affecting the viability of the ecosystems by decreasing the variability in their responses to disturbance and altering their functioning. A landscape management for grasslands that promotes the maintenance of small patch sizes and a diversity of land uses in the surrounding landscape (within 250-1000 m) is recommended for the conservation of diverse butterfly communities. These strategies could also benefit government programmes such as the EU 2020 Biodiversity Strategy in their efforts to reduce the loss of biodiversity in agricultural landscapes. |
Author | Steckel, Juliane Perović, David Gámez‐Virués, Sagrario Krauss, Jochen Westphal, Catrin Kleijn, David Tscharntke, Teja Börschig, Carmen Erasmi, Stefan Klein, Alexandra‐Maria Rothenwöhrer, Christoph |
Author_xml | – sequence: 1 fullname: Perović, David – sequence: 2 fullname: Gámez‐Virués, Sagrario – sequence: 3 fullname: Börschig, Carmen – sequence: 4 fullname: Klein, Alexandra‐Maria – sequence: 5 fullname: Krauss, Jochen – sequence: 6 fullname: Steckel, Juliane – sequence: 7 fullname: Rothenwöhrer, Christoph – sequence: 8 fullname: Erasmi, Stefan – sequence: 9 fullname: Tscharntke, Teja – sequence: 10 fullname: Westphal, Catrin – sequence: 11 fullname: Kleijn, David |
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Cites_doi | 10.1016/S0169-5347(03)00011-9 10.1016/j.baae.2010.07.009 10.1111/j.2007.0906-7590.05171.x 10.1111/j.1365-2656.2009.01642.x 10.1111/j.1461-0248.2008.01255.x 10.2307/3565770 10.1146/annurev.ecolsys.35.112202.130148 10.1098/rspb.2004.3002 10.1016/j.agee.2006.08.013 10.1016/j.agee.2012.08.013 10.1111/j.1469-185X.2009.00119.x 10.1111/j.1600-0587.2008.05546.x 10.1111/j.1461-0248.2011.01709.x 10.1016/j.biocon.2014.02.015 10.1098/rstb.2004.1585 10.1016/j.baae.2013.09.002 10.1007/s10980-013-9852-6 10.1146/annurev.es.04.110173.000245 10.1007/s00442-011-1965-5 10.1890/08-2244.1 10.1007/BF00131172 10.1111/1365-2664.12394 10.1007/s10841-008-9135-8 10.1046/j.1365-2745.1998.00306.x 10.1111/jvs.12022 10.2307/3544901 10.1111/j.1461-0248.2010.01457.x 10.1111/j.1461-0248.2010.01487.x 10.1371/journal.pone.0037359 10.1016/j.biocon.2005.10.022 10.1007/s10980-010-9473-2 10.1016/S0167-8809(96)01143-7 10.1016/B978-012323445-2/50020-1 10.1016/j.baae.2012.04.001 10.1111/j.1469-185X.2011.00216.x 10.1098/rspb.2009.2221 10.1111/j.0030-1299.2007.15559.x 10.1111/j.1461-0248.2005.00782.x 10.18637/jss.v022.i04 10.1016/j.biocon.2012.03.038 10.1111/j.1461-0248.2010.01559.x |
ContentType | Journal Article |
Copyright | 2015 British Ecological Society 2015 The Authors. Journal of Applied Ecology © 2015 British Ecological Society Copyright Blackwell Publishing Ltd. Apr 2015 |
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References | 1989; 3 2010; 11 1997; 62 2005; 272 2013; 28 2010; 79 2010; 13 2011 2013; 24 2007; 120 2009 1997 2013; 166 1995 2014; 172 2003; 18 1970 2003 2007; 30 2011; 14 1991 2002 2012; 15 2012; 13 1998; 86 2010; 85 1999 2009; 12 2012; 152 2009; 13 2013; 14 2005; 360 2009; 32 2010; 25 2007; 116 2005; 8 2010; 277 2004; 35 2015 2013 1992; 65 2012; 7 2007; 22 2006; 128 2011; 167 2012; 87 1987; 49 1973; 4 e_1_2_7_5_1 e_1_2_7_3_1 e_1_2_7_9_1 e_1_2_7_7_1 e_1_2_7_19_1 e_1_2_7_17_1 e_1_2_7_15_1 e_1_2_7_41_1 e_1_2_7_13_1 e_1_2_7_43_1 e_1_2_7_11_1 e_1_2_7_45_1 e_1_2_7_47_1 e_1_2_7_26_1 e_1_2_7_49_1 e_1_2_7_28_1 e_1_2_7_50_1 e_1_2_7_25_1 e_1_2_7_31_1 Settele J. (e_1_2_7_39_1) 1999 e_1_2_7_52_1 e_1_2_7_23_1 e_1_2_7_33_1 e_1_2_7_35_1 Settele J. (e_1_2_7_40_1) 2009 e_1_2_7_37_1 Higgins L.G. (e_1_2_7_21_1) 1970 e_1_2_7_6_1 e_1_2_7_4_1 e_1_2_7_8_1 e_1_2_7_18_1 e_1_2_7_16_1 e_1_2_7_2_1 e_1_2_7_14_1 e_1_2_7_42_1 e_1_2_7_12_1 e_1_2_7_44_1 e_1_2_7_10_1 e_1_2_7_46_1 e_1_2_7_48_1 e_1_2_7_27_1 e_1_2_7_29_1 e_1_2_7_51_1 e_1_2_7_30_1 Koch M. (e_1_2_7_24_1) 1991 e_1_2_7_32_1 e_1_2_7_22_1 e_1_2_7_34_1 e_1_2_7_20_1 e_1_2_7_36_1 e_1_2_7_38_1 |
References_xml | – year: 2011 – volume: 62 start-page: 81 year: 1997 end-page: 91 article-title: Biodiversity evaluation in agricultural landscapes: an approach at two different scales publication-title: Agriculture, Ecosystems and Environment – volume: 120 start-page: 179 year: 2007 end-page: 184 article-title: Community richness and stability in agricultural landscapes: the importance of surrounding habitats publication-title: Agriculture, Ecosystems & Environment – volume: 167 start-page: 181 year: 2011 end-page: 188 article-title: CWM and Rao's quadratic diversity: a unified framework for functional ecology publication-title: Oecologia – year: 2009 – volume: 18 start-page: 182 year: 2003 end-page: 188 article-title: Farmland biodiversity: is habitat heterogeneity the key? publication-title: Trends in Ecology & Evolution – volume: 13 start-page: 207 year: 2012 end-page: 220 article-title: A quantitative index of land‐use intensity in grasslands: integrating mowing, grazing and fertilization publication-title: Basic and Applied Ecology – volume: 3 start-page: 87 year: 1989 end-page: 96 article-title: Scaling of ‘landscapes’ in landscape ecology, or, landscape ecology from a beetle's perspective publication-title: Landscape Ecology – volume: 14 start-page: 101 year: 2011 end-page: 112 article-title: Functional landscape heterogeneity and animal biodiversity in agricultural landscapes publication-title: Ecology Letters – volume: 25 start-page: 941 year: 2010 end-page: 954 article-title: Response of arthropod species richness and functional groups to urban habitat structure and management publication-title: Landscape Ecology – volume: 360 start-page: 339 year: 2005 end-page: 357 article-title: Monitoring change in the abundance and distribution of insect using butterflies and other indicator groups publication-title: Philosophical Transactions of the Royal Society B: Biological Sciences – volume: 14 start-page: 547 year: 2013 end-page: 554 article-title: Traits of butterfly communities change from specialist to generalist characteristics with increasing land‐use intensity publication-title: Basic and Applied Ecology – volume: 13 start-page: 969 year: 2010 end-page: 979 article-title: Life‐history traits predict species responses to habitat area and isolation: a cross‐continental synthesis publication-title: Ecology Letters – volume: 116 start-page: 882 year: 2007 end-page: 892 article-title: Let the concept of trait be functional! publication-title: Oikos – volume: 79 start-page: 491 year: 2010 end-page: 500 article-title: How do landscape composition and configuration, organic farming and fallow strips affect the diversity of bees, wasps and their parasitoids? publication-title: Journal of Animal Ecology – volume: 13 start-page: 597 year: 2010 end-page: 605 article-title: Habitat fragmentation causes immediate and time‐delayed biodiversity loss at different trophic levels publication-title: Ecology Letters – volume: 128 start-page: 542 year: 2006 end-page: 552 article-title: The severe decline of butterflies on western German calcareous grasslands during the last 30 years: a conservation problem publication-title: Biological Conservation – volume: 8 start-page: 857 year: 2005 end-page: 874 article-title: Landscape perspectives on agricultural intensification and biodiversity – Ecosystem service management publication-title: Ecology Letters – volume: 65 start-page: 169 year: 1992 end-page: 175 article-title: Ecological processes that affect populations in complex landscapes publication-title: Oikos – volume: 7 start-page: e37359 year: 2012 article-title: Species‐Area relationships are controlled by species traits publication-title: PLoS ONE – volume: 166 start-page: 3 year: 2013 end-page: 14 article-title: The cropping systems mosaic: how does the hidden heterogeneity of agricultural landscapes drive arthropod populations? publication-title: Agriculture, Ecosystems & Environment – volume: 11 start-page: 473 year: 2010 end-page: 485 article-title: Implementing large‐scale and long‐term functional biodiversity research: the biodiversity exploratories publication-title: Basic and Applied Ecology – year: 2015 – volume: 35 start-page: 491 year: 2004 end-page: 522 article-title: Ecological responses to habitat edges: mechanisms, models, and variability explained publication-title: Annual Review of Ecology and Systematics – volume: 15 start-page: 74 year: 2012 end-page: 86 article-title: How is dispersal integrated in life histories: a quantitative analysis using butterflies? publication-title: Ecology Letters – volume: 85 start-page: 625 year: 2010 end-page: 642 article-title: A meta‐analysis of dispersal in butterflies publication-title: Biological Reviews – volume: 30 start-page: 609 year: 2007 end-page: 628 article-title: Methods to account for spatial autocorrelation in the analysis of species distributional data: a review publication-title: Ecography – volume: 12 start-page: 22 year: 2009 end-page: 33 article-title: Loss of functional diversity under land use intensification across multiple taxa publication-title: Ecology Letters – volume: 172 start-page: 56 year: 2014 end-page: 64 article-title: Landscape composition and configuration differently affect trap‐nesting bees, wasps and their antagonists publication-title: Biological Conservation – volume: 277 start-page: 2075 year: 2010 end-page: 2082 article-title: Dispersal capacity and diet breadth modify the response of wild bees to habitat loss publication-title: Proceedings of the Royal Society B: Biological Sciences – year: 2003 – volume: 86 start-page: 902 year: 1998 end-page: 910 article-title: Benefits of plant diversity to ecosystems: immediate, filter and founder effects publication-title: Journal of Ecology – volume: 152 start-page: 253 year: 2012 end-page: 261 article-title: Effects of landscape and habitat quality on butterfly communities in pre‐alpine calcareous grasslands publication-title: Biological Conservation – volume: 272 start-page: 785 year: 2005 end-page: 790 article-title: Tracking butterfly flight paths across the landscape with harmonic radar publication-title: Proceedings of the Royal Society B: Biological Sciences – volume: 49 start-page: 340 year: 1987 end-page: 346 article-title: Ecological neighborhoods: scaling environmental patterns publication-title: Oikos – volume: 32 start-page: 321 year: 2009 end-page: 333 article-title: Linking bird, carabid beetle and butterfly life‐history traits to habitat fragmentation in mosaic landscapes publication-title: Ecography – volume: 87 start-page: 661 year: 2012 end-page: 685 article-title: Landscape moderation of biodiversity patterns and processes – eight hypotheses publication-title: Biological Reviews – volume: 4 start-page: 1 year: 1973 end-page: 23 article-title: Resilience and stability of ecological systems publication-title: Annual Review of Ecological Systems – year: 2002 – volume: 13 start-page: 3 year: 2009 end-page: 27 article-title: The influences of landscape structure on butterfly distribution and movement: a review publication-title: Journal of Insect Conservation – start-page: 359 year: 1997 end-page: 386 – year: 1995 – year: 1970 – volume: 28 start-page: 371 year: 2013 end-page: 383 article-title: Optimizing landscape selection for estimating relative effects of landscape variables on ecological responses publication-title: Landscape Ecology – year: 1991 – volume: 22 start-page: 1 year: 2007 end-page: 20 article-title: The ade4 package: implementing the duality diagram for ecologists publication-title: Journal of Statistical Software – volume: 24 start-page: 949 year: 2013 end-page: 962 article-title: Linking traits between plants and invertebrate herbivores to track functional effects on land‐use changes publication-title: Journal of Vegetation Science – year: 2013 – year: 1999 – ident: e_1_2_7_5_1 doi: 10.1016/S0169-5347(03)00011-9 – ident: e_1_2_7_34_1 – ident: e_1_2_7_17_1 doi: 10.1016/j.baae.2010.07.009 – ident: e_1_2_7_11_1 doi: 10.1111/j.2007.0906-7590.05171.x – ident: e_1_2_7_23_1 doi: 10.1111/j.1365-2656.2009.01642.x – ident: e_1_2_7_18_1 doi: 10.1111/j.1461-0248.2008.01255.x – ident: e_1_2_7_3_1 – ident: e_1_2_7_2_1 doi: 10.2307/3565770 – ident: e_1_2_7_36_1 doi: 10.1146/annurev.ecolsys.35.112202.130148 – ident: e_1_2_7_9_1 doi: 10.1098/rspb.2004.3002 – ident: e_1_2_7_33_1 – ident: e_1_2_7_10_1 doi: 10.1016/j.agee.2006.08.013 – ident: e_1_2_7_48_1 doi: 10.1016/j.agee.2012.08.013 – ident: e_1_2_7_42_1 doi: 10.1111/j.1469-185X.2009.00119.x – ident: e_1_2_7_4_1 doi: 10.1111/j.1600-0587.2008.05546.x – ident: e_1_2_7_43_1 doi: 10.1111/j.1461-0248.2011.01709.x – ident: e_1_2_7_41_1 doi: 10.1016/j.biocon.2014.02.015 – volume-title: Schmetterlinge. Die Tagfalter Deutschlands year: 2009 ident: e_1_2_7_40_1 – ident: e_1_2_7_44_1 doi: 10.1098/rstb.2004.1585 – ident: e_1_2_7_8_1 doi: 10.1016/j.baae.2013.09.002 – ident: e_1_2_7_31_1 doi: 10.1007/s10980-013-9852-6 – ident: e_1_2_7_22_1 doi: 10.1146/annurev.es.04.110173.000245 – ident: e_1_2_7_35_1 doi: 10.1007/s00442-011-1965-5 – ident: e_1_2_7_27_1 doi: 10.1890/08-2244.1 – volume-title: A Field Guide to the Butterflies of Britain & Europe year: 1970 ident: e_1_2_7_21_1 – ident: e_1_2_7_52_1 doi: 10.1007/BF00131172 – ident: e_1_2_7_32_1 doi: 10.1111/1365-2664.12394 – ident: e_1_2_7_37_1 – ident: e_1_2_7_12_1 doi: 10.1007/s10841-008-9135-8 – ident: e_1_2_7_20_1 doi: 10.1046/j.1365-2745.1998.00306.x – volume-title: Schmetterlinge year: 1991 ident: e_1_2_7_24_1 – ident: e_1_2_7_29_1 doi: 10.1111/jvs.12022 – ident: e_1_2_7_15_1 doi: 10.2307/3544901 – ident: e_1_2_7_26_1 doi: 10.1111/j.1461-0248.2010.01457.x – ident: e_1_2_7_30_1 doi: 10.1111/j.1461-0248.2010.01487.x – ident: e_1_2_7_19_1 doi: 10.1371/journal.pone.0037359 – ident: e_1_2_7_28_1 – ident: e_1_2_7_51_1 doi: 10.1016/j.biocon.2005.10.022 – ident: e_1_2_7_38_1 doi: 10.1007/s10980-010-9473-2 – ident: e_1_2_7_14_1 doi: 10.1016/S0167-8809(96)01143-7 – ident: e_1_2_7_45_1 doi: 10.1016/B978-012323445-2/50020-1 – ident: e_1_2_7_6_1 doi: 10.1016/j.baae.2012.04.001 – volume-title: Die Tagfalter Deutschlands year: 1999 ident: e_1_2_7_39_1 – ident: e_1_2_7_47_1 doi: 10.1111/j.1469-185X.2011.00216.x – ident: e_1_2_7_7_1 doi: 10.1098/rspb.2009.2221 – ident: e_1_2_7_49_1 doi: 10.1111/j.0030-1299.2007.15559.x – ident: e_1_2_7_50_1 – ident: e_1_2_7_46_1 doi: 10.1111/j.1461-0248.2005.00782.x – ident: e_1_2_7_13_1 doi: 10.18637/jss.v022.i04 – ident: e_1_2_7_25_1 doi: 10.1016/j.biocon.2012.03.038 – ident: e_1_2_7_16_1 doi: 10.1111/j.1461-0248.2010.01559.x |
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Snippet | Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii)... 1. Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii)... Summary Landscape heterogeneity represents two aspects of landscape simplification: (i) compositional heterogeneity (diversity of habitat types); and (ii)... |
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SubjectTerms | Agricultural land Biodiversity Biodiversity loss Body size butterflies Butterflies & moths Community composition community structure conservation Ecosystems European Union functional diversity functional maps Germany governmental programs and projects Grasslands Habitat management Habitat preferences Habitats Heterogeneity homogenization Land use Landscape Landscape ecology landscape management landscapes land‐use intensity larvae Lepidoptera management migratory behavior species diversity Taxonomy Threatened species trait dominance viability Wildlife conservation wings |
Title | Configurational landscape heterogeneity shapes functional community composition of grassland butterflies |
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