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En el instante 23 de junio de 2026, 16:04:13 UTC,
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Modificado el valor del campo
spatial_coverage
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en Assessment of the Programme of Measures for Coastal Lagoon Environmental Restoration Using Cost-Benefit Analysis
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| 93 | "notes": "The degradation of marine and coastal ecosystems has given | 93 | "notes": "The degradation of marine and coastal ecosystems has given | ||
| 94 | rise to the creation of specific protection rules. The Marine Strategy | 94 | rise to the creation of specific protection rules. The Marine Strategy | ||
| 95 | Framework Directive and the Water Framework Directive are the | 95 | Framework Directive and the Water Framework Directive are the | ||
| 96 | standards agreed in the European Union with the aim of obtaining a | 96 | standards agreed in the European Union with the aim of obtaining a | ||
| 97 | good ecological status in marine and coastal waters by applying a | 97 | good ecological status in marine and coastal waters by applying a | ||
| 98 | programme of measures, if necessary. These measures must be technical, | 98 | programme of measures, if necessary. These measures must be technical, | ||
| 99 | social and economically feasible, in such a way that costs do not | 99 | social and economically feasible, in such a way that costs do not | ||
| 100 | exceed benefits. This work expounds the implementation of two economic | 100 | exceed benefits. This work expounds the implementation of two economic | ||
| 101 | tools to assess the programme of measures intended for the | 101 | tools to assess the programme of measures intended for the | ||
| 102 | environmental restoration of one of the most important coastal | 102 | environmental restoration of one of the most important coastal | ||
| 103 | ecosystems in Europe, the Mar Menor coastal lagoon (SE Spain). Thus, | 103 | ecosystems in Europe, the Mar Menor coastal lagoon (SE Spain). Thus, | ||
| 104 | the costbenefit analysis (CBA) (and its extensions) and the contingent | 104 | the costbenefit analysis (CBA) (and its extensions) and the contingent | ||
| 105 | valuation method are used to assess the aforementioned programme in | 105 | valuation method are used to assess the aforementioned programme in | ||
| 106 | terms of economic and environmental profitability. Results prove the | 106 | terms of economic and environmental profitability. Results prove the | ||
| 107 | socioeconomic and environmental profitability of the actions due to be | 107 | socioeconomic and environmental profitability of the actions due to be | ||
| 108 | undertaken, with rates of return of around 10%. From a methodological | 108 | undertaken, with rates of return of around 10%. From a methodological | ||
| 109 | point of view, there is a clear need to widen the classic CBA scheme | 109 | point of view, there is a clear need to widen the classic CBA scheme | ||
| 110 | by using the extended CBA and the dual CBA to gauge this type of | 110 | by using the extended CBA and the dual CBA to gauge this type of | ||
| 111 | environmental restoration actions.", | 111 | environmental restoration actions.", | ||
| 112 | "notes_translated": { | 112 | "notes_translated": { | ||
| 113 | "es": "The degradation of marine and coastal ecosystems has given | 113 | "es": "The degradation of marine and coastal ecosystems has given | ||
| 114 | rise to the creation of specific protection rules. The Marine Strategy | 114 | rise to the creation of specific protection rules. The Marine Strategy | ||
| 115 | Framework Directive and the Water Framework Directive are the | 115 | Framework Directive and the Water Framework Directive are the | ||
| 116 | standards agreed in the European Union with the aim of obtaining a | 116 | standards agreed in the European Union with the aim of obtaining a | ||
| 117 | good ecological status in marine and coastal waters by applying a | 117 | good ecological status in marine and coastal waters by applying a | ||
| 118 | programme of measures, if necessary. These measures must be technical, | 118 | programme of measures, if necessary. These measures must be technical, | ||
| 119 | social and economically feasible, in such a way that costs do not | 119 | social and economically feasible, in such a way that costs do not | ||
| 120 | exceed benefits. This work expounds the implementation of two economic | 120 | exceed benefits. This work expounds the implementation of two economic | ||
| 121 | tools to assess the programme of measures intended for the | 121 | tools to assess the programme of measures intended for the | ||
| 122 | environmental restoration of one of the most important coastal | 122 | environmental restoration of one of the most important coastal | ||
| 123 | ecosystems in Europe, the Mar Menor coastal lagoon (SE Spain). Thus, | 123 | ecosystems in Europe, the Mar Menor coastal lagoon (SE Spain). Thus, | ||
| 124 | the costbenefit analysis (CBA) (and its extensions) and the contingent | 124 | the costbenefit analysis (CBA) (and its extensions) and the contingent | ||
| 125 | valuation method are used to assess the aforementioned programme in | 125 | valuation method are used to assess the aforementioned programme in | ||
| 126 | terms of economic and environmental profitability. Results prove the | 126 | terms of economic and environmental profitability. Results prove the | ||
| 127 | socioeconomic and environmental profitability of the actions due to be | 127 | socioeconomic and environmental profitability of the actions due to be | ||
| 128 | undertaken, with rates of return of around 10%. From a methodological | 128 | undertaken, with rates of return of around 10%. From a methodological | ||
| 129 | point of view, there is a clear need to widen the classic CBA scheme | 129 | point of view, there is a clear need to widen the classic CBA scheme | ||
| 130 | by using the extended CBA and the dual CBA to gauge this type of | 130 | by using the extended CBA and the dual CBA to gauge this type of | ||
| 131 | environmental restoration actions." | 131 | environmental restoration actions." | ||
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| 311 | "name": "restauracion", | 282 | "name": "restauracion", | ||
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| 314 | }, | 285 | }, | ||
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| 318 | "name": "sostenibilidad", | 289 | "name": "sostenibilidad", | ||
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| 320 | "vocabulary_id": null | 291 | "vocabulary_id": null | ||
| 321 | } | 292 | } | ||
| 322 | ], | 293 | ], | ||
| 323 | "thematic_area": [ | 294 | "thematic_area": [ | ||
| 324 | "espacios_protegidos" | 295 | "espacios_protegidos" | ||
| 325 | ], | 296 | ], | ||
| 326 | "theme_es": [ | 297 | "theme_es": [ | ||
| 327 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 298 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 328 | ], | 299 | ], | ||
| 329 | "title": "Assessment of the Programme of Measures for Coastal Lagoon | 300 | "title": "Assessment of the Programme of Measures for Coastal Lagoon | ||
| 330 | Environmental Restoration Using Cost-Benefit Analysis", | 301 | Environmental Restoration Using Cost-Benefit Analysis", | ||
| 331 | "title_translated": { | 302 | "title_translated": { | ||
| 332 | "es": "Assessment of the Programme of Measures for Coastal Lagoon | 303 | "es": "Assessment of the Programme of Measures for Coastal Lagoon | ||
| 333 | Environmental Restoration Using Cost-Benefit Analysis" | 304 | Environmental Restoration Using Cost-Benefit Analysis" | ||
| 334 | }, | 305 | }, | ||
| 335 | "topic": | 306 | "topic": | ||
| 336 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 307 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 337 | "type": "dataset", | 308 | "type": "dataset", | ||
| 338 | "url": | 309 | "url": | ||
| 339 | //iepnb.es:443/catalogo/dataset/8b2d21f6-fbda-5569-a0ca-49c05346f120", | 310 | //iepnb.es:443/catalogo/dataset/8b2d21f6-fbda-5569-a0ca-49c05346f120", | ||
| 340 | "version_notes": { | 311 | "version_notes": { | ||
| 341 | "es": "" | 312 | "es": "" | ||
| 342 | } | 313 | } | ||
| 343 | } | 314 | } |