Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades

Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic sna...
Ausführliche Beschreibung

Gespeichert in:

Autor*in:	O’Hare, Nancy K. [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2010

Schlagwörter:	Mid-hydroperiod wetlands Restoration

Anmerkung:	© Society of Wetland Scientists 2010

Übergeordnetes Werk:	Enthalten in: Wetlands - [S.l.] : Springer, 1981, 30(2010), 6 vom: 03. Nov., Seite 1045-1052
Übergeordnetes Werk:	volume:30 ; year:2010 ; number:6 ; day:03 ; month:11 ; pages:1045-1052

Links:	Volltext

DOI / URN:	10.1007/s13157-010-0110-2

Katalog-ID:	SPR030688981

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520			\|a Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years.
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912			\|a GBV_ILN_161
912			\|a GBV_ILN_165
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
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912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
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912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2008
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
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912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
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912			\|a GBV_ILN_2057
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912			\|a GBV_ILN_2061
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912			\|a GBV_ILN_2070
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912			\|a GBV_ILN_2093
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912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2108
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912			\|a GBV_ILN_2111
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912			\|a GBV_ILN_2113
912			\|a GBV_ILN_2116
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912			\|a GBV_ILN_2232
912			\|a GBV_ILN_2336
912			\|a GBV_ILN_2446
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matchkey_str	article:19436246:2010----::oaepldsfoiaplsalerdcinnetrdnntrles
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publishDate	2010
allfields	10.1007/s13157-010-0110-2 doi (DE-627)SPR030688981 (SPR)s13157-010-0110-2-e DE-627 ger DE-627 rakwb eng O’Hare, Nancy K. verfasserin aut Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Society of Wetland Scientists 2010 Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. Mid-hydroperiod wetlands (dpeaa)DE-He213 Restoration (dpeaa)DE-He213 Enthalten in Wetlands [S.l.] : Springer, 1981 30(2010), 6 vom: 03. Nov., Seite 1045-1052 (DE-627)478509081 (DE-600)2175922-4 1943-6246 nnns volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052 https://dx.doi.org/10.1007/s13157-010-0110-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A 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_65 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_165 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_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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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 30 2010 6 03 11 1045-1052
spelling	10.1007/s13157-010-0110-2 doi (DE-627)SPR030688981 (SPR)s13157-010-0110-2-e DE-627 ger DE-627 rakwb eng O’Hare, Nancy K. verfasserin aut Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Society of Wetland Scientists 2010 Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. Mid-hydroperiod wetlands (dpeaa)DE-He213 Restoration (dpeaa)DE-He213 Enthalten in Wetlands [S.l.] : Springer, 1981 30(2010), 6 vom: 03. Nov., Seite 1045-1052 (DE-627)478509081 (DE-600)2175922-4 1943-6246 nnns volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052 https://dx.doi.org/10.1007/s13157-010-0110-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A 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_65 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_165 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_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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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 30 2010 6 03 11 1045-1052
allfields_unstemmed	10.1007/s13157-010-0110-2 doi (DE-627)SPR030688981 (SPR)s13157-010-0110-2-e DE-627 ger DE-627 rakwb eng O’Hare, Nancy K. verfasserin aut Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Society of Wetland Scientists 2010 Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. Mid-hydroperiod wetlands (dpeaa)DE-He213 Restoration (dpeaa)DE-He213 Enthalten in Wetlands [S.l.] : Springer, 1981 30(2010), 6 vom: 03. Nov., Seite 1045-1052 (DE-627)478509081 (DE-600)2175922-4 1943-6246 nnns volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052 https://dx.doi.org/10.1007/s13157-010-0110-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A 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_65 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_165 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_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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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 30 2010 6 03 11 1045-1052
allfieldsGer	10.1007/s13157-010-0110-2 doi (DE-627)SPR030688981 (SPR)s13157-010-0110-2-e DE-627 ger DE-627 rakwb eng O’Hare, Nancy K. verfasserin aut Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Society of Wetland Scientists 2010 Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. Mid-hydroperiod wetlands (dpeaa)DE-He213 Restoration (dpeaa)DE-He213 Enthalten in Wetlands [S.l.] : Springer, 1981 30(2010), 6 vom: 03. Nov., Seite 1045-1052 (DE-627)478509081 (DE-600)2175922-4 1943-6246 nnns volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052 https://dx.doi.org/10.1007/s13157-010-0110-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A 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_65 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_165 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_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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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 30 2010 6 03 11 1045-1052
allfieldsSound	10.1007/s13157-010-0110-2 doi (DE-627)SPR030688981 (SPR)s13157-010-0110-2-e DE-627 ger DE-627 rakwb eng O’Hare, Nancy K. verfasserin aut Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Society of Wetland Scientists 2010 Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. Mid-hydroperiod wetlands (dpeaa)DE-He213 Restoration (dpeaa)DE-He213 Enthalten in Wetlands [S.l.] : Springer, 1981 30(2010), 6 vom: 03. Nov., Seite 1045-1052 (DE-627)478509081 (DE-600)2175922-4 1943-6246 nnns volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052 https://dx.doi.org/10.1007/s13157-010-0110-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A 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_65 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_165 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_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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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 30 2010 6 03 11 1045-1052
language	English
source	Enthalten in Wetlands 30(2010), 6 vom: 03. Nov., Seite 1045-1052 volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052
sourceStr	Enthalten in Wetlands 30(2010), 6 vom: 03. Nov., Seite 1045-1052 volume:30 year:2010 number:6 day:03 month:11 pages:1045-1052
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Mid-hydroperiod wetlands Restoration
isfreeaccess_bool	false
container_title	Wetlands
authorswithroles_txt_mv	O’Hare, Nancy K. @@aut@@
publishDateDaySort_date	2010-11-03T00:00:00Z
hierarchy_top_id	478509081
id	SPR030688981
language_de	englisch
fullrecord	<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR030688981</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230519071122.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201007s2010 xx \|\|\|\|\|o 00\| \|\|eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s13157-010-0110-2</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR030688981</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s13157-010-0110-2-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="100" ind1="1" ind2=" "><subfield code="a">O’Hare, Nancy K.</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2010</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">© Society of Wetland Scientists 2010</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. 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author	O’Hare, Nancy K.
spellingShingle	O’Hare, Nancy K. misc Mid-hydroperiod wetlands misc Restoration Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades
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topic_title	Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades Mid-hydroperiod wetlands (dpeaa)DE-He213 Restoration (dpeaa)DE-He213
topic	misc Mid-hydroperiod wetlands misc Restoration
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title	Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades
ctrlnum	(DE-627)SPR030688981 (SPR)s13157-010-0110-2-e
title_full	Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades
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doi_str_mv	10.1007/s13157-010-0110-2
title_sort	pomacea paludosa (florida apple snail) reproduction in restored and natural seasonal wetlands in the everglades
title_auth	Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades
abstract	Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. © Society of Wetland Scientists 2010
abstractGer	Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. © Society of Wetland Scientists 2010
abstract_unstemmed	Abstract Seasonal wetlands have high variability in the timing, depth, and duration of flooding. The timing of hydroperiod relative to reproduction may be especially critical since reproductive timing may be constrained by other factors. Pomacea paludosa (Florida apple snail) is a large, aquatic snail that tolerates a range of hydroperiods. This study compared P. paludosa reproduction in depressions in natural (N = 20) and restored (N = 60) seasonal wetlands (wet 6 to 8 months) in the southern Everglades for five years. The total number of egg clusters in a year ranged from 260 to 621. Restored sites always had fewer egg clusters per year (mean±standard error of 54.6 ± 4.8 to 64.2 ± 23.1) compared to a natural site (207.0 ± 38.4). Peak oviposition occurred after the onset of the wet season, typically in July, and then decreased approximately two months later even though similar surface water levels occurred. Compared to long hydroperiod wetlands, the average number of eggs per cluster was lower and reproductive timing shifted from the non-rainy/dry season to early wet season. A combination of hydrological characteristics appeared to influence the timing and amount of oviposition. Moreover, functionality of seasonal wetlands in the southern Everglades may change depending upon cumulative hydrological conditions over several years. © Society of Wetland Scientists 2010
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container_issue	6
title_short	Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades
url	https://dx.doi.org/10.1007/s13157-010-0110-2
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doi_str	10.1007/s13157-010-0110-2
up_date	2024-07-03T19:33:53.330Z
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Pomacea paludosa (Florida Apple Snail) Reproduction in Restored and Natural Seasonal Wetlands in the Everglades

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