Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed
Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby...
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Gespeichert in:
| Autor*in: |
Bórquez, Jéssica [verfasserIn] Sampertegui, Sandra [verfasserIn] Wallberg, Britt N. [verfasserIn] Coral-Santacruz, Diana [verfasserIn] Ruiz, Víctor H. [verfasserIn] Samollow, Paul B. [verfasserIn] Gouin, Nicolas [verfasserIn] Bertin, Angéline [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2023 |
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| Schlagwörter: |
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| Anmerkung: |
© The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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| Übergeordnetes Werk: |
Enthalten in: Aquatic ecology - Springer Netherlands, 1968, 58(2023), 2 vom: 19. Aug., Seite 139-158 |
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| Übergeordnetes Werk: |
volume:58 ; year:2023 ; number:2 ; day:19 ; month:08 ; pages:139-158 |
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| DOI / URN: |
10.1007/s10452-023-10051-9 |
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SPR055859259 |
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| 520 | |a Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. | ||
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10.1007/s10452-023-10051-9 doi (DE-627)SPR055859259 (SPR)s10452-023-10051-9-e DE-627 ger DE-627 rakwb eng 570 VZ 42.92 bkl Bórquez, Jéssica verfasserin (orcid)0000-0002-2376-771X aut Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. Biodiversity indicators (dpeaa)DE-He213 Community composition (dpeaa)DE-He213 Ecological uniqueness (dpeaa)DE-He213 Genetic diversity (dpeaa)DE-He213 Morphological diversity (dpeaa)DE-He213 Sampertegui, Sandra verfasserin aut Wallberg, Britt N. verfasserin (orcid)0000-0003-4633-6637 aut Coral-Santacruz, Diana verfasserin (orcid)0000-0002-4153-2033 aut Ruiz, Víctor H. verfasserin aut Samollow, Paul B. verfasserin (orcid)0000-0002-5755-9230 aut Gouin, Nicolas verfasserin (orcid)0000-0002-7111-2582 aut Bertin, Angéline verfasserin (orcid)0000-0003-0527-9584 aut Enthalten in Aquatic ecology Springer Netherlands, 1968 58(2023), 2 vom: 19. Aug., Seite 139-158 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:58 year:2023 number:2 day:19 month:08 pages:139-158 https://dx.doi.org/10.1007/s10452-023-10051-9 X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 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_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.92 VZ AR 58 2023 2 19 08 139-158 |
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10.1007/s10452-023-10051-9 doi (DE-627)SPR055859259 (SPR)s10452-023-10051-9-e DE-627 ger DE-627 rakwb eng 570 VZ 42.92 bkl Bórquez, Jéssica verfasserin (orcid)0000-0002-2376-771X aut Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. Biodiversity indicators (dpeaa)DE-He213 Community composition (dpeaa)DE-He213 Ecological uniqueness (dpeaa)DE-He213 Genetic diversity (dpeaa)DE-He213 Morphological diversity (dpeaa)DE-He213 Sampertegui, Sandra verfasserin aut Wallberg, Britt N. verfasserin (orcid)0000-0003-4633-6637 aut Coral-Santacruz, Diana verfasserin (orcid)0000-0002-4153-2033 aut Ruiz, Víctor H. verfasserin aut Samollow, Paul B. verfasserin (orcid)0000-0002-5755-9230 aut Gouin, Nicolas verfasserin (orcid)0000-0002-7111-2582 aut Bertin, Angéline verfasserin (orcid)0000-0003-0527-9584 aut Enthalten in Aquatic ecology Springer Netherlands, 1968 58(2023), 2 vom: 19. Aug., Seite 139-158 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:58 year:2023 number:2 day:19 month:08 pages:139-158 https://dx.doi.org/10.1007/s10452-023-10051-9 X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 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_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.92 VZ AR 58 2023 2 19 08 139-158 |
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10.1007/s10452-023-10051-9 doi (DE-627)SPR055859259 (SPR)s10452-023-10051-9-e DE-627 ger DE-627 rakwb eng 570 VZ 42.92 bkl Bórquez, Jéssica verfasserin (orcid)0000-0002-2376-771X aut Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. Biodiversity indicators (dpeaa)DE-He213 Community composition (dpeaa)DE-He213 Ecological uniqueness (dpeaa)DE-He213 Genetic diversity (dpeaa)DE-He213 Morphological diversity (dpeaa)DE-He213 Sampertegui, Sandra verfasserin aut Wallberg, Britt N. verfasserin (orcid)0000-0003-4633-6637 aut Coral-Santacruz, Diana verfasserin (orcid)0000-0002-4153-2033 aut Ruiz, Víctor H. verfasserin aut Samollow, Paul B. verfasserin (orcid)0000-0002-5755-9230 aut Gouin, Nicolas verfasserin (orcid)0000-0002-7111-2582 aut Bertin, Angéline verfasserin (orcid)0000-0003-0527-9584 aut Enthalten in Aquatic ecology Springer Netherlands, 1968 58(2023), 2 vom: 19. Aug., Seite 139-158 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:58 year:2023 number:2 day:19 month:08 pages:139-158 https://dx.doi.org/10.1007/s10452-023-10051-9 X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 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_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.92 VZ AR 58 2023 2 19 08 139-158 |
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10.1007/s10452-023-10051-9 doi (DE-627)SPR055859259 (SPR)s10452-023-10051-9-e DE-627 ger DE-627 rakwb eng 570 VZ 42.92 bkl Bórquez, Jéssica verfasserin (orcid)0000-0002-2376-771X aut Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. Biodiversity indicators (dpeaa)DE-He213 Community composition (dpeaa)DE-He213 Ecological uniqueness (dpeaa)DE-He213 Genetic diversity (dpeaa)DE-He213 Morphological diversity (dpeaa)DE-He213 Sampertegui, Sandra verfasserin aut Wallberg, Britt N. verfasserin (orcid)0000-0003-4633-6637 aut Coral-Santacruz, Diana verfasserin (orcid)0000-0002-4153-2033 aut Ruiz, Víctor H. verfasserin aut Samollow, Paul B. verfasserin (orcid)0000-0002-5755-9230 aut Gouin, Nicolas verfasserin (orcid)0000-0002-7111-2582 aut Bertin, Angéline verfasserin (orcid)0000-0003-0527-9584 aut Enthalten in Aquatic ecology Springer Netherlands, 1968 58(2023), 2 vom: 19. Aug., Seite 139-158 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:58 year:2023 number:2 day:19 month:08 pages:139-158 https://dx.doi.org/10.1007/s10452-023-10051-9 X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 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_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.92 VZ AR 58 2023 2 19 08 139-158 |
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10.1007/s10452-023-10051-9 doi (DE-627)SPR055859259 (SPR)s10452-023-10051-9-e DE-627 ger DE-627 rakwb eng 570 VZ 42.92 bkl Bórquez, Jéssica verfasserin (orcid)0000-0002-2376-771X aut Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. Biodiversity indicators (dpeaa)DE-He213 Community composition (dpeaa)DE-He213 Ecological uniqueness (dpeaa)DE-He213 Genetic diversity (dpeaa)DE-He213 Morphological diversity (dpeaa)DE-He213 Sampertegui, Sandra verfasserin aut Wallberg, Britt N. verfasserin (orcid)0000-0003-4633-6637 aut Coral-Santacruz, Diana verfasserin (orcid)0000-0002-4153-2033 aut Ruiz, Víctor H. verfasserin aut Samollow, Paul B. verfasserin (orcid)0000-0002-5755-9230 aut Gouin, Nicolas verfasserin (orcid)0000-0002-7111-2582 aut Bertin, Angéline verfasserin (orcid)0000-0003-0527-9584 aut Enthalten in Aquatic ecology Springer Netherlands, 1968 58(2023), 2 vom: 19. Aug., Seite 139-158 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:58 year:2023 number:2 day:19 month:08 pages:139-158 https://dx.doi.org/10.1007/s10452-023-10051-9 X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_647 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 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_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.92 VZ AR 58 2023 2 19 08 139-158 |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000naa a22002652 4500</leader><controlfield tag="001">SPR055859259</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20240516064704.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">240516s2023 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s10452-023-10051-9</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR055859259</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s10452-023-10051-9-e</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="082" ind1="0" ind2="4"><subfield code="a">570</subfield><subfield code="q">VZ</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">42.92</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Bórquez, Jéssica</subfield><subfield code="e">verfasserin</subfield><subfield code="0">(orcid)0000-0002-2376-771X</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2023</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="500" ind1=" " ind2=" "><subfield code="a">© The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. 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Bórquez, Jéssica |
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570 VZ 42.92 bkl Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed Biodiversity indicators (dpeaa)DE-He213 Community composition (dpeaa)DE-He213 Ecological uniqueness (dpeaa)DE-He213 Genetic diversity (dpeaa)DE-He213 Morphological diversity (dpeaa)DE-He213 |
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ecological uniqueness across multiple levels of biodiversity in a chilean watershed |
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Ecological uniqueness across multiple levels of biodiversity in a Chilean watershed |
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Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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Abstract To effectively address biodiversity loss, it is essential to prioritize conservation efforts by identifying areas of high conservation value. Ecological uniqueness is a valuable metric for this purpose that decomposes beta diversity into local contributions to beta diversity (LCBD), thereby measuring the contribution of each site within a region to overall biodiversity variation. LCBD has been used extensively to evaluate ecological uniqueness from community composition data, but biodiversity is a multifaceted concept, and community-based ecological uniqueness may not capture the full range of ecological uniqueness occurring at other levels of biological organization. We investigated ecological uniqueness estimates derived from community and species population levels in a watershed of south-central Chile and analyzed their responses to water and habitat quality variables. Ecological uniqueness was estimated at the community level from fish and macroinvertebrate assemblages and at the population level using genetic and morphological data gathered for two invertebrates, the gastropod Chilina dombeiana and the water bug Aquarius chilensis. Our results revealed low spatial congruence between the levels of ecological uniqueness calculated for these different biodiversity components, with mismatches occurring among sites with high LCBD values. Water and habitat quality were major drivers of beta diversity in this watershed, accounting for 43.8% to 74.3% of the spatial variation in LCBDs, and their effects differed among the ecological uniqueness estimates. Overall, our results underscore the idiosyncratic nature of ecological uniqueness metrics, emphasizing the importance of using multiple components of biodiversity to guide conservation actions. © The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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| score |
7.399823 |