42 results on '"Lindborg R"'
Search Results
2. Nature conservation for what? Analyses of urban and rural nature reserves in southern Sweden 1909–2006
- Author
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Borgström, S., Lindborg, R., and Elmqvist, T.
- Published
- 2013
- Full Text
- View/download PDF
3. Outside the boundary – Land use changes in the surroundings of urban nature reserves
- Author
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Borgström, S., Cousins, S.A.O., and Lindborg, R.
- Published
- 2012
- Full Text
- View/download PDF
4. Services écosystémiques fournis par les prairies seminaturelles et améliorées - synergies, compromis et bouquets de services.
- Author
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Lindborg, R., Bernués, A., Hartel, T., Helm, A., and Ripoll-Bosch, R.
- Published
- 2023
5. Benchmarking plant diversity of Palaearctic grasslands and other open habitats
- Author
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Biurrun, I., Pielech, R., Dembicz, I., Gillet, F., Kozub, Ł., Marcenò, C., Reitalu, T., Van Meerbeek, K., Guarino, R., Chytrý, M., Pakeman, R.J., Preislerová, Z., Axmanová, I., Burrascano, S., Bartha, S., Boch, S., Bruun, H.H., Conradi, T., De Frenne, P., Essl, F., Filibeck, G., Hájek, M., Jiménez-Alfaro, B., Kuzemko, A., Molnár, Z., Pärtel, M., Pätsch, R., Prentice, H.C., Roleček, J., Sutcliffe, L.M.E., Terzi, M., Winkler, M., Wu, J., Aćić, S., Acosta, A.T.R., Afif, E., Akasaka, M., Alatalo, J.M., Aleffi, M., Aleksanyan, A., Ali, A., Apostolova, I., Ashouri, P., Bátori, Z., Baumann, E., Becker, T., Belonovskaya, E., Benito Alonso, J.L., Berastegi, A., Bergamini, A., Bhatta, K.P., Bonini, I., Büchler, M.-O., Budzhak, V., Bueno, Á., Buldrini, F., Campos, J.A., Cancellieri, L., Carboni, M., Ceulemans, T., Chiarucci, A., Chocarro, C., Conti, L., Csergő, A.M., Cykowska-Marzencka, B., Czarniecka-Wiera, M., Czarnocka-Cieciura, M., Czortek, P., Danihelka, J., de Bello, F., Deák, B., Demeter, L., Deng, L., Diekmann, M., Dolezal, J., Dolnik, C., Dřevojan, P., Dupré, C., Ecker, K., Ejtehadi, H., Erschbamer, B., Etayo, J., Etzold, J., Farkas, T., Farzam, M., Fayvush, G., Fernández Calzado, M.R., Finckh, M., Fjellstad, W., Fotiadis, G., García-Magro, D., García-Mijangos, I., Gavilán, R.G., Germany, M., Ghafari, S., Giusso del Galdo, G.P., Grytnes, J.-A., Güler, B., Gutiérrez-Girón, A., Helm, A., Herrera, M., Hüllbusch, E.M., Ingerpuu, N., Jägerbrand, A.K., Jandt, U., Janišová, M., Jeanneret, P., Jeltsch, F., Jensen, K., Jentsch, A., Kącki, Z., Kakinuma, K., Kapfer, J., Kargar, M., Kelemen, A., Kiehl, K., Kirschner, P., Koyama, A., Langer, N., Lazzaro, L., Lepš, J., Li, C.-F., Li, F.Y., Liendo, D., Lindborg, R., Löbel, S., Lomba, A., Lososová, Z., Lustyk, P., Luzuriaga, A.L., Ma, W., Maccherini, S., Magnes, M., Malicki, M., Manthey, M., Mardari, C., May, F., Mayrhofer, H., Meier, E.S., Memariani, F., Merunková, K., Michelsen, O., Molero Mesa, J., Moradi, H., Moysiyenko, I., Mugnai, M., Naqinezhad, A., Natcheva, R., Ninot, J.M., Nobis, M., Noroozi, J., Nowak, A., Onipchenko, V., Palpurina, S., Pauli, H., Pedashenko, H., Pedersen, C., Peet, R.K., Pérez-Haase, A., Peters, J., Pipenbaher, N., Pirini, C., Pladevall-Izard, E., Plesková, Z., Potenza, G., Rahmanian, S., Rodríguez-Rojo, M.P., Ronkin, V., Rosati, L., Ruprecht, E., Rusina, S., Sabovljević, M., Sanaei, A., Sánchez, A.M., Santi, F., Savchenko, G., Sebastià, M.T., Shyriaieva, D., Silva, V., Škornik, S., Šmerdová, E., Sonkoly, J., Sperandii, M.G., Staniaszek-Kik, M., Stevens, C., Stifter, S., Suchrow, S., Swacha, G., Świerszcz, S., Talebi, A., Teleki, B., Tichý, L., Tölgyesi, C., Torca, M., Török, P., Tsarevskaya, N., Tsiripidis, I., Turisová, I., Ushimaru, A., Valkó, O., Van Mechelen, C., Vanneste, T., Vasheniak, I., Vassilev, K., Viciani, D., Villar, L., Virtanen, R., Vitasović-Kosić, I., Vojtkó, A., Vynokurov, D., Waldén, E., Wang, Y., Weiser, F., Wen, L., Wesche, K., White, H., Widmer, S., Wolfrum, S., Wróbel, A., Yuan, Z., Zelený, D., Zhao, L., Dengler, J., Biurrun, I., Pielech, R., Dembicz, I., Gillet, F., Kozub, Ł., Marcenò, C., Reitalu, T., Van Meerbeek, K., Guarino, R., Chytrý, M., Pakeman, R.J., Preislerová, Z., Axmanová, I., Burrascano, S., Bartha, S., Boch, S., Bruun, H.H., Conradi, T., De Frenne, P., Essl, F., Filibeck, G., Hájek, M., Jiménez-Alfaro, B., Kuzemko, A., Molnár, Z., Pärtel, M., Pätsch, R., Prentice, H.C., Roleček, J., Sutcliffe, L.M.E., Terzi, M., Winkler, M., Wu, J., Aćić, S., Acosta, A.T.R., Afif, E., Akasaka, M., Alatalo, J.M., Aleffi, M., Aleksanyan, A., Ali, A., Apostolova, I., Ashouri, P., Bátori, Z., Baumann, E., Becker, T., Belonovskaya, E., Benito Alonso, J.L., Berastegi, A., Bergamini, A., Bhatta, K.P., Bonini, I., Büchler, M.-O., Budzhak, V., Bueno, Á., Buldrini, F., Campos, J.A., Cancellieri, L., Carboni, M., Ceulemans, T., Chiarucci, A., Chocarro, C., Conti, L., Csergő, A.M., Cykowska-Marzencka, B., Czarniecka-Wiera, M., Czarnocka-Cieciura, M., Czortek, P., Danihelka, J., de Bello, F., Deák, B., Demeter, L., Deng, L., Diekmann, M., Dolezal, J., Dolnik, C., Dřevojan, P., Dupré, C., Ecker, K., Ejtehadi, H., Erschbamer, B., Etayo, J., Etzold, J., Farkas, T., Farzam, M., Fayvush, G., Fernández Calzado, M.R., Finckh, M., Fjellstad, W., Fotiadis, G., García-Magro, D., García-Mijangos, I., Gavilán, R.G., Germany, M., Ghafari, S., Giusso del Galdo, G.P., Grytnes, J.-A., Güler, B., Gutiérrez-Girón, A., Helm, A., Herrera, M., Hüllbusch, E.M., Ingerpuu, N., Jägerbrand, A.K., Jandt, U., Janišová, M., Jeanneret, P., Jeltsch, F., Jensen, K., Jentsch, A., Kącki, Z., Kakinuma, K., Kapfer, J., Kargar, M., Kelemen, A., Kiehl, K., Kirschner, P., Koyama, A., Langer, N., Lazzaro, L., Lepš, J., Li, C.-F., Li, F.Y., Liendo, D., Lindborg, R., Löbel, S., Lomba, A., Lososová, Z., Lustyk, P., Luzuriaga, A.L., Ma, W., Maccherini, S., Magnes, M., Malicki, M., Manthey, M., Mardari, C., May, F., Mayrhofer, H., Meier, E.S., Memariani, F., Merunková, K., Michelsen, O., Molero Mesa, J., Moradi, H., Moysiyenko, I., Mugnai, M., Naqinezhad, A., Natcheva, R., Ninot, J.M., Nobis, M., Noroozi, J., Nowak, A., Onipchenko, V., Palpurina, S., Pauli, H., Pedashenko, H., Pedersen, C., Peet, R.K., Pérez-Haase, A., Peters, J., Pipenbaher, N., Pirini, C., Pladevall-Izard, E., Plesková, Z., Potenza, G., Rahmanian, S., Rodríguez-Rojo, M.P., Ronkin, V., Rosati, L., Ruprecht, E., Rusina, S., Sabovljević, M., Sanaei, A., Sánchez, A.M., Santi, F., Savchenko, G., Sebastià, M.T., Shyriaieva, D., Silva, V., Škornik, S., Šmerdová, E., Sonkoly, J., Sperandii, M.G., Staniaszek-Kik, M., Stevens, C., Stifter, S., Suchrow, S., Swacha, G., Świerszcz, S., Talebi, A., Teleki, B., Tichý, L., Tölgyesi, C., Torca, M., Török, P., Tsarevskaya, N., Tsiripidis, I., Turisová, I., Ushimaru, A., Valkó, O., Van Mechelen, C., Vanneste, T., Vasheniak, I., Vassilev, K., Viciani, D., Villar, L., Virtanen, R., Vitasović-Kosić, I., Vojtkó, A., Vynokurov, D., Waldén, E., Wang, Y., Weiser, F., Wen, L., Wesche, K., White, H., Widmer, S., Wolfrum, S., Wróbel, A., Yuan, Z., Zelený, D., Zhao, L., and Dengler, J.
- Abstract
Aims: Understanding fine-grain diversity patterns across large spatial extents is fundamental for macroecological research and biodiversity conservation. Using the GrassPlot database, we provide benchmarks of fine-grain richness values of Palaearctic open habitats for vascular plants, bryophytes, lichens and complete vegetation (i.e., the sum of the former three groups). Location: Palaearctic biogeographic realm. Methods: We used 126,524 plots of eight standard grain sizes from the GrassPlot database: 0.0001, 0.001, 0.01, 0.1, 1, 10, 100 and 1,000 m2 and calculated the mean richness and standard deviations, as well as maximum, minimum, median, and first and third quartiles for each combination of grain size, taxonomic group, biome, region, vegetation type and phytosociological class. Results: Patterns of plant diversity in vegetation types and biomes differ across grain sizes and taxonomic groups. Overall, secondary (mostly semi-natural) grasslands and natural grasslands are the richest vegetation type. The open-access file ”GrassPlot Diversity Benchmarks” and the web tool “GrassPlot Diversity Explorer” are now available online (https://edgg.org/databases/GrasslandDiversityExplorer) and provide more insights into species richness patterns in the Palaearctic open habitats. Conclusions: The GrassPlot Diversity Benchmarks provide high-quality data on species richness in open habitat types across the Palaearctic. These benchmark data can be used in vegetation ecology, macroecology, biodiversity conservation and data quality checking. While the amount of data in the underlying GrassPlot database and their spatial coverage are smaller than in other extensive vegetation-plot databases, species recordings in GrassPlot are on average more complete, making it a valuable complementary data source in macroecology.
- Published
- 2021
6. Benchmarking plant diversity of Palaearctic grasslands and other open habitats
- Author
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Biurrun, I. (Idoia), Pielech, R. (Remigiusz), Dembicz, I. (Iwona), Gillet, F. (Francois), Kozub, L. (Lukasz), Marceno, C. (Corrado), Reitalu, T. (Triin), Van Meerbeek, K. (Koenraad), Guarino, R. (Riccardo), Chytry, M. (Milan), Pakeman, R. J. (Robin J.), Preislerova, Z. (Zdenka), Axmanova, I. (Irena), Burrascano, S. (Sabina), Bartha, S. (Sandor), Boch, S. (Steffen), Bruun, H. H. (Hans Henrik), Conradi, T. (Timo), De Frenne, P. (Pieter), Essl, F. (Franz), Filibeck, G. (Goffredo), Hajek, M. (Michal), Jimenez-Alfaro, B. (Borja), Kuzemko, A. (Anna), Molnar, Z. (Zsolt), Partel, M. (Meelis), Patsch, R. (Ricarda), Prentice, H. C. (Honor C.), Rolecek, J. (Jan), Sutcliffe, L. M. (Laura M. E.), Terzi, M. (Massimo), Winkler, M. (Manuela), Wu, J. (Jianshuang), Acic, S. (Svetlana), Acosta, A. T. (Alicia T. R.), Afif, E. (Elias), Akasaka, M. (Munemitsu), Alatalo, J. M. (Juha M.), Aleffi, M. (Michele), Aleksanyan, A. (Alla), Ali, A. (Arshad), Apostolova, I. (Iva), Ashouri, P. (Parvaneh), Batori, Z. (Zoltan), Baumann, E. (Esther), Becker, T. (Thomas), Belonovskaya, E. (Elena), Benito Alonso, J. L. (Jose Luis), Berastegi, A. (Asun), Bergamini, A. (Ariel), Bhatta, K. P. (Kuber Prasad), Bonini, I. (Ilaria), Buchler, M.-O. (Marc-Olivier), Budzhak, V. (Vasyl), Bueno, A. (Alvaro), Buldrini, F. (Fabrizio), Campos, J. A. (Juan Antonio), Cancellieri, L. (Laura), Carboni, M. (Marta), Ceulemans, T. (Tobias), Chiarucci, A. (Alessandro), Chocarro, C. (Cristina), Conti, L. (Luisa), Csergo, A. M. (Anna Maria), Cykowska-Marzencka, B. (Beata), Czarniecka-Wiera, M. (Marta), Czarnocka-Cieciura, M. (Marta), Czortek, P. (Patryk), Danihelka, J. (Jiri), Bello, F. (Francesco), Deak, B. (Balazs), Demeter, L. (Laszlo), Deng, L. (Lei), Diekmann, M. (Martin), Dolezal, J. (Jiri), Dolnik, C. (Christian), Drevojan, P. (Pavel), Dupre, C. (Cecilia), Ecker, K. (Klaus), Ejtehadi, H. (Hamid), Erschbamer, B. (Brigitta), Etayo, J. (Javier), Etzold, J. (Jonathan), Farkas, T. (Tunde), Farzam, M. (Mohammad), Fayvush, G. (George), Fernandez Calzado, M. R. (Maria Rosa), Finckh, M. (Manfred), Fjellstad, W. (Wendy), Fotiadis, G. (Georgios), Garcia-Magro, D. (Daniel), Garcia-Mijangos, I. (Itziar), Gavilan, R. G. (Rosario G.), Germany, M. (Markus), Ghafari, S. (Sahar), del Galdo, G. P. (Gian Pietro Giusso), Grytnes, J.-A. (John-Arvid), Guler, B. (Behlul), Gutierrez-Giron, A. (Alba), Helm, A. (Aveliina), Herrera, M. (Mercedes), Hullbusch, E. M. (Elisabeth M.), Ingerpuu, N. (Nele), Jaegerbrand, A. K. (Annika K.), Jandt, U. (Ute), Janisova, M. (Monika), Jeanneret, P. (Philippe), Jeltsch, F. (Florian), Jensen, K. (Kai), Jentsch, A. (Anke), Kacki, Z. (Zygmunt), Kakinuma, K. (Kaoru), Kapfer, J. (Jutta), Kargar, M. (Mansoureh), Kelemen, A. (Andras), Kiehl, K. (Kathrin), Kirschner, P. (Philipp), Koyama, A. (Asuka), Langer, N. (Nancy), Lazzaro, L. (Lorenzo), Leps, J. (Jan), Li, C.-F. (Ching-Feng), Li, F. Y. (Frank Yonghong), Liendo, D. (Diego), Lindborg, R. (Regina), Loebel, S. (Swantje), Lomba, A. (Angela), Lososova, Z. (Zdenka), Lustyk, P. (Pavel), Luzuriaga, A. L. (Arantzazu L.), Ma, W. (Wenhong), Maccherini, S. (Simona), Magnes, M. (Martin), Malicki, M. (Marek), Manthey, M. (Michael), Mardari, C. (Constantin), May, F. (Felix), Mayrhofer, H. (Helmut), Meier, E. S. (Eliane Seraina), Memariani, F. (Farshid), Merunkova, K. (Kristina), Michelsen, O. (Ottar), Molero Mesa, J. (Joaquin), Moradi, H. (Halime), Moysiyenko, I. (Ivan), Mugnai, M. (Michele), Naqinezhad, A. (Alireza), Natcheva, R. (Rayna), Ninot, J. M. (Josep M.), Nobis, M. (Marcin), Noroozi, J. (Jalil), Nowak, A. (Arkadiusz), Onipchenko, V. (Vladimir), Palpurina, S. (Salza), Pauli, H. (Harald), Pedashenko, H. (Hristo), Pedersen, C. (Christian), Peet, R. K. (Robert K.), Perez-Haase, A. (Aaron), Peters, J. (Jan), Pipenbaher, N. (Natasa), Pirini, C. (Chrisoula), Pladevall-Izard, E. (Eulalia), Pleskova, Z. (Zuzana), Potenza, G. (Giovanna), Rahmanian, S. (Soroor), Rodriguez-Rojo, M. P. (Maria Pilar), Ronkin, V. (Vladimir), Rosati, L. (Leonardo), Ruprecht, E. (Eszter), Rusina, S. (Solvita), Sabovljevic, M. (Marko), Sanaei, A. (Anvar), Sanchez, A. M. (Ana M.), Santi, F. (Francesco), Savchenko, G. (Galina), Teresa Sebastia, M. (Maria), Shyriaieva, D. (Dariia), Silva, V. (Vasco), Skornik, S. (Sonja), Smerdova, E. (Eva), Sonkoly, J. (Judit), Sperandii, M. G. (Marta Gaia), Staniaszek-Kik, M. (Monika), Stevens, C. (Carly), Stifter, S. (Simon), Suchrow, S. (Sigrid), Swacha, G. (Grzegorz), Swierszcz, S. (Sebastian), Talebi, A. (Amir), Teleki, B. (Balazs), Tichy, L. (Lubomir), Tolgyesi, C. (Csaba), Torca, M. (Marta), Torok, P. (Peter), Tsarevskaya, N. (Nadezda), Tsiripidis, I. (Ioannis), Turisova, I. (Ingrid), Ushimaru, A. (Atushi), Valko, O. (Orsolya), Van Mechelen, C. (Carmen), Vanneste, T. (Thomas), Vasheniak, I. (Iuliia), Vassilev, K. (Kiril), Viciani, D. (Daniele), Villar, L. (Luis), Virtanen, R. (Risto), Vitasovic-Kosic, I. (Ivana), Vojtko, A. (Andras), Vynokurov, D. (Denys), Walden, E. (Emelie), Wang, Y. (Yun), Weiser, F. (Frank), Wen, L. (Lu), Wesche, K. (Karsten), White, H. (Hannah), Widmer, S. (Stefan), Wolfrum, S. (Sebastian), Wrobel, A. (Anna), Yuan, Z. (Zuoqiang), Zeleny, D. (David), Zhao, L. (Liqing), Dengler, J. (Jurgen), Biurrun, I. (Idoia), Pielech, R. (Remigiusz), Dembicz, I. (Iwona), Gillet, F. (Francois), Kozub, L. (Lukasz), Marceno, C. (Corrado), Reitalu, T. (Triin), Van Meerbeek, K. (Koenraad), Guarino, R. (Riccardo), Chytry, M. (Milan), Pakeman, R. J. (Robin J.), Preislerova, Z. (Zdenka), Axmanova, I. (Irena), Burrascano, S. (Sabina), Bartha, S. (Sandor), Boch, S. (Steffen), Bruun, H. H. (Hans Henrik), Conradi, T. (Timo), De Frenne, P. (Pieter), Essl, F. (Franz), Filibeck, G. (Goffredo), Hajek, M. (Michal), Jimenez-Alfaro, B. (Borja), Kuzemko, A. (Anna), Molnar, Z. (Zsolt), Partel, M. (Meelis), Patsch, R. (Ricarda), Prentice, H. C. (Honor C.), Rolecek, J. (Jan), Sutcliffe, L. M. (Laura M. E.), Terzi, M. (Massimo), Winkler, M. (Manuela), Wu, J. (Jianshuang), Acic, S. (Svetlana), Acosta, A. T. (Alicia T. R.), Afif, E. (Elias), Akasaka, M. (Munemitsu), Alatalo, J. M. (Juha M.), Aleffi, M. (Michele), Aleksanyan, A. (Alla), Ali, A. (Arshad), Apostolova, I. (Iva), Ashouri, P. (Parvaneh), Batori, Z. (Zoltan), Baumann, E. (Esther), Becker, T. (Thomas), Belonovskaya, E. (Elena), Benito Alonso, J. L. (Jose Luis), Berastegi, A. (Asun), Bergamini, A. (Ariel), Bhatta, K. P. (Kuber Prasad), Bonini, I. (Ilaria), Buchler, M.-O. (Marc-Olivier), Budzhak, V. (Vasyl), Bueno, A. (Alvaro), Buldrini, F. (Fabrizio), Campos, J. A. (Juan Antonio), Cancellieri, L. (Laura), Carboni, M. (Marta), Ceulemans, T. (Tobias), Chiarucci, A. (Alessandro), Chocarro, C. (Cristina), Conti, L. (Luisa), Csergo, A. M. (Anna Maria), Cykowska-Marzencka, B. (Beata), Czarniecka-Wiera, M. (Marta), Czarnocka-Cieciura, M. (Marta), Czortek, P. (Patryk), Danihelka, J. (Jiri), Bello, F. (Francesco), Deak, B. (Balazs), Demeter, L. (Laszlo), Deng, L. (Lei), Diekmann, M. (Martin), Dolezal, J. (Jiri), Dolnik, C. (Christian), Drevojan, P. (Pavel), Dupre, C. (Cecilia), Ecker, K. (Klaus), Ejtehadi, H. (Hamid), Erschbamer, B. (Brigitta), Etayo, J. (Javier), Etzold, J. (Jonathan), Farkas, T. (Tunde), Farzam, M. (Mohammad), Fayvush, G. (George), Fernandez Calzado, M. R. (Maria Rosa), Finckh, M. (Manfred), Fjellstad, W. (Wendy), Fotiadis, G. (Georgios), Garcia-Magro, D. (Daniel), Garcia-Mijangos, I. (Itziar), Gavilan, R. G. (Rosario G.), Germany, M. (Markus), Ghafari, S. (Sahar), del Galdo, G. P. (Gian Pietro Giusso), Grytnes, J.-A. (John-Arvid), Guler, B. (Behlul), Gutierrez-Giron, A. (Alba), Helm, A. (Aveliina), Herrera, M. (Mercedes), Hullbusch, E. M. (Elisabeth M.), Ingerpuu, N. (Nele), Jaegerbrand, A. K. (Annika K.), Jandt, U. (Ute), Janisova, M. (Monika), Jeanneret, P. (Philippe), Jeltsch, F. (Florian), Jensen, K. (Kai), Jentsch, A. (Anke), Kacki, Z. (Zygmunt), Kakinuma, K. (Kaoru), Kapfer, J. (Jutta), Kargar, M. (Mansoureh), Kelemen, A. (Andras), Kiehl, K. (Kathrin), Kirschner, P. (Philipp), Koyama, A. (Asuka), Langer, N. (Nancy), Lazzaro, L. (Lorenzo), Leps, J. (Jan), Li, C.-F. (Ching-Feng), Li, F. Y. (Frank Yonghong), Liendo, D. (Diego), Lindborg, R. (Regina), Loebel, S. (Swantje), Lomba, A. (Angela), Lososova, Z. (Zdenka), Lustyk, P. (Pavel), Luzuriaga, A. L. (Arantzazu L.), Ma, W. (Wenhong), Maccherini, S. (Simona), Magnes, M. (Martin), Malicki, M. (Marek), Manthey, M. (Michael), Mardari, C. (Constantin), May, F. (Felix), Mayrhofer, H. (Helmut), Meier, E. S. (Eliane Seraina), Memariani, F. (Farshid), Merunkova, K. (Kristina), Michelsen, O. (Ottar), Molero Mesa, J. (Joaquin), Moradi, H. (Halime), Moysiyenko, I. (Ivan), Mugnai, M. (Michele), Naqinezhad, A. (Alireza), Natcheva, R. (Rayna), Ninot, J. M. (Josep M.), Nobis, M. (Marcin), Noroozi, J. (Jalil), Nowak, A. (Arkadiusz), Onipchenko, V. (Vladimir), Palpurina, S. (Salza), Pauli, H. (Harald), Pedashenko, H. (Hristo), Pedersen, C. (Christian), Peet, R. K. (Robert K.), Perez-Haase, A. (Aaron), Peters, J. (Jan), Pipenbaher, N. (Natasa), Pirini, C. (Chrisoula), Pladevall-Izard, E. (Eulalia), Pleskova, Z. (Zuzana), Potenza, G. (Giovanna), Rahmanian, S. (Soroor), Rodriguez-Rojo, M. P. (Maria Pilar), Ronkin, V. (Vladimir), Rosati, L. (Leonardo), Ruprecht, E. (Eszter), Rusina, S. (Solvita), Sabovljevic, M. (Marko), Sanaei, A. (Anvar), Sanchez, A. M. (Ana M.), Santi, F. (Francesco), Savchenko, G. (Galina), Teresa Sebastia, M. (Maria), Shyriaieva, D. (Dariia), Silva, V. (Vasco), Skornik, S. (Sonja), Smerdova, E. (Eva), Sonkoly, J. (Judit), Sperandii, M. G. (Marta Gaia), Staniaszek-Kik, M. (Monika), Stevens, C. (Carly), Stifter, S. (Simon), Suchrow, S. (Sigrid), Swacha, G. (Grzegorz), Swierszcz, S. (Sebastian), Talebi, A. (Amir), Teleki, B. (Balazs), Tichy, L. (Lubomir), Tolgyesi, C. (Csaba), Torca, M. (Marta), Torok, P. (Peter), Tsarevskaya, N. (Nadezda), Tsiripidis, I. (Ioannis), Turisova, I. (Ingrid), Ushimaru, A. (Atushi), Valko, O. (Orsolya), Van Mechelen, C. (Carmen), Vanneste, T. (Thomas), Vasheniak, I. (Iuliia), Vassilev, K. (Kiril), Viciani, D. (Daniele), Villar, L. (Luis), Virtanen, R. (Risto), Vitasovic-Kosic, I. (Ivana), Vojtko, A. (Andras), Vynokurov, D. (Denys), Walden, E. (Emelie), Wang, Y. (Yun), Weiser, F. (Frank), Wen, L. (Lu), Wesche, K. (Karsten), White, H. (Hannah), Widmer, S. (Stefan), Wolfrum, S. (Sebastian), Wrobel, A. (Anna), Yuan, Z. (Zuoqiang), Zeleny, D. (David), Zhao, L. (Liqing), and Dengler, J. (Jurgen)
- Abstract
Aims: Understanding fine-grain diversity patterns across large spatial extents is fundamental for macroecological research and biodiversity conservation. Using the GrassPlot database, we provide benchmarks of fine-grain richness values of Palaearctic open habitats for vascular plants, bryophytes, lichens and complete vegetation (i.e., the sum of the former three groups). Location: Palaearctic biogeographic realm. Methods: We used 126,524 plots of eight standard grain sizes from the GrassPlot database: 0.0001, 0.001, 0.01, 0.1, 1, 10, 100 and 1,000 m² and calculated the mean richness and standard deviations, as well as maximum, minimum, median, and first and third quartiles for each combination of grain size, taxonomic group, biome, region, vegetation type and phytosociological class. Results: Patterns of plant diversity in vegetation types and biomes differ across grain sizes and taxonomic groups. Overall, secondary (mostly semi-natural) grasslands and natural grasslands are the richest vegetation type. The open-access file ”GrassPlot Diversity Benchmarks” and the web tool “GrassPlot Diversity Explorer” are now available online (https://edgg.org/databases/GrasslandDiversityExplorer) and provide more insights into species richness patterns in the Palaearctic open habitats. Conclusions: The GrassPlot Diversity Benchmarks provide high-quality data on species richness in open habitat types across the Palaearctic. These benchmark data can be used in vegetation ecology, macroecology, biodiversity conservation and data quality checking. While the amount of data in the underlying GrassPlot database and their spatial coverage are smaller than in other extensive vegetation-plot databases, species recordings in GrassPlot are on average more complete, making it a valuable complementary data source in macroecology.
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- 2021
7. Land use history and the build-up and decline of species richness in Scandinavian semi-natural grasslands
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Eriksson, O., primary, Cousins, S.A.O., additional, and Lindborg, R., additional
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- 2005
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8. Grasslands - more important for ecosystem services than you might think
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Bengtsson, J., Bullock, J.M., Egoh, B., Everson, C., Everson, T., O'Connor, T., O'Farrell, P.J., Smith, H.G., and Lindborg, R.
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Ecology and Environment - Abstract
Extensively managed grasslands are recognized globally for their high biodiversity and their social and cultural values. However, their capacity to deliver multiple ecosystem services (ES) as parts of agricultural systems is surprisingly understudied compared to other production systems. We undertook a comprehensive overview of ES provided by natural and semi‐natural grasslands, using southern Africa (SA) and northwest Europe as case studies, respectively. We show that these grasslands can supply additional non‐agricultural services, such as water supply and flow regulation, carbon storage, erosion control, climate mitigation, pollination, and cultural ES. While demand for ecosystems services seems to balance supply in natural grasslands of SA, the smaller areas of semi‐natural grasslands in Europe appear to not meet the demand for many services. We identified three bundles of related ES from grasslands: water ES including fodder production, cultural ES connected to livestock production, and population‐based regulating services (e.g., pollination and biological control), which also linked to biodiversity. Greenhouse gas emission mitigation seemed unrelated to the three bundles. The similarities among the bundles in SA and northwestern Europe suggest that there are generalities in ES relations among natural and semi‐natural grassland areas. We assessed trade‐offs and synergies among services in relation to management practices and found that although some trade‐offs are inevitable, appropriate management may create synergies and avoid trade‐offs among many services. We argue that ecosystem service and food security research and policy should give higher priority to how grasslands can be managed for fodder and meat production alongside other ES. By integrating grasslands into agricultural production systems and land‐use decisions locally and regionally, their potential to contribute to functional landscapes and to food security and sustainable livelihoods can be greatly enhanced.
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- 2019
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9. Grasslands—more important for ecosystem services than you might think
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Bengtsson, J., primary, Bullock, J. M., additional, Egoh, B., additional, Everson, C., additional, Everson, T., additional, O'Connor, T., additional, O'Farrell, P. J., additional, Smith, H. G., additional, and Lindborg, R., additional
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- 2019
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10. Land-use simplification weakens the association between terrestrial producer and consumer diversity in Europe
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Dainese, M, Isaac, NJB, Powney, GD, Bommarco, R, Ockinger, E, Kuussaari, M, Poyry, J, Benton, TG, Gabriel, D, Hodgson, JA, Kunin, WE, Lindborg, R, Sait, SM, and Marini, L
- Abstract
Land-use change is one of the primary drivers of species loss, yet little is known about its effect on other components of biodiversity that may be at risk, such as local associations between trophic levels. Here, we ask whether, and to what extent, landscape simplification, measured as the percentage of arable land in the landscape, disrupts the functional and phylogenetic association between plants and primary consumers. Across seven European regions, we inferred the potential associations (functional and phylogenetic) between host plants and butterflies in 561 semi-natural grasslands. Local plant diversity showed a strong bottom-up effect on butterfly diversity in the most complex landscapes, but this effect disappeared in simple landscapes. The functional associations between plant and butterflies are, therefore, the results of processes that act not only locally but are also dependent on the surrounding landscape context. Similarly, landscape simplification reduced the phylogenetic congruence among host plants and butterflies indicating that closely related butterfly species are more generalist in the potential resource lineages used. These processes occurred without any detectable change in species richness of plants or butterflies along the gradient of arable land. The structural properties of ecosystems are experiencing substantial erosion, with potentially pervasive effects on ecosystem functions and future evolutionary trajectories. Loss of interacting species might trigger cascading extinction events and reduce the stability of trophic interactions, as well as influence the longer-term resilience of ecosystem functions. This underscores a growing realization that species richness is a crude and insensitive metric and that both functional and phylogenetic associations, measured across multiple trophic levels, are likely to provide far deeper insights into the resilience of ecosystems, and the functions they provide.
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- 2017
11. Sustained functional composition of pollinators in restored pastures despite slow functional restoration of plants
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Winsa, Marie, Öckinger, E., Bommarco, Riccardo, Lindborg, R., Roberts, Suart P.M., Wärnsberg, J., Bartomeus, Ignasi, Winsa, Marie, Öckinger, E., Bommarco, Riccardo, Lindborg, R., Roberts, Suart P.M., Wärnsberg, J., and Bartomeus, Ignasi
- Abstract
Habitat restoration is a key measure to counteract negative impacts on biodiversity from habitat loss and fragmentation. To assess success in restoring not only biodiversity, but also functionality of communities, we should take into account the re-assembly of species trait composition across taxa. Attaining such functional restoration would depend on the landscape context, vegetation structure, and time since restoration. We assessed how trait composition of plant and pollinator (bee and hoverfly) communities differ between abandoned, restored (formerly abandoned) or continuously grazed (intact) semi-natural pastures. In restored pastures, we also explored trait composition in relation to landscape context, vegetation structure, and pasture management history. Abandoned pastures differed from intact and restored pastures in trait composition of plant communities, and as expected, had lower abundances of species with traits associated with grazing adaptations. Further, plant trait composition in restored pastures became increasingly similar to that in intact pastures with increasing time since restoration. On the contrary, the trait composition of pollinator communities in both abandoned and restored pastures remained similar to intact pastures. The trait composition for both bees and hoverflies was influenced by flower abundance and, for bees, by connectivity to other intact grasslands in the landscape. The divergent responses across organism groups appeared to be mainly related to the limited dispersal ability and long individual life span in plants, the high mobility of pollinators, and the dependency of semi-natural habitat for bees. Our results, encompassing restoration effects on trait composition for multiple taxa along a gradient in both time (time since restoration) and space (connectivity), reveal how interacting communities of plants and pollinators are shaped by different trait–environmental relationships. Complete functional restoration of pastures need
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- 2017
12. Applying resilience thinking to production ecosystems
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Rist, L., Felton, A., Nyström, M., Troell, M., Sponseller, R. A., Bengtsson, J., Österblom, H., Lindborg, R., Tidåker, P., Angeler, D. G., Milestad, Rebecka, Moen, J., Rist, L., Felton, A., Nyström, M., Troell, M., Sponseller, R. A., Bengtsson, J., Österblom, H., Lindborg, R., Tidåker, P., Angeler, D. G., Milestad, Rebecka, and Moen, J.
- Abstract
Production ecosystems typically have a high dependence on supporting and regulating ecosystem services and while they have thus far managed to sustain production, this has often been at the cost of externalities imposed on other systems and locations. One of the largest challenges facing humanity is to secure the production of food and fiber while avoiding long-term negative impacts on ecosystems and the range of services that they provide. Resilience has been used as a framework for understanding sustainability challenges in a range of ecosystem types, but has not been systematically applied across the range of systems specifically used for the production of food and fiber in terrestrial, freshwater, and marine environments. This paper applied a resilience lens to production ecosystems in which anthropogenic inputs play varying roles in determining system dynamics and outputs. We argue that the traditional resilience framework requires important additions when applied to production systems. We show how sustained anthropogenic inputs of external resources can lead to a "coercion'' of resilience and describe how the global interconnectedness of many production systems can camouflage signals indicating resilience loss., QC 20140818
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- 2014
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13. Harnessing the biodiversity value of Central and Eastern European farmland
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Sutcliffe, L.M.E., Batáry, P., Kormann, U., Báldi, A., Dicks, L.V., Herzon, I., Kleijn, D., Tryjanowski, P., Apostolova, I., Arlettaz, R., Aunins, A., Aviron, S., Baležentiené, L., Fischer, C., Halada, L., Hartel, T., Helm, A., Hristov, I., Jelaska, S.D., Kaligarič, M., Kamp, J., Klimek, S., Koorberg, P., Kostiuková, J., Kovács-Hostyánszki, A., Kuemmerle, T., Leuschner, C., Lindborg, R., Loos, J., Maccherini, S., Marja, R., Máthé, O., Paulini, I., Proença, V., Rey-Benayas, J., Sans, F.X., Seifert, C., Stalenga, J., Timaeus, Johannes, Török, P., van Swaay, C., Viik, E., Tscharntke, T., Sutcliffe, L.M.E., Batáry, P., Kormann, U., Báldi, A., Dicks, L.V., Herzon, I., Kleijn, D., Tryjanowski, P., Apostolova, I., Arlettaz, R., Aunins, A., Aviron, S., Baležentiené, L., Fischer, C., Halada, L., Hartel, T., Helm, A., Hristov, I., Jelaska, S.D., Kaligarič, M., Kamp, J., Klimek, S., Koorberg, P., Kostiuková, J., Kovács-Hostyánszki, A., Kuemmerle, T., Leuschner, C., Lindborg, R., Loos, J., Maccherini, S., Marja, R., Máthé, O., Paulini, I., Proença, V., Rey-Benayas, J., Sans, F.X., Seifert, C., Stalenga, J., Timaeus, Johannes, Török, P., van Swaay, C., Viik, E., and Tscharntke, T.
- Abstract
A large proportion of European biodiversity today depends on habitat provided by low-intensity farming practices, yet this resource is declining as European agriculture intensifies. Within the European Union, particularly the central and eastern new member states have retained relatively large areas of species-rich farmland, but despite increased investment in nature conservation here in recent years, farmland biodiversity trends appear to be worsening. Although the high biodiversity value of Central and Eastern European farmland has long been reported, the amount of research in the international literature focused on farmland biodiversity in this region remains comparatively tiny, and measures within the EU Common Agricultural Policy are relatively poorly adapted to support it. In this opinion study, we argue that, 10 years after the accession of the first eastern EU new member states, the continued under-representation of the low-intensity farmland in Central and Eastern Europe in the international literature and EU policy is impeding the development of sound, evidence-based conservation interventions. The biodiversity benefits for Europe of existing low-intensity farmland, particularly in the central and eastern states, should be harnessed before they are lost. Instead of waiting for species-rich farmland to further decline, targeted research and monitoring to create locally appropriate conservation strategies for these habitats is needed now.
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- 2014
14. Applying resilience thinking to production ecosystems
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Rist, L., primary, Felton, A., additional, Nyström, M., additional, Troell, M., additional, Sponseller, R. A., additional, Bengtsson, J., additional, Österblom, H., additional, Lindborg, R., additional, Tidåker, P., additional, Angeler, D. G., additional, Milestad, R., additional, and Moen, J., additional
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- 2014
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15. Function of small habitat elements for enhancing plant diversity in different agricultural landscapes
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Lindborg, R., primary, Plue, J., additional, Andersson, K., additional, and Cousins, S.A.O., additional
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- 2014
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16. Traits related to species persistence and dispersal explain changes in plant communities subjected to habitat loss
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Marini, L., Bruun, H.H., Heikkinen, R.K., Helm, A., Honnay, O., Krauss, J., Kühn, Ingolf, Lindborg, R., Pärtel, M., Bommarco, R., Marini, L., Bruun, H.H., Heikkinen, R.K., Helm, A., Honnay, O., Krauss, J., Kühn, Ingolf, Lindborg, R., Pärtel, M., and Bommarco, R.
- Abstract
Aim Habitat fragmentation is a major driver of biodiversity loss but it is insufficiently known how much its effects vary among species with different life-history traits; especially in plant communities, the understanding of the role of traits related to species persistence and dispersal in determining dynamics of species communities in fragmented landscapes is still limited. The primary aim of this study was to test how plant traits related to persistence and dispersal and their interactions modify plant species vulnerability to decreasing habitat area and increasing isolation. Location Five regions distributed over four countries in Central and Northern Europe. Methods Our dataset was composed of primary data from studies on the distribution of plant communities in 300 grassland fragments in five regions. The regional datasets were consolidated by standardizing nomenclature and species life-history traits and by recalculating standardized landscape measures from the original geographical data. We assessed the responses of plant species richness to habitat area, connectivity, plant life-history traits and their interactions using linear mixed models. Results We found that the negative effect of habitat loss on plant species richness was pervasive across different regions, whereas the effect of habitat isolation on species richness was not evident. This area effect was, however, not equal for all the species, and life-history traits related to both species persistence and dispersal modified plant sensitivity to habitat loss, indicating that both landscape and local processes determined large-scale dynamics of plant communities. High competitive ability for light, annual life cycle and animal dispersal emerged as traits enabling species to cope with habitat loss. Main conclusions In highly fragmented rural landscapes in NW Europe, mitigating the spatial isolation of remaining grasslands should be accompanied by restoration measures aimed at improving habitat qu
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- 2012
17. Effect of habitat area and isolation on plant trait distribution in European forests and grasslands
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Lindborg, R., Helm, A., Bommarco, R., Heikkinen, R.K., Kühn, Ingolf, Pykälä, J., Pärtel, M., Lindborg, R., Helm, A., Bommarco, R., Heikkinen, R.K., Kühn, Ingolf, Pykälä, J., and Pärtel, M.
- Abstract
A number of studies show contrasting results in how plant species with specific life-history strategies respond to fragmentation, but a general analysis on whether traits affect plant species occurrences in relation to habitat area and isolation has not been performed. We used published data from forests and grasslands in north-central Europe to analyse if there are general patterns of sensitivity to isolation and dependency of area for species using three traits: life-span, clonality, and seed weight. We show that a larger share of all forest species was affected by habitat isolation and area as compared to grassland species. Persistence-related traits, life-span and clonality, were associated to habitat area and the dispersal and recruitment related trait, seed weight, to isolation in both forest and grassland patches. Occurrence of clonal plant species decreased with habitat area, opposite to non-clonal plant species, and long-lived plant species decreased with grassland area. The directions of these responses partly challenge some earlier views, suggesting that further decrease in habitat area will lead to a change in plant species community composition, towards relatively fewer clonal and long-lived plants with large seeds in small forest patches and fewer clonal plants with small seeds in small grassland patches. It is likely that this altered community has been reached in many fragmented European landscapes consisting of small and isolated natural and semi-natural patches, where many non-clonal and short-lived species have already disappeared. Our study based on a large-scale dataset reveals general and useful insights concerning area and isolation effects on plant species composition that can improve the outcome of conservation and restoration efforts of plant communities in rural landscapes.
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- 2012
18. Benchmarking plant diversity of Palaearctic grasslands and other open habitats
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Monika Janišová, Georgios Fotiadis, Honor C. Prentice, Farshid Memariani, Ivan I. Moysiyenko, Pavel Lustyk, Zdenka Preislerová, Hristo Pedashenko, Francesco Santi, Atushi Ushimaru, Steffen Boch, Galina Savchenko, Fabrizio Buldrini, Irena Axmanová, Milan Chytrý, Jiri Dolezal, Denys Vynokurov, Marta Czarniecka-Wiera, Zdeňka Lososová, Robert K. Peet, Simon Stifter, Ricarda Pätsch, Koenraad Van Meerbeek, Alba Gutiérrez-Girón, Simona Maccherini, András Kelemen, Thomas Becker, Michal Hájek, Christian Pedersen, Stefan Widmer, Remigiusz Pielech, Vladimir Ronkin, Kai Jensen, Anna Wróbel, Cristina Chocarro, Sebastian Świerszcz, Lei Deng, Arkadiusz Nowak, Luisa Conti, Eulàlia Pladevall-Izard, Swantje Löbel, Jonathan Etzold, Jan Peters, Hans Henrik Bruun, Elisabeth M. Hüllbusch, Anna Kuzemko, Martin Magnes, Rayna Natcheva, Riccardo Guarino, Joaquín Molero Mesa, Vasco Silva, Pavel Dřevojan, Iuliia Vasheniak, Jan Lepš, Péter Török, Timo Conradi, Marcin Nobis, Aaron Pérez-Haase, Yun Wang, María Rosa Fernández Calzado, Ilaria Bonini, Massimo Terzi, Meelis Pärtel, Liqing Zhao, Csaba Tölgyesi, Frank Weiser, Philipp Kirschner, Juan Antonio Campos, Zuzana Plesková, László Demeter, George Fayvush, Asun Berastegi, Behlül Güler, Diego Liendo, Nancy Langer, Manfred Finckh, Martin Diekmann, Florian Jeltsch, Anke Jentsch, Robin J. Pakeman, Tobias Ceulemans, Javier Etayo, Orsolya Valkó, Carly J. Stevens, Kaoru Kakinuma, Michele Aleffi, Jiří Danihelka, Alicia Teresa Rosario Acosta, Balázs Teleki, Laura M. E. Sutcliffe, Solvita Rusina, Rosario G. Gavilán, Pieter De Frenne, Michele Mugnai, Arantzazu L. Luzuriaga, Marc Olivier Büchler, Lubomír Tichý, Soroor Rahmanian, Zsolt Molnár, Itziar García-Mijangos, Jürgen Dengler, Harald Pauli, Asuka Koyama, Anvar Sanaei, Cecilia Dupré, Parvaneh Ashouri, Vladimir G. Onipchenko, Ute Jandt, Zoltán Bátori, François Gillet, Alla Aleksanyan, Ariel Bergamini, Corrado Marcenò, Constantin Mardari, Nadezda Tsarevskaya, José Luis Benito Alonso, Łukasz Kozub, Ottar Michelsen, Felix May, Goffredo Filibeck, Jan Roleček, Jalil Noroozi, Karsten Wesche, Eva Šmerdová, Michael Manthey, Triin Reitalu, Ana M. Sánchez, Eszter Ruprecht, Regina Lindborg, Idoia Biurrun, Risto Virtanen, Gianpietro Giusso del Galdo, Helmut Mayrhofer, Annika K. Jägerbrand, Mansoureh Kargar, Chrisoula B. Pirini, Dariia Shyriaieva, Sabina Burrascano, Esther Baumann, Christian Dolnik, Kristina Merunková, Ching-Feng Li, Eliane S. Meier, Kuber Prasad Bhatta, Mercedes Herrera, Klaus Ecker, Mohammad Farzam, Marta Torca, Nele Ingerpuu, Philippe Jeanneret, Francesco de Bello, Alireza Naqinezhad, Tünde Farkas, Elena Belonovskaya, Josep M. Ninot, Elias Afif, Munemitsu Akasaka, Lorenzo Lazzaro, András Vojtkó, Leonardo Rosati, Jianshuang Wu, Arshad Ali, Sándor Bartha, Zuoqiang Yuan, Wenhong Ma, Patryk Czortek, Marta Carboni, Franz Essl, Hannah J. White, Carmen Van Mechelen, Brigitta Erschbamer, Marek Malicki, Vasyl Budzhak, Jutta Kapfer, Manuela Winkler, Angela Lomba, Hamid Ejtehadi, Judit Sonkoly, Ingrid Turisová, Thomas Vanneste, Laura Cancellieri, Sonja Škornik, David Zelený, Zygmunt Kącki, Alessandro Chiarucci, Salza Palpurina, Sigrid Suchrow, Kathrin Kiehl, Amir Talebi, Beata Cykowska-Marzencka, Borja Jiménez-Alfaro, Nataša Pipenbaher, Frank Yonghong Li, Wendy Fjellstad, Ivana Vitasović-Kosić, Maria Pilar Rodríguez-Rojo, Álvaro Bueno, Daniele Viciani, Juha M. Alatalo, Emelie Waldén, Sahar Ghafari, Grzegorz Swacha, Anna Mária Csergő, Lu Wen, Balázs Deák, Ioannis Tsiripidis, Luis Villar, Maria-Teresa Sebastià, Svetlana Aćić, Halime Moradi, Kiril Vassilev, Daniel García-Magro, Sebastian Wolfrum, Iva Apostolova, Marko Sabovljevic, Giovanna Potenza, Monika Staniaszek-Kik, Iwona Dembicz, Aveliina Helm, Marta Czarnocka-Cieciura, Marta Gaia Sperandii, John-Arvid Grytnes, Laboratoire Chrono-environnement - CNRS - UBFC (UMR 6249) (LCE), Centre National de la Recherche Scientifique (CNRS)-Université de Franche-Comté (UFC), Université Bourgogne Franche-Comté [COMUE] (UBFC)-Université Bourgogne Franche-Comté [COMUE] (UBFC), Biurrun I., Pielech R., Dembicz I., Gillet F., Kozub L., Marceno C., Reitalu T., Van Meerbeek K., Guarino R., Chytry M., Pakeman R.J., Preislerova Z., Axmanova I., Burrascano S., Bartha S., Boch S., Bruun H.H., Conradi T., De Frenne P., Essl F., Filibeck G., Hajek M., Jimenez-Alfaro B., Kuzemko A., Molnar Z., Partel M., Patsch R., Prentice H.C., Rolecek J., Sutcliffe L.M.E., Terzi M., Winkler M., Wu J., Acic S., Acosta A.T.R., Afif E., Akasaka M., Alatalo J.M., Aleffi M., Aleksanyan A., Ali A., Apostolova I., Ashouri P., Batori Z., Baumann E., Becker T., Belonovskaya E., Benito Alonso J.L., Berastegi A., Bergamini A., Bhatta K.P., Bonini I., Buchler M.-O., Budzhak V., Bueno A., Buldrini F., Campos J.A., Cancellieri L., Carboni M., Ceulemans T., Chiarucci A., Chocarro C., Conti L., Csergo A.M., Cykowska-Marzencka B., Czarniecka-Wiera M., Czarnocka-Cieciura M., Czortek P., Danihelka J., de Bello F., Deak B., Demeter L., Deng L., Diekmann M., Dolezal J., Dolnik C., Drevojan P., Dupre C., Ecker K., Ejtehadi H., Erschbamer B., Etayo J., Etzold J., Farkas T., Farzam M., Fayvush G., Fernandez Calzado M.R., Finckh M., Fjellstad W., Fotiadis G., Garcia-Magro D., Garcia-Mijangos I., Gavilan R.G., Germany M., Ghafari S., Giusso del Galdo G.P., Grytnes J.-A., Guler B., Gutierrez-Giron A., Helm A., Herrera M., Hullbusch E.M., Ingerpuu N., Jagerbrand A.K., Jandt U., Janisova M., Jeanneret P., Jeltsch F., Jensen K., Jentsch A., Kacki Z., Kakinuma K., Kapfer J., Kargar M., Kelemen A., Kiehl K., Kirschner P., Koyama A., Langer N., Lazzaro L., Leps J., Li C.-F., Li F.Y., Liendo D., Lindborg R., Lobel S., Lomba A., Lososova Z., Lustyk P., Luzuriaga A.L., Ma W., Maccherini S., Magnes M., Malicki M., Manthey M., Mardari C., May F., Mayrhofer H., Meier E.S., Memariani F., Merunkova K., Michelsen O., Molero Mesa J., Moradi H., Moysiyenko I., Mugnai M., Naqinezhad A., Natcheva R., Ninot J.M., Nobis M., Noroozi J., Nowak A., Onipchenko V., Palpurina S., Pauli H., Pedashenko H., Pedersen C., Peet R.K., Perez-Haase A., Peters J., Pipenbaher N., Pirini C., Pladevall-Izard E., Pleskova Z., Potenza G., Rahmanian S., Rodriguez-Rojo M.P., Ronkin V., Rosati L., Ruprecht E., Rusina S., Sabovljevic M., Sanaei A., Sanchez A.M., Santi F., Savchenko G., Sebastia M.T., Shyriaieva D., Silva V., Skornik S., Smerdova E., Sonkoly J., Sperandii M.G., Staniaszek-Kik M., Stevens C., Stifter S., Suchrow S., Swacha G., Swierszcz S., Talebi A., Teleki B., Tichy L., Tolgyesi C., Torca M., Torok P., Tsarevskaya N., Tsiripidis I., Turisova I., Ushimaru A., Valko O., Van Mechelen C., Vanneste T., Vasheniak I., Vassilev K., Viciani D., Villar L., Virtanen R., Vitasovic-Kosic I., Vojtko A., Vynokurov D., Walden E., Wang Y., Weiser F., Wen L., Wesche K., White H., Widmer S., Wolfrum S., Wrobel A., Yuan Z., Zeleny D., Zhao L., Dengler J., Biurrun, Idoia, Pielech, Remigiusz, Dembicz, Iwona, Gillet, Françoi, Kozub, Łukasz, Marcenò, Corrado, Reitalu, Triin, Van Meerbeek, Koenraad, Guarino, Riccardo, Chytrý, Milan, Pakeman, Robin J., Preislerová, Zdenka, Axmanová, Irena, Burrascano, Sabina, Bartha, Sándor, Boch, Steffen, Bruun, Hans Henrik, Conradi, Timo, De Frenne, Pieter, Essl, Franz, Filibeck, Goffredo, Hájek, Michal, Jiménez‐Alfaro, Borja, Kuzemko, Anna, Molnár, Zsolt, Pärtel, Meeli, Pätsch, Ricarda, Prentice, Honor C., Roleček, Jan, Sutcliffe, Laura M.E., Terzi, Massimo, Winkler, Manuela, Wu, Jianshuang, Aćić, Svetlana, Acosta, Alicia T.R., Afif, Elia, Akasaka, Munemitsu, Alatalo, Juha M., Aleffi, Michele, Aleksanyan, Alla, Ali, Arshad, Apostolova, Iva, Ashouri, Parvaneh, Bátori, Zoltán, Baumann, Esther, Becker, Thoma, Belonovskaya, Elena, Benito Alonso, José Lui, Berastegi, Asun, Bergamini, Ariel, Bhatta, Kuber Prasad, Bonini, Ilaria, Büchler, Marc‐Olivier, Budzhak, Vasyl, Bueno, Álvaro, Buldrini, Fabrizio, Campos, Juan Antonio, Cancellieri, Laura, Carboni, Marta, Ceulemans, Tobia, Chiarucci, Alessandro, Chocarro, Cristina, Conti, Luisa, Csergő, Anna Mária, Cykowska‐Marzencka, Beata, Czarniecka‐Wiera, Marta, Czarnocka‐Cieciura, Marta, Czortek, Patryk, Danihelka, Jiří, de Bello, Francesco, Deák, Baláz, Demeter, László, Deng, Lei, Diekmann, Martin, Dolezal, Jiri, Dolnik, Christian, Dřevojan, Pavel, Dupré, Cecilia, Ecker, Klau, Ejtehadi, Hamid, Erschbamer, Brigitta, Etayo, Javier, Etzold, Jonathan, Farkas, Tünde, Farzam, Mohammad, Fayvush, George, Fernández Calzado, María Rosa, Finckh, Manfred, Fjellstad, Wendy, Fotiadis, Georgio, García‐Magro, Daniel, García‐Mijangos, Itziar, Gavilán, Rosario G., Germany, Marku, Ghafari, Sahar, Giusso del Galdo, Gian Pietro, Grytnes, John‐Arvid, Güler, Behlül, Gutiérrez‐Girón, Alba, Helm, Aveliina, Herrera, Mercede, Hüllbusch, Elisabeth M., Ingerpuu, Nele, Jägerbrand, Annika K., Jandt, Ute, Janišová, Monika, Jeanneret, Philippe, Jeltsch, Florian, Jensen, Kai, Jentsch, Anke, Kącki, Zygmunt, Kakinuma, Kaoru, Kapfer, Jutta, Kargar, Mansoureh, Kelemen, Andrá, Kiehl, Kathrin, Kirschner, Philipp, Koyama, Asuka, Langer, Nancy, Lazzaro, Lorenzo, Lepš, Jan, Li, Ching‐Feng, Li, Frank Yonghong, Liendo, Diego, Lindborg, Regina, Löbel, Swantje, Lomba, Angela, Lososová, Zdeňka, Lustyk, Pavel, Luzuriaga, Arantzazu L., Ma, Wenhong, Maccherini, Simona, Magnes, Martin, Malicki, Marek, Manthey, Michael, Mardari, Constantin, May, Felix, Mayrhofer, Helmut, Meier, Eliane Seraina, Memariani, Farshid, Merunková, Kristina, Michelsen, Ottar, Molero Mesa, Joaquín, Moradi, Halime, Moysiyenko, Ivan, Mugnai, Michele, Naqinezhad, Alireza, Natcheva, Rayna, Ninot, Josep M., Nobis, Marcin, Noroozi, Jalil, Nowak, Arkadiusz, Onipchenko, Vladimir, Palpurina, Salza, Pauli, Harald, Pedashenko, Hristo, Pedersen, Christian, Peet, Robert K., Pérez‐Haase, Aaron, Peters, Jan, Pipenbaher, Nataša, Pirini, Chrisoula, Pladevall‐Izard, Eulàlia, Plesková, Zuzana, Potenza, Giovanna, Rahmanian, Soroor, Rodríguez‐Rojo, Maria Pilar, Ronkin, Vladimir, Rosati, Leonardo, Ruprecht, Eszter, Rusina, Solvita, Sabovljević, Marko, Sanaei, Anvar, Sánchez, Ana M., Santi, Francesco, Savchenko, Galina, Sebastià, Maria Teresa, Shyriaieva, Dariia, Silva, Vasco, Škornik, Sonja, Šmerdová, Eva, Sonkoly, Judit, Sperandii, Marta Gaia, Staniaszek‐Kik, Monika, Stevens, Carly, Stifter, Simon, Suchrow, Sigrid, Swacha, Grzegorz, Świerszcz, Sebastian, Talebi, Amir, Teleki, Baláz, Tichý, Lubomír, Tölgyesi, Csaba, Torca, Marta, Török, Péter, Tsarevskaya, Nadezda, Tsiripidis, Ioanni, Turisova, Ingrid, Ushimaru, Atushi, Valkó, Orsolya, Van Mechelen, Carmen, Vanneste, Thoma, Vasheniak, Iuliia, Vassilev, Kiril, Viciani, Daniele, Villar, Lui, Virtanen, Risto, Vitasović‐Kosić, Ivana, Vojtkó, Andrá, Vynokurov, Deny, Waldén, Emelie, Wang, Yun, Weiser, Frank, Wen, Lu, Wesche, Karsten, White, Hannah, Widmer, Stefan, Wolfrum, Sebastian, Wróbel, Anna, Yuan, Zuoqiang, Zelený, David, Zhao, Liqing, Dengler, Jürgen, Bavarian Research Foundation, International Association for Vegetation Science, Eusko Jaurlaritza, Czech Science Foundation, Estonian Research Council, Scottish Government's Rural and Environment Science and Analytical Services, Ministero dell'Istruzione, dell'Università e della Ricerca, Agencia Estatal de Investigación (España), Science and Technology Center in Ukraine, Swedish Research Council for Environment, Agricultural Sciences and Spatial Planning, Swedish Institute, Foundation for Introducing Talent of Nanjing University of Information Science and Technology, Hebei Province, Academy of Sciences of the Czech Republic, Hungarian Academy of Sciences, Tyrolean Science Fund, Austrian Academy of Sciences, University of Innsbruck, Ministerio de Economía y Competitividad (España), Comunidad de Madrid, National Geographic Society, Slovak Academy of Sciences, Fundação para a Ciência e a Tecnologia (Portugal), National Science Centre (Poland), Russian Science Foundation, University of Latvia Foundation, Slovenian Research Agency, Biurrun, I, Pielech, R, Dembicz, I, Gillet, F, Kozub, L, Marceno, C, Reitalu, T, Van Meerbeek, K, Guarino, R, Chytry, M, Pakeman, RJ, Preislerova, Z, Axmanova, I, Burrascano, S, Bartha, S, Boch, S, Bruun, HH, Conradi, T, De Frenne, P, Essl, F, Filibeck, G, Hajek, M, Jimenez-Alfaro, B, Kuzemko, A, MOLNAR, Zsolt, Partel, M, Patsch, R, Prentice, HC, Rolecek, J, Sutcliffe, LME, Terzi, M, Winkler, M, Wu, JS, Acic, S, Acosta, ATR, Afif, E, Akasaka, M, Alatalo, JM, Aleffi, M, Aleksanyan, A, Ali, A, Apostolova, I, Ashouri, P, Batori, Z, Baumann, E, BECKER, T, Belonovskaya, E, Alonso, JLB, Berastegi, A, Bergamini, A, Bhatta, KP, Bonini, I, Buchler, MO, Budzhak, V, Bueno, A, Buldrini, F, Campos, JA, Cancellieri, L, Carboni, M, Ceulemans, T, Chiarucci, A, Chocarro, C, Conti, L, Csergo, AM, Cykowska-Marzencka, B, Czarniecka-Wiera, M, Czarnocka-Cieciura, M, Czortek, P, Danihelka, J, Bello, F, Deak, B, Demeter, L, Deng, L, Diekmann, M, Dolezal, J, Dolnik, C, Drevojan, P, Dupre, C, Ecker, K, Ejtehadi, H, Erschbamer, B, Etayo, J, Etzold, J, Farkas, T, Farzam, M, Fayvush, G, Calzado, MRF, Finckh, M, Fjellstad, W, Fotiadis, G, Garcia-Magro, D, Garcia-Mijangos, I, Gavilan, RG, Germany, M, Ghafari, S, del Galdo, GPG, Grytnes, JA, Guler, B, Gutierrez-Giron, A, Helm, A, Herrera, M, Hullbusch, EM, Ingerpuu, N, Jagerbrand, AK, Jandt, U, Janisova, M, Jeanneret, P, Jeltsch, F, Jensen, K, Jentsch, A, Kacki, Z, Kakinuma, K, Kapfer, J, Kargar, M, Kelemen, A, Kiehl, K, Kirschner, P, Koyama, A, Langer, N, Lazzaro, L, Leps, J, Li, CF, Li, FY, Liendo, D, Lindborg, R, Lobel, S, Lomba, A, Lososova, Z, Lustyk, P, Luzuriaga, AL, Ma, WH, Maccherini, S, Magnes, M, Malicki, M, Manthey, M, Mardari, C, May, F, Mayrhofer, H, Meier, ES, Memariani, F, Merunkova, K, Michelsen, O, Mesa, JM, Moradi, H, Moysiyenko, I, Mugnai, M, Naqinezhad, A, Natcheva, R, Ninot, JM, Nobis, M, Noroozi, J, Nowak, A, Onipchenko, V, Palpurina, S, Pauli, H, Pedashenko, H, Pedersen, C, Peet, RK, Perez-Haase, A, Peters, J, Pipenbaher, N, Pirini, C, Pladevall-Izard, E, Pleskova, Z, Potenza, G, Rahmanian, S, Rodriguez-Rojo, MP, Ronkin, V, Rosati, L, Ruprecht, E, Rusina, S, Sabovljevic, M, Sanaei, A, Sanchez, AM, Santi, F, Savchenko, G, Sebastia, MT, Shyriaieva, D, Silva, V, Skornik, S, Smerdova, E, Sonkoly, J, Sperandii, MG, Staniaszek-Kik, M, Stevens, C, Stifter, S, Suchrow, S, Swacha, G, Swierszcz, S, Talebi, A, Teleki, B, Tichy, L, Tolgyesi, C, Torca, M, Torok, P, Tsarevskaya, N, Tsiripidis, I, Turisova, I, Ushimaru, A, Valko, O, VAN MECHELEN, Carmen, Vanneste, T, Vasheniak, I, Vassilev, K, Viciani, D, Villar, L, Virtanen, R, Vitasovic-Kosic, I, Vojtko, A, Vynokurov, D, Walden, E, Wang, Y., Weiser, F, Wen, L, Wesche, K, White, H, Widmer, S, Wolfrum, S, Wrobel, A, Yuan, ZQ, Zeleny, D, Zhao, LQ, Dengler, J., Jiménez‐alfaro, Borja, Sutcliffe, Laura M. E., Acosta, Alicia, Büchler, Marc‐olivier, Cykowska‐marzencka, Beata, Czarniecka‐wiera, Marta, Czarnocka‐cieciura, Marta, Bello, Francesco, García‐magro, Daniel, García‐mijangos, Itziar, Grytnes, John‐arvid, Gutiérrez‐girón, Alba, Li, Ching‐feng, Pérez‐haase, Aaron, Pladevall‐izard, Eulàlia, Rodríguez‐rojo, Maria Pilar, Staniaszek‐kik, Monika, Turisová, Ingrid, and Vitasović‐kosić, Ivana
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Vascular plant ,SURROGATE ,333.7: Landflächen, Naturerholungsgebiete ,Biome ,Lichen ,open habitat ,Plant Science ,DATABASES ,Benchmark ,Grassland ,Scale dependence ,benchmark ,RICHNESS HOTSPOTS ,Vegetation type ,Taxonomic rank ,SCALE ,Macroecology ,ComputingMilieux_MISCELLANEOUS ,2. Zero hunger ,bryophyte ,GLOBAL PATTERNS ,geography.geographical_feature_category ,Ecology ,Open habitat ,vascular plant ,Forestry ,ichen ,Vegetation ,Vegetation plot ,Palaearctic ,580: Pflanzen (Botanik) ,Geography ,Habitat ,scale dependence ,fine-grain biodiversity ,grassland ,GrassPlot Diversity Explorer ,lichen ,species–area relationship ,vegetation plot ,Life Sciences & Biomedicine ,CONSERVATION ,Environmental Sciences & Ecology ,Fine-grain biodiversity ,benchmark, bryophyte, fine-grain biodiversity, grassland, GrassPlot Diversity Explorer, lichen, open habitat, Palaearctic, scale dependence, species–area relationship, vascular plant, vegetation plot ,species-area relationship ,benchmark, bryophyte, fine-grain biodiversity, grassland, GrassPlot Diversity Explorer, lichen, open habitat, Palaearctic, scale dependence, species-area relationship, vascular plant, vegetation plot ,Species–area relationship ,Science & Technology ,Plant Sciences ,Biology and Life Sciences ,15. Life on land ,plant diversity ,13. Climate action ,Bryophyte ,SPECIES-AREA RELATIONSHIPS ,VASCULAR PLANTS ,BIODIVERSITY ,Species richness ,[SDE.BE]Environmental Sciences/Biodiversity and Ecology ,BRYOPHYTES - Abstract
© 2021 The Authors., Aims: Understanding fine-grain diversity patterns across large spatial extents is fundamental for macroecological research and biodiversity conservation. Using the GrassPlot database, we provide benchmarks of fine-grain richness values of Palaearctic open habitats for vascular plants, bryophytes, lichens and complete vegetation (i.e., the sum of the former three groups). Location: Palaearctic biogeographic realm. Methods: We used 126,524 plots of eight standard grain sizes from the GrassPlot database: 0.0001, 0.001, 0.01, 0.1, 1, 10, 100 and 1,000 m and calculated the mean richness and standard deviations, as well as maximum, minimum, median, and first and third quartiles for each combination of grain size, taxonomic group, biome, region, vegetation type and phytosociological class. Results: Patterns of plant diversity in vegetation types and biomes differ across grain sizes and taxonomic groups. Overall, secondary (mostly semi-natural) grasslands and natural grasslands are the richest vegetation type. The open-access file ”GrassPlot Diversity Benchmarks” and the web tool “GrassPlot Diversity Explorer” are now available online (https://edgg.org/databases/GrasslandDiversityExplorer) and provide more insights into species richness patterns in the Palaearctic open habitats. Conclusions: The GrassPlot Diversity Benchmarks provide high-quality data on species richness in open habitat types across the Palaearctic. These benchmark data can be used in vegetation ecology, macroecology, biodiversity conservation and data quality checking. While the amount of data in the underlying GrassPlot database and their spatial coverage are smaller than in other extensive vegetation-plot databases, species recordings in GrassPlot are on average more complete, making it a valuable complementary data source in macroecology., GrassPlot development has been supported by the Bavarian Research Alliance (BayIntAn_UBT_2017_58), the Eurasian Dry Grassland Group (EDGG) and the International Association for Vegetation Science (IAVS); IB, CorM, JAC, IGM, DGM, MHe, DL and MTo were supported by the Basque Government (IT936‐16); CorM, IAx, MCh, JDa, PD, MHá, ZL, ZPr, EŠ and LT were supported by the Czech Science Foundation (19‐28491X); TR was supported by the Estonian Research Council (PUT1173); RJP was funded by the Strategic Research Programme of the Scottish Government’s Rural and Environmental Science and Analytical Services Division”; SBa was supported by the GINOP‐2.3.2‐15‐2016‐00019 project; GFi was partially supported by the MIUR initiative “Department of excellence” (Law 232/2016)"; BJA was funded by the Spanish Research Agency (grant AEI/ 10.13039/501100011033); AK, VB, IM, DS, IV and DV were supported by the National Research Foundation of Ukraine (2020.01/0140); MP and AH were supported by the Estonian Research Council (PRG874, PRG609), and the European Regional Development Fund (Centre of Excellence EcolChange); Data collection of HCP was funded by FORMAS (Swedish Research Council for Environment, Agricultural Science and Spatial Planning) and The Swedish Institute; JR was supported by the Czech Science Foundation (grant No. 20‐09895S) and the long‐term developmental project of the Czech Academy of Sciences (RVO 67985939); ATRA was funded by the Grant of Excellence Departments, MIUR‐Italy (ARTICOLO 1, COMMI 314 – 337 LEGGE 232/2016); JMA was supported by Carl Tryggers stiftelse för vetenskaplig forskning and Qatar Petroleum; AAli was supported by the Jiangsu Science and Technology Special Project (Grant No. BX2019084), and Metasequoia Faculty Research Startup Funding at Nanjing Forestry University (Grant No. 163010230), and he is currently supported by Hebei University through Faculty Research Startup Funding Program; ZB was supported by the NKFI K 124796 grant; The GLORIA‐ Aragón project of JLBA was funded by the Dirección General de Cambio Climático del Gobierno de Aragón (Spain); MCs and LDem were supported by DG Environment through the European Forum on Nature Conservation and Pastoralism and Barbara Knowles Fund, in collaboration with Pogány‐havas Association, Romania; JDa was partially supported by long‐term research development project no. RVO 67985939 of the Czech Academy of Sciences; BD and OV were supported by the NKFI KH 126476, NKFI KH 130338, NKFI FK 124404 and NKFI FK 135329 grants; BD, OV and AKe were supported by the Bolyai János Scholarship of the Hungarian Academy of Sciences; BE was funded by the Environmental Department of the Tyrolean Federal State Government, the MAB Programme of the Austrian Academy of Science, the Mountain Agriculture Research Unit and the Alpine Research Centre Obergurgl of Innsbruck University. The GLORIA projects of BE were funded by the EU project no. EVK2‐CT‐2000‐00056, the Earth System Sciences Program of the Austrian Academy of Sciences (project MEDIALPS), the Amt für Naturparke, Autonome Provinz Bozen‐Südtirol, the Südtiroler Wissenschaftsfonds and the Tiroler Wissenschaftsfonds; RGG was supported by the Spanish Ministry of Research to sample GLORIA sites in central Spain (CGL 2008‐00901/BOS) and present works by the Autonomous Region of Madrid (REMEDINAL TE‐CM, S2018/EMT‐4338); MJ was supporteLatviaed by Latvia Grant No. 194051; NP and SŠ were partly supported by the Slovenian Research Agency, core fundings P1‐0403 and J7‐1822.
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- 2021
19. Effects on biodiversity in semi-natural pastures of giving the grazing animals access to additional nutrient sources: a systematic review.
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Jakobsson S, Envall I, Bengtsson J, Rundlöf M, Svensson M, Åberg C, and Lindborg R
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Background: Traditionally managed semi-natural pastures are recognised for their high biodiversity. One drawback is that these pastures are often low in fodder production and hence rather unprofitable, which may lead to abandonment. Two ways to increase production and profitability and maintain grazing are to (i) offer the grazers supplementary feed, or (ii) co-enclose the semi-natural pasture with an improved pasture. Both practices may transfer nutrients to the semi-natural pasture, with potential negative effects on biodiversity. This systematic review aimed to analyse the available evidence concerning the following primary question: "What is the effect of giving grazers access to additional nutrient sources on biodiversity in semi-natural pastures?" (Q1). We also used two supporting questions: "What is the effect of giving grazers access to additional nutrient sources on nutrient status of the soils of semi-natural pastures?" (Q2) and "How do the grazers of semi-natural pastures behave while having access to additional nutrient sources?" (Q3)., Methods: Searches for peer-reviewed and grey literature were made using bibliographic databases, search engines, specialist websites, and stakeholder contacts. Literature was screened for relevance according to predefined eligibility criteria, and critical appraisal was performed using the tool CEECAT. A database of the relevant studies was compiled. Descriptive information about the evidence base is presented in tables and an interactive evidence atlas. Because of absent study setup replication, Q1 and Q2 were not analysed quantitatively. However, sample size allowed the use of mixed modelling to quantitatively analyse Q3 regarding the effects of (i) co-enclosing an improved pasture on grazers' electivity for the improved area, and (ii) supplementary feed on the forage intake of grazers., Review Findings: A total of 12 articles on the effects of supplementary feeding and 19 on the effects of co-enclosing an improved pasture were included, of which some targeted multiple review questions. Because of the limited literature, it is not possible to draw any conclusions concerning the effects on biodiversity (Q1) or nutritional status (Q2) in semi-natural pastures. For Q3, 28 studies fulfilled our criteria, of which 18 investigated the behaviour of grazers related to co-enclosing an improved pasture, and 10 investigated their forage intake while having access to supplementary fodder. The results show that all grazer species except goats preferred grazing in the improved areas regardless of whether they were grazing together with other grazer species or not. We found no effect of supplementary feeding on forage intake of the grazers., Conclusions: We detected a knowledge gap concerning the effects of the two additional nutrient sources on semi-natural pasture biodiversity (Q1) and nutrient status (Q2), which points toward further research needs. Analysis of Q3 showed that grazers prefer to graze improved compared to semi-natural pasture areas. However, how this behaviour subsequently affects nutrient transport and biodiversity is unclear and cannot be translated into management recommendations. To gain better knowledge about the primary question of our review, research focusing specifically on this question is needed. We provide suggestions for how such studies could be designed, including spatio-temporal setup, and key management and environmental conditions to consider., (© 2024. The Author(s).)
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- 2024
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20. Pathways from research to sustainable development: Insights from ten research projects in sustainability and resilience.
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Scaini A, Mulligan J, Berg H, Brangarí A, Bukachi V, Carenzo S, Chau Thi D, Courtney-Mustaphi C, Ekblom A, Fjelde H, Fridahl M, Hansson A, Hicks L, Höjer M, Juma B, Kain JH, Kariuki RW, Kim S, Lane P, Leizeaga A, Lindborg R, Livsey J, Lyon SW, Marchant R, McConville JR, Munishi L, Nilsson D, Olang L, Olin S, Olsson L, Rogers PM, Rousk J, Sandén H, Sasaki N, Shoemaker A, Smith B, Thai Huynh Phuong L, Varela Varela A, Venkatappa M, Vico G, Von Uexkull N, Wamsler C, Wondie M, Zapata P, Zapata Campos MJ, Manzoni S, and Tompsett A
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- Humans, Resilience, Psychological
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Drawing on collective experience from ten collaborative research projects focused on the Global South, we identify three major challenges that impede the translation of research on sustainability and resilience into better-informed choices by individuals and policy-makers that in turn can support transformation to a sustainable future. The three challenges comprise: (i) converting knowledge produced during research projects into successful knowledge application; (ii) scaling up knowledge in time when research projects are short-term and potential impacts are long-term; and (iii) scaling up knowledge across space, from local research sites to larger-scale or even global impact. Some potential pathways for funding agencies to overcome these challenges include providing targeted prolonged funding for dissemination and outreach, and facilitating collaboration and coordination across different sites, research teams, and partner organizations. By systematically documenting these challenges, we hope to pave the way for further innovations in the research cycle., (© 2024. The Author(s).)
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- 2024
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21. Biodiversity mitigates trade-offs among species functional traits underpinning multiple ecosystem services.
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Waldén E, Queiroz C, Plue J, and Lindborg R
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- Computer Simulation, Plant Physiological Phenomena, Grassland, Ecosystem, Biodiversity
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Biodiversity loss and its effects on humanity is of major global concern. While a growing body of literature confirms positive relationships between biodiversity and multiple ecological functions, the links between biodiversity, ecological functions and multiple ecosystem services is yet unclear. Studies of biodiversity-functionality relationships are mainly based on computer simulations or controlled field experiments using only few species. Here, we use a trait-based approach to integrate plant functions into an ecosystem service assessment to address impacts of restoration on species-rich grasslands over time. We found trade-offs among functions and services when analysing contributions from individual species. At the community level, these trade-offs disappeared for almost all services with time since restoration as an effect of increased species diversity and more evenly distributed species. Restoration to enhance biodiversity also in species-rich communities is therefore essential to secure higher functional redundancy towards disturbances and sustainable provision of multiple ecosystem services over time., (© 2023 The Authors. Ecology Letters published by John Wiley & Sons Ltd.)
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- 2023
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22. Mapping cumulative pressures on the grazing lands of northern Fennoscandia.
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Stoessel M, Moen J, and Lindborg R
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- Animals, Climate Change, Ecosystem, Europe, Forestry, Sheep, Reindeer
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Traditional grazing areas in Europe have declined substantially over the last century. Specifically, in northern Fennoscandia, the grazing land is disturbed by cumulative land-use pressures. Here we analysed the configuration of the grazing land for reindeer and sheep in northern Fennoscandia in relation to the concurrent land-use pressures from tourism, road and railway networks, forestry, industrial and wind energy facilities, together with predator presence and climate change. Our results show that 85% of the region is affected by at least one land-use pressure and 60% is affected by multiple land-use pressures, co-occurring with predator presence and rising temperatures. As such, a majority of the grazing land is exposed to cumulative pressures in northern Fennoscandia. We stress that, if the expansion of cumulative pressures leads to grazing abandonment of disturbed areas and grazing intensification in other areas, it could irreversibly change northern vegetation and the Fennoscandian mountain landscape., (© 2022. The Author(s).)
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- 2022
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23. How does a wetland plant respond to increasing temperature along a latitudinal gradient?
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Lindborg R, Ermold M, Kuglerová L, Jansson R, Larson KW, Milbau A, and Cousins SAO
- Abstract
Global warming affects plant fitness through changes in functional traits and thereby ecosystem function. Wetlands are declining worldwide, and hence, ecosystem functions linked to wetlands are threatened. We use Caltha palustris "a common wetland plant" to study whether warming affects growth and reproduction differently depending on origin of source population, potentially affecting phenotypic response to local climate. We conducted a 2-year in situ temperature manipulation experiment using clone pairs of C . palustris in four regions, along a 1300-km latitudinal gradient of Sweden. Open-top chambers were used to passively increase temperature, paired with controls. Growth and reproductive traits were measured from 320 plants (four regions × five sites × two treatments × eight plants) over two consecutive seasons to assess the effect of warming over time. We found that warming increased plant height, leaf area, number of leaves, and roots. High-latitude populations responded more strongly to warming than low-latitude populations, especially by increasing leaf area. Warming increased number of flowers in general, but only in the second year, while number of fruits increased in low-latitude populations the first year. Prolonged warming leads to an increase in both number of leaves and flowers over time. While reproduction shows varying and regional responses to warming, impacts on plant growth, especially in high-latitude populations, have more profound effects. Such effects could lead to changes in plant community composition with increased abundance of fast-growing plants with larger leaves and more clones, affecting plant competition and ecological functions such as decomposition and nutrient retention. Effects of warming were highly context dependent; thus, we encourage further use of warming experiments to predict changes in growth, reproduction, and community composition across wetland types and climate gradients targeting different plant forms., (© 2021 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.)
- Published
- 2021
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24. A different type of perforation: appendicitis after colonoscopy.
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Jambhekar A, Robinson S, Lindborg R, Rucinski J, and Borriello R
- Abstract
Physicians who perform colonoscopy should consider appendicitis in the differential diagnosis of post procedure abdominal pain. Diagnostic laparoscopy is a safe adjunct for evaluation in patients with suspected perforation after colonoscopy. It is important that all physicians be aware of this complication to ensure prompt diagnosis and intervention.
- Published
- 2018
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25. Facing the future for grassland restoration - What about the farmers?
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Waldén E and Lindborg R
- Subjects
- Agriculture, Biodiversity, Ecosystem, Europe, Conservation of Natural Resources, Farmers, Grassland
- Abstract
In line with the 2010 Aichi Convention for Biological Diversity, the European Union has a goal to restore 15% of degraded ecosystems and their services by the year 2020 (target 2, Europe 2020). This includes restoration of semi-natural grasslands (SNGs). Management of both intact and restored SNGs is dependent on people's willingness to manage them. Due to low profitability, management abandonment still occurs all over Europe, which highlights the need to raise farmers' and landowners' perspectives. In this study, we combined survey data and in-depth interviews with farmers/landowners managing previously restored SNGs, to understand how they perceive the restoration process, the outcome and future management. Survey and interview data were analysed in relation to biodiversity and Agri-environmental payments data from the restored sites. Almost all respondents considered the restoration successful and the re-inventoried restored SNGs also showed an increase in plant diversity. Nevertheless, 10% of the restored SNGs were abandoned again post-restoration and 40% of the respondents were unsure if they would continue the management in the future. Abandoned management may cause a negative trend in terms of decreased biological, cultural and aesthetic values, in the local community, as well as for the society in general. Most respondents explained a strong dependency on Agri-environmental payments, both as a restoration incentive and for post-restoration management. Also non-financial support from authorities in form of feedback and advice was requested, as well as support from the local community and society as a whole. Future management in a longer time perspective was strongly coupled to the farm economy, i.e. received Agri-environmental payments at farm-level and profit from selling agricultural products, and whether the farmers had successors. We conclude that both social and ecological factors, here farm economy, authority support and proper management, must be in place for long-term success of grassland restoration., (Copyright © 2018 Elsevier Ltd. All rights reserved.)
- Published
- 2018
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26. Distracting injury defined: does an isolated hip fracture constitute a distracting injury for clearance of the cervical spine?
- Author
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Lindborg R, Jambhekar A, Chan V, Laskey D, Rucinski J, and Fahoum B
- Subjects
- Accidental Falls, Aged, Female, Hip Fractures epidemiology, Humans, Male, Neck Injuries epidemiology, Prospective Studies, Spinal Fractures epidemiology, Cervical Vertebrae injuries, Hip Fractures diagnostic imaging, Neck Injuries diagnostic imaging, Spinal Fractures diagnostic imaging
- Abstract
Objectives: As the population within the USA ages, the number of hip fractures seen yearly in the emergency department is expected to rise. According to the NEXUS criteria, many of these patients receive computerized tomographic scan (CT) evaluation of the cervical spine because a hip fracture may constitute a distracting injury. The objective of this study is to determine if an isolated hip fracture constitutes a distracting injury which requires imaging of the cervical spine., Methods: Data were prospectively collected on 158 trauma patients with isolated hip fractures between April 1, 2015 and March 9, 2016. Patient demographics were analyzed and compared to the National Emergency X-Radiography Utilization Study (NEXUS)., Results: Patients with isolated hip fractures were predominantly elderly, on average 78.6 +/- 15.9 years old, and 94.3% of these injuries occurred after a fall from standing. Only one patient also had a cervical spine fracture which was not clinically significant. When compared to the established rate of cervical spine injury of 2.4%, the absolute risk reduction (ARR) was 0.35% (95% CI, - 1.06 to 1.75%) and the number needed to treat (NNT) was 290., Conclusion: In the case of an elderly patient with an isolated hip fracture and no cervical midline tenderness, cervical spine imaging may be reserved for those who have other NEXUS criteria for further workup.
- Published
- 2018
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27. Over the hill and falling down: Can the NEXUS criteria be applied to the elderly?
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Jambhekar A, Lindborg R, Chan V, Fulginiti A, Fahoum B, and Rucinski J
- Subjects
- Accidental Falls, Aged, Aged, 80 and over, Cervical Vertebrae diagnostic imaging, Female, Humans, Male, Prospective Studies, Risk Assessment methods, Sensitivity and Specificity, Cervical Vertebrae injuries, Geriatric Assessment methods, Tomography, X-Ray Computed methods, Trauma Severity Indices
- Abstract
Introduction: The National Emergency X-Radiography Utilization Study (NEXUS) criteria have been criticized due to the presumed unreliability of the clinical exam in elderly patients. The objective of this study was to determine if the NEXUS criteria can be safely applied to this vulnerable group of patients., Methods: 596 trauma patients over the age of 65 were enrolled in a prospectively designed study between April 1, 2015 and October 1, 2016. The study was designed to encourage the use of the NEXUS criteria for all trauma patients including the elderly. NEXUS-negative patients (n = 226) were defined as individuals fulfilling none of the low risk criteria. The specificity and sensitivity of the NEXUS criteria were calculated based on any cervical spine injuries which were missed in NEXUS-positive patients (n = 129) who met one or more criteria., Results: Out of the 596 included elderly patients, 355 patients underwent computed tomography (CT) of the cervical spine. 129 patients were NEXUS-positive and in this group ten nonoperative cervical spine injuries were detected. There were no NEXUS-positive patients who did not undergo CT scans of the cervical spine. No cervical spine injuries were detected in the 226 NEXUS-negative patients. In elderly patients, the NEXUS criteria had a sensitivity of 100% and specificity of 100%., Conclusion: The NEXUS criteria have been criticized in prior literature as less sensitive in elderly patients. Based on the current study, the use of the NEXUS criteria may lead to decreased radiation exposure and healthcare costs allowing for better allocation of resources for patients who warrant imaging of the cervical spine., (Copyright © 2017. Published by Elsevier Ltd.)
- Published
- 2018
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28. Landscape simplification weakens the association between terrestrial producer and consumer diversity in Europe.
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Dainese M, Isaac NJB, Powney GD, Bommarco R, Öckinger E, Kuussaari M, Pöyry J, Benton TG, Gabriel D, Hodgson JA, Kunin WE, Lindborg R, Sait SM, and Marini L
- Subjects
- Animals, Ecosystem, Europe, Biodiversity, Butterflies, Phylogeny
- Abstract
Land-use change is one of the primary drivers of species loss, yet little is known about its effect on other components of biodiversity that may be at risk. Here, we ask whether, and to what extent, landscape simplification, measured as the percentage of arable land in the landscape, disrupts the functional and phylogenetic association between primary producers and consumers. Across seven European regions, we inferred the potential associations (functional and phylogenetic) between host plants and butterflies in 561 seminatural grasslands. Local plant diversity showed a strong bottom-up effect on butterfly diversity in the most complex landscapes, but this effect disappeared in simple landscapes. The functional associations between plant and butterflies are, therefore, the results of processes that act not only locally but are also dependent on the surrounding landscape context. Similarly, landscape simplification reduced the phylogenetic congruence among host plants and butterflies indicating that closely related butterflies become more generalist in the resources used. These processes occurred without any detectable change in species richness of plants or butterflies along the gradient of arable land. The structural properties of ecosystems are experiencing substantial erosion, with potentially pervasive effects on ecosystem functions and future evolutionary trajectories. Loss of interacting species might trigger cascading extinction events and reduce the stability of trophic interactions, as well as influence the longer term resilience of ecosystem functions. This underscores a growing realization that species richness is a crude and insensitive metric and that both functional and phylogenetic associations, measured across multiple trophic levels, are likely to provide additional and deeper insights into the resilience of ecosystems and the functions they provide., (© 2017 John Wiley & Sons Ltd.)
- Published
- 2017
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29. Sustained functional composition of pollinators in restored pastures despite slow functional restoration of plants.
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Winsa M, Öckinger E, Bommarco R, Lindborg R, Roberts SPM, Wärnsberg J, and Bartomeus I
- Abstract
Habitat restoration is a key measure to counteract negative impacts on biodiversity from habitat loss and fragmentation. To assess success in restoring not only biodiversity, but also functionality of communities, we should take into account the re-assembly of species trait composition across taxa. Attaining such functional restoration would depend on the landscape context, vegetation structure, and time since restoration. We assessed how trait composition of plant and pollinator (bee and hoverfly) communities differ between abandoned, restored (formerly abandoned) or continuously grazed (intact) semi-natural pastures. In restored pastures, we also explored trait composition in relation to landscape context, vegetation structure, and pasture management history. Abandoned pastures differed from intact and restored pastures in trait composition of plant communities, and as expected, had lower abundances of species with traits associated with grazing adaptations. Further, plant trait composition in restored pastures became increasingly similar to that in intact pastures with increasing time since restoration. On the contrary, the trait composition of pollinator communities in both abandoned and restored pastures remained similar to intact pastures. The trait composition for both bees and hoverflies was influenced by flower abundance and, for bees, by connectivity to other intact grasslands in the landscape. The divergent responses across organism groups appeared to be mainly related to the limited dispersal ability and long individual life span in plants, the high mobility of pollinators, and the dependency of semi-natural habitat for bees. Our results, encompassing restoration effects on trait composition for multiple taxa along a gradient in both time (time since restoration) and space (connectivity), reveal how interacting communities of plants and pollinators are shaped by different trait-environmental relationships. Complete functional restoration of pastures needs for more detailed assessments of both plants dispersal in time and of resources available within pollinator dispersal range.
- Published
- 2017
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30. Readmission Following Laparoscopic Sleeve Gastrectomy.
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Jambhekar A, Maselli A, Lindborg R, Kabata K, Tortolani A, and Gorecki P
- Abstract
Background and Objectives: Prior studies have established a 1.7-4.33% readmission rate for laparoscopic sleeve gastrectomy (LSG), a rate that falls within the reported range for other bariatric procedures. The current report describes the incidence of 30-day readmission after primary LSG procedures performed at a single bariatric center of excellence (COE) and examines factors that may be associated with readmission., Methods: Data on 343 consecutive LSG operations performed from February 2010 to May 2014 by a single surgeon (PG) were analyzed. Patients readmitted within 30 d were compared to the remaining patients by using Student's t test for continuous variables and the χ
2 test for categorical variables., Results: All LSGs were completed laparoscopically with no conversions to open procedures. There were no reoperations, leaks, perioperative hemorrhages, or mortalities. Twelve patients (3.5%) were readmitted; 1 was readmitted twice. There were no identified risk factors for readmission, including patient demographics, comorbidities, and perioperative factors. Notably, 7 (7%) readmissions occurred in the initial 100 patients and 5 (2%) in the remaining 243 patients ( P = .04). Clinical pathways were modified after the initial 100 patients; routine contrast esophagograms were no longer performed, and a 1-day routine postoperative stay was adopted. Operative time also decreased from 94.2 ± 23.8 to 78.2 ± 20.0 min ( P < .001)., Conclusions: Readmission rates after LSG remain in a range similar to those described for other laparoscopic bariatric procedures. Larger prospective studies are needed to identify patterns of complications and readmissions in patients undergoing LSG that may differ from other bariatric procedures.- Published
- 2016
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31. Long Term Positive Effect of Grassland Restoration on Plant Diversity - Success or Not?
- Author
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Waldén E and Lindborg R
- Subjects
- Conservation of Natural Resources, Ecosystem, Humans, Poaceae, Species Specificity, Sweden, Biodiversity, Grassland, Plants classification
- Abstract
Restoration is important for biodiversity conservation worldwide, but surprisingly little is known about its efficiency in a long-term perspective. In this study, we re-examined Swedish semi-natural grasslands 12-20 years after the restoration, by comparing field inventories of vascular plant species diversity made in 2001 with follow-up inventories in 2012. We also analysed restoration effect in relation to six environmental factors and used continuously managed semi-natural grasslands as references of desired state after restoration. We found that total species richness increased over time but not to reference levels, while there were no significant changes in species density or number of grassland specialists. However, the overall species composition in the restored sites, as well as grassland specialist composition, now largely resembled reference conditions. Fertilisation and time between abandonment and restoration were the only environmental variables that affected total species composition change, while site area affected change in grassland specialist composition. Our results show that restoration of semi-natural grasslands can contribute to conservation of semi-natural habitats and their associated biodiversity. Yet, due to the vague restoration goals for these sites, it is difficult to evaluate the restoration success, which emphasise the general need for clear and measurable goals.
- Published
- 2016
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32. A social-ecological analysis of ecosystem services in two different farming systems.
- Author
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Andersson E, Nykvist B, Malinga R, Jaramillo F, and Lindborg R
- Subjects
- Biodiversity, Agriculture, Conservation of Natural Resources methods, Ecosystem
- Abstract
In this exploratory study we use existing in situ qualitative and quantitative data on biophysical and social indicators to compare two contrasting Swedish farming systems (low intensity and high intensity) with regard to ecosystem service supply and demand of a broad suite of services. We show that the value (demand) placed on a service is not necessarily connected to the quantity (supply) of the service, most clearly shown for the services recreation, biodiversity, esthetic experience, identity, and cultural heritage. To better capture this complexity we argue for the need to develop portfolios of indicators for different ecosystem services and to further investigate the different aspects of supply and demand. The study indicates that available data are often ill-suited to answer questions about local delivery of services. If ecosystem services are to be included in policy, planning, and management, census data need to be formatted and scaled appropriately.
- Published
- 2015
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33. Implications of climate and land-use change for landscape processes, biodiversity, ecosystem services, and governance.
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Elmhagen B, Eriksson O, and Lindborg R
- Subjects
- Biodiversity, Sweden, Climate Change, Conservation of Natural Resources methods, Ecosystem
- Abstract
This introduction to the Special Issue summarizes the results of 14 scientific articles from the interdisciplinary research program Ekoklim at Stockholm University, Sweden. In this program, we investigate effects of changing climate and land use on landscape processes, biodiversity, and ecosystem services, and analyze issues related to adaptive governance in the face of climate and land-use change. We not only have a research focus on the 22 650 km(2) Norrström catchment surrounding lake Mälaren in south-central Sweden, but we also conduct research in other Swedish regions. The articles presented here show complex interactions between multiple drivers of change, as well as feedback processes at different spatiotemporal scales. Thus, the Ekoklim program highlights and deals with issues relevant for the future challenges society will face when land-use change interacts with climate change.
- Published
- 2015
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34. Species richness and assemblages in landscapes of different farming intensity--time to revise conservation strategies?
- Author
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Andersson E and Lindborg R
- Subjects
- Animals, Birds physiology, Plant Physiological Phenomena, Sweden, Trees physiology, Agriculture methods, Biodiversity, Conservation of Natural Resources methods
- Abstract
Worldwide conservation goals to protect biodiversity emphasize the need to rethink which objectives are most suitable for different landscapes. Comparing two different Swedish farming landscapes, we used survey data on birds and vascular plants to test whether landscapes with large, intensively managed farms had lower richness and diversity of the two taxa than landscapes with less intensively managed small farms, and if they differed in species composition. Landscapes with large intensively managed farms did not have lower richness than smaller low intensively managed farms. The landscape types were also similar in that they had few red listed species, normally targeted in conservation. Differences in species composition demonstrate that by having both types of agricultural landscapes regional diversity is increased, which is seldom captured in the objectives for agro-environmental policies. Thus we argue that focus on species richness or red listed species would miss the actual diversity found in the two landscape types. Biodiversity conservation, especially in production landscapes, would therefore benefit from a hierarchy of local to regional objectives with explicit targets in terms of which aspects of biodiversity to focus on.
- Published
- 2014
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35. Density of insect-pollinated grassland plants decreases with increasing surrounding land-use intensity.
- Author
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Clough Y, Ekroos J, Báldi A, Batáry P, Bommarco R, Gross N, Holzschuh A, Hopfenmüller S, Knop E, Kuussaari M, Lindborg R, Marini L, Öckinger E, Potts SG, Pöyry J, Roberts SP, Steffan-Dewenter I, and Smith HG
- Subjects
- Animals, Bees physiology, Linear Models, Population Density, Ecosystem, Insecta physiology, Models, Biological, Plant Physiological Phenomena, Pollination
- Abstract
Pollinator declines have raised concerns about the persistence of plant species that depend on insect pollination, in particular by bees, for their reproduction. The impact of pollinator declines remains unknown for species-rich plant communities found in temperate seminatural grasslands. We investigated effects of land-use intensity in the surrounding landscape on the distribution of plant traits related to insect pollination in 239 European seminatural grasslands. Increasing arable land use in the surrounding landscape consistently reduced the density of plants depending on bee and insect pollination. Similarly, the relative abundance of bee-pollination-dependent plants increased with higher proportions of non-arable agricultural land (e.g. permanent grassland). This was paralleled by an overall increase in bee abundance and diversity. By isolating the impact of the surrounding landscape from effects of local habitat quality, we show for the first time that grassland plants dependent on insect pollination are particularly susceptible to increasing land-use intensity in the landscape., (© 2014 John Wiley & Sons Ltd/CNRS.)
- Published
- 2014
- Full Text
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36. Political systems affect mobile and sessile species diversity--a legacy from the post-WWII period.
- Author
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Cousins SA, Kaligarič M, Bakan B, and Lindborg R
- Subjects
- Agriculture, Animals, Conservation of Natural Resources, Ecosystem, Europe, Geography, History, 20th Century, Population Density, Population Dynamics, World War I, World War II, Biodiversity, Birds, Plants, Political Systems
- Abstract
Political ideologies, policies and economy affect land use which in turn may affect biodiversity patterns and future conservation targets. However, few studies have investigated biodiversity in landscapes with similar physical properties but governed by different political systems. Here we investigate land use and biodiversity patterns, and number and composition of birds and plants, in the borderland of Austria, Slovenia and Hungary. It is a physically uniform landscape but managed differently during the last 70 years as a consequence of the political "map" of Europe after World War I and II. We used a historical map from 1910 and satellite data to delineate land use within three 10-kilometre transects starting from the point where the three countries meet. There was a clear difference between countries detectable in current biodiversity patterns, which relates to land use history. Mobile species richness was associated with current land use whereas diversity of sessile species was more associated with past land use. Heterogeneous landscapes were positively and forest cover was negatively correlated to bird species richness. Our results provide insights into why landscape history is important to understand present and future biodiversity patterns, which is crucial for designing policies and conservation strategies across the world.
- Published
- 2014
- Full Text
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37. Plant uptake of elements in soil and pore water: field observations versus model assumptions.
- Author
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Raguž V, Jarsjö J, Grolander S, Lindborg R, and Avila R
- Subjects
- Elements, Hordeum chemistry, Plants chemistry, Risk Assessment, Soil chemistry, Sweden, Hordeum metabolism, Models, Theoretical, Plants metabolism, Soil Pollutants pharmacokinetics
- Abstract
Contaminant concentrations in various edible plant parts transfer hazardous substances from polluted areas to animals and humans. Thus, the accurate prediction of plant uptake of elements is of significant importance. The processes involved contain many interacting factors and are, as such, complex. In contrast, the most common way to currently quantify element transfer from soils into plants is relatively simple, using an empirical soil-to-plant transfer factor (TF). This practice is based on theoretical assumptions that have been previously shown to not generally be valid. Using field data on concentrations of 61 basic elements in spring barley, soil and pore water at four agricultural sites in mid-eastern Sweden, we quantify element-specific TFs. Our aim is to investigate to which extent observed element-specific uptake is consistent with TF model assumptions and to which extent TF's can be used to predict observed differences in concentrations between different plant parts (root, stem and ear). Results show that for most elements, plant-ear concentrations are not linearly related to bulk soil concentrations, which is congruent with previous studies. This behaviour violates a basic TF model assumption of linearity. However, substantially better linear correlations are found when weighted average element concentrations in whole plants are used for TF estimation. The highest number of linearly-behaving elements was found when relating average plant concentrations to soil pore-water concentrations. In contrast to other elements, essential elements (micronutrients and macronutrients) exhibited relatively small differences in concentration between different plant parts. Generally, the TF model was shown to work reasonably well for micronutrients, whereas it did not for macronutrients. The results also suggest that plant uptake of elements from sources other than the soil compartment (e.g. from air) may be non-negligible., (Copyright © 2013 Elsevier Ltd. All rights reserved.)
- Published
- 2013
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38. Ecological assembly rules in plant communities--approaches, patterns and prospects.
- Author
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Götzenberger L, de Bello F, Bråthen KA, Davison J, Dubuis A, Guisan A, Lepš J, Lindborg R, Moora M, Pärtel M, Pellissier L, Pottier J, Vittoz P, Zobel K, and Zobel M
- Subjects
- Models, Biological, Models, Statistical, Plants genetics, Species Specificity, Ecosystem, Plants classification
- Abstract
Understanding how communities of living organisms assemble has been a central question in ecology since the early days of the discipline. Disentangling the different processes involved in community assembly is not only interesting in itself but also crucial for an understanding of how communities will behave under future environmental scenarios. The traditional concept of assembly rules reflects the notion that species do not co-occur randomly but are restricted in their co-occurrence by interspecific competition. This concept can be redefined in a more general framework where the co-occurrence of species is a product of chance, historical patterns of speciation and migration, dispersal, abiotic environmental factors, and biotic interactions, with none of these processes being mutually exclusive. Here we present a survey and meta-analyses of 59 papers that compare observed patterns in plant communities with null models simulating random patterns of species assembly. According to the type of data under study and the different methods that are applied to detect community assembly, we distinguish four main types of approach in the published literature: species co-occurrence, niche limitation, guild proportionality and limiting similarity. Results from our meta-analyses suggest that non-random co-occurrence of plant species is not a widespread phenomenon. However, whether this finding reflects the individualistic nature of plant communities or is caused by methodological shortcomings associated with the studies considered cannot be discerned from the available metadata. We advocate that more thorough surveys be conducted using a set of standardized methods to test for the existence of assembly rules in data sets spanning larger biological and geographical scales than have been considered until now. We underpin this general advice with guidelines that should be considered in future assembly rules research. This will enable us to draw more accurate and general conclusions about the non-random aspect of assembly in plant communities., (© 2011 The Authors. Biological Reviews © 2011 Cambridge Philosophical Society.)
- Published
- 2012
- Full Text
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39. Habitat fragmentation causes immediate and time-delayed biodiversity loss at different trophic levels.
- Author
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Krauss J, Bommarco R, Guardiola M, Heikkinen RK, Helm A, Kuussaari M, Lindborg R, Ockinger E, Pärtel M, Pino J, Pöyry J, Raatikainen KM, Sang A, Stefanescu C, Teder T, Zobel M, and Steffan-Dewenter I
- Subjects
- Animals, Europe, Extinction, Biological, Biodiversity, Butterflies classification, Ecosystem, Plants classification
- Abstract
Intensification or abandonment of agricultural land use has led to a severe decline of semi-natural habitats across Europe. This can cause immediate loss of species but also time-delayed extinctions, known as the extinction debt. In a pan-European study of 147 fragmented grassland remnants, we found differences in the extinction debt of species from different trophic levels. Present-day species richness of long-lived vascular plant specialists was better explained by past than current landscape patterns, indicating an extinction debt. In contrast, short-lived butterfly specialists showed no evidence for an extinction debt at a time scale of c. 40 years. Our results indicate that management strategies maintaining the status quo of fragmented habitats are insufficient, as time-delayed extinctions and associated co-extinctions will lead to further biodiversity loss in the future.
- Published
- 2010
- Full Text
- View/download PDF
40. Investigating biodiversity trajectories using scenarios--lessons from two contrasting agricultural landscapes.
- Author
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Lindborg R, Stenseke M, Cousins SA, Bengtsson J, Berg A, Gustafsson T, Sjödin NE, and Eriksson O
- Subjects
- Conservation of Natural Resources, Recreation, Sweden, Agriculture, Biodiversity
- Abstract
Agriculture is the major land use at a global scale. In addition to food production, multifunctionality of landscapes, including values and ecosystem services like biodiversity, recreation and culture, is now focus for management. This study explores how a scenario approach, involving different stakeholders, may help to improve landscape management for biodiversity conservation. Local farmers and executives at the County Administrative Board were invited to discuss rural development and conditions for farmland biodiversity in two Swedish landscapes. The potential biodiversity for three future land use scenarios for the two landscapes was discussed: nature conservation, outdoor recreation and energy production, and compared with current and historical landscapes in each region. Analyses of habitat areas, connectedness and landscape diversity suggested that the energy and recreation scenarios had a negative impact on farmland biodiversity, whereas the nature conservation scenario, the current and historically reconstructed landscapes had a higher potential for biodiversity. The farmers appreciated the nature conservation scenario, but also the energy production scenario and they highlighted the need of increased subsidies for management of biodiversity. The farmers in the high production area were less interested in nature quality per se. The executives had similar opinions as the farmers, but disagreed on the advantages with energy production, as this would be in conflict with the high biodiversity and recreational values. The local physical and socio-economical conditions differ between landscapes and potentially shaped the stakeholders emotional attachment to the local environment, their opinions and decisions on how to manage the land. We stress the importance of incorporating local knowledge, visions and regional prerequisites for different land uses in conservation, since site and landscape specific planning for biodiversity together with a flexible subsidy system are necessary to reach the conservation goals within EU.
- Published
- 2009
- Full Text
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41. Extinction debt: a challenge for biodiversity conservation.
- Author
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Kuussaari M, Bommarco R, Heikkinen RK, Helm A, Krauss J, Lindborg R, Ockinger E, Pärtel M, Pino J, Rodà F, Stefanescu C, Teder T, Zobel M, and Steffan-Dewenter I
- Subjects
- Animals, Biodiversity, Conservation of Natural Resources, Extinction, Biological
- Abstract
Local extinction of species can occur with a substantial delay following habitat loss or degradation. Accumulating evidence suggests that such extinction debts pose a significant but often unrecognized challenge for biodiversity conservation across a wide range of taxa and ecosystems. Species with long generation times and populations near their extinction threshold are most likely to have an extinction debt. However, as long as a species that is predicted to become extinct still persists, there is time for conservation measures such as habitat restoration and landscape management. Standardized long-term monitoring, more high-quality empirical studies on different taxa and ecosystems and further development of analytical methods will help to better quantify extinction debt and protect biodiversity.
- Published
- 2009
- Full Text
- View/download PDF
42. A strategy for describing the biosphere at candidate sites for repositories of nuclear waste: linking ecosystem and landscape modeling.
- Author
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Lindborg T, Lindborg R, Löfgren A, Söderbäck B, Bradshaw C, and Kautsky U
- Subjects
- Licensure, Safety, Sweden, Waste Management standards, Ecosystem, Radioactive Waste, Waste Management methods
- Abstract
To provide information necessary for a license application for a deep repository for spent nuclear fuel, the Swedish Nuclear Fuel and Waste Management Co. has started site investigations at two sites in Sweden. In this paper, we present a strategy to integrate site-specific ecosystem data into spatially explicit models needed for safety assessment studies and the environmental impact assessment. The site-specific description of ecosystems is developed by building discipline-specific models from primary data and by identifying interactions and stocks and flows of matter among functional units at the sites. The conceptual model is a helpful initial tool for defining properties needed to quantify system processes, which may reveal new interfaces between disciplines, providing a variety of new opportunities to enhance the understanding of the linkages between ecosystem characteristics and the functional properties of landscapes. This type of integrated ecosystem-landscape characterization model has an important role in forming the implementation of a safety assessment for a deep repository.
- Published
- 2006
- Full Text
- View/download PDF
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