Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan
Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April an...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Kaneko, Seiya [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2018 |
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| Schlagwörter: |
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| Anmerkung: |
© Japanese Society of Fisheries Science 2018 |
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| Übergeordnetes Werk: |
Enthalten in: Fisheries science - Tokyo : Springer Japan, 1994, 85(2018), 1 vom: 12. Nov., Seite 113-125 |
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| Übergeordnetes Werk: |
volume:85 ; year:2018 ; number:1 ; day:12 ; month:11 ; pages:113-125 |
| Links: |
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| DOI / URN: |
10.1007/s12562-018-1269-3 |
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| Katalog-ID: |
SPR026767597 |
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| 520 | |a Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. | ||
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| 700 | 1 | |a Kanou, Kouki |4 aut | |
| 700 | 1 | |a Sano, Mitsuhiko |4 aut | |
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10.1007/s12562-018-1269-3 doi (DE-627)SPR026767597 (SPR)s12562-018-1269-3-e DE-627 ger DE-627 rakwb eng Kaneko, Seiya verfasserin aut Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan 2018 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Japanese Society of Fisheries Science 2018 Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. Creek (dpeaa)DE-He213 Fish distribution (dpeaa)DE-He213 Food availability (dpeaa)DE-He213 Physical environment (dpeaa)DE-He213 Prey abundance (dpeaa)DE-He213 Species composition (dpeaa)DE-He213 Trophic guild (dpeaa)DE-He213 Kanou, Kouki aut Sano, Mitsuhiko aut Enthalten in Fisheries science Tokyo : Springer Japan, 1994 85(2018), 1 vom: 12. Nov., Seite 113-125 (DE-627)32060215X (DE-600)2020302-0 1444-2906 nnns volume:85 year:2018 number:1 day:12 month:11 pages:113-125 https://dx.doi.org/10.1007/s12562-018-1269-3 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_206 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_2056 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 85 2018 1 12 11 113-125 |
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10.1007/s12562-018-1269-3 doi (DE-627)SPR026767597 (SPR)s12562-018-1269-3-e DE-627 ger DE-627 rakwb eng Kaneko, Seiya verfasserin aut Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan 2018 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Japanese Society of Fisheries Science 2018 Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. Creek (dpeaa)DE-He213 Fish distribution (dpeaa)DE-He213 Food availability (dpeaa)DE-He213 Physical environment (dpeaa)DE-He213 Prey abundance (dpeaa)DE-He213 Species composition (dpeaa)DE-He213 Trophic guild (dpeaa)DE-He213 Kanou, Kouki aut Sano, Mitsuhiko aut Enthalten in Fisheries science Tokyo : Springer Japan, 1994 85(2018), 1 vom: 12. Nov., Seite 113-125 (DE-627)32060215X (DE-600)2020302-0 1444-2906 nnns volume:85 year:2018 number:1 day:12 month:11 pages:113-125 https://dx.doi.org/10.1007/s12562-018-1269-3 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_206 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_2056 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 85 2018 1 12 11 113-125 |
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10.1007/s12562-018-1269-3 doi (DE-627)SPR026767597 (SPR)s12562-018-1269-3-e DE-627 ger DE-627 rakwb eng Kaneko, Seiya verfasserin aut Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan 2018 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Japanese Society of Fisheries Science 2018 Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. Creek (dpeaa)DE-He213 Fish distribution (dpeaa)DE-He213 Food availability (dpeaa)DE-He213 Physical environment (dpeaa)DE-He213 Prey abundance (dpeaa)DE-He213 Species composition (dpeaa)DE-He213 Trophic guild (dpeaa)DE-He213 Kanou, Kouki aut Sano, Mitsuhiko aut Enthalten in Fisheries science Tokyo : Springer Japan, 1994 85(2018), 1 vom: 12. Nov., Seite 113-125 (DE-627)32060215X (DE-600)2020302-0 1444-2906 nnns volume:85 year:2018 number:1 day:12 month:11 pages:113-125 https://dx.doi.org/10.1007/s12562-018-1269-3 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_206 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_2056 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 85 2018 1 12 11 113-125 |
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10.1007/s12562-018-1269-3 doi (DE-627)SPR026767597 (SPR)s12562-018-1269-3-e DE-627 ger DE-627 rakwb eng Kaneko, Seiya verfasserin aut Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan 2018 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Japanese Society of Fisheries Science 2018 Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. Creek (dpeaa)DE-He213 Fish distribution (dpeaa)DE-He213 Food availability (dpeaa)DE-He213 Physical environment (dpeaa)DE-He213 Prey abundance (dpeaa)DE-He213 Species composition (dpeaa)DE-He213 Trophic guild (dpeaa)DE-He213 Kanou, Kouki aut Sano, Mitsuhiko aut Enthalten in Fisheries science Tokyo : Springer Japan, 1994 85(2018), 1 vom: 12. Nov., Seite 113-125 (DE-627)32060215X (DE-600)2020302-0 1444-2906 nnns volume:85 year:2018 number:1 day:12 month:11 pages:113-125 https://dx.doi.org/10.1007/s12562-018-1269-3 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_206 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_2056 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 85 2018 1 12 11 113-125 |
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10.1007/s12562-018-1269-3 doi (DE-627)SPR026767597 (SPR)s12562-018-1269-3-e DE-627 ger DE-627 rakwb eng Kaneko, Seiya verfasserin aut Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan 2018 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Japanese Society of Fisheries Science 2018 Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. Creek (dpeaa)DE-He213 Fish distribution (dpeaa)DE-He213 Food availability (dpeaa)DE-He213 Physical environment (dpeaa)DE-He213 Prey abundance (dpeaa)DE-He213 Species composition (dpeaa)DE-He213 Trophic guild (dpeaa)DE-He213 Kanou, Kouki aut Sano, Mitsuhiko aut Enthalten in Fisheries science Tokyo : Springer Japan, 1994 85(2018), 1 vom: 12. Nov., Seite 113-125 (DE-627)32060215X (DE-600)2020302-0 1444-2906 nnns volume:85 year:2018 number:1 day:12 month:11 pages:113-125 https://dx.doi.org/10.1007/s12562-018-1269-3 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_206 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_2056 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 85 2018 1 12 11 113-125 |
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Kaneko, Seiya @@aut@@ Kanou, Kouki @@aut@@ Sano, Mitsuhiko @@aut@@ |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR026767597</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230331231101.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201007s2018 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s12562-018-1269-3</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR026767597</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s12562-018-1269-3-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">Kaneko, Seiya</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2018</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">© Japanese Society of Fisheries Science 2018</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Creek</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Fish distribution</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Food availability</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Physical environment</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Prey abundance</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Species composition</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Trophic guild</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Kanou, Kouki</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Sano, Mitsuhiko</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Fisheries science</subfield><subfield code="d">Tokyo : Springer Japan, 1994</subfield><subfield code="g">85(2018), 1 vom: 12. 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Kaneko, Seiya |
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Kaneko, Seiya misc Creek misc Fish distribution misc Food availability misc Physical environment misc Prey abundance misc Species composition misc Trophic guild Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan |
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Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan Creek (dpeaa)DE-He213 Fish distribution (dpeaa)DE-He213 Food availability (dpeaa)DE-He213 Physical environment (dpeaa)DE-He213 Prey abundance (dpeaa)DE-He213 Species composition (dpeaa)DE-He213 Trophic guild (dpeaa)DE-He213 |
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Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan |
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Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan |
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comparison of fish assemblage structures among microhabitats in a salt marsh in lake hinuma, eastern japan |
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Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan |
| abstract |
Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. © Japanese Society of Fisheries Science 2018 |
| abstractGer |
Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. © Japanese Society of Fisheries Science 2018 |
| abstract_unstemmed |
Abstract A total of 33 fish species, including commercially important and threatened species, were collected in three microhabitats (upper and lower areas of a small creek, and a marsh edge separate from the creek) of a salt marsh in Lake Hinuma, eastern Japan, in October 2014, and January, April and July 2015. Five species (Acanthogobius lactipes, Oryzias latipes, Mugil cephalus cephalus, Tribolodon brandtii and Salangichthys microdon) were dominant and accounted for 90.7% of the total number of individuals. The fish assemblage structures differed remarkably among the microhabitats, tending toward higher species and individual numbers on the marsh edge than in the upper creek. Species compositions also differed between the upper creek and the other microhabitats. Food availability (e.g., mysids, chironomid larvae and detritus) was considered to be a causative factor of the assemblage structure differences. In addition, microhabitat variations in water depth, dissolved oxygen level and bottom sediment, the upper creek being shallower with lower dissolved oxygen and higher sediment silt–clay proportion compared with the marsh edge, were also causative factors that indicated the importance of both biotic and abiotic environmental factors in the determination of fish distribution patterns across salt marsh microhabitats. © Japanese Society of Fisheries Science 2018 |
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Comparison of fish assemblage structures among microhabitats in a salt marsh in Lake Hinuma, eastern Japan |
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https://dx.doi.org/10.1007/s12562-018-1269-3 |
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Kanou, Kouki Sano, Mitsuhiko |
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10.1007/s12562-018-1269-3 |
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2024-07-03T22:40:22.425Z |
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| score |
7.4010057 |