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| 35 | "created": "2024-11-05", | 35 | "created": "2024-11-05", | ||
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| 39 | "name": "Marin-Guirao, L., Lloret, J. y Marin, A." | 39 | "name": "Marin-Guirao, L., Lloret, J. y Marin, A." | ||
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| 61 | "diversidad", | 61 | "diversidad", | ||
| 62 | "eutrofizacion", | 62 | "eutrofizacion", | ||
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| 72 | "Science of The Total Environment", | 72 | "Science of The Total Environment", | ||
| 73 | "vol 393", | 73 | "vol 393", | ||
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| 93 | "modified": "2026-06-23", | 93 | "modified": "2026-06-23", | ||
| 94 | "name": "ff502426-bacc-5c81-ad73-1e5254d2a55b", | 94 | "name": "ff502426-bacc-5c81-ad73-1e5254d2a55b", | ||
| 95 | "notes": "Two food webs from the Mar Menor coastal lagoon, differing | 95 | "notes": "Two food webs from the Mar Menor coastal lagoon, differing | ||
| 96 | in the distance from the desert-stream through which mining wastes | 96 | in the distance from the desert-stream through which mining wastes | ||
| 97 | were discharged, were examined by reference to essential (Zn and Cu) | 97 | were discharged, were examined by reference to essential (Zn and Cu) | ||
| 98 | and non-essential (Pb and Cd) metal concentrations and stable isotopes | 98 | and non-essential (Pb and Cd) metal concentrations and stable isotopes | ||
| 99 | content (C and N). The partial extraction technique applied, which | 99 | content (C and N). The partial extraction technique applied, which | ||
| 100 | reflects the availability of metals to organisms after sediment | 100 | reflects the availability of metals to organisms after sediment | ||
| 101 | ingestion, showed higher bioavailable metal concentrations in | 101 | ingestion, showed higher bioavailable metal concentrations in | ||
| 102 | sediments from the station influenced by the mining discharges, in | 102 | sediments from the station influenced by the mining discharges, in | ||
| 103 | agreement with the higher metal concentrations observed in organisms, | 103 | agreement with the higher metal concentrations observed in organisms, | ||
| 104 | which in many cases exceeded the regulatory limits established in | 104 | which in many cases exceeded the regulatory limits established in | ||
| 105 | Spanish legislation concerning seafood. Spatial differences in | 105 | Spanish legislation concerning seafood. Spatial differences in | ||
| 106 | essential metal concentrations in the fauna suggest that several | 106 | essential metal concentrations in the fauna suggest that several | ||
| 107 | organisms are exposed to metal levels above their regulation capacity. | 107 | organisms are exposed to metal levels above their regulation capacity. | ||
| 108 | Differences in isotopic composition were found between both food webs, | 108 | Differences in isotopic composition were found between both food webs, | ||
| 109 | the wadi-influenced station showing higher delta N-15 values and lower | 109 | the wadi-influenced station showing higher delta N-15 values and lower | ||
| 110 | delta C-13 levels, due to the discharge of urban waste waters and by | 110 | delta C-13 levels, due to the discharge of urban waste waters and by | ||
| 111 | the entrance of freshwater and allochthonous marsh plants. The | 111 | the entrance of freshwater and allochthonous marsh plants. The | ||
| 112 | linear-regressions between trophic levels (as indicated by delta N-15) | 112 | linear-regressions between trophic levels (as indicated by delta N-15) | ||
| 113 | and the metal content indicated that biomagnification does not occur. | 113 | and the metal content indicated that biomagnification does not occur. | ||
| 114 | In the case of invertebrates, since the \"handle strategy\" of the | 114 | In the case of invertebrates, since the \"handle strategy\" of the | ||
| 115 | species and the physiological requirements of the organisms, among | 115 | species and the physiological requirements of the organisms, among | ||
| 116 | other factors, determine the final concentration of a specific | 116 | other factors, determine the final concentration of a specific | ||
| 117 | element, no clear relationships between trophic level and the metal | 117 | element, no clear relationships between trophic level and the metal | ||
| 118 | content are to be expected. For their part, fish communities did not | 118 | content are to be expected. For their part, fish communities did not | ||
| 119 | show clear patterns in the case of any of the analyzed metals, | 119 | show clear patterns in the case of any of the analyzed metals, | ||
| 120 | probably because most fish species have similar metal requirements, | 120 | probably because most fish species have similar metal requirements, | ||
| 121 | and because biological factors also intervened. Finally, since the | 121 | and because biological factors also intervened. Finally, since the | ||
| 122 | study deals with metals, assumptions concerning trophic transfer | 122 | study deals with metals, assumptions concerning trophic transfer | ||
| 123 | factors calculation may not be suitable since the metal burden | 123 | factors calculation may not be suitable since the metal burden | ||
| 124 | originates not only from the prey but also from adsorption over the | 124 | originates not only from the prey but also from adsorption over the | ||
| 125 | body surfaces and seawater ingestion. (c) 2007 Elsevier B.V. All | 125 | body surfaces and seawater ingestion. (c) 2007 Elsevier B.V. All | ||
| 126 | rights reserved.", | 126 | rights reserved.", | ||
| 127 | "notes_translated": { | 127 | "notes_translated": { | ||
| 128 | "es": "Two food webs from the Mar Menor coastal lagoon, differing | 128 | "es": "Two food webs from the Mar Menor coastal lagoon, differing | ||
| 129 | in the distance from the desert-stream through which mining wastes | 129 | in the distance from the desert-stream through which mining wastes | ||
| 130 | were discharged, were examined by reference to essential (Zn and Cu) | 130 | were discharged, were examined by reference to essential (Zn and Cu) | ||
| 131 | and non-essential (Pb and Cd) metal concentrations and stable isotopes | 131 | and non-essential (Pb and Cd) metal concentrations and stable isotopes | ||
| 132 | content (C and N). The partial extraction technique applied, which | 132 | content (C and N). The partial extraction technique applied, which | ||
| 133 | reflects the availability of metals to organisms after sediment | 133 | reflects the availability of metals to organisms after sediment | ||
| 134 | ingestion, showed higher bioavailable metal concentrations in | 134 | ingestion, showed higher bioavailable metal concentrations in | ||
| 135 | sediments from the station influenced by the mining discharges, in | 135 | sediments from the station influenced by the mining discharges, in | ||
| 136 | agreement with the higher metal concentrations observed in organisms, | 136 | agreement with the higher metal concentrations observed in organisms, | ||
| 137 | which in many cases exceeded the regulatory limits established in | 137 | which in many cases exceeded the regulatory limits established in | ||
| 138 | Spanish legislation concerning seafood. Spatial differences in | 138 | Spanish legislation concerning seafood. Spatial differences in | ||
| 139 | essential metal concentrations in the fauna suggest that several | 139 | essential metal concentrations in the fauna suggest that several | ||
| 140 | organisms are exposed to metal levels above their regulation capacity. | 140 | organisms are exposed to metal levels above their regulation capacity. | ||
| 141 | Differences in isotopic composition were found between both food webs, | 141 | Differences in isotopic composition were found between both food webs, | ||
| 142 | the wadi-influenced station showing higher delta N-15 values and lower | 142 | the wadi-influenced station showing higher delta N-15 values and lower | ||
| 143 | delta C-13 levels, due to the discharge of urban waste waters and by | 143 | delta C-13 levels, due to the discharge of urban waste waters and by | ||
| 144 | the entrance of freshwater and allochthonous marsh plants. The | 144 | the entrance of freshwater and allochthonous marsh plants. The | ||
| 145 | linear-regressions between trophic levels (as indicated by delta N-15) | 145 | linear-regressions between trophic levels (as indicated by delta N-15) | ||
| 146 | and the metal content indicated that biomagnification does not occur. | 146 | and the metal content indicated that biomagnification does not occur. | ||
| 147 | In the case of invertebrates, since the \"handle strategy\" of the | 147 | In the case of invertebrates, since the \"handle strategy\" of the | ||
| 148 | species and the physiological requirements of the organisms, among | 148 | species and the physiological requirements of the organisms, among | ||
| 149 | other factors, determine the final concentration of a specific | 149 | other factors, determine the final concentration of a specific | ||
| 150 | element, no clear relationships between trophic level and the metal | 150 | element, no clear relationships between trophic level and the metal | ||
| 151 | content are to be expected. For their part, fish communities did not | 151 | content are to be expected. For their part, fish communities did not | ||
| 152 | show clear patterns in the case of any of the analyzed metals, | 152 | show clear patterns in the case of any of the analyzed metals, | ||
| 153 | probably because most fish species have similar metal requirements, | 153 | probably because most fish species have similar metal requirements, | ||
| 154 | and because biological factors also intervened. Finally, since the | 154 | and because biological factors also intervened. Finally, since the | ||
| 155 | study deals with metals, assumptions concerning trophic transfer | 155 | study deals with metals, assumptions concerning trophic transfer | ||
| 156 | factors calculation may not be suitable since the metal burden | 156 | factors calculation may not be suitable since the metal burden | ||
| 157 | originates not only from the prey but also from adsorption over the | 157 | originates not only from the prey but also from adsorption over the | ||
| 158 | body surfaces and seawater ingestion. (c) 2007 Elsevier B.V. All | 158 | body surfaces and seawater ingestion. (c) 2007 Elsevier B.V. All | ||
| 159 | rights reserved." | 159 | rights reserved." | ||
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| 285 | }, | 285 | }, | ||
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| 289 | "name": "bioindicadores", | 289 | "name": "bioindicadores", | ||
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| 299 | }, | 299 | }, | ||
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| 312 | "vocabulary_id": null | 312 | "vocabulary_id": null | ||
| 313 | }, | 313 | }, | ||
| 314 | { | 314 | { | ||
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| 348 | ], | 348 | ], | ||
| 349 | "title": "Carbon and nitrogen stable isotopes and metal | 349 | "title": "Carbon and nitrogen stable isotopes and metal | ||
| 350 | concentration in food webs from a mining-impacted coastal lagoon", | 350 | concentration in food webs from a mining-impacted coastal lagoon", | ||
| 351 | "title_translated": { | 351 | "title_translated": { | ||
| 352 | "es": "Carbon and nitrogen stable isotopes and metal concentration | 352 | "es": "Carbon and nitrogen stable isotopes and metal concentration | ||
| 353 | in food webs from a mining-impacted coastal lagoon" | 353 | in food webs from a mining-impacted coastal lagoon" | ||
| 354 | }, | 354 | }, | ||
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| 360 | "version_notes": { | 360 | "version_notes": { | ||
| 361 | "es": "" | 361 | "es": "" | ||
| 362 | } | 362 | } | ||
| 363 | } | 363 | } |