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En el instante 23 de junio de 2026, 16:04:31 UTC,
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Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-2.34, 37.38], [-0.69, 37.38], [-0.69, 38.76], [-2.34, 38.76], [-2.34, 37.38]]]}', 'centroid': '{"type": "Point", "coordinates": [-1.515, 38.07]}', 'text': 'Región de Murcia', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia'}]
en Changes in benthic fish assemblages as a consequence of coastal works in a coastal lagoon: The Mar Menor (Spain, Western Mediterranean)
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| 93 | "notes": "The benthic fish assemblage of the Mar Menor consisted of | 93 | "notes": "The benthic fish assemblage of the Mar Menor consisted of | ||
| 94 | 37 species. Dominant species are: Gobius cobitis, Lipophrys pavo and | 94 | 37 species. Dominant species are: Gobius cobitis, Lipophrys pavo and | ||
| 95 | Trip\u0002terygion tripteronotus on infralittoral rocks; | 95 | Trip\u0002terygion tripteronotus on infralittoral rocks; | ||
| 96 | Pomatoschistus marmoratus, Callionymus pussillus, Callionymus risso | 96 | Pomatoschistus marmoratus, Callionymus pussillus, Callionymus risso | ||
| 97 | and Solea vulgaris on sandy bottoms and Gobius niger, Syngnathus | 97 | and Solea vulgaris on sandy bottoms and Gobius niger, Syngnathus | ||
| 98 | abaster, Hippocampus ramulosus and Symphodus cinereus on Cymodocea | 98 | abaster, Hippocampus ramulosus and Symphodus cinereus on Cymodocea | ||
| 99 | nodosa\u2013Caulerpa prolifera mixed beds. From 1985 to 1989 tourist | 99 | nodosa\u2013Caulerpa prolifera mixed beds. From 1985 to 1989 tourist | ||
| 100 | development has led to the creation of new beaches and the | 100 | development has led to the creation of new beaches and the | ||
| 101 | installation of artificial rocky structures for retaining sediments. | 101 | installation of artificial rocky structures for retaining sediments. | ||
| 102 | Dredging for the extraction of sand and subsequent pumping altered | 102 | Dredging for the extraction of sand and subsequent pumping altered | ||
| 103 | sediment characteristics causing a real stress leading to the | 103 | sediment characteristics causing a real stress leading to the | ||
| 104 | substitution of typical sandy bottoms communities with Cymodocea | 104 | substitution of typical sandy bottoms communities with Cymodocea | ||
| 105 | nodosa by Caulerpa prolifera communities on mud. Soft bottom fish | 105 | nodosa by Caulerpa prolifera communities on mud. Soft bottom fish | ||
| 106 | assemblages responded to changes in vegetation cover and substratum | 106 | assemblages responded to changes in vegetation cover and substratum | ||
| 107 | characteristics mainly changing the spe\u0002cies composition, while | 107 | characteristics mainly changing the spe\u0002cies composition, while | ||
| 108 | artificial hard substrata contain a similar fish community than | 108 | artificial hard substrata contain a similar fish community than | ||
| 109 | natural ones, harbouring even richer and more diverse assemblages. | 109 | natural ones, harbouring even richer and more diverse assemblages. | ||
| 110 | This positive effect of breakwaters should not obscure their likely | 110 | This positive effect of breakwaters should not obscure their likely | ||
| 111 | negative effects on hydrodynamics and the sub\u0002sequent changes of | 111 | negative effects on hydrodynamics and the sub\u0002sequent changes of | ||
| 112 | sediment quality and vegetation cover on the breakwaters\u0002 area of | 112 | sediment quality and vegetation cover on the breakwaters\u0002 area of | ||
| 113 | influence. \u0002 2005 Elsevier Ltd. All rights reserved.", | 113 | influence. \u0002 2005 Elsevier Ltd. All rights reserved.", | ||
| 114 | "notes_translated": { | 114 | "notes_translated": { | ||
| 115 | "es": "The benthic fish assemblage of the Mar Menor consisted of | 115 | "es": "The benthic fish assemblage of the Mar Menor consisted of | ||
| 116 | 37 species. Dominant species are: Gobius cobitis, Lipophrys pavo and | 116 | 37 species. Dominant species are: Gobius cobitis, Lipophrys pavo and | ||
| 117 | Trip\u0002terygion tripteronotus on infralittoral rocks; | 117 | Trip\u0002terygion tripteronotus on infralittoral rocks; | ||
| 118 | Pomatoschistus marmoratus, Callionymus pussillus, Callionymus risso | 118 | Pomatoschistus marmoratus, Callionymus pussillus, Callionymus risso | ||
| 119 | and Solea vulgaris on sandy bottoms and Gobius niger, Syngnathus | 119 | and Solea vulgaris on sandy bottoms and Gobius niger, Syngnathus | ||
| 120 | abaster, Hippocampus ramulosus and Symphodus cinereus on Cymodocea | 120 | abaster, Hippocampus ramulosus and Symphodus cinereus on Cymodocea | ||
| 121 | nodosa\u2013Caulerpa prolifera mixed beds. From 1985 to 1989 tourist | 121 | nodosa\u2013Caulerpa prolifera mixed beds. From 1985 to 1989 tourist | ||
| 122 | development has led to the creation of new beaches and the | 122 | development has led to the creation of new beaches and the | ||
| 123 | installation of artificial rocky structures for retaining sediments. | 123 | installation of artificial rocky structures for retaining sediments. | ||
| 124 | Dredging for the extraction of sand and subsequent pumping altered | 124 | Dredging for the extraction of sand and subsequent pumping altered | ||
| 125 | sediment characteristics causing a real stress leading to the | 125 | sediment characteristics causing a real stress leading to the | ||
| 126 | substitution of typical sandy bottoms communities with Cymodocea | 126 | substitution of typical sandy bottoms communities with Cymodocea | ||
| 127 | nodosa by Caulerpa prolifera communities on mud. Soft bottom fish | 127 | nodosa by Caulerpa prolifera communities on mud. Soft bottom fish | ||
| 128 | assemblages responded to changes in vegetation cover and substratum | 128 | assemblages responded to changes in vegetation cover and substratum | ||
| 129 | characteristics mainly changing the spe\u0002cies composition, while | 129 | characteristics mainly changing the spe\u0002cies composition, while | ||
| 130 | artificial hard substrata contain a similar fish community than | 130 | artificial hard substrata contain a similar fish community than | ||
| 131 | natural ones, harbouring even richer and more diverse assemblages. | 131 | natural ones, harbouring even richer and more diverse assemblages. | ||
| 132 | This positive effect of breakwaters should not obscure their likely | 132 | This positive effect of breakwaters should not obscure their likely | ||
| 133 | negative effects on hydrodynamics and the sub\u0002sequent changes of | 133 | negative effects on hydrodynamics and the sub\u0002sequent changes of | ||
| 134 | sediment quality and vegetation cover on the breakwaters\u0002 area of | 134 | sediment quality and vegetation cover on the breakwaters\u0002 area of | ||
| 135 | influence. \u0002 2005 Elsevier Ltd. All rights reserved." | 135 | influence. \u0002 2005 Elsevier Ltd. All rights reserved." | ||
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| 269 | "uri": | 240 | "uri": | ||
| 270 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | 241 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | ||
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| 272 | ], | 243 | ], | ||
| 273 | "spatial_uri": | 244 | "spatial_uri": | ||
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| 275 | "state": "active", | 246 | "state": "active", | ||
| 276 | "study_variables": { | 247 | "study_variables": { | ||
| 277 | "es": "" | 248 | "es": "" | ||
| 278 | }, | 249 | }, | ||
| 279 | "tag_uri": [ | 250 | "tag_uri": [ | ||
| 280 | 251 | ||||
| 281 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 252 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 282 | ], | 253 | ], | ||
| 283 | "tags": [ | 254 | "tags": [ | ||
| 284 | { | 255 | { | ||
| 285 | "display_name": "habitats", | 256 | "display_name": "habitats", | ||
| 286 | "id": "5d75ced3-7300-46a6-85cb-464f2694d183", | 257 | "id": "5d75ced3-7300-46a6-85cb-464f2694d183", | ||
| 287 | "name": "habitats", | 258 | "name": "habitats", | ||
| 288 | "state": "active", | 259 | "state": "active", | ||
| 289 | "vocabulary_id": null | 260 | "vocabulary_id": null | ||
| 290 | }, | 261 | }, | ||
| 291 | { | 262 | { | ||
| 292 | "display_name": "impacto_ambiental", | 263 | "display_name": "impacto_ambiental", | ||
| 293 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | 264 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | ||
| 294 | "name": "impacto_ambiental", | 265 | "name": "impacto_ambiental", | ||
| 295 | "state": "active", | 266 | "state": "active", | ||
| 296 | "vocabulary_id": null | 267 | "vocabulary_id": null | ||
| 297 | }, | 268 | }, | ||
| 298 | { | 269 | { | ||
| 299 | "display_name": "lagunas-costeras-salobres-saladas", | 270 | "display_name": "lagunas-costeras-salobres-saladas", | ||
| 300 | "id": "92dd4d50-2752-4df9-8eeb-64128064bda8", | 271 | "id": "92dd4d50-2752-4df9-8eeb-64128064bda8", | ||
| 301 | "name": "lagunas-costeras-salobres-saladas", | 272 | "name": "lagunas-costeras-salobres-saladas", | ||
| 302 | "state": "active", | 273 | "state": "active", | ||
| 303 | "vocabulary_id": null | 274 | "vocabulary_id": null | ||
| 304 | }, | 275 | }, | ||
| 305 | { | 276 | { | ||
| 306 | "display_name": "marino", | 277 | "display_name": "marino", | ||
| 307 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 278 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 308 | "name": "marino", | 279 | "name": "marino", | ||
| 309 | "state": "active", | 280 | "state": "active", | ||
| 310 | "vocabulary_id": null | 281 | "vocabulary_id": null | ||
| 311 | }, | 282 | }, | ||
| 312 | { | 283 | { | ||
| 313 | "display_name": "peces", | 284 | "display_name": "peces", | ||
| 314 | "id": "f9d27297-868e-4f22-9db0-790db7820b41", | 285 | "id": "f9d27297-868e-4f22-9db0-790db7820b41", | ||
| 315 | "name": "peces", | 286 | "name": "peces", | ||
| 316 | "state": "active", | 287 | "state": "active", | ||
| 317 | "vocabulary_id": null | 288 | "vocabulary_id": null | ||
| 318 | } | 289 | } | ||
| 319 | ], | 290 | ], | ||
| 320 | "thematic_area": [ | 291 | "thematic_area": [ | ||
| 321 | "espacios_protegidos" | 292 | "espacios_protegidos" | ||
| 322 | ], | 293 | ], | ||
| 323 | "theme_es": [ | 294 | "theme_es": [ | ||
| 324 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 295 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 325 | ], | 296 | ], | ||
| 326 | "title": "Changes in benthic fish assemblages as a consequence of | 297 | "title": "Changes in benthic fish assemblages as a consequence of | ||
| 327 | coastal works in a coastal lagoon: The Mar Menor (Spain, Western | 298 | coastal works in a coastal lagoon: The Mar Menor (Spain, Western | ||
| 328 | Mediterranean)", | 299 | Mediterranean)", | ||
| 329 | "title_translated": { | 300 | "title_translated": { | ||
| 330 | "es": "Changes in benthic fish assemblages as a consequence of | 301 | "es": "Changes in benthic fish assemblages as a consequence of | ||
| 331 | coastal works in a coastal lagoon: The Mar Menor (Spain, Western | 302 | coastal works in a coastal lagoon: The Mar Menor (Spain, Western | ||
| 332 | Mediterranean)" | 303 | Mediterranean)" | ||
| 333 | }, | 304 | }, | ||
| 334 | "topic": | 305 | "topic": | ||
| 335 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 306 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 336 | "type": "dataset", | 307 | "type": "dataset", | ||
| 337 | "url": | 308 | "url": | ||
| 338 | //iepnb.es:443/catalogo/dataset/86d52d13-19c4-5cd7-9ef3-acb47ff273e8", | 309 | //iepnb.es:443/catalogo/dataset/86d52d13-19c4-5cd7-9ef3-acb47ff273e8", | ||
| 339 | "version_notes": { | 310 | "version_notes": { | ||
| 340 | "es": "" | 311 | "es": "" | ||
| 341 | } | 312 | } | ||
| 342 | } | 313 | } |