Soil seed bank can complement restoration efforts in a coastal freshwater creek
Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank a...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Ling, Joanne E. [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: |
© Crown 2023 |
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| Übergeordnetes Werk: |
Enthalten in: Wetlands ecology and management - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1989, 31(2023), 6 vom: 27. Sept., Seite 825-852 |
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| Übergeordnetes Werk: |
volume:31 ; year:2023 ; number:6 ; day:27 ; month:09 ; pages:825-852 |
| Links: |
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| DOI / URN: |
10.1007/s11273-023-09954-z |
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| Katalog-ID: |
SPR053509803 |
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| 520 | |a Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. | ||
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| 650 | 4 | |a Grazing |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a New South Wales |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Australia |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Livestock exclusion |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Powell, Megan |4 aut | |
| 700 | 1 | |a Wen, Li |4 aut | |
| 700 | 1 | |a Pinto, Uthpala |4 aut | |
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10.1007/s11273-023-09954-z doi (DE-627)SPR053509803 (SPR)s11273-023-09954-z-e DE-627 ger DE-627 rakwb eng Ling, Joanne E. verfasserin (orcid)0000-0001-6801-3789 aut Soil seed bank can complement restoration efforts in a coastal freshwater creek 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Crown 2023 Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. Riparian vegetation (dpeaa)DE-He213 Grazing (dpeaa)DE-He213 New South Wales (dpeaa)DE-He213 Australia (dpeaa)DE-He213 Livestock exclusion (dpeaa)DE-He213 Powell, Megan aut Wen, Li aut Pinto, Uthpala aut Enthalten in Wetlands ecology and management Dordrecht [u.a.] : Springer Science + Business Media B.V, 1989 31(2023), 6 vom: 27. Sept., Seite 825-852 (DE-627)320569985 (DE-600)2016379-4 1572-9834 nnns volume:31 year:2023 number:6 day:27 month:09 pages:825-852 https://dx.doi.org/10.1007/s11273-023-09954-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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 AR 31 2023 6 27 09 825-852 |
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10.1007/s11273-023-09954-z doi (DE-627)SPR053509803 (SPR)s11273-023-09954-z-e DE-627 ger DE-627 rakwb eng Ling, Joanne E. verfasserin (orcid)0000-0001-6801-3789 aut Soil seed bank can complement restoration efforts in a coastal freshwater creek 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Crown 2023 Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. Riparian vegetation (dpeaa)DE-He213 Grazing (dpeaa)DE-He213 New South Wales (dpeaa)DE-He213 Australia (dpeaa)DE-He213 Livestock exclusion (dpeaa)DE-He213 Powell, Megan aut Wen, Li aut Pinto, Uthpala aut Enthalten in Wetlands ecology and management Dordrecht [u.a.] : Springer Science + Business Media B.V, 1989 31(2023), 6 vom: 27. Sept., Seite 825-852 (DE-627)320569985 (DE-600)2016379-4 1572-9834 nnns volume:31 year:2023 number:6 day:27 month:09 pages:825-852 https://dx.doi.org/10.1007/s11273-023-09954-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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 AR 31 2023 6 27 09 825-852 |
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10.1007/s11273-023-09954-z doi (DE-627)SPR053509803 (SPR)s11273-023-09954-z-e DE-627 ger DE-627 rakwb eng Ling, Joanne E. verfasserin (orcid)0000-0001-6801-3789 aut Soil seed bank can complement restoration efforts in a coastal freshwater creek 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Crown 2023 Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. Riparian vegetation (dpeaa)DE-He213 Grazing (dpeaa)DE-He213 New South Wales (dpeaa)DE-He213 Australia (dpeaa)DE-He213 Livestock exclusion (dpeaa)DE-He213 Powell, Megan aut Wen, Li aut Pinto, Uthpala aut Enthalten in Wetlands ecology and management Dordrecht [u.a.] : Springer Science + Business Media B.V, 1989 31(2023), 6 vom: 27. Sept., Seite 825-852 (DE-627)320569985 (DE-600)2016379-4 1572-9834 nnns volume:31 year:2023 number:6 day:27 month:09 pages:825-852 https://dx.doi.org/10.1007/s11273-023-09954-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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 AR 31 2023 6 27 09 825-852 |
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10.1007/s11273-023-09954-z doi (DE-627)SPR053509803 (SPR)s11273-023-09954-z-e DE-627 ger DE-627 rakwb eng Ling, Joanne E. verfasserin (orcid)0000-0001-6801-3789 aut Soil seed bank can complement restoration efforts in a coastal freshwater creek 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Crown 2023 Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. Riparian vegetation (dpeaa)DE-He213 Grazing (dpeaa)DE-He213 New South Wales (dpeaa)DE-He213 Australia (dpeaa)DE-He213 Livestock exclusion (dpeaa)DE-He213 Powell, Megan aut Wen, Li aut Pinto, Uthpala aut Enthalten in Wetlands ecology and management Dordrecht [u.a.] : Springer Science + Business Media B.V, 1989 31(2023), 6 vom: 27. Sept., Seite 825-852 (DE-627)320569985 (DE-600)2016379-4 1572-9834 nnns volume:31 year:2023 number:6 day:27 month:09 pages:825-852 https://dx.doi.org/10.1007/s11273-023-09954-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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 AR 31 2023 6 27 09 825-852 |
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10.1007/s11273-023-09954-z doi (DE-627)SPR053509803 (SPR)s11273-023-09954-z-e DE-627 ger DE-627 rakwb eng Ling, Joanne E. verfasserin (orcid)0000-0001-6801-3789 aut Soil seed bank can complement restoration efforts in a coastal freshwater creek 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Crown 2023 Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. Riparian vegetation (dpeaa)DE-He213 Grazing (dpeaa)DE-He213 New South Wales (dpeaa)DE-He213 Australia (dpeaa)DE-He213 Livestock exclusion (dpeaa)DE-He213 Powell, Megan aut Wen, Li aut Pinto, Uthpala aut Enthalten in Wetlands ecology and management Dordrecht [u.a.] : Springer Science + Business Media B.V, 1989 31(2023), 6 vom: 27. Sept., Seite 825-852 (DE-627)320569985 (DE-600)2016379-4 1572-9834 nnns volume:31 year:2023 number:6 day:27 month:09 pages:825-852 https://dx.doi.org/10.1007/s11273-023-09954-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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 AR 31 2023 6 27 09 825-852 |
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Enthalten in Wetlands ecology and management 31(2023), 6 vom: 27. Sept., Seite 825-852 volume:31 year:2023 number:6 day:27 month:09 pages:825-852 |
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Riparian vegetation Grazing New South Wales Australia Livestock exclusion |
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Ling, Joanne E. @@aut@@ Powell, Megan @@aut@@ Wen, Li @@aut@@ Pinto, Uthpala @@aut@@ |
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Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. 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| author |
Ling, Joanne E. |
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Ling, Joanne E. misc Riparian vegetation misc Grazing misc New South Wales misc Australia misc Livestock exclusion Soil seed bank can complement restoration efforts in a coastal freshwater creek |
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Ling, Joanne E. |
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Soil seed bank can complement restoration efforts in a coastal freshwater creek Riparian vegetation (dpeaa)DE-He213 Grazing (dpeaa)DE-He213 New South Wales (dpeaa)DE-He213 Australia (dpeaa)DE-He213 Livestock exclusion (dpeaa)DE-He213 |
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misc Riparian vegetation misc Grazing misc New South Wales misc Australia misc Livestock exclusion |
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misc Riparian vegetation misc Grazing misc New South Wales misc Australia misc Livestock exclusion |
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Soil seed bank can complement restoration efforts in a coastal freshwater creek |
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Soil seed bank can complement restoration efforts in a coastal freshwater creek |
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Ling, Joanne E. |
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Wetlands ecology and management |
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Ling, Joanne E. Powell, Megan Wen, Li Pinto, Uthpala |
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Ling, Joanne E. |
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soil seed bank can complement restoration efforts in a coastal freshwater creek |
| title_auth |
Soil seed bank can complement restoration efforts in a coastal freshwater creek |
| abstract |
Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. © Crown 2023 |
| abstractGer |
Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. © Crown 2023 |
| abstract_unstemmed |
Abstract Riparian vegetation is a keystone ecosystem element heavily impacted by livestock grazing. Historically, regeneration approaches of the riparian vegetation use either active (planting) or passive (natural regeneration) strategies. Frameworks based on an understanding of the soil seed bank are needed to help guide the approach adopted. This study compared the soil seed bank composition to the extant riparian vegetation to assess the potential for natural regeneration to supplement active plantings, following livestock exclusion on the south-coast of Australia. At each of four sites, we surveyed the extant vegetation, and collected five soil samples from each of three zones (instream, slope, bank). Our results show that the proportions of species nativeness, growth forms, and life cycle was similar for both communities. However, while there were more terrestrial species recorded in the standing vegetation, there were more wetland specialists in the soil seed bank. A persistent native seed bank, combined with other basic management strategies, could potentially compete and limit the abundance of non-native or invasive grasses. The high abundance of native grass-types (Cyperaceae, Juncaceae, Juncaginaceae, Asparagaceae, Poaceae, Typhaceae), can be relied upon to regenerate the understorey to complement active planting of the trees and shrubs. As such, resources could be prioritised to sites where native species abundance in the seed bank is low. This study recommends that land managers should investigate the composition of the soil seed bank prior to allocating resources for active planting activities to ensure the most efficient use of resources across the landscape. © Crown 2023 |
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| container_issue |
6 |
| title_short |
Soil seed bank can complement restoration efforts in a coastal freshwater creek |
| url |
https://dx.doi.org/10.1007/s11273-023-09954-z |
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Powell, Megan Wen, Li Pinto, Uthpala |
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| doi_str |
10.1007/s11273-023-09954-z |
| up_date |
2024-07-03T20:02:52.252Z |
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1803589488218210304 |
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| score |
7.4020357 |