Protected habitats of Natura 2000 do not coincide with important diversity hotspots of arthropods in mountain grasslands

Biodiversity assessments for conservation planning are often restricted to a limited set of species. This is also the case in the context of Natura 2000, where surveys focus strongly on vegetation and selected vertebrate species. Without cross‐taxon congruence, however, this approach does not guarantee that the relevant aspects of biodiversity are appropriately represented. We here assess the diversity of vascular plants, carabid beetles and spiders in mountain grasslands of the European Alps. We address the questions whether there are distinct species assemblages in different habitats and whether these assemblages show sufficient cross‐taxon congruence. Furthermore, we test whether habitats that are protected based on vegetation characteristics also inhabit an arthropod fauna with highest conservation value. We found only weak agreement in assemblage composition and no positive correlation in species richness across the three focal taxa. Furthermore, we found a negative correlation between species richness of plants and carabids, indicating opposing taxon‐specific responses to habitat differences and land use intensity. Species richness was higher at protected sites for plants, but not for carabids and spiders. This applied also to the subset of species with highest conservation value. Our results show that prioritisation of sites for conservation based solely on vegetational aspects does not necessarily coincide with important sites for arthropods. This calls for a multi‐taxon approach in conservation planning to cover more of the endangered and range‐restricted species. Species‐ and surrogate‐based conservation efforts, like the Natura 2000 directive, should therefore be extended to embrace the diversity of arthropods.

[1]  J. Lobo,et al.  Effectiveness of the Natura 2000 network in protecting Iberian endemic fauna , 2018 .

[2]  J. Heino,et al.  Biological surrogates: A word of caution , 2018 .

[3]  C. Hallmann,et al.  Analysis of insect monitoring data from De Kaaistoep and Drenthe , 2018 .

[4]  H. de Kroon,et al.  More than 75 percent decline over 27 years in total flying insect biomass in protected areas , 2017, PloS one.

[5]  Donald A. Jackson,et al.  How well do multivariate data sets match? The advantages of a Procrustean superimposition approach over the Mantel test , 2001, Oecologia.

[6]  Wolfgang Nentwig,et al.  World Spider Catalog , 2017 .

[7]  Malgorzata Blicharska,et al.  Gaps in ecological research on the world's largest internationally coordinated network of protected areas: A review of Natura 2000 , 2016 .

[8]  C. Wirth,et al.  Multitrophic diversity in a biodiverse forest is highly nonlinear across spatial scales , 2015, Nature Communications.

[9]  D. Lindenmayer,et al.  Robustness of habitat‐based surrogates of animal diversity: a multitaxa comparison over time , 2014 .

[10]  P. Peres‐Neto,et al.  Much beyond Mantel: Bringing Procrustes Association Metric to the Plant and Soil Ecologist’s Toolbox , 2014, PloS one.

[11]  P. W. Lane,et al.  Global meta-analysis reveals low consistency of biodiversity congruence relationships , 2014, Nature Communications.

[12]  T. Wrbka,et al.  Species richness in dry grassland patches of eastern Austria: A multi-taxon study on the role of local, landscape and habitat quality variables , 2014 .

[13]  A. Proelss,et al.  Europe Needs a New Vision for a Natura 2020 Network , 2013 .

[14]  A. Provenzale,et al.  Patterns of biodiversity in the northwestern Italian Alps: a multi-taxa approach , 2013 .

[15]  W. Blanckenhorn,et al.  Vascular plants as surrogates of butterfly and grasshopper diversity on two Swiss subalpine summer pastures , 2013, Biodiversity and Conservation.

[16]  P. Cardoso Habitats Directive species lists: urgent need of revision , 2012 .

[17]  C. Drees,et al.  When to sample in an inaccessible landscape: a case study with carabids from the Allgäu (northern Alps) (Coleoptera, Carabidae) , 2011, ZooKeys.

[18]  J. Feehan,et al.  Evaluating and interpreting cross-taxon congruence: Potential pitfalls and solutions , 2011 .

[19]  P. Vera,et al.  Land use and biodiversity congruences at local scale: applications to conservation strategies , 2011, Biodiversity and Conservation.

[20]  J. Habel,et al.  Biodiversity Hotspots: Distribution and Protection of Conservation Priority Areas , 2011 .

[21]  D. Bedford Vascular plants , 2011 .

[22]  M. Cadotte,et al.  Quantifying Biodiversity: Does It Matter What We Measure? , 2011 .

[23]  William N. Venables,et al.  Modern Applied Statistics with S , 2010 .

[24]  A. Schuldt,et al.  Invertebrate diversity and national responsibility for species conservation across Europe – A multi-taxon approach , 2010 .

[25]  R. Noss,et al.  The Effectiveness of Surrogate Taxa for the Representation of Biodiversity , 2010, Conservation biology : the journal of the Society for Conservation Biology.

[26]  J. Lamarque,et al.  Global Biodiversity: Indicators of Recent Declines , 2010, Science.

[27]  J. Heino Are indicator groups and cross-taxon congruence useful for predicting biodiversity in aquatic ecosystems? , 2010 .

[28]  D. Rocchini,et al.  Simple to sample: Vascular plants as surrogate group in a nature reserve , 2010 .

[29]  Oliver-D. Finch,et al.  Indicators of species richness at the local scale in an alpine region: a comparative approach between plant and invertebrate taxa , 2010, Biodiversity and Conservation.

[30]  P. Fontana,et al.  Impact of farm size and topography on plant and insect diversity of managed grasslands in the Alps , 2009 .

[31]  J. Barlow,et al.  The cost-effectiveness of biodiversity surveys in tropical forests. , 2008, Ecology letters.

[32]  M. Vellend,et al.  Using subsets of species in biodiversity surveys , 2007 .

[33]  R. Slotow,et al.  Assessment of congruency across invertebrate taxa and taxonomic levels to identify potential surrogates , 2007 .

[34]  M. Cabeza,et al.  Top predators: hot or not? A call for systematic assessment of biodiversity surrogates , 2007 .

[35]  Eddy van der Maarel Transformation of cover-abundance values for appropriate numerical treatment – Alternatives to the proposals by Podani , 2007 .

[36]  A. Klein,et al.  Importance of pollinators in changing landscapes for world crops , 2007, Proceedings of the Royal Society B: Biological Sciences.

[37]  Taylor H. Ricketts,et al.  Effectiveness of biodiversity indicators varies with extent, grain, and region , 2006 .

[38]  Volkmar Wolters,et al.  Relationship among the species richness of different taxa. , 2006, Ecology.

[39]  J. Heino,et al.  Spatial scale affects community concordance among fishes, benthic macroinvertebrates, and bryophytes in streams. , 2006, Ecological applications : a publication of the Ecological Society of America.

[40]  Katherine A. Eschelbach,et al.  Recommendations for Assessing the Effectiveness of Surrogate Species Approaches , 2006, Biodiversity & Conservation.

[41]  S. Dorn,et al.  Cross-taxon congruence of species diversity and community similarity among three insect taxa in a mosaic landscape , 2005 .

[42]  M. Anand,et al.  Diversity Relationships among Taxonomic Groups in Recovering and Restored Forests , 2005 .

[43]  Joanna Grand,et al.  A Multiscale Landscape Approach to Predicting Bird and Moth Rarity Hotspots in a Threatened Pitch Pine–Scrub Oak Community , 2004 .

[44]  A. Tribsch Areas of endemism of vascular plants in the Eastern Alps in relation to Pleistocene glaciation , 2004 .

[45]  Norbert Sauberer,et al.  Surrogate taxa for biodiversity in agricultural landscapes of eastern Austria , 2004 .

[46]  Mark E. Jakubauskas,et al.  Beyond Species Richness: Community Similarity as a Measure of Cross‐Taxon Congruence for Coarse‐Filter Conservation , 2004 .

[47]  D. J. Kotze,et al.  Support for the Multi-taxa Approach in Biodiversity Assessment, as Shown by Epigaeic Invertebrates in an Afromontane Forest Archipelago , 1999, Journal of Insect Conservation.

[48]  J. Niemelä,et al.  Threatened species in a vanishing habitat: plants and invertebrates in calcareous grasslands in the Swiss Jura mountains , 1998, Biodiversity & Conservation.

[49]  T. Solhøy,et al.  Vascular plants as a surrogate species group in complementary site selection for bryophytes, macrolichens, spiders, carabids, staphylinids, snails, and wood living polypore fungi in a northern forest , 2004 .

[50]  B. Söderström,et al.  Species‐Richness Correlations of Six Different Taxa in Swedish Seminatural Grasslands , 2002 .

[51]  R. Mittermeier,et al.  Biodiversity hotspots for conservation priorities , 2000, Nature.

[52]  D. Pearson,et al.  The influence of spatial scale on cross‐taxon congruence patterns and prediction accuracy of species richness , 1999 .

[53]  J. Lawton,et al.  The Gaps between Theory and Practice in Selecting Nature Reserves , 1999 .

[54]  C. Margules Biodiversity: A biology of numbers and differences: Edited by Kevin J. Gaston Blackwell Science, 1996. £24.50 pbk (x + 396 pages) ISBN 0 86542 804 2 , 1997 .

[55]  Kevin J. Gaston,et al.  Biodiversity : a biology of numbers and difference , 1996 .

[56]  C. Romão,et al.  Interpretation manual of European Union habitats. , 1996 .

[57]  Donald A. Jackson PROTEST: A PROcrustean Randomization TEST of community environment concordance , 1995 .

[58]  J. Lawton,et al.  Rare species, the coincidence of diversity hotspots and conservation strategies , 1993, Nature.

[59]  R. Noss Indicators for Monitoring Biodiversity: A Hierarchical Approach , 1990 .

[60]  S. Rushton,et al.  The ground beetle and spider fauna of managed and unimproved upland pasture. , 1989 .

[61]  M. Roberts The Spiders of Great Britain and Ireland. , 1985 .

[62]  John C. Gower,et al.  Statistical methods of comparing different multivariate analyses of the same data , 1971 .

[63]  F. Fukarek Pflanzensoziologie , 1964 .

[64]  K. Holdhaus Die Spuren der Eiszeit in der Tierwelt Europas. : Zool-Botan Ges , 1954 .

[65]  Do ent Dr. J. Braun-Blanquet,et al.  Pflan?enso?iologie: Grund?uge der Vegetationskunde , 1928 .