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Land Use Change Consistently Reduces α‐ But Not β‐ and γ‐Diversity of Bees

2025, Tsang, Toby P. N., De Santis, A. A. Amado, Armas‐Quiñonez, Gabriela, Ascher, John S., Ávila‐Gómez, Eva Samanta, Báldi, András, Ballare, Kimberly M., Balzan, Mario V., Banaszak-Cibicka, Weronika, Bänsch, Svenja, Basset, Yves, Bates, Adam J., Baumann, Jessica M., Beal‐Neves, Mariana, Bennett, Ashley, Bezerra, Antonio Diego M., Blochtein, Betina, Bommarco, Riccardo, Brosi, Berry, Burkle, Laura A., Carvalheiro, Luísa G., Castellanos, Ignacio, Cely‐Santos, Marcela, Cohen, Hamutahl, Coulibaly, Drissa, Cunningham, Saul A., Cusser, Sarah, Dajoz, Isabelle, Delaney, Deborah A., Del‐Val, Ek, Egerer, Monika, Eichhorn, Markus P., Enríquez, Eunice, Entling, Martin H., Escobedo‐Kenefic, Natalia, Ferreira, Pedro Maria Abreu, Fitch, Gordon, Forrest, Jessica R. K., Fournier, Valérie, Fowler, Robert, Freitas, Breno M., Gaines‐Day, Hannah R., Geslin, Benoît, Ghazoul, Jaboury, Glaum, Paul, Gonzalez‐Andujar, Jose L., González‐Chaves, Adrian, Grab, Heather, Gratton, Claudio, Guenat, Solène, Gutiérrez‐Chacón, Catalina, Hall, Mark A., Hanley, Mick E., Hass, Annika, Hennig, Ernest Ireneusz, Hermy, Martin, Hipólito, Juliana, Holzschuh, Andrea, Hopfenmüller, Sebastian, Hung, Keng‐Lou James, Hylander, Kristoffer, Izquierdo, Jordi, Jamieson, Mary A., Jauker, Birgit, Javorek, Steve, Jha, Shalene, Klatt, Björn K., Kleijn, David, Klein, Alexandra‐Maria, Kovács‐Hostyánszki, Anikó, Krauss, Jochen, Kuhlmann, Michael, Landaverde‐González, Patricia, Latty, Tanya, Leong, Misha, Lerman, Susannah B., Liu, Yunhui, Machado, Ana Carolina Pereira, Main, Anson, Mallinger, Rachel, Mandelik, Yael, Marques, Bruno Ferreira, Matteson, Kevin, McCune, Frédéric, Meng, Ling‐Zeng, Metzger, Jean Paul, Montoya‐Pfeiffer, Paula María, Morales, Carolina, Morandin, Lora, Morrison, Jane, Mudri‐Stojnić, Sonja, Nalinrachatakan, Pakorn, Norfolk, Olivia, Otieno, Mark, Park, Mia G., Philpott, Stacy M., Pisanty, Gideon, Plascencia, Montserrat, Potts, Simon G., Power, Eileen F., Prendergast, Kit, Quistberg, Robyn D., de Lacerda Ramos, Davi, Rech, André Rodrigo, Reynolds, Victoria, Richards, Miriam H., Roberts, Stuart P. M., Sabatino, Malena, Samnegård, Ulrika, Sardiñas, Hillary, Sánchez‐Echeverría, Karina, Saturni, Fernanda Teixeira, Scheper, Jeroen, Sciligo, Amber R., Sidhu, C. Sheena, Spiesman, Brian J., Sritongchuay, Tuanjit, Steffan‐Dewenter, Ingolf, Stein, Katharina, Stewart, Alyssa B., Stout, Jane C., Taki, Hisatomo, Tangtorwongsakul, Pornpimon, Threlfall, Caragh G., Tinoco, Carla Faleiro, Tscharntke, Teja, Turo, Katherine J., Vaidya, Chatura, Vandame, Rémy, Vergara, Carlos H., Viana, Blandina F., Vides‐Borrell, Eric, Warrit, Natapot, Webb, Elisabeth, Westphal, Catrin, Wickens, Jennifer B., Williams, Neal M., Williams, Nicholas S. G., Wilson, Caleb J., Wu, Panlong, Youngsteadt, Elsa, Zou, Yi, Ponisio, Lauren C., Bonebrake, Timothy C.

ABSTRACTLand use change threatens global biodiversity and compromises ecosystem functions, including pollination and food production. Reduced taxonomic α‐diversity is often reported under land use change, yet the impacts could be different at larger spatial scales (i.e., γ‐diversity), either due to reduced β‐diversity amplifying diversity loss or increased β‐diversity dampening diversity loss. Additionally, studies often focus on taxonomic diversity, while other important biodiversity components, including phylogenetic diversity, can exhibit differential responses. Here, we evaluated how agricultural and urban land use alters the taxonomic and phylogenetic α‐, β‐, and γ‐diversity of an important pollinator taxon—bees. Using a multicontinental dataset of 3117 bee assemblages from 157 studies, we found that taxonomic α‐diversity was reduced by 16%–18% in both agricultural and urban habitats relative to natural habitats. Phylogenetic α‐diversity was decreased by 11%–12% in agricultural and urban habitats. Compared with natural habitats, taxonomic and phylogenetic β‐diversity increased by 11% and 6% in urban habitats, respectively, but exhibited no systematic change in agricultural habitats. We detected a 22% decline in taxonomic γ‐diversity and a 17% decline in phylogenetic γ‐diversity in agricultural habitats, but γ‐diversity of urban habitats was not significantly different from natural habitats. These findings highlight the threat of agricultural expansions to large‐scale bee diversity due to systematic γ‐diversity decline. In addition, while both urbanization and agriculture lead to consistent declines in α‐diversity, their impacts on β‐ or γ‐diversity vary, highlighting the need to study the effects of land use change at multiple scales.

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Pollinator‐Promoting Interventions in European Urban Habitats—A Synthesis

2025, Süle, Gabriella, Báldi, András, Kleijn, David, Steffan‐Dewenter, Ingolf, Venn, Stephen, Goulson, Dave, Dietzel, Simon, Muratet, Audrey, Cole, Lorna J., Öckinger, Erik, Tzortzakaki, Olga, Banaszak-Cibicka, Weronika, Betz, Oliver, Blackmore, Lorna M., Dylewski, Łukasz, Fontaine, Benoît, Fournier, Bertrand, Geppert, Costanza, Griffiths‐Lee, Janine, Hawthorn, Catriona, Holzschuh, Andrea, Horák, Jakub, Horstmann, Svenja, Hoyle, Helen, Kati, Vassiliki, Kovács‐Hostyánszki, Anikó, Marini, Lorenzo, Michelot‐Antalik, Alice, Moretti, Marco, Norton, Briony A., Phillips, Benjamin B., Plećaš, Milan, Rada, Patrik, Sárospataki, Miklós, Schulze, Sonja, Shwartz, Assaf, Unterweger, Philipp, Szigeti, Viktor

ABSTRACTPollinators receive considerable interest due to their fundamental role in ecosystem functioning and human well‐being. Unlike farmlands, studies of urban pollinator‐promoting interventions are scarce and have not been synthesised, hampering policy implementation. To fill this gap, we compared pollinator‐promoting interventions (treatment) with conventionally managed (control) sites regarding vegetation, floral resources, and pollinators. Our synthesis investigated 1051 sampling sites with different interventions (abandonment, extensive mowing, flower sowing, and combined practices) and habitats (parks, grasslands, road verges, private and public gardens) from 28 European datasets at pooled‐ and study‐levels. Urban pollinator‐promoting interventions generally benefited plants and pollinators with taxon, intervention, habitat, and spatio‐temporal specific differences. Pooled analyses showed mostly positive and never negative treatment effects, while study‐level details described primarily positive and neutral but rarely negative effects. Bumblebees and butterflies benefited most from the interventions. Some effects were stronger for interventions involving flower sowing, interventions occurring in road verges, and interventions located in Northwestern Europe. Although regulations, guidelines, and monitoring are improving, knowledge gaps remain for some pollinator taxa (e.g., beetles), regions (e.g., Mediterranean), and novel interventions (e.g., for ground‐nesting insects). Further collaborative studies from around the world could help cities bring people, plants, and pollinators together by creating resilient, multi‐functional urban spaces.