Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen
Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Vaas, K. F. [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
1979 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Aquatic ecology - Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968, 13(1979), 2-3 vom: 01. Dez., Seite 177-188 |
|---|---|
| Übergeordnetes Werk: |
volume:13 ; year:1979 ; number:2-3 ; day:01 ; month:12 ; pages:177-188 |
| Links: |
|---|
| DOI / URN: |
10.1007/BF02284753 |
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| Katalog-ID: |
SPR010133615 |
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| 245 | 1 | 0 | |a Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen |
| 264 | 1 | |c 1979 | |
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| 520 | |a Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. | ||
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| 650 | 4 | |a Fishing Trip |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Open Connection |7 (dpeaa)DE-He213 | |
| 773 | 0 | 8 | |i Enthalten in |t Aquatic ecology |d Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968 |g 13(1979), 2-3 vom: 01. Dez., Seite 177-188 |w (DE-627)302724257 |w (DE-600)1492493-6 |x 1573-5125 |7 nnns |
| 773 | 1 | 8 | |g volume:13 |g year:1979 |g number:2-3 |g day:01 |g month:12 |g pages:177-188 |
| 856 | 4 | 0 | |u https://dx.doi.org/10.1007/BF02284753 |z lizenzpflichtig |3 Volltext |
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10.1007/BF02284753 doi (DE-627)SPR010133615 (SPR)BF02284753-e DE-627 ger DE-627 rakwb eng 570 ASE 42.92 bkl Vaas, K. F. verfasserin aut Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen 1979 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. Fish Fauna (dpeaa)DE-He213 Demersal Fish (dpeaa)DE-He213 Sand Goby (dpeaa)DE-He213 Fishing Trip (dpeaa)DE-He213 Open Connection (dpeaa)DE-He213 Enthalten in Aquatic ecology Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968 13(1979), 2-3 vom: 01. Dez., Seite 177-188 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 https://dx.doi.org/10.1007/BF02284753 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_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_121 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_224 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 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_2018 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_2043 GBV_ILN_2044 GBV_ILN_2048 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_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_2158 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2193 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_2808 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 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_4346 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 42.92 ASE AR 13 1979 2-3 01 12 177-188 |
| spelling |
10.1007/BF02284753 doi (DE-627)SPR010133615 (SPR)BF02284753-e DE-627 ger DE-627 rakwb eng 570 ASE 42.92 bkl Vaas, K. F. verfasserin aut Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen 1979 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. Fish Fauna (dpeaa)DE-He213 Demersal Fish (dpeaa)DE-He213 Sand Goby (dpeaa)DE-He213 Fishing Trip (dpeaa)DE-He213 Open Connection (dpeaa)DE-He213 Enthalten in Aquatic ecology Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968 13(1979), 2-3 vom: 01. Dez., Seite 177-188 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 https://dx.doi.org/10.1007/BF02284753 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_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_121 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_224 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 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_2018 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_2043 GBV_ILN_2044 GBV_ILN_2048 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_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_2158 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2193 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_2808 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 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_4346 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 42.92 ASE AR 13 1979 2-3 01 12 177-188 |
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10.1007/BF02284753 doi (DE-627)SPR010133615 (SPR)BF02284753-e DE-627 ger DE-627 rakwb eng 570 ASE 42.92 bkl Vaas, K. F. verfasserin aut Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen 1979 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. Fish Fauna (dpeaa)DE-He213 Demersal Fish (dpeaa)DE-He213 Sand Goby (dpeaa)DE-He213 Fishing Trip (dpeaa)DE-He213 Open Connection (dpeaa)DE-He213 Enthalten in Aquatic ecology Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968 13(1979), 2-3 vom: 01. Dez., Seite 177-188 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 https://dx.doi.org/10.1007/BF02284753 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_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_121 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_224 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 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_2018 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_2043 GBV_ILN_2044 GBV_ILN_2048 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_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_2158 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2193 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_2808 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 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_4346 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 42.92 ASE AR 13 1979 2-3 01 12 177-188 |
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10.1007/BF02284753 doi (DE-627)SPR010133615 (SPR)BF02284753-e DE-627 ger DE-627 rakwb eng 570 ASE 42.92 bkl Vaas, K. F. verfasserin aut Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen 1979 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. Fish Fauna (dpeaa)DE-He213 Demersal Fish (dpeaa)DE-He213 Sand Goby (dpeaa)DE-He213 Fishing Trip (dpeaa)DE-He213 Open Connection (dpeaa)DE-He213 Enthalten in Aquatic ecology Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968 13(1979), 2-3 vom: 01. Dez., Seite 177-188 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 https://dx.doi.org/10.1007/BF02284753 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_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_121 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_224 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 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_2018 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_2043 GBV_ILN_2044 GBV_ILN_2048 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_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_2158 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2193 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_2808 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 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_4346 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 42.92 ASE AR 13 1979 2-3 01 12 177-188 |
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10.1007/BF02284753 doi (DE-627)SPR010133615 (SPR)BF02284753-e DE-627 ger DE-627 rakwb eng 570 ASE 42.92 bkl Vaas, K. F. verfasserin aut Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen 1979 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. Fish Fauna (dpeaa)DE-He213 Demersal Fish (dpeaa)DE-He213 Sand Goby (dpeaa)DE-He213 Fishing Trip (dpeaa)DE-He213 Open Connection (dpeaa)DE-He213 Enthalten in Aquatic ecology Dordrecht [u.a.] : Springer Science + Business Media B.V., 1968 13(1979), 2-3 vom: 01. Dez., Seite 177-188 (DE-627)302724257 (DE-600)1492493-6 1573-5125 nnns volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 https://dx.doi.org/10.1007/BF02284753 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_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_121 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_224 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 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_2018 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_2043 GBV_ILN_2044 GBV_ILN_2048 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_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_2158 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2193 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_2808 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4277 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_4346 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 GBV_ILN_4753 42.92 ASE AR 13 1979 2-3 01 12 177-188 |
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Enthalten in Aquatic ecology 13(1979), 2-3 vom: 01. Dez., Seite 177-188 volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 |
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Enthalten in Aquatic ecology 13(1979), 2-3 vom: 01. Dez., Seite 177-188 volume:13 year:1979 number:2-3 day:01 month:12 pages:177-188 |
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F.</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">1979</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. 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Vaas, K. F. |
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Vaas, K. F. ddc 570 bkl 42.92 misc Fish Fauna misc Demersal Fish misc Sand Goby misc Fishing Trip misc Open Connection Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen |
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570 ASE 42.92 bkl Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen Fish Fauna (dpeaa)DE-He213 Demersal Fish (dpeaa)DE-He213 Sand Goby (dpeaa)DE-He213 Fishing Trip (dpeaa)DE-He213 Open Connection (dpeaa)DE-He213 |
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10.1007/BF02284753 |
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570 |
| title_sort |
studies on the fish fauna of an estuary in the s. w. netherlands, before and after its change into the stagnant, saline, lake grevelingen |
| title_auth |
Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen |
| abstract |
Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. |
| abstractGer |
Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. |
| abstract_unstemmed |
Summary The Grevelingen was fished with a beam-trawl during the years 1960–1963, when in open connection with the North Sea as well as with the river Rhine, during the years 1966–1969, when the connection with the river was blocked by a dyke, and from 1971–1976, when the connection with the sea was also blocked by a dyke and the stagnant, saline Lake Grevelingen was created. The (mainly) demersal fishes captured were classified into (1) frequent species spawning within the area; (2) frequent species spawning outside the area, and (3) incidental visitors from the coastal sea. After closure the incidental visitors either became much less frequent or dropped out entirely. Some of the langer spawners decreased in numbers. Their place was occupied by smaller fishes, such as sand smelts and the stickleback. As piscivorous fishes almost completely dropped out, the above small species were able to increase and so were the two gobies present before the closure. The black goby (Gobius niger) invaded the lake and built a large, propagating population, in a similar way as it had done in Lake Veere, a neighbouring saline lake, created in a similar way. The turbot and the brill increased in numbers and there are indications that both spawn in the lake. These two species are the only large piscivorous fishes left at the moment and the nearly empty niche, created by the absence of other, incidental visiting, marine piscivores, is now filled by numbers of markedly increased grebes and cormorants. The flatfishes, used to spawn at sea, were trapped inside the lake. They grew on, but, as no reproduction was possible and recruitment through the locks in the dyke on the land side was minimal, their population decreased, the more rapidly as many were captured by fishermen. It is concluded that in the stagnant, saline lake, species diversity decreased and food chains became shorter, as compared with the more mature situation in the open estuary. |
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| container_issue |
2-3 |
| title_short |
Studies on the fish fauna of an estuary in the S. W. Netherlands, before and after its change into the stagnant, saline, Lake Grevelingen |
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https://dx.doi.org/10.1007/BF02284753 |
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10.1007/BF02284753 |
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2024-07-03T14:08:40.628Z |
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| score |
7.4012613 |