Urban brownfields as temporary habitats: driving forces for the diversity of phytophagous insects

In urban brownfields (derelict sites), we studied the influence of local factors (successional age, vegetation structure, soil) and landscape context (spatial arrangement of brownfields of different successional stages) on the diversity of phytophagous insects, grasshoppers and leafhoppers (Orthopte...

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Published inEcography (Copenhagen) Vol. 29; no. 6; pp. 928 - 940
Main Author Strauss and Robert Biedermann, Barbara
Format Journal Article
LanguageEnglish
Published Copenhagen Copenhagen : Blackwell Publishing Ltd 01.12.2006
Blackwell Publishing Ltd
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Abstract In urban brownfields (derelict sites), we studied the influence of local factors (successional age, vegetation structure, soil) and landscape context (spatial arrangement of brownfields of different successional stages) on the diversity of phytophagous insects, grasshoppers and leafhoppers (Orthoptera and Hemiptera: Auchenorrhyncha). The study was conducted on a total of 246 plots in the cities of Bremen and Berlin, Germany. We used a habitat modelling approach, enabling us to predict the community from single species models (30 species in Bremen, 28 in Berlin). The results revealed that communities were predominantly determined by vegetation structure, followed by landscape context, soil parameters and site age. For most species, local factors were the most important. Only few species were strongly influenced by landscape context, even though some showed clear negative reactions to low proportions of brownfields in the surroundings. Along a successional gradient of vegetation structure, from scarce and low to dense and high vegetation, the insect community was not static. Even though species numbers remained comparatively constant, species composition changed considerably. Many species showed clear preferences for certain successional stages. Thus, maintaining the regional species pool of a city requires a mosaic of all successional stages.
AbstractList In urban brownfields (derelict sites), we studied the influence of local factors (successional age, vegetation structure, soil) and landscape context (spatial arrangement of brownfields of different successional stages) on the diversity of phytophagous insects, grasshoppers and leafhoppers (Orthoptera and Hemiptera: Auchenorrhyncha). The study was conducted on a total of 246 plots in the cities of Bremen and Berlin, Germany. We used a habitat modelling approach, enabling us to predict the community from single species models (30 species in Bremen, 28 in Berlin). The results revealed that communities were predominantly determined by vegetation structure, followed by landscape context, soil parameters and site age. For most species, local factors were the most important. Only few species were strongly influenced by landscape context, even though some showed clear negative reactions to low proportions of brownfields in the surroundings. Along a successional gradient of vegetation structure, from scarce and low to dense and high vegetation, the insect community was not static. Even though species numbers remained comparatively constant, species composition changed considerably. Many species showed clear preferences for certain successional stages. Thus, maintaining the regional species pool of a city requires a mosaic of all successional stages.
In urban brownfields (derelict sites), we studied the influence of local factors (successional age, vegetation structure, soil) and landscape context (spatial arrangement of brownfields of different successional stages) on the diversity of phytophagous insects, grasshoppers and leafhoppers (Orthoptera and Hemiptera: Auchenorrhyncha). The study was conducted on a total of 246 plots in the cities of Bremen and Berlin, Germany. We used a habitat modelling approach, enabling us to predict the community from single species models (30 species in Bremen, 28 in Berlin). The results revealed that communities were predominantly determined by vegetation structure, followed by landscape context, soil parameters and site age. For most species, local factors were the most important. Only few species were strongly influenced by landscape context, even though some showed clear negative reactions to low proportions of brownfields in the surroundings. Along a successional gradient of vegetation structure, from scarce and low to dense and high vegetation, the insect community was not static. Even though species numbers remained comparatively constant, species composition changed considerably. Many species showed clear preferences for certain successional stages. Thus, maintaining the regional species pool of a city requires a mosaic of all successional stages.
Author Strauss, Barbara
Biedermann, Robert
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Issue 6
Keywords Insecta
Orthoptera
Urban area
Biodiversity
Vegetation succession
Species diversity
Phytophagous
Temporary
Industrial wasteland
Arthropoda
Habitat
Invertebrata
Vegetation structure
Language English
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Hollier, J. A. et al. 1994. Successional leafhopper assemblages-pattern and process. Ecol. Res. 9: 185 - 191.
Manel, S. et al. 2001. Evaluating presence-absence models in ecology: the need to account for prevalence. J. Appl. Ecol. 38: 921 - 931.
Cherrill, A. J. and Rushton, S. P.. 1993. The Auchenorhyncha of an unimproved moorland in northern England. Ecol. Entomol. 18: 95 - 103.
Brown, V. K. et al. 1992. Community organisation in leaf hoppers. Oikos 65: 97 - 106.
Cushman, S. A. and McGarigal, K.. 2004. Patterns in the species-environment relationship depend on both scale and choice of response variables. Oikos 105: 117 - 124.
Brocksieper, R.. 1978. Der Einfluß des Mikroklimas auf die Verbreitung der Laubheuschrecken, Grillen und Feldheuschrecken im Siebengebirge und auf dem Rodderberg bei Bonn (Orthopera: Saltatoria). Decheniana-Beihefte 21: 1 - 141.
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Guisan, A. and Zimmermann, N. E.. 2000. Predictive habitat distribution models in ecology. Ecol. Modell. 135: 147 - 186.
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Rebele, F. and Lehmann, C.. 2002. Restoration of a landfill site in Berlin, Germany by spontaneous and directed succession. Restor. Ecol. 10: 340 - 347.
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Fisher, J. T. et al. 2005. The protean relationship between boreal forest landscape structure and red squirrel distribution at multiple spatial scales. Landscape Ecol. 20: 73 - 82.
Morris, M. G.. 2000. The effects of structure and its dynamics on the ecology and conservation of arthropods in British grasslands. Biol. Conserv. 95: 129 - 142.
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Hirzel, A. and Guisan, A.. 2002. Which is the optimal sampling strategy for habitat suitability modelling. Ecol. Modell. 157: 331 - 341.
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Wood, B. C. and Pullin, A. S.. 2002. Persistence of species in a fragmented urban landscape: the importance of dispersal ability and habitat availability for grassland butterflies. Biodiv. Conserv. 11: 1451 - 1468.
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Radford, J. Q. and Bennett, A. F.. 2004. Thresholds in landscape parameters: occurrence of the white-browed treecreeper Climacteris affinis in Victoria, Australia. Biol. Conserv. 117: 375 - 391.
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Steffan-Dewenter, I. and Tscharntke, T.. 1997. Early succession of butterfly and plant communities on set-aside fields. Oecologia 109: 294 - 302.
Sanderson, R. A.. 1992. Hemiptera of naturally vegetated derelict land in north-west England. Entomol. Gaz. 43: 221 - 226.
Schuhmacher, O. and Fartmann, T.. 2003. Wie mobil ist der Warzenbeißer? Eine populationsökologische Studie zum Ausbreitungsverhalten von Decticus verrucivoris. Naturschutz und Landschaftsplanung 35: 20 - 28.
Olden, J. D. and Jackson, D. A.. 2000. Torturing data for the sake of generality: how valid are our regression models?. Ecoscience 7: 501 - 510.
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References_xml – reference: Manel, S. et al. 2001. Evaluating presence-absence models in ecology: the need to account for prevalence. J. Appl. Ecol. 38: 921 - 931.
– reference: Eyre, M. D. et al. 2003. Beetles (Coleoptera) on brownfield sites in England: an important conservation resource?. J. Insect Conserv. 7: 223 - 231.
– reference: Rebele, F.. 1994. Urban ecology and special features of urban ecosystems. Global Ecol. Biogeogr. Lett. 4: 173 - 187.
– reference: Kuhn, W. and Kleyer, M.. 1999/2000. A statistical habitat model for the blue winged grasshopper (Oedipoda caerulescens) considering the habitat connectivity. Zeitschrift für Ökologie und Naturschutz 8: 207 - 218.
– reference: Rebele, F. and Lehmann, C.. 2002. Restoration of a landfill site in Berlin, Germany by spontaneous and directed succession. Restor. Ecol. 10: 340 - 347.
– reference: Fisher, J. T. et al. 2005. The protean relationship between boreal forest landscape structure and red squirrel distribution at multiple spatial scales. Landscape Ecol. 20: 73 - 82.
– reference: Mazerolle, M. J. and Villard, M. A.. 1999. Patch characteristics and landscape context as predictors of species presence and abundance: a review. Ecoscience 6: 117 - 124.
– reference: Eversham, B. C. et al. 1996. Urban, industrial and other manmade sites as analogues of natural habitats for Carabidae. Ann. Zool. Fenn. 33: 149 - 156.
– reference: Ferrier, S. et al. 2002. Extended statistical approaches to modelling spatial pattern in biodiversity in northeast New South Wales. I. Species-level modelling. Biodiv. Conserv. 11: 2275 - 2307.
– reference: Gibson, L. A. et al. 2004. Spatial prediction of rufous bristlebird habitat in a coastal heathland: a GIS-based approach. J. Appl. Ecol. 41: 213 - 223.
– reference: Hirzel, A. and Guisan, A.. 2002. Which is the optimal sampling strategy for habitat suitability modelling. Ecol. Modell. 157: 331 - 341.
– reference: Rushton, S. P. et al. 2004. New paradigms for modelling species distributions?. J. Appl. Ecol. 41: 193 - 200.
– reference: Olden, J. D. and Jackson, D. A.. 2000. Torturing data for the sake of generality: how valid are our regression models?. Ecoscience 7: 501 - 510.
– reference: Peppler-Lisbach, C. and Schröder, B.. 2004. Predicting the species composition of Nardus stricta communities by logistic regression modelling. J. Veg. Sci. 15: 623 - 634.
– reference: Cronin, J.. 2004. Host-parasitoid extinction and colonization in a fragmented prairie landscape. Oecologia 139: 503 - 514.
– reference: Olden, J. D.. 2003. A species-specific approach to modeling biological communities and its potential for conservation. Conserv. Biol. 17: 854 - 863.
– reference: Schuhmacher, O. and Fartmann, T.. 2003. Wie mobil ist der Warzenbeißer? Eine populationsökologische Studie zum Ausbreitungsverhalten von Decticus verrucivoris. Naturschutz und Landschaftsplanung 35: 20 - 28.
– reference: Holland, J. D. et al. 2004. Determining the spatial scale of species' response to habitat. Bioscience 54: 227 - 233.
– reference: Sadler, J. P. et al. 2006. Investigating environmental variation and landscape characteristics of an urban-rural gradient using woodland carabid assemblages. J. Biogeogr. 33: 1126 - 1138.
– reference: Brocksieper, R.. 1978. Der Einfluß des Mikroklimas auf die Verbreitung der Laubheuschrecken, Grillen und Feldheuschrecken im Siebengebirge und auf dem Rodderberg bei Bonn (Orthopera: Saltatoria). Decheniana-Beihefte 21: 1 - 141.
– reference: Niemelä, J. et al. 2002. Carabid beetle assemblages (Coleoptera, Carabidae) across urban-rural gradients: an international comparison. Landscape Ecol. 17: 387 - 401.
– reference: Small, E. et al. 2006. Do landscape factors affect brownfield carabid assemblages?. Sci. Total Environ. 360: 205 - 222.
– reference: Vaughan, I. P. and Ormerod, S. J.. 2005. The continuing challenges of testing species distribution models. J. Appl. Ecol. 42: 720 - 730.
– reference: Grand, J. and Mello, M. J.. 2004. A multi-scale analysis of species-environment relationships: rare moths in a pitch pine-scrub oak (Pinus rigida-Quercus ilicifolia) community. Biol. Conserv. 119: 495 - 506.
– reference: Zehm, A. et al. 2003. Muliparameter analysis of vertical vegetation structure based on digital imaging processing. Flora 198: 142 - 160.
– reference: Steffan-Dewenter, I. and Tscharntke, T.. 1997. Early succession of butterfly and plant communities on set-aside fields. Oecologia 109: 294 - 302.
– reference: Guisan, A. and Zimmermann, N. E.. 2000. Predictive habitat distribution models in ecology. Ecol. Modell. 135: 147 - 186.
– reference: Wood, B. C. and Pullin, A. S.. 2002. Persistence of species in a fragmented urban landscape: the importance of dispersal ability and habitat availability for grassland butterflies. Biodiv. Conserv. 11: 1451 - 1468.
– reference: Hollier, J. A. et al. 1994. Successional leafhopper assemblages-pattern and process. Ecol. Res. 9: 185 - 191.
– reference: Cushman, S. A. and McGarigal, K.. 2004. Patterns in the species-environment relationship depend on both scale and choice of response variables. Oikos 105: 117 - 124.
– reference: Pearce, J. and Ferrier, S.. 2001. The practical value of modelling relative abundance of species for regional conservation planning: a case study. Biol. Conserv. 98: 33 - 43.
– reference: Sanderson, R. A.. 1992. Hemiptera of naturally vegetated derelict land in north-west England. Entomol. Gaz. 43: 221 - 226.
– reference: Fielding, A. H. and Bell, J. F.. 1997. A review of methods for the assessment of prediction errors in conservation presence-absence models. Environ. Conserv. 24: 38 - 49.
– reference: Small, E. C. et al. 2003. Carabid beetle assemblages on urban derelict sites in Birmingham, UK. J. Insect Conserv. 6: 233 - 246.
– reference: Brown, V. K. et al. 1992. Community organisation in leaf hoppers. Oikos 65: 97 - 106.
– reference: Radford, J. Q. and Bennett, A. F.. 2004. Thresholds in landscape parameters: occurrence of the white-browed treecreeper Climacteris affinis in Victoria, Australia. Biol. Conserv. 117: 375 - 391.
– reference: Morris, M. G.. 2000. The effects of structure and its dynamics on the ecology and conservation of arthropods in British grasslands. Biol. Conserv. 95: 129 - 142.
– reference: Purtauf, T. et al. 2004. Carabid communities in the spatio-temporal mosaic of a rural landscape. Landscape Urban Plann. 67: 185 - 193.
– reference: Cherrill, A. J. and Rushton, S. P.. 1993. The Auchenorhyncha of an unimproved moorland in northern England. Ecol. Entomol. 18: 95 - 103.
– reference: Gustafson, E. J.. 1998. Quantifying landscape spatial pattern: What is the state of the art?. Ecosystems 1: 143 - 156.
– reference: Austin, M. P.. 2002. Spatial prediction of species distribution: an interface between ecological theory and statistical modelling. Ecol. Modell. 157: 101 - 118.
– reference: Biedermann, R.. 2002. Mating success in the spittlebug Cercopis sanguinolenta (Scopoli, 1763) (Homoptera, Cercopidae): the role of body size and mobility. J. Ethol. 20: 13 - 18.
– reference: Heinze, G. and Schemper, M.. 2002. A solution to the problem of separation in logistic regression. Stat. Med. 21: 2409 - 2419.
– reference: Niemelä, J.. 1999. Is there a need for a theory of urban ecology?. Urban Ecosyst. 3: 57 - 65.
– volume: 21
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Snippet In urban brownfields (derelict sites), we studied the influence of local factors (successional age, vegetation structure, soil) and landscape context (spatial...
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SubjectTerms Animal and plant ecology
Animal, plant and microbial ecology
Biological and medical sciences
Brownfields
Ecological modeling
Fundamental and applied biological sciences. Psychology
Grasses
Insecta
Invertebrates
Landscapes
Modeling
Pioneer species
Species
Synecology
Terrestrial ecosystems
Urban habitats
Vegetation
Vegetation structure
Title Urban brownfields as temporary habitats: driving forces for the diversity of phytophagous insects
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https://www.jstor.org/stable/30243187
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Volume 29
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