Legacy effects of experimental environmental change on soil micro‐arthropod communities

Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable. Ausführliche Beschreibung

Gespeichert in:

Autor*in:	Ruben Erik Roos [verfasserIn] Tone Birkemoe [verfasserIn] Johan Asplund [verfasserIn] Peter Ľuptáčik [verfasserIn] Natália Raschmanová [verfasserIn] Juha M. Alatalo [verfasserIn] Siri Lie Olsen [verfasserIn] Kari Klanderud [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2020

Schlagwörter:	Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery

Übergeordnetes Werk:	In: Ecosphere - Wiley, 2016, 11(2020), 2, Seite n/a-n/a
Übergeordnetes Werk:	volume:11 ; year:2020 ; number:2 ; pages:n/a-n/a

Links:	Link aufrufen Link aufrufen Link aufrufen Journal toc

DOI / URN:	10.1002/ecs2.3030

Katalog-ID:	DOAJ06430955X

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520			\|a Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable.
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700	0		\|a Natália Raschmanová \|e verfasserin \|4 aut
700	0		\|a Juha M. Alatalo \|e verfasserin \|4 aut
700	0		\|a Siri Lie Olsen \|e verfasserin \|4 aut
700	0		\|a Kari Klanderud \|e verfasserin \|4 aut
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author_variant	r e r rer t b tb j a ja p ľ pľ n r nr j m a jma s l o slo k k kk
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allfields	10.1002/ecs2.3030 doi (DE-627)DOAJ06430955X (DE-599)DOAJ801793c3d1a949029e811942c52da7d8 DE-627 ger DE-627 rakwb eng QH540-549.5 Ruben Erik Roos verfasserin aut Legacy effects of experimental environmental change on soil micro‐arthropod communities 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable. Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery Ecology Tone Birkemoe verfasserin aut Johan Asplund verfasserin aut Peter Ľuptáčik verfasserin aut Natália Raschmanová verfasserin aut Juha M. Alatalo verfasserin aut Siri Lie Olsen verfasserin aut Kari Klanderud verfasserin aut In Ecosphere Wiley, 2016 11(2020), 2, Seite n/a-n/a (DE-627)635133679 (DE-600)2572257-8 21508925 nnns volume:11 year:2020 number:2 pages:n/a-n/a https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/article/801793c3d1a949029e811942c52da7d8 kostenfrei https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/toc/2150-8925 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4367 GBV_ILN_4700 AR 11 2020 2 n/a-n/a
spelling	10.1002/ecs2.3030 doi (DE-627)DOAJ06430955X (DE-599)DOAJ801793c3d1a949029e811942c52da7d8 DE-627 ger DE-627 rakwb eng QH540-549.5 Ruben Erik Roos verfasserin aut Legacy effects of experimental environmental change on soil micro‐arthropod communities 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable. Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery Ecology Tone Birkemoe verfasserin aut Johan Asplund verfasserin aut Peter Ľuptáčik verfasserin aut Natália Raschmanová verfasserin aut Juha M. Alatalo verfasserin aut Siri Lie Olsen verfasserin aut Kari Klanderud verfasserin aut In Ecosphere Wiley, 2016 11(2020), 2, Seite n/a-n/a (DE-627)635133679 (DE-600)2572257-8 21508925 nnns volume:11 year:2020 number:2 pages:n/a-n/a https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/article/801793c3d1a949029e811942c52da7d8 kostenfrei https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/toc/2150-8925 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4367 GBV_ILN_4700 AR 11 2020 2 n/a-n/a
allfields_unstemmed	10.1002/ecs2.3030 doi (DE-627)DOAJ06430955X (DE-599)DOAJ801793c3d1a949029e811942c52da7d8 DE-627 ger DE-627 rakwb eng QH540-549.5 Ruben Erik Roos verfasserin aut Legacy effects of experimental environmental change on soil micro‐arthropod communities 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable. Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery Ecology Tone Birkemoe verfasserin aut Johan Asplund verfasserin aut Peter Ľuptáčik verfasserin aut Natália Raschmanová verfasserin aut Juha M. Alatalo verfasserin aut Siri Lie Olsen verfasserin aut Kari Klanderud verfasserin aut In Ecosphere Wiley, 2016 11(2020), 2, Seite n/a-n/a (DE-627)635133679 (DE-600)2572257-8 21508925 nnns volume:11 year:2020 number:2 pages:n/a-n/a https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/article/801793c3d1a949029e811942c52da7d8 kostenfrei https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/toc/2150-8925 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4367 GBV_ILN_4700 AR 11 2020 2 n/a-n/a
allfieldsGer	10.1002/ecs2.3030 doi (DE-627)DOAJ06430955X (DE-599)DOAJ801793c3d1a949029e811942c52da7d8 DE-627 ger DE-627 rakwb eng QH540-549.5 Ruben Erik Roos verfasserin aut Legacy effects of experimental environmental change on soil micro‐arthropod communities 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable. Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery Ecology Tone Birkemoe verfasserin aut Johan Asplund verfasserin aut Peter Ľuptáčik verfasserin aut Natália Raschmanová verfasserin aut Juha M. Alatalo verfasserin aut Siri Lie Olsen verfasserin aut Kari Klanderud verfasserin aut In Ecosphere Wiley, 2016 11(2020), 2, Seite n/a-n/a (DE-627)635133679 (DE-600)2572257-8 21508925 nnns volume:11 year:2020 number:2 pages:n/a-n/a https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/article/801793c3d1a949029e811942c52da7d8 kostenfrei https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/toc/2150-8925 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4367 GBV_ILN_4700 AR 11 2020 2 n/a-n/a
allfieldsSound	10.1002/ecs2.3030 doi (DE-627)DOAJ06430955X (DE-599)DOAJ801793c3d1a949029e811942c52da7d8 DE-627 ger DE-627 rakwb eng QH540-549.5 Ruben Erik Roos verfasserin aut Legacy effects of experimental environmental change on soil micro‐arthropod communities 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable. Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery Ecology Tone Birkemoe verfasserin aut Johan Asplund verfasserin aut Peter Ľuptáčik verfasserin aut Natália Raschmanová verfasserin aut Juha M. Alatalo verfasserin aut Siri Lie Olsen verfasserin aut Kari Klanderud verfasserin aut In Ecosphere Wiley, 2016 11(2020), 2, Seite n/a-n/a (DE-627)635133679 (DE-600)2572257-8 21508925 nnns volume:11 year:2020 number:2 pages:n/a-n/a https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/article/801793c3d1a949029e811942c52da7d8 kostenfrei https://doi.org/10.1002/ecs2.3030 kostenfrei https://doaj.org/toc/2150-8925 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4367 GBV_ILN_4700 AR 11 2020 2 n/a-n/a
language	English
source	In Ecosphere 11(2020), 2, Seite n/a-n/a volume:11 year:2020 number:2 pages:n/a-n/a
sourceStr	In Ecosphere 11(2020), 2, Seite n/a-n/a volume:11 year:2020 number:2 pages:n/a-n/a
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery Ecology
isfreeaccess_bool	true
container_title	Ecosphere
authorswithroles_txt_mv	Ruben Erik Roos @@aut@@ Tone Birkemoe @@aut@@ Johan Asplund @@aut@@ Peter Ľuptáčik @@aut@@ Natália Raschmanová @@aut@@ Juha M. Alatalo @@aut@@ Siri Lie Olsen @@aut@@ Kari Klanderud @@aut@@
publishDateDaySort_date	2020-01-01T00:00:00Z
hierarchy_top_id	635133679
id	DOAJ06430955X
language_de	englisch
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However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. 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callnumber-first	Q - Science
author	Ruben Erik Roos
spellingShingle	Ruben Erik Roos misc QH540-549.5 misc Acari misc alpine ecology misc Collembola misc community recovery misc ecological resilience misc ecosystem recovery misc Ecology Legacy effects of experimental environmental change on soil micro‐arthropod communities
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topic_title	QH540-549.5 Legacy effects of experimental environmental change on soil micro‐arthropod communities Acari alpine ecology Collembola community recovery ecological resilience ecosystem recovery
topic	misc QH540-549.5 misc Acari misc alpine ecology misc Collembola misc community recovery misc ecological resilience misc ecosystem recovery misc Ecology
topic_unstemmed	misc QH540-549.5 misc Acari misc alpine ecology misc Collembola misc community recovery misc ecological resilience misc ecosystem recovery misc Ecology
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title	Legacy effects of experimental environmental change on soil micro‐arthropod communities
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title_full	Legacy effects of experimental environmental change on soil micro‐arthropod communities
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author_browse	Ruben Erik Roos Tone Birkemoe Johan Asplund Peter Ľuptáčik Natália Raschmanová Juha M. Alatalo Siri Lie Olsen Kari Klanderud
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title_sort	legacy effects of experimental environmental change on soil micro‐arthropod communities
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title_auth	Legacy effects of experimental environmental change on soil micro‐arthropod communities
abstract	Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable.
abstractGer	Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable.
abstract_unstemmed	Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. We therefore conclude that the environmental treatments had only temporary effects on micro‐arthropods in terms of overall abundance, but that effects on individual species and therefore species composition may be long‐lasting and less predictable.
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title_short	Legacy effects of experimental environmental change on soil micro‐arthropod communities
url	https://doi.org/10.1002/ecs2.3030 https://doaj.org/article/801793c3d1a949029e811942c52da7d8 https://doaj.org/toc/2150-8925
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up_date	2024-07-03T22:15:05.831Z
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fullrecord_marcxml	<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">DOAJ06430955X</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230309035311.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">230228s2020 xx \|\|\|\|\|o 00\| \|\|eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1002/ecs2.3030</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)DOAJ06430955X</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-599)DOAJ801793c3d1a949029e811942c52da7d8</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="050" ind1=" " ind2="0"><subfield code="a">QH540-549.5</subfield></datafield><datafield tag="100" ind1="0" ind2=" "><subfield code="a">Ruben Erik Roos</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Legacy effects of experimental environmental change on soil micro‐arthropod communities</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2020</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract Global change experiments such as experimental warming and nutrient addition strongly affect the structure and functioning of high latitude and altitude ecosystems. However, it is often unknown to what extend such effects are permanent or whether changes persist after environmental conditions return to pre‐treatment levels. In this study, we assess the legacy effects of temperature manipulation and nutrient addition experiments on alpine soil micro‐arthropod (i.e., Collembola and Oribatida) communities nine years after the treatments were discontinued. Treatment effects on the vegetation were still detectable six years after cessation, although grazing increased the recovery rate. Because micro‐arthropods are often closely associated with vegetation, we expected to find that treatment effects on Collembola and Oribatida abundance and species composition persisted to date, reflecting plant community dynamics. Also, we expected large‐bodied, drought‐resistant Collembola species that live on top of the soil to show less strong legacy effects. We did not find legacy effects of environmental treatments on Collembola and Mesostigmata in terms of abundance. However, we found persistent changes in community composition of Collembola and Oribatida, suggesting treatment effects persist to date. The generalist Folsomia quadrioculata was the most responsive Collembola species to initial treatments, most likely due to its variable life‐history strategy. Although its abundance recovered, F. quadrioculata remained dominant in Collembola communities after cessation of the treatments. Grazing affected community composition of both Collembola and Oribatida, but we did not find grazing to reduce legacy effects on micro‐arthropod as it did for vegetation. 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Legacy effects of experimental environmental change on soil micro‐arthropod communities

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