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en Biodiversity impacts by multiple anthropogenic stressors in Mediterranean coastal wetlands -
Modificado el valor del campo
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del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Biodiversity impacts by multiple anthropogenic stressors in Mediterranean coastal wetlands
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| 90 | "notes": "Mediterranean coastal wetlands are considered biodiversity | 100 | "notes": "Mediterranean coastal wetlands are considered biodiversity | ||
| 91 | hot-spots and contain a high number of endemic species. The | 101 | hot-spots and contain a high number of endemic species. The | ||
| 92 | biodiversity of these ecosystems is endangered by several pressures | 102 | biodiversity of these ecosystems is endangered by several pressures | ||
| 93 | resulting from agricultural and urban expansion, climate change, and | 103 | resulting from agricultural and urban expansion, climate change, and | ||
| 94 | the alteration of their hydrological cycle. In this study we assess | 104 | the alteration of their hydrological cycle. In this study we assess | ||
| 95 | the state-of-the-art regarding the impact of several stressor groups | 105 | the state-of-the-art regarding the impact of several stressor groups | ||
| 96 | on the biodiversity of Mediterranean coastal wetlands (i.e., lagoons, | 106 | on the biodiversity of Mediterranean coastal wetlands (i.e., lagoons, | ||
| 97 | marshes, estuaries). Particularly, we describe the impacts of | 107 | marshes, estuaries). Particularly, we describe the impacts of | ||
| 98 | eutrophication, chemical pollution, invasive species, salinization, | 108 | eutrophication, chemical pollution, invasive species, salinization, | ||
| 99 | and temperature rise, and analyze the existing literature regarding | 109 | and temperature rise, and analyze the existing literature regarding | ||
| 100 | the impact of multiple stressors on these ecosystems. Our study | 110 | the impact of multiple stressors on these ecosystems. Our study | ||
| 101 | denotes a clear asymmetry both in terms of study areas and stressors | 111 | denotes a clear asymmetry both in terms of study areas and stressors | ||
| 102 | evaluated. The majority of studies focus on lagoons and estuaries of | 112 | evaluated. The majority of studies focus on lagoons and estuaries of | ||
| 103 | the north-west parts of the Mediterranean basin, while the African and | 113 | the north-west parts of the Mediterranean basin, while the African and | ||
| 104 | the Asian coast have been less represented. Eutrophication and | 114 | the Asian coast have been less represented. Eutrophication and | ||
| 105 | chemical pollution were the most studied stressors compared to others | 115 | chemical pollution were the most studied stressors compared to others | ||
| 106 | like temperature rise or species invasions. Most studies evaluating | 116 | like temperature rise or species invasions. Most studies evaluating | ||
| 107 | these stressors individually show direct or indirect effects on the | 117 | these stressors individually show direct or indirect effects on the | ||
| 108 | biodiversity of primary producers and invertebrate communities, and | 118 | biodiversity of primary producers and invertebrate communities, and | ||
| 109 | changes in species dominance patterns that contribute to a decline of | 119 | changes in species dominance patterns that contribute to a decline of | ||
| 110 | endemic populations. The few available studies addressing stressor | 120 | endemic populations. The few available studies addressing stressor | ||
| 111 | interactions have shown non-additive responses, which are important to | 121 | interactions have shown non-additive responses, which are important to | ||
| 112 | define appropriate ecosystem management and restoration measures. | 122 | define appropriate ecosystem management and restoration measures. | ||
| 113 | Finally, we propose research needs to advance our understanding on the | 123 | Finally, we propose research needs to advance our understanding on the | ||
| 114 | impacts of anthropogenic stressors on Mediterranean coastal wetlands | 124 | impacts of anthropogenic stressors on Mediterranean coastal wetlands | ||
| 115 | and to guide future interventions to protect biodiversity.", | 125 | and to guide future interventions to protect biodiversity.", | ||
| 116 | "notes_translated": { | 126 | "notes_translated": { | ||
| 117 | "es": "Mediterranean coastal wetlands are considered biodiversity | 127 | "es": "Mediterranean coastal wetlands are considered biodiversity | ||
| 118 | hot-spots and contain a high number of endemic species. The | 128 | hot-spots and contain a high number of endemic species. The | ||
| 119 | biodiversity of these ecosystems is endangered by several pressures | 129 | biodiversity of these ecosystems is endangered by several pressures | ||
| 120 | resulting from agricultural and urban expansion, climate change, and | 130 | resulting from agricultural and urban expansion, climate change, and | ||
| 121 | the alteration of their hydrological cycle. In this study we assess | 131 | the alteration of their hydrological cycle. In this study we assess | ||
| 122 | the state-of-the-art regarding the impact of several stressor groups | 132 | the state-of-the-art regarding the impact of several stressor groups | ||
| 123 | on the biodiversity of Mediterranean coastal wetlands (i.e., lagoons, | 133 | on the biodiversity of Mediterranean coastal wetlands (i.e., lagoons, | ||
| 124 | marshes, estuaries). Particularly, we describe the impacts of | 134 | marshes, estuaries). Particularly, we describe the impacts of | ||
| 125 | eutrophication, chemical pollution, invasive species, salinization, | 135 | eutrophication, chemical pollution, invasive species, salinization, | ||
| 126 | and temperature rise, and analyze the existing literature regarding | 136 | and temperature rise, and analyze the existing literature regarding | ||
| 127 | the impact of multiple stressors on these ecosystems. Our study | 137 | the impact of multiple stressors on these ecosystems. Our study | ||
| 128 | denotes a clear asymmetry both in terms of study areas and stressors | 138 | denotes a clear asymmetry both in terms of study areas and stressors | ||
| 129 | evaluated. The majority of studies focus on lagoons and estuaries of | 139 | evaluated. The majority of studies focus on lagoons and estuaries of | ||
| 130 | the north-west parts of the Mediterranean basin, while the African and | 140 | the north-west parts of the Mediterranean basin, while the African and | ||
| 131 | the Asian coast have been less represented. Eutrophication and | 141 | the Asian coast have been less represented. Eutrophication and | ||
| 132 | chemical pollution were the most studied stressors compared to others | 142 | chemical pollution were the most studied stressors compared to others | ||
| 133 | like temperature rise or species invasions. Most studies evaluating | 143 | like temperature rise or species invasions. Most studies evaluating | ||
| 134 | these stressors individually show direct or indirect effects on the | 144 | these stressors individually show direct or indirect effects on the | ||
| 135 | biodiversity of primary producers and invertebrate communities, and | 145 | biodiversity of primary producers and invertebrate communities, and | ||
| 136 | changes in species dominance patterns that contribute to a decline of | 146 | changes in species dominance patterns that contribute to a decline of | ||
| 137 | endemic populations. The few available studies addressing stressor | 147 | endemic populations. The few available studies addressing stressor | ||
| 138 | interactions have shown non-additive responses, which are important to | 148 | interactions have shown non-additive responses, which are important to | ||
| 139 | define appropriate ecosystem management and restoration measures. | 149 | define appropriate ecosystem management and restoration measures. | ||
| 140 | Finally, we propose research needs to advance our understanding on the | 150 | Finally, we propose research needs to advance our understanding on the | ||
| 141 | impacts of anthropogenic stressors on Mediterranean coastal wetlands | 151 | impacts of anthropogenic stressors on Mediterranean coastal wetlands | ||
| 142 | and to guide future interventions to protect biodiversity." | 152 | and to guide future interventions to protect biodiversity." | ||
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| 238 | 37.38]]]}", | 248 | 37.38]]]}", | ||
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| 245 | 38.07]}", | 255 | 38.07]}", | ||
| 246 | "text": "Regi\u00f3n de Murcia", | 256 | "text": "Regi\u00f3n de Murcia", | ||
| 247 | "uri": | 257 | "uri": | ||
| 248 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | 258 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | ||
| 249 | } | 259 | } | ||
| 250 | ], | 260 | ], | ||
| 251 | "spatial_uri": | 261 | "spatial_uri": | ||
| 252 | tos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia", | 262 | tos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia", | ||
| 253 | "state": "active", | 263 | "state": "active", | ||
| 254 | "study_variables": { | 264 | "study_variables": { | ||
| 255 | "es": "" | 265 | "es": "" | ||
| 256 | }, | 266 | }, | ||
| 257 | "tag_uri": [ | 267 | "tag_uri": [ | ||
| 258 | 268 | ||||
| 259 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 269 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 260 | ], | 270 | ], | ||
| 261 | "tags": [ | 271 | "tags": [ | ||
| 262 | { | 272 | { | ||
| 263 | "display_name": "contaminacion", | 273 | "display_name": "contaminacion", | ||
| 264 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 274 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 265 | "name": "contaminacion", | 275 | "name": "contaminacion", | ||
| 266 | "state": "active", | 276 | "state": "active", | ||
| 267 | "vocabulary_id": null | 277 | "vocabulary_id": null | ||
| 268 | }, | 278 | }, | ||
| 269 | { | 279 | { | ||
| 270 | "display_name": "diversidad", | 280 | "display_name": "diversidad", | ||
| 271 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | 281 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | ||
| 272 | "name": "diversidad", | 282 | "name": "diversidad", | ||
| 273 | "state": "active", | 283 | "state": "active", | ||
| 274 | "vocabulary_id": null | 284 | "vocabulary_id": null | ||
| 275 | }, | 285 | }, | ||
| 276 | { | 286 | { | ||
| 277 | "display_name": "especies_protegidas", | 287 | "display_name": "especies_protegidas", | ||
| 278 | "id": "79febedc-eba6-448a-8ea6-85afa410888d", | 288 | "id": "79febedc-eba6-448a-8ea6-85afa410888d", | ||
| 279 | "name": "especies_protegidas", | 289 | "name": "especies_protegidas", | ||
| 280 | "state": "active", | 290 | "state": "active", | ||
| 281 | "vocabulary_id": null | 291 | "vocabulary_id": null | ||
| 282 | }, | 292 | }, | ||
| 283 | { | 293 | { | ||
| 284 | "display_name": "habitats_amenazados", | 294 | "display_name": "habitats_amenazados", | ||
| 285 | "id": "53f69b08-6e69-4dee-a2f2-d375b8464e33", | 295 | "id": "53f69b08-6e69-4dee-a2f2-d375b8464e33", | ||
| 286 | "name": "habitats_amenazados", | 296 | "name": "habitats_amenazados", | ||
| 287 | "state": "active", | 297 | "state": "active", | ||
| 288 | "vocabulary_id": null | 298 | "vocabulary_id": null | ||
| 289 | }, | 299 | }, | ||
| 290 | { | 300 | { | ||
| 291 | "display_name": "humedales", | 301 | "display_name": "humedales", | ||
| 292 | "id": "649ff5bb-8f7c-45ae-8cda-3aaf630a2857", | 302 | "id": "649ff5bb-8f7c-45ae-8cda-3aaf630a2857", | ||
| 293 | "name": "humedales", | 303 | "name": "humedales", | ||
| 294 | "state": "active", | 304 | "state": "active", | ||
| 295 | "vocabulary_id": null | 305 | "vocabulary_id": null | ||
| 296 | }, | 306 | }, | ||
| 297 | { | 307 | { | ||
| 298 | "display_name": "marino", | 308 | "display_name": "marino", | ||
| 299 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 309 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 300 | "name": "marino", | 310 | "name": "marino", | ||
| 301 | "state": "active", | 311 | "state": "active", | ||
| 302 | "vocabulary_id": null | 312 | "vocabulary_id": null | ||
| 303 | }, | 313 | }, | ||
| 304 | { | 314 | { | ||
| 305 | "display_name": "presiones_y_amenazas", | 315 | "display_name": "presiones_y_amenazas", | ||
| 306 | "id": "7d9c66f1-e5b3-4236-9e0f-e51d7a9d4653", | 316 | "id": "7d9c66f1-e5b3-4236-9e0f-e51d7a9d4653", | ||
| 307 | "name": "presiones_y_amenazas", | 317 | "name": "presiones_y_amenazas", | ||
| 308 | "state": "active", | 318 | "state": "active", | ||
| 309 | "vocabulary_id": null | 319 | "vocabulary_id": null | ||
| 310 | } | 320 | } | ||
| 311 | ], | 321 | ], | ||
| 312 | "thematic_area": [ | 322 | "thematic_area": [ | ||
| 313 | "espacios_protegidos" | 323 | "espacios_protegidos" | ||
| 314 | ], | 324 | ], | ||
| 315 | "theme_es": [ | 325 | "theme_es": [ | ||
| 316 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 326 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 317 | ], | 327 | ], | ||
| 318 | "title": "Biodiversity impacts by multiple anthropogenic stressors | 328 | "title": "Biodiversity impacts by multiple anthropogenic stressors | ||
| 319 | in Mediterranean coastal wetlands", | 329 | in Mediterranean coastal wetlands", | ||
| 320 | "title_translated": { | 330 | "title_translated": { | ||
| 321 | "es": "Biodiversity impacts by multiple anthropogenic stressors in | 331 | "es": "Biodiversity impacts by multiple anthropogenic stressors in | ||
| 322 | Mediterranean coastal wetlands" | 332 | Mediterranean coastal wetlands" | ||
| 323 | }, | 333 | }, | ||
| 324 | "topic": | 334 | "topic": | ||
| 325 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 335 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 326 | "type": "dataset", | 336 | "type": "dataset", | ||
| 327 | "url": | 337 | "url": | ||
| 328 | //iepnb.es:443/catalogo/dataset/6e2cb675-0517-5a13-ace2-aafe5eeecda2", | 338 | //iepnb.es:443/catalogo/dataset/6e2cb675-0517-5a13-ace2-aafe5eeecda2", | ||
| 329 | "version_notes": { | 339 | "version_notes": { | ||
| 330 | "es": "" | 340 | "es": "" | ||
| 331 | } | 341 | } | ||
| 332 | } | 342 | } |