Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway
Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus de...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Källgren, Emma K. [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2014 |
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| Schlagwörter: |
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| Anmerkung: |
© Springer-Verlag Berlin Heidelberg 2014 |
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| Übergeordnetes Werk: |
Enthalten in: Polar biology - Berlin : Springer, 1982, 38(2014), 4 vom: 14. Nov., Seite 583-589 |
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| Übergeordnetes Werk: |
volume:38 ; year:2014 ; number:4 ; day:14 ; month:11 ; pages:583-589 |
| Links: |
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| DOI / URN: |
10.1007/s00300-014-1611-x |
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| Katalog-ID: |
SPR003939448 |
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| 520 | |a Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. | ||
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10.1007/s00300-014-1611-x doi (DE-627)SPR003939448 (SPR)s00300-014-1611-x-e DE-627 ger DE-627 rakwb eng Källgren, Emma K. verfasserin aut Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. δ (dpeaa)DE-He213 C (dpeaa)DE-He213 δ (dpeaa)DE-He213 N (dpeaa)DE-He213 Arctic fjord (dpeaa)DE-He213 Nutrient flow (dpeaa)DE-He213 Poacher (dpeaa)DE-He213 Sculpin (dpeaa)DE-He213 Pedersen, Torstein aut Nilssen, Einar M. aut Enthalten in Polar biology Berlin : Springer, 1982 38(2014), 4 vom: 14. Nov., Seite 583-589 (DE-627)271175427 (DE-600)1478942-5 1432-2056 nnns volume:38 year:2014 number:4 day:14 month:11 pages:583-589 https://dx.doi.org/10.1007/s00300-014-1611-x 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_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_267 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_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_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 AR 38 2014 4 14 11 583-589 |
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10.1007/s00300-014-1611-x doi (DE-627)SPR003939448 (SPR)s00300-014-1611-x-e DE-627 ger DE-627 rakwb eng Källgren, Emma K. verfasserin aut Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. δ (dpeaa)DE-He213 C (dpeaa)DE-He213 δ (dpeaa)DE-He213 N (dpeaa)DE-He213 Arctic fjord (dpeaa)DE-He213 Nutrient flow (dpeaa)DE-He213 Poacher (dpeaa)DE-He213 Sculpin (dpeaa)DE-He213 Pedersen, Torstein aut Nilssen, Einar M. aut Enthalten in Polar biology Berlin : Springer, 1982 38(2014), 4 vom: 14. Nov., Seite 583-589 (DE-627)271175427 (DE-600)1478942-5 1432-2056 nnns volume:38 year:2014 number:4 day:14 month:11 pages:583-589 https://dx.doi.org/10.1007/s00300-014-1611-x 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_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_267 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_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_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 AR 38 2014 4 14 11 583-589 |
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10.1007/s00300-014-1611-x doi (DE-627)SPR003939448 (SPR)s00300-014-1611-x-e DE-627 ger DE-627 rakwb eng Källgren, Emma K. verfasserin aut Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. δ (dpeaa)DE-He213 C (dpeaa)DE-He213 δ (dpeaa)DE-He213 N (dpeaa)DE-He213 Arctic fjord (dpeaa)DE-He213 Nutrient flow (dpeaa)DE-He213 Poacher (dpeaa)DE-He213 Sculpin (dpeaa)DE-He213 Pedersen, Torstein aut Nilssen, Einar M. aut Enthalten in Polar biology Berlin : Springer, 1982 38(2014), 4 vom: 14. Nov., Seite 583-589 (DE-627)271175427 (DE-600)1478942-5 1432-2056 nnns volume:38 year:2014 number:4 day:14 month:11 pages:583-589 https://dx.doi.org/10.1007/s00300-014-1611-x 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_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_267 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_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_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 AR 38 2014 4 14 11 583-589 |
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10.1007/s00300-014-1611-x doi (DE-627)SPR003939448 (SPR)s00300-014-1611-x-e DE-627 ger DE-627 rakwb eng Källgren, Emma K. verfasserin aut Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. δ (dpeaa)DE-He213 C (dpeaa)DE-He213 δ (dpeaa)DE-He213 N (dpeaa)DE-He213 Arctic fjord (dpeaa)DE-He213 Nutrient flow (dpeaa)DE-He213 Poacher (dpeaa)DE-He213 Sculpin (dpeaa)DE-He213 Pedersen, Torstein aut Nilssen, Einar M. aut Enthalten in Polar biology Berlin : Springer, 1982 38(2014), 4 vom: 14. Nov., Seite 583-589 (DE-627)271175427 (DE-600)1478942-5 1432-2056 nnns volume:38 year:2014 number:4 day:14 month:11 pages:583-589 https://dx.doi.org/10.1007/s00300-014-1611-x 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_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_267 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_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_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 AR 38 2014 4 14 11 583-589 |
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10.1007/s00300-014-1611-x doi (DE-627)SPR003939448 (SPR)s00300-014-1611-x-e DE-627 ger DE-627 rakwb eng Källgren, Emma K. verfasserin aut Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. δ (dpeaa)DE-He213 C (dpeaa)DE-He213 δ (dpeaa)DE-He213 N (dpeaa)DE-He213 Arctic fjord (dpeaa)DE-He213 Nutrient flow (dpeaa)DE-He213 Poacher (dpeaa)DE-He213 Sculpin (dpeaa)DE-He213 Pedersen, Torstein aut Nilssen, Einar M. aut Enthalten in Polar biology Berlin : Springer, 1982 38(2014), 4 vom: 14. Nov., Seite 583-589 (DE-627)271175427 (DE-600)1478942-5 1432-2056 nnns volume:38 year:2014 number:4 day:14 month:11 pages:583-589 https://dx.doi.org/10.1007/s00300-014-1611-x 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_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_267 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_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_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 AR 38 2014 4 14 11 583-589 |
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Enthalten in Polar biology 38(2014), 4 vom: 14. Nov., Seite 583-589 volume:38 year:2014 number:4 day:14 month:11 pages:583-589 |
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Enthalten in Polar biology 38(2014), 4 vom: 14. Nov., Seite 583-589 volume:38 year:2014 number:4 day:14 month:11 pages:583-589 |
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Källgren, Emma K. @@aut@@ Pedersen, Torstein @@aut@@ Nilssen, Einar M. @@aut@@ |
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This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. 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Källgren, Emma K. |
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Källgren, Emma K. misc δ misc C misc N misc Arctic fjord misc Nutrient flow misc Poacher misc Sculpin Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway |
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Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway δ (dpeaa)DE-He213 C (dpeaa)DE-He213 N (dpeaa)DE-He213 Arctic fjord (dpeaa)DE-He213 Nutrient flow (dpeaa)DE-He213 Poacher (dpeaa)DE-He213 Sculpin (dpeaa)DE-He213 |
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food resource partitioning between three sympatric fish species in porsangerfjord, norway |
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Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway |
| abstract |
Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. © Springer-Verlag Berlin Heidelberg 2014 |
| abstractGer |
Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. © Springer-Verlag Berlin Heidelberg 2014 |
| abstract_unstemmed |
Abstract Understanding predator–prey relationships and resource overlap between sympatric species is fundamental for enhanced scientific knowledge and management. This study compared the trophic ecology of three small demersal fishes (Artediellus atlanticus, Myoxocephalus scorpius, and Leptagonus decagonus) using stomach data and stable isotope analyses. All fish were sampled during 2009–2011 from the inner basin of Porsangerfjord (70°N, 25°E) in northern Norway. The dominant prey found in A. atlanticus was polychaetes, while M. scorpius had fed on juvenile fishes and decapods, and L. decagonus had mainly consumed copepods. The trophic positions of the fishes overlapped extensively (A. atlanticus: trophic level (TL) 3.4–4.2; M. scorpius: TL 3.6–4.3; L. decagonus: TL 3.7–4.6). Although the nutritional origin ($ δ^{13} $C) of the prey varied among the fishes, A. atlanticus and M. scorpius were associated with benthic prey ($ δ^{13} $C −18.64 to −17.28 and $ δ^{13} $C −18.67 to −17.04, respectively), whereas L. decagonus was associated with pelagic prey ($ δ^{13} $C −19.95 to −18.74). The combined results of the stomach data and stable isotope analyses further suggested that M. scorpius had a dietary preference for benthic–pelagic prey. Thus, the fish diets were considered to be species specific, and the study indicated that the three species utilize different prey groups within the food web of the Porsangerfjord ecosystem. © Springer-Verlag Berlin Heidelberg 2014 |
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| title_short |
Food resource partitioning between three sympatric fish species in Porsangerfjord, Norway |
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https://dx.doi.org/10.1007/s00300-014-1611-x |
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Pedersen, Torstein Nilssen, Einar M. |
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| score |
7.398258 |