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en Establishing the ecological quality status of soft-bottom mining-impacted coastal water bodies in the scope of the Water Framework Directive -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Establishing the ecological quality status of soft-bottom mining-impacted coastal water bodies in the scope of the Water Framework Directive
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| 94 | "notes": "The aim of the present study was to check the usefulness | 104 | "notes": "The aim of the present study was to check the usefulness | ||
| 95 | of the benthic biotic indices proposed for application in the European | 105 | of the benthic biotic indices proposed for application in the European | ||
| 96 | water framework directive (WFD 2000/60/EC) for the ecological quality | 106 | water framework directive (WFD 2000/60/EC) for the ecological quality | ||
| 97 | classification of coastal water bodies, together with some other | 107 | classification of coastal water bodies, together with some other | ||
| 98 | benthic methodologies used in different countries of the world. The | 108 | benthic methodologies used in different countries of the world. The | ||
| 99 | different approaches were applied in two marine ecosystems affected by | 109 | different approaches were applied in two marine ecosystems affected by | ||
| 100 | the same heavy metal contamination source, coastal waters off Portman | 110 | the same heavy metal contamination source, coastal waters off Portman | ||
| 101 | and the Mar Menor coastal lagoon, both in SE Spain. Two marine biotic | 111 | and the Mar Menor coastal lagoon, both in SE Spain. Two marine biotic | ||
| 102 | indices proposed for application in the Directive (AMBI and BENTIX) | 112 | indices proposed for application in the Directive (AMBI and BENTIX) | ||
| 103 | were used, together with community descriptors (abundance, | 113 | were used, together with community descriptors (abundance, | ||
| 104 | Shannon-Wiener diversity, Margalef's species richness, Pielou's | 114 | Shannon-Wiener diversity, Margalef's species richness, Pielou's | ||
| 105 | evenness and Simpson's Dominance), the relative benthic index (RBI) | 115 | evenness and Simpson's Dominance), the relative benthic index (RBI) | ||
| 106 | and the abundance-biomass comparison method (ABC). Water-sediment | 116 | and the abundance-biomass comparison method (ABC). Water-sediment | ||
| 107 | interface toxicity bioassays using sea urchin embryos and sediment | 117 | interface toxicity bioassays using sea urchin embryos and sediment | ||
| 108 | metal analysis served to check the classifications obtained. The | 118 | metal analysis served to check the classifications obtained. The | ||
| 109 | classical community descriptors pointed to a progressive variation in | 119 | classical community descriptors pointed to a progressive variation in | ||
| 110 | benthic communities along the metal contamination gradient of Portman, | 120 | benthic communities along the metal contamination gradient of Portman, | ||
| 111 | but, they did not correctly characterize the environmental status of | 121 | but, they did not correctly characterize the environmental status of | ||
| 112 | the lagoon stations. Although the RBI was the index that best | 122 | the lagoon stations. Although the RBI was the index that best | ||
| 113 | classified the sites according to their degree of pollution, the | 123 | classified the sites according to their degree of pollution, the | ||
| 114 | selection of indicator species can bias the results. Since the AMBI, | 124 | selection of indicator species can bias the results. Since the AMBI, | ||
| 115 | the BENTIX and the ABC method are based on the pollution resulting | 125 | the BENTIX and the ABC method are based on the pollution resulting | ||
| 116 | from organic enrichment, their application in the case of purely toxic | 126 | from organic enrichment, their application in the case of purely toxic | ||
| 117 | pollution may not be successful, as was found to be the case in these | 127 | pollution may not be successful, as was found to be the case in these | ||
| 118 | two mining-polluted ecosystems. Therefore, the development of new | 128 | two mining-polluted ecosystems. Therefore, the development of new | ||
| 119 | indicator lists according to the type of pollutant may serve to | 129 | indicator lists according to the type of pollutant may serve to | ||
| 120 | improve the results obtained with organic enrichment-based indices | 130 | improve the results obtained with organic enrichment-based indices | ||
| 121 | when studying other kinds of disturbance. Finally, we found the | 131 | when studying other kinds of disturbance. Finally, we found the | ||
| 122 | toxicity tests to be useful tools for the environmental assessment of | 132 | toxicity tests to be useful tools for the environmental assessment of | ||
| 123 | aquatic ecosystems, and recommend their inclusion in the WFD. (c) 2004 | 133 | aquatic ecosystems, and recommend their inclusion in the WFD. (c) 2004 | ||
| 124 | Elsevier Ltd. All rights reserved.", | 134 | Elsevier Ltd. All rights reserved.", | ||
| 125 | "notes_translated": { | 135 | "notes_translated": { | ||
| 126 | "es": "The aim of the present study was to check the usefulness of | 136 | "es": "The aim of the present study was to check the usefulness of | ||
| 127 | the benthic biotic indices proposed for application in the European | 137 | the benthic biotic indices proposed for application in the European | ||
| 128 | water framework directive (WFD 2000/60/EC) for the ecological quality | 138 | water framework directive (WFD 2000/60/EC) for the ecological quality | ||
| 129 | classification of coastal water bodies, together with some other | 139 | classification of coastal water bodies, together with some other | ||
| 130 | benthic methodologies used in different countries of the world. The | 140 | benthic methodologies used in different countries of the world. The | ||
| 131 | different approaches were applied in two marine ecosystems affected by | 141 | different approaches were applied in two marine ecosystems affected by | ||
| 132 | the same heavy metal contamination source, coastal waters off Portman | 142 | the same heavy metal contamination source, coastal waters off Portman | ||
| 133 | and the Mar Menor coastal lagoon, both in SE Spain. Two marine biotic | 143 | and the Mar Menor coastal lagoon, both in SE Spain. Two marine biotic | ||
| 134 | indices proposed for application in the Directive (AMBI and BENTIX) | 144 | indices proposed for application in the Directive (AMBI and BENTIX) | ||
| 135 | were used, together with community descriptors (abundance, | 145 | were used, together with community descriptors (abundance, | ||
| 136 | Shannon-Wiener diversity, Margalef's species richness, Pielou's | 146 | Shannon-Wiener diversity, Margalef's species richness, Pielou's | ||
| 137 | evenness and Simpson's Dominance), the relative benthic index (RBI) | 147 | evenness and Simpson's Dominance), the relative benthic index (RBI) | ||
| 138 | and the abundance-biomass comparison method (ABC). Water-sediment | 148 | and the abundance-biomass comparison method (ABC). Water-sediment | ||
| 139 | interface toxicity bioassays using sea urchin embryos and sediment | 149 | interface toxicity bioassays using sea urchin embryos and sediment | ||
| 140 | metal analysis served to check the classifications obtained. The | 150 | metal analysis served to check the classifications obtained. The | ||
| 141 | classical community descriptors pointed to a progressive variation in | 151 | classical community descriptors pointed to a progressive variation in | ||
| 142 | benthic communities along the metal contamination gradient of Portman, | 152 | benthic communities along the metal contamination gradient of Portman, | ||
| 143 | but, they did not correctly characterize the environmental status of | 153 | but, they did not correctly characterize the environmental status of | ||
| 144 | the lagoon stations. Although the RBI was the index that best | 154 | the lagoon stations. Although the RBI was the index that best | ||
| 145 | classified the sites according to their degree of pollution, the | 155 | classified the sites according to their degree of pollution, the | ||
| 146 | selection of indicator species can bias the results. Since the AMBI, | 156 | selection of indicator species can bias the results. Since the AMBI, | ||
| 147 | the BENTIX and the ABC method are based on the pollution resulting | 157 | the BENTIX and the ABC method are based on the pollution resulting | ||
| 148 | from organic enrichment, their application in the case of purely toxic | 158 | from organic enrichment, their application in the case of purely toxic | ||
| 149 | pollution may not be successful, as was found to be the case in these | 159 | pollution may not be successful, as was found to be the case in these | ||
| 150 | two mining-polluted ecosystems. Therefore, the development of new | 160 | two mining-polluted ecosystems. Therefore, the development of new | ||
| 151 | indicator lists according to the type of pollutant may serve to | 161 | indicator lists according to the type of pollutant may serve to | ||
| 152 | improve the results obtained with organic enrichment-based indices | 162 | improve the results obtained with organic enrichment-based indices | ||
| 153 | when studying other kinds of disturbance. Finally, we found the | 163 | when studying other kinds of disturbance. Finally, we found the | ||
| 154 | toxicity tests to be useful tools for the environmental assessment of | 164 | toxicity tests to be useful tools for the environmental assessment of | ||
| 155 | aquatic ecosystems, and recommend their inclusion in the WFD. (c) 2004 | 165 | aquatic ecosystems, and recommend their inclusion in the WFD. (c) 2004 | ||
| 156 | Elsevier Ltd. All rights reserved." | 166 | Elsevier Ltd. All rights reserved." | ||
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