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) en User-friendly guide for using benthic ecological indicators in coastal and marine quality assessment
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| 95 | "notes": "Experience demonstrates that none of the available | 105 | "notes": "Experience demonstrates that none of the available | ||
| 96 | measures on biological effects of pollution should be considered | 106 | measures on biological effects of pollution should be considered | ||
| 97 | ideal. The use of a single approach does not seem appropriate due to | 107 | ideal. The use of a single approach does not seem appropriate due to | ||
| 98 | the complexity inherent in assessing the environmental quality of a | 108 | the complexity inherent in assessing the environmental quality of a | ||
| 99 | system. Rather, this should be evaluated by combining a suite of | 109 | system. Rather, this should be evaluated by combining a suite of | ||
| 100 | indices providing complementary information.Having this in mind, a key | 110 | indices providing complementary information.Having this in mind, a key | ||
| 101 | table is proposed in this work with the aim of helping managers and | 111 | table is proposed in this work with the aim of helping managers and | ||
| 102 | authorities of coastal areas in selecting the most suitable ecological | 112 | authorities of coastal areas in selecting the most suitable ecological | ||
| 103 | indicators taking into account the type of disturbance and the data | 113 | indicators taking into account the type of disturbance and the data | ||
| 104 | available. Such key includes numerous indices based on benthic | 114 | available. Such key includes numerous indices based on benthic | ||
| 105 | invertebrate fauna information, because in the case of coastal and | 115 | invertebrate fauna information, because in the case of coastal and | ||
| 106 | transitional waters ecosystems there is a clear preference for benthic | 116 | transitional waters ecosystems there is a clear preference for benthic | ||
| 107 | communities, which integrate environmental conditions and changes in | 117 | communities, which integrate environmental conditions and changes in | ||
| 108 | an a very effective way if we want to monitor long-term responses and | 118 | an a very effective way if we want to monitor long-term responses and | ||
| 109 | site-specific impacts.The development of this key was based not only | 119 | site-specific impacts.The development of this key was based not only | ||
| 110 | on theoretical approaches, but also on results from its application | 120 | on theoretical approaches, but also on results from its application | ||
| 111 | using data bases corresponding to different geographical areas (the | 121 | using data bases corresponding to different geographical areas (the | ||
| 112 | Mondego estuary, in the North-Western Coast of Portugal, and Mar Menor | 122 | Mondego estuary, in the North-Western Coast of Portugal, and Mar Menor | ||
| 113 | coastal lagoon, Escombreras basin, and Cabo Tinoso in the | 123 | coastal lagoon, Escombreras basin, and Cabo Tinoso in the | ||
| 114 | South-Eastern coast of Spain).Some recommendations are provided with | 124 | South-Eastern coast of Spain).Some recommendations are provided with | ||
| 115 | regard to the most adequate application of the indices, as for | 125 | regard to the most adequate application of the indices, as for | ||
| 116 | example, in what situations it is not advisable the use of some of | 126 | example, in what situations it is not advisable the use of some of | ||
| 117 | them, depending on the type of disturbance or the level of taxonomic | 127 | them, depending on the type of disturbance or the level of taxonomic | ||
| 118 | identification of the organisms. (c) 2006 Elsevier Ltd. All rights | 128 | identification of the organisms. (c) 2006 Elsevier Ltd. All rights | ||
| 119 | reserved.", | 129 | reserved.", | ||
| 120 | "notes_translated": { | 130 | "notes_translated": { | ||
| 121 | "es": "Experience demonstrates that none of the available measures | 131 | "es": "Experience demonstrates that none of the available measures | ||
| 122 | on biological effects of pollution should be considered ideal. The use | 132 | on biological effects of pollution should be considered ideal. The use | ||
| 123 | of a single approach does not seem appropriate due to the complexity | 133 | of a single approach does not seem appropriate due to the complexity | ||
| 124 | inherent in assessing the environmental quality of a system. Rather, | 134 | inherent in assessing the environmental quality of a system. Rather, | ||
| 125 | this should be evaluated by combining a suite of indices providing | 135 | this should be evaluated by combining a suite of indices providing | ||
| 126 | complementary information.Having this in mind, a key table is proposed | 136 | complementary information.Having this in mind, a key table is proposed | ||
| 127 | in this work with the aim of helping managers and authorities of | 137 | in this work with the aim of helping managers and authorities of | ||
| 128 | coastal areas in selecting the most suitable ecological indicators | 138 | coastal areas in selecting the most suitable ecological indicators | ||
| 129 | taking into account the type of disturbance and the data available. | 139 | taking into account the type of disturbance and the data available. | ||
| 130 | Such key includes numerous indices based on benthic invertebrate fauna | 140 | Such key includes numerous indices based on benthic invertebrate fauna | ||
| 131 | information, because in the case of coastal and transitional waters | 141 | information, because in the case of coastal and transitional waters | ||
| 132 | ecosystems there is a clear preference for benthic communities, which | 142 | ecosystems there is a clear preference for benthic communities, which | ||
| 133 | integrate environmental conditions and changes in an a very effective | 143 | integrate environmental conditions and changes in an a very effective | ||
| 134 | way if we want to monitor long-term responses and site-specific | 144 | way if we want to monitor long-term responses and site-specific | ||
| 135 | impacts.The development of this key was based not only on theoretical | 145 | impacts.The development of this key was based not only on theoretical | ||
| 136 | approaches, but also on results from its application using data bases | 146 | approaches, but also on results from its application using data bases | ||
| 137 | corresponding to different geographical areas (the Mondego estuary, in | 147 | corresponding to different geographical areas (the Mondego estuary, in | ||
| 138 | the North-Western Coast of Portugal, and Mar Menor coastal lagoon, | 148 | the North-Western Coast of Portugal, and Mar Menor coastal lagoon, | ||
| 139 | Escombreras basin, and Cabo Tinoso in the South-Eastern coast of | 149 | Escombreras basin, and Cabo Tinoso in the South-Eastern coast of | ||
| 140 | Spain).Some recommendations are provided with regard to the most | 150 | Spain).Some recommendations are provided with regard to the most | ||
| 141 | adequate application of the indices, as for example, in what | 151 | adequate application of the indices, as for example, in what | ||
| 142 | situations it is not advisable the use of some of them, depending on | 152 | situations it is not advisable the use of some of them, depending on | ||
| 143 | the type of disturbance or the level of taxonomic identification of | 153 | the type of disturbance or the level of taxonomic identification of | ||
| 144 | the organisms. (c) 2006 Elsevier Ltd. All rights reserved." | 154 | the organisms. (c) 2006 Elsevier Ltd. All rights reserved." | ||
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| 231 | "state": "active", | 241 | "state": "active", | ||
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| 250 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 260 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 255 | "state": "active", | 265 | "state": "active", | ||
| 256 | "study_variables": { | 266 | "study_variables": { | ||
| 257 | "es": "" | 267 | "es": "" | ||
| 258 | }, | 268 | }, | ||
| 259 | "tag_uri": [ | 269 | "tag_uri": [ | ||
| 260 | 270 | ||||
| 261 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 271 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 262 | ], | 272 | ], | ||
| 263 | "tags": [ | 273 | "tags": [ | ||
| 264 | { | 274 | { | ||
| 265 | "display_name": "bioindicadores", | 275 | "display_name": "bioindicadores", | ||
| 266 | "id": "012ee1ac-e8fa-4a30-993a-14ac13854137", | 276 | "id": "012ee1ac-e8fa-4a30-993a-14ac13854137", | ||
| 267 | "name": "bioindicadores", | 277 | "name": "bioindicadores", | ||
| 268 | "state": "active", | 278 | "state": "active", | ||
| 269 | "vocabulary_id": null | 279 | "vocabulary_id": null | ||
| 270 | }, | 280 | }, | ||
| 271 | { | 281 | { | ||
| 272 | "display_name": "diversidad", | 282 | "display_name": "diversidad", | ||
| 273 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | 283 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | ||
| 274 | "name": "diversidad", | 284 | "name": "diversidad", | ||
| 275 | "state": "active", | 285 | "state": "active", | ||
| 276 | "vocabulary_id": null | 286 | "vocabulary_id": null | ||
| 277 | }, | 287 | }, | ||
| 278 | { | 288 | { | ||
| 279 | "display_name": "habitats", | 289 | "display_name": "habitats", | ||
| 280 | "id": "5d75ced3-7300-46a6-85cb-464f2694d183", | 290 | "id": "5d75ced3-7300-46a6-85cb-464f2694d183", | ||
| 281 | "name": "habitats", | 291 | "name": "habitats", | ||
| 282 | "state": "active", | 292 | "state": "active", | ||
| 283 | "vocabulary_id": null | 293 | "vocabulary_id": null | ||
| 284 | }, | 294 | }, | ||
| 285 | { | 295 | { | ||
| 286 | "display_name": "marino", | 296 | "display_name": "marino", | ||
| 287 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 297 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 288 | "name": "marino", | 298 | "name": "marino", | ||
| 289 | "state": "active", | 299 | "state": "active", | ||
| 290 | "vocabulary_id": null | 300 | "vocabulary_id": null | ||
| 291 | }, | 301 | }, | ||
| 292 | { | 302 | { | ||
| 293 | "display_name": "medidas_de_gestion", | 303 | "display_name": "medidas_de_gestion", | ||
| 294 | "id": "c82d981c-d4ad-45e5-8229-afe383d5ea3d", | 304 | "id": "c82d981c-d4ad-45e5-8229-afe383d5ea3d", | ||
| 295 | "name": "medidas_de_gestion", | 305 | "name": "medidas_de_gestion", | ||
| 296 | "state": "active", | 306 | "state": "active", | ||
| 297 | "vocabulary_id": null | 307 | "vocabulary_id": null | ||
| 298 | } | 308 | } | ||
| 299 | ], | 309 | ], | ||
| 300 | "thematic_area": [ | 310 | "thematic_area": [ | ||
| 301 | "espacios_protegidos" | 311 | "espacios_protegidos" | ||
| 302 | ], | 312 | ], | ||
| 303 | "theme_es": [ | 313 | "theme_es": [ | ||
| 304 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 314 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 305 | ], | 315 | ], | ||
| 306 | "title": "User-friendly guide for using benthic ecological | 316 | "title": "User-friendly guide for using benthic ecological | ||
| 307 | indicators in coastal and marine quality assessment", | 317 | indicators in coastal and marine quality assessment", | ||
| 308 | "title_translated": { | 318 | "title_translated": { | ||
| 309 | "es": "User-friendly guide for using benthic ecological indicators | 319 | "es": "User-friendly guide for using benthic ecological indicators | ||
| 310 | in coastal and marine quality assessment" | 320 | in coastal and marine quality assessment" | ||
| 311 | }, | 321 | }, | ||
| 312 | "topic": | 322 | "topic": | ||
| 313 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 323 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 314 | "type": "dataset", | 324 | "type": "dataset", | ||
| 315 | "url": | 325 | "url": | ||
| 316 | //iepnb.es:443/catalogo/dataset/a8435a3c-0bd0-5178-84c5-03fab70f3d03", | 326 | //iepnb.es:443/catalogo/dataset/a8435a3c-0bd0-5178-84c5-03fab70f3d03", | ||
| 317 | "version_notes": { | 327 | "version_notes": { | ||
| 318 | "es": "" | 328 | "es": "" | ||
| 319 | } | 329 | } | ||
| 320 | } | 330 | } |