Non-indigenous fish in the northern branch of the central European invasion corridor
Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has forme...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Rakauskas, Vytautas [verfasserIn] Stakėnas, Saulius [verfasserIn] Virbickas, Tomas [verfasserIn] Bukelskis, Egidijus [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2016 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Reviews in fish biology and fisheries - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991, 26(2016), 3 vom: 03. Juni, Seite 491-508 |
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| Übergeordnetes Werk: |
volume:26 ; year:2016 ; number:3 ; day:03 ; month:06 ; pages:491-508 |
| Links: |
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| DOI / URN: |
10.1007/s11160-016-9438-x |
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| Katalog-ID: |
SPR017197279 |
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| 520 | |a Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. | ||
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| 650 | 4 | |a Central European invasion corridor |7 (dpeaa)DE-He213 | |
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10.1007/s11160-016-9438-x doi (DE-627)SPR017197279 (SPR)s11160-016-9438-x-e DE-627 ger DE-627 rakwb eng 630 640 590 ASE 42.00 bkl Rakauskas, Vytautas verfasserin aut Non-indigenous fish in the northern branch of the central European invasion corridor 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. Aquatic invasion (dpeaa)DE-He213 Alien species (dpeaa)DE-He213 Fish introductions (dpeaa)DE-He213 Central European invasion corridor (dpeaa)DE-He213 Stakėnas, Saulius verfasserin aut Virbickas, Tomas verfasserin aut Bukelskis, Egidijus verfasserin aut Enthalten in Reviews in fish biology and fisheries Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991 26(2016), 3 vom: 03. Juni, Seite 491-508 (DE-627)306591383 (DE-600)1498719-3 1573-5184 nnns volume:26 year:2016 number:3 day:03 month:06 pages:491-508 https://dx.doi.org/10.1007/s11160-016-9438-x lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 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_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_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 42.00 ASE AR 26 2016 3 03 06 491-508 |
| spelling |
10.1007/s11160-016-9438-x doi (DE-627)SPR017197279 (SPR)s11160-016-9438-x-e DE-627 ger DE-627 rakwb eng 630 640 590 ASE 42.00 bkl Rakauskas, Vytautas verfasserin aut Non-indigenous fish in the northern branch of the central European invasion corridor 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. Aquatic invasion (dpeaa)DE-He213 Alien species (dpeaa)DE-He213 Fish introductions (dpeaa)DE-He213 Central European invasion corridor (dpeaa)DE-He213 Stakėnas, Saulius verfasserin aut Virbickas, Tomas verfasserin aut Bukelskis, Egidijus verfasserin aut Enthalten in Reviews in fish biology and fisheries Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991 26(2016), 3 vom: 03. Juni, Seite 491-508 (DE-627)306591383 (DE-600)1498719-3 1573-5184 nnns volume:26 year:2016 number:3 day:03 month:06 pages:491-508 https://dx.doi.org/10.1007/s11160-016-9438-x lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 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_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_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 42.00 ASE AR 26 2016 3 03 06 491-508 |
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10.1007/s11160-016-9438-x doi (DE-627)SPR017197279 (SPR)s11160-016-9438-x-e DE-627 ger DE-627 rakwb eng 630 640 590 ASE 42.00 bkl Rakauskas, Vytautas verfasserin aut Non-indigenous fish in the northern branch of the central European invasion corridor 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. Aquatic invasion (dpeaa)DE-He213 Alien species (dpeaa)DE-He213 Fish introductions (dpeaa)DE-He213 Central European invasion corridor (dpeaa)DE-He213 Stakėnas, Saulius verfasserin aut Virbickas, Tomas verfasserin aut Bukelskis, Egidijus verfasserin aut Enthalten in Reviews in fish biology and fisheries Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991 26(2016), 3 vom: 03. Juni, Seite 491-508 (DE-627)306591383 (DE-600)1498719-3 1573-5184 nnns volume:26 year:2016 number:3 day:03 month:06 pages:491-508 https://dx.doi.org/10.1007/s11160-016-9438-x lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 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_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_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 42.00 ASE AR 26 2016 3 03 06 491-508 |
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10.1007/s11160-016-9438-x doi (DE-627)SPR017197279 (SPR)s11160-016-9438-x-e DE-627 ger DE-627 rakwb eng 630 640 590 ASE 42.00 bkl Rakauskas, Vytautas verfasserin aut Non-indigenous fish in the northern branch of the central European invasion corridor 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. Aquatic invasion (dpeaa)DE-He213 Alien species (dpeaa)DE-He213 Fish introductions (dpeaa)DE-He213 Central European invasion corridor (dpeaa)DE-He213 Stakėnas, Saulius verfasserin aut Virbickas, Tomas verfasserin aut Bukelskis, Egidijus verfasserin aut Enthalten in Reviews in fish biology and fisheries Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991 26(2016), 3 vom: 03. Juni, Seite 491-508 (DE-627)306591383 (DE-600)1498719-3 1573-5184 nnns volume:26 year:2016 number:3 day:03 month:06 pages:491-508 https://dx.doi.org/10.1007/s11160-016-9438-x lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 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_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_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 42.00 ASE AR 26 2016 3 03 06 491-508 |
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10.1007/s11160-016-9438-x doi (DE-627)SPR017197279 (SPR)s11160-016-9438-x-e DE-627 ger DE-627 rakwb eng 630 640 590 ASE 42.00 bkl Rakauskas, Vytautas verfasserin aut Non-indigenous fish in the northern branch of the central European invasion corridor 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. Aquatic invasion (dpeaa)DE-He213 Alien species (dpeaa)DE-He213 Fish introductions (dpeaa)DE-He213 Central European invasion corridor (dpeaa)DE-He213 Stakėnas, Saulius verfasserin aut Virbickas, Tomas verfasserin aut Bukelskis, Egidijus verfasserin aut Enthalten in Reviews in fish biology and fisheries Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991 26(2016), 3 vom: 03. Juni, Seite 491-508 (DE-627)306591383 (DE-600)1498719-3 1573-5184 nnns volume:26 year:2016 number:3 day:03 month:06 pages:491-508 https://dx.doi.org/10.1007/s11160-016-9438-x lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 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_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_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 42.00 ASE AR 26 2016 3 03 06 491-508 |
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Enthalten in Reviews in fish biology and fisheries 26(2016), 3 vom: 03. Juni, Seite 491-508 volume:26 year:2016 number:3 day:03 month:06 pages:491-508 |
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Rakauskas, Vytautas @@aut@@ Stakėnas, Saulius @@aut@@ Virbickas, Tomas @@aut@@ Bukelskis, Egidijus @@aut@@ |
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The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Aquatic invasion</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Alien species</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Fish introductions</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Central European invasion corridor</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Stakėnas, Saulius</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Virbickas, Tomas</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Bukelskis, Egidijus</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Reviews in fish biology and fisheries</subfield><subfield code="d">Dordrecht [u.a.] : Springer Science + Business Media B.V, 1991</subfield><subfield code="g">26(2016), 3 vom: 03. 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Rakauskas, Vytautas |
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630 640 590 ASE 42.00 bkl Non-indigenous fish in the northern branch of the central European invasion corridor Aquatic invasion (dpeaa)DE-He213 Alien species (dpeaa)DE-He213 Fish introductions (dpeaa)DE-He213 Central European invasion corridor (dpeaa)DE-He213 |
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Non-indigenous fish in the northern branch of the central European invasion corridor |
| abstract |
Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. |
| abstractGer |
Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. |
| abstract_unstemmed |
Abstract The assessment of risks associated with non-indigenous species implies a detailed knowledge of their taxonomical composition and distribution within a certain region. The northern branch of the central European ‘invasion corridor’—a series of canals connecting different watersheds—has formed an important migratory route for Ponto-Caspian fish (i.e. fish from the Black Sea, the Sea of Azov and the Caspian Sea). However, the current status of non-indigenous fish species in this region is very scarce. This article presents a comprehensive overview of recent distribution data of non-indigenous fish species in the northern branch of the central European invasion corridor. Here, extensive data are integrated based on studies performed during 2003–2014 comprising reliable published and unpublished records from the last 12 years. Altogether, ten non-indigenous fish species were currently found in the northern branch of the central European invasion corridor, constituting 19 % of its freshwater fish diversity. Three species, including the Prussian carp (Carassius gibelio), the round goby (Neogobius melanostomus), and the Chinese sleeper (Perccottus glenii), are considered invasive species. Eight species may potentially invade this region in the near future. A comparison of the history of non-indigenous fish species introduction in the inland waters of the northern branch and other countries of the central European invasion corridor revealed similar introduction trends. Potential expansion of non-indigenous fish species across the central European invasion corridor has international implications that require awareness, cooperation, and government support from each individual country. Disclosure of recently operating vectors for non-indigenous fish introductions within the central European invasion corridor will help predict and prevent their further spread and establishment in this region. |
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3 |
| title_short |
Non-indigenous fish in the northern branch of the central European invasion corridor |
| url |
https://dx.doi.org/10.1007/s11160-016-9438-x |
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| author2 |
Stakėnas, Saulius Virbickas, Tomas Bukelskis, Egidijus |
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Stakėnas, Saulius Virbickas, Tomas Bukelskis, Egidijus |
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| doi_str |
10.1007/s11160-016-9438-x |
| up_date |
2024-07-04T02:33:01.782Z |
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| score |
7.4005013 |