Abstract
The regionally threatened damselfly Sympecma peadisca is one of the few Central European dragonfly species included is considered as Near Threatened in the European Red list. The major threats to this species remain unclear. This species has a unique life history and several adaptations to enabling survival even in semidesert areas, such as overwintering in the adult stage. However, the closely related, more thermophilic species Sympecma fusca has undergone a major range expansion in Europe. Based on data from 129 sites and combining several analytical approaches, I found the following: 1. According to local freshwater conditions, S. paedisca is a typical habitat generalist occupying a wide range of habitats. 2. It requires a wide range of terrestrial habitats to complete its life cycle. 3. An analysis of the land used by both species clearly indicates that both species avoid intensive agricultural areas; however, S. fusca can also occur in suburban areas, where S. paedisca is absent. 4. Projections of the Least Cost Path analysis indicate that the only localities where the species is currently spreading are habitats arising as a consequence of mining activities. The example of S. paedisca is clear evidence of a freshwater species that responds very negatively to the homogenization of the terrestrial environment, even when its natal habitat is not significantly affected. The frequent occurrence of species in postmining areas suggests that species with complex habitat requirements can find suitable secondary habitats where they can prosper in the long term.
Implications for insect conservation
Even semi-aquatic groups like damselflies can be very sensitive to gradual changes in surrounding land use. Species with very complex habitat requirements also require comprehensive conservation strategies affecting all habitats utilized by the species. However, the return of some landscape features requires a reduction in the area of production areas in favor of hedgerows and ruderals. Such restoration management requires long-term planning and close cooperation with farmers.
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References
Baessler C, Klotz S (2006) Effects of changes in agricultural land-use on landscape structure and arable weed vegetation over the last 50 years. Agric Ecosyst Environ 115:43–50. https://doi.org/10.1016/j.agee.2005.12.007
Bartoń K (2009) MuMIn: Multi-Model Inference
Bates D, Maechler M, Bolker B et al (2015) Package ‘lme4’
Bellard C, Bertelsmeier C, Leadley P et al (2012) Impacts of climate change on the future of biodiversity. Ecol Lett 15:365–377. https://doi.org/10.1111/j.1461-0248.2011.01736.x.Impacts
Bossard M, Feranec J, Otahel J (2000) CORINE land cover technical guide – addendum 2000. EEA Tech Rep
Boudot J-P, Kalkman VJ (2015) Atlas of the european Dragonflies and Damselflies. KNNV Publishing, Zeist
Bried JT, Samways MJ (2015) A review of odonatology in freshwater applied ecology and conservation science. Freshw Sci 34:1023–1031. https://doi.org/10.1086/682174
Chang K-T (2018) Introduction to geographic information systems, 9th editio. McGraw Hill, New York
Chin KS, Taylor PD (2009) Interactive effects of distance and matrix on the movements of a peatland dragonfly. Ecography (Cop) 32:715–722. https://doi.org/10.1111/j.1600-0587.2009.05744.x
Clausnitzer V, Kalkman VJ, Ram M et al (2009) Odonata enter the biodiversity crisis debate: the first global assessment of an insect group. Biol Conserv 142:1864–1869. https://doi.org/10.1016/j.biocon.2009.03.028
Darwall WRT, Smith K, Allen D et al (2008) Freshwater biodiversity. a hidden resource under threat
De Knijf G, Termaat T, Ott J (2015) Conservation of european dragonflies and damselflies. In: Boudot J-P, Kalkman VJ (eds) Atlas of the european dragonflies and damselflies. KNNV publishing, the Netherlands, pp 26–35
Delpon G, Vogt-Schilb H, Munoz F et al (2019) Diachronic variations in the distribution of butterflies and dragonflies linked to recent habitat changes in Western Europe. Insect Conserv Divers 12:49–68. https://doi.org/10.1111/icad.12309
Dolný A, Bárta D, Waldhauser M et al (2007) The Dragonflies of the Czech Republic: Ecology, conservation and distribution. Český svaz ochránců přírody Vlašim, Vlašim
Dolný A, Harabiš F, Bárta D et al (2012) Aquatic insects indicate terrestrial habitat degradation: changes in taxonomical structure and functional diversity of dragonflies in tropical rainforest of East Kalimantan. Trop Zool 25:141–157. https://doi.org/10.1080/03946975.2012.717480
Dudgeon D, Arthington AH, Gessner MO et al (2006) Freshwater biodiversity: importance, threats, status and conservation challenges. Biol Rev Camb Philos Soc 81:163–182. https://doi.org/10.1017/S1464793105006950
Esri (2011) ArcGIS Release 10.7. Redlands, CA. available from: http://www.esri.com/software/arcgis
Fincke OM (1994) Population regulation of a tropical damselfly in the larval stage by food limitation, cannibalism, intraguild predation and habitat drying. Oecologia 100–100:118–127. https://doi.org/10.1007/BF00317138
Hallmann CA, Sorg M, Jongejans E et al (2017) More than 75% decline over 27 years in total flying insect biomass in protected areas. PLoS ONE 12. https://doi.org/10.1371/journal.pone.0185809
Harabis F (2016) High diversity of odonates in post-mining areas: Meta-analysis uncovers potential pitfalls associated with the formation and management of valuable habitats. Ecol Eng 90:438–446. https://doi.org/10.1016/j.ecoleng.2016.01.070
Harabis F (2017) Does the management of surrounding terrestrial habitats increase the tendency of odonates to leave aquatic habitats? Biodivers Conserv 26:2155–2167. https://doi.org/10.1007/s10531-017-1350-8
Harabis F, Dolny A (2011) The effect of ecological determinants on the dispersal abilities of central european dragonflies (Odonata). Odonatologica 40:17–26
Harabiš F (2016) The value of terrestrial ecotones as refuges for winter damselflies (Odonata: Lestidae). J Insect Conserv 20:971–977. https://doi.org/10.1007/s10841-016-9929-z
Harabiš F, Dolný A, Šipoš J et al (2012) Enigmatic adult overwintering in damselflies: coexistence as weaker intraguild competitors due to niche separation in time. Popul Ecol 54:549–556. https://doi.org/10.1007/s10144-012-0331-8
Hassall C, Thompson DJ (2008) The effects of environmental warming on Odonata: a review. Int J Odonatol 11:131–153. https://doi.org/10.1080/13887890.2008.9748319
Jödicke R (1997) Die Binsenjungfern und Winterlibellen Europas: Lestidae. Die Neue Brehm-Bücherei; Bd. 631, die Libellen Europas-Band 3). Westarp Wissenschaften, Magdeburg
Jödicke R, Mitamura T (1995) Contribution towards an annotated bibliography on hibernation in Sympecma Burmeister (Odonata: Lestidae). Opusc Zool Flum 1–9
Kalkman VJ, Boudot J-P, Bernard R et al (2010) European Red List of Dragonflies. Publications Office of the European Union, Luxembourg
Kraft NJB, Adler PB, Godoy O et al (2015) Community assembly, coexistence and the environmental filtering metaphor. Funct Ecol 29:592–599. https://doi.org/10.1111/1365-2435.12345
Manger R, Dingemanse N (2009) Adult survival of Sympecma Paedisca (Brauer) during hibernation (Zygoptera: Lestidae): short Communications. Odonatologica 38:55–59
Oksanen J, Blanchet FG, Friendly M, Kindt R, Legendre P, McGlinn D, Minchin PR, O’Hara RB, Simpson GL, Solymos P, Stevens MHH, Szoecs E, Wagner H (2020) vegan: Community Ecology. Package. R package version 2.5-7
Ott J (2009) The Big Trek northwards: recent changes in the european Dragonfly Fauna. Atlas Biodivers Chap 3:78–79
Pires MM, Sahlén G, Périco E (2022) Agricultural land use affects the heterogeneity of Odonata communities in the brazilian pampa. J Insect Conserv 26:503–514. https://doi.org/10.1007/s10841-021-00349-0
Prach K (2003) Spontaneous succession in central-european man-made habitats: what information can be used in restoration practice? App Veg Sci 6:125–129
R Core Team (2018) R A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, Vienna. URL: www.r-project.org
Raebel EM, Merckx T, Feber RE et al (2012) Multi-scale effects of farmland management on dragonfly and damselfly assemblages of farmland ponds. Agric Ecosyst Environ 161:80–87. https://doi.org/10.1016/j.agee.2012.07.015
Raven PH, Wagner DL (2021) Agricultural intensification and climate change are rapidly decreasing insect biodiversity. Proc Natl Acad Sci U S A 118:1–6. https://doi.org/10.1073/PNAS.2002548117
Reidsma P, Tekelenburg T, Van Den Berg M, Alkemade R (2006) Impacts of land-use change on biodiversity: an assessment of agricultural biodiversity in the European Union. Agric Ecosyst Environ 114:86–102. https://doi.org/10.1016/j.agee.2005.11.026
Samways MJ, Barton PS, Birkhofer K et al (2020) Solutions for humanity on how to conserve insects. Biol Conserv 242:108427. https://doi.org/10.1016/j.biocon.2020.108427
Sánchez-Bayo F, Wyckhuys KAG (2019) Worldwide decline of the entomofauna: a review of its drivers. Biol Conserv 232:8–27. https://doi.org/10.1016/j.biocon.2019.01.020
Schmidt B (1993) Sympecma paedisca in SW-Germany. Carolinea
Stevens VM, Trochet A, Van Dyck H et al (2012) How is dispersal integrated in life histories: a quantitative analysis using butterflies. Ecol Lett 15:74–86. https://doi.org/10.1111/j.1461-0248.2011.01709.x
Termaat T, van Strien AJ, van Grunsven RH, A D et al (2019) Distribution trends of european dragonflies under climate change. Divers Distrib 25:936–950. https://doi.org/10.1111/ddi.12913
Tews J, Brose U, Grimm V et al (2004) Animal species diversity driven by habitat heterogeneity/diversity: the importance of keystone structures. J Biogeogr 31:79–92. https://doi.org/10.1046/j.0305-0270.2003.00994.x
Thomas CD, Jones TH, Hartley SE (2019) Insectageddon”: a call for more robust data and rigorous analyses. Glob Chang Biol 26–27. https://doi.org/10.1111/gcb.14608
Van Dyck H, Baguette M (2005) Dispersal behaviour in fragmented landscapes: routine or special movements? Basic Appl Ecol 6:535–545. https://doi.org/10.1016/j.baae.2005.03.005
Verburg PH, Schulp CJE, Witte N, Veldkamp A (2006) Downscaling of land use change scenarios to assess the dynamics of european landscapes. Agric Ecosyst Environ 114:39–56. https://doi.org/10.1016/j.agee.2005.11.024
Acknowledgements
I thank Jakub Mráz for help with the least cost path analysis and Kristýna Abrahámová, Adéla Käschnerová, Zuzana Šorová, Kamila Černá and Petra Černochová for their assistance with data collection.
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This research was funded by the Ministry of Education, Youth and Sports of the Czech Republic, grant number CZ.02.1.01/0.0/0.0/16_026/0008403.
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F.H. compiled all data samples, wrote the main manuscript and prepared all figures.
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We declare that all other manipulations with animals were performed in accordance with relevant guidelines, regulations and ethics. This study was carried out in compliance with the ARRIVE guidelines and with the permission of the Nature Conservation Agency of the Czech Republic.
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Harabiš, F. Post-mining areas as the last area for the expansion of the declining Siberian Winter damselfly (Odonata: Lestidae). J Insect Conserv 27, 707–715 (2023). https://doi.org/10.1007/s10841-023-00491-x
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DOI: https://doi.org/10.1007/s10841-023-00491-x