Cambios
En el instante 23 de junio de 2026, 16:06:50 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Rhizosphere and flooding regime as key factors for the mobilisation of arsenic and potentially harmful metals in basic, mining-polluted salt marsh soils
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| 99 | "notes": "The occurrence of mining areas in the vicinities of salt | 99 | "notes": "The occurrence of mining areas in the vicinities of salt | ||
| 100 | marshes may affect their ecological functions and facilitate the | 100 | marshes may affect their ecological functions and facilitate the | ||
| 101 | transfer of pollutants into the food chain. The mobilisation of metals | 101 | transfer of pollutants into the food chain. The mobilisation of metals | ||
| 102 | in salt marsh soils is controlled by abiotic (pH, redox potential) and | 102 | in salt marsh soils is controlled by abiotic (pH, redox potential) and | ||
| 103 | biotic (influence of rhizosphere) factors. The effect of the | 103 | biotic (influence of rhizosphere) factors. The effect of the | ||
| 104 | rhizosphere of two plant species (Sarcocornia fruticosa and Phragmites | 104 | rhizosphere of two plant species (Sarcocornia fruticosa and Phragmites | ||
| 105 | australis) and different flooding regimes on potentially harmful | 105 | australis) and different flooding regimes on potentially harmful | ||
| 106 | metals and As mobilisation from salt marsh soil polluted by mining | 106 | metals and As mobilisation from salt marsh soil polluted by mining | ||
| 107 | activ ities were investigated (total concentrations: 536 mg kg 1 As, | 107 | activ ities were investigated (total concentrations: 536 mg kg 1 As, | ||
| 108 | 37 mg kg 1 Cd, 6746 mg kg 1 Pb, 15,320 mg kg 1 Zn). The results show | 108 | 37 mg kg 1 Cd, 6746 mg kg 1 Pb, 15,320 mg kg 1 Zn). The results show | ||
| 109 | that the changes in redox conditions (from 300 mV to 100 mV) and pH | 109 | that the changes in redox conditions (from 300 mV to 100 mV) and pH | ||
| 110 | after flooding and rewetting periods may mobilise the contaminant | 110 | after flooding and rewetting periods may mobilise the contaminant | ||
| 111 | elements into soil solution (e.g., 100 lg L 1 Cd, 30 lg L 1 Pb, 7 mg L | 111 | elements into soil solution (e.g., 100 lg L 1 Cd, 30 lg L 1 Pb, 7 mg L | ||
| 112 | 1 Zn), where they are available for plants or may be leached from the | 112 | 1 Zn), where they are available for plants or may be leached from the | ||
| 113 | soil. Drying periods generated peaks of concentrations in the soil | 113 | soil. Drying periods generated peaks of concentrations in the soil | ||
| 114 | solution (up to 120 lg L 1 Cd and 50 lg L 1 Pb). The risk assessment | 114 | solution (up to 120 lg L 1 Cd and 50 lg L 1 Pb). The risk assessment | ||
| 115 | of As and metal-polluted salt marshes should take into account flood | 115 | of As and metal-polluted salt marshes should take into account flood | ||
| 116 | dynamics in order to prevent metal(loid) mobilisation.", | 116 | dynamics in order to prevent metal(loid) mobilisation.", | ||
| 117 | "notes_translated": { | 117 | "notes_translated": { | ||
| 118 | "es": "The occurrence of mining areas in the vicinities of salt | 118 | "es": "The occurrence of mining areas in the vicinities of salt | ||
| 119 | marshes may affect their ecological functions and facilitate the | 119 | marshes may affect their ecological functions and facilitate the | ||
| 120 | transfer of pollutants into the food chain. The mobilisation of metals | 120 | transfer of pollutants into the food chain. The mobilisation of metals | ||
| 121 | in salt marsh soils is controlled by abiotic (pH, redox potential) and | 121 | in salt marsh soils is controlled by abiotic (pH, redox potential) and | ||
| 122 | biotic (influence of rhizosphere) factors. The effect of the | 122 | biotic (influence of rhizosphere) factors. The effect of the | ||
| 123 | rhizosphere of two plant species (Sarcocornia fruticosa and Phragmites | 123 | rhizosphere of two plant species (Sarcocornia fruticosa and Phragmites | ||
| 124 | australis) and different flooding regimes on potentially harmful | 124 | australis) and different flooding regimes on potentially harmful | ||
| 125 | metals and As mobilisation from salt marsh soil polluted by mining | 125 | metals and As mobilisation from salt marsh soil polluted by mining | ||
| 126 | activ ities were investigated (total concentrations: 536 mg kg 1 As, | 126 | activ ities were investigated (total concentrations: 536 mg kg 1 As, | ||
| 127 | 37 mg kg 1 Cd, 6746 mg kg 1 Pb, 15,320 mg kg 1 Zn). The results show | 127 | 37 mg kg 1 Cd, 6746 mg kg 1 Pb, 15,320 mg kg 1 Zn). The results show | ||
| 128 | that the changes in redox conditions (from 300 mV to 100 mV) and pH | 128 | that the changes in redox conditions (from 300 mV to 100 mV) and pH | ||
| 129 | after flooding and rewetting periods may mobilise the contaminant | 129 | after flooding and rewetting periods may mobilise the contaminant | ||
| 130 | elements into soil solution (e.g., 100 lg L 1 Cd, 30 lg L 1 Pb, 7 mg L | 130 | elements into soil solution (e.g., 100 lg L 1 Cd, 30 lg L 1 Pb, 7 mg L | ||
| 131 | 1 Zn), where they are available for plants or may be leached from the | 131 | 1 Zn), where they are available for plants or may be leached from the | ||
| 132 | soil. Drying periods generated peaks of concentrations in the soil | 132 | soil. Drying periods generated peaks of concentrations in the soil | ||
| 133 | solution (up to 120 lg L 1 Cd and 50 lg L 1 Pb). The risk assessment | 133 | solution (up to 120 lg L 1 Cd and 50 lg L 1 Pb). The risk assessment | ||
| 134 | of As and metal-polluted salt marshes should take into account flood | 134 | of As and metal-polluted salt marshes should take into account flood | ||
| 135 | dynamics in order to prevent metal(loid) mobilisation." | 135 | dynamics in order to prevent metal(loid) mobilisation." | ||
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| 269 | "uri": | 240 | "uri": | ||
| 270 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 241 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 271 | } | 242 | } | ||
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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": "acidificacion", | 256 | "display_name": "acidificacion", | ||
| 286 | "id": "580f79ea-fe82-4c5f-81d1-74c9d2f6c2a0", | 257 | "id": "580f79ea-fe82-4c5f-81d1-74c9d2f6c2a0", | ||
| 287 | "name": "acidificacion", | 258 | "name": "acidificacion", | ||
| 288 | "state": "active", | 259 | "state": "active", | ||
| 289 | "vocabulary_id": null | 260 | "vocabulary_id": null | ||
| 290 | }, | 261 | }, | ||
| 291 | { | 262 | { | ||
| 292 | "display_name": "agricultura", | 263 | "display_name": "agricultura", | ||
| 293 | "id": "34809f0c-ffb1-4169-a701-6e9b9b10278b", | 264 | "id": "34809f0c-ffb1-4169-a701-6e9b9b10278b", | ||
| 294 | "name": "agricultura", | 265 | "name": "agricultura", | ||
| 295 | "state": "active", | 266 | "state": "active", | ||
| 296 | "vocabulary_id": null | 267 | "vocabulary_id": null | ||
| 297 | }, | 268 | }, | ||
| 298 | { | 269 | { | ||
| 299 | "display_name": "contaminacion", | 270 | "display_name": "contaminacion", | ||
| 300 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 271 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 301 | "name": "contaminacion", | 272 | "name": "contaminacion", | ||
| 302 | "state": "active", | 273 | "state": "active", | ||
| 303 | "vocabulary_id": null | 274 | "vocabulary_id": null | ||
| 304 | }, | 275 | }, | ||
| 305 | { | 276 | { | ||
| 306 | "display_name": "degradacion", | 277 | "display_name": "degradacion", | ||
| 307 | "id": "81475918-96ad-426c-adfa-98dee207c4b4", | 278 | "id": "81475918-96ad-426c-adfa-98dee207c4b4", | ||
| 308 | "name": "degradacion", | 279 | "name": "degradacion", | ||
| 309 | "state": "active", | 280 | "state": "active", | ||
| 310 | "vocabulary_id": null | 281 | "vocabulary_id": null | ||
| 311 | }, | 282 | }, | ||
| 312 | { | 283 | { | ||
| 313 | "display_name": "humedales", | 284 | "display_name": "humedales", | ||
| 314 | "id": "649ff5bb-8f7c-45ae-8cda-3aaf630a2857", | 285 | "id": "649ff5bb-8f7c-45ae-8cda-3aaf630a2857", | ||
| 315 | "name": "humedales", | 286 | "name": "humedales", | ||
| 316 | "state": "active", | 287 | "state": "active", | ||
| 317 | "vocabulary_id": null | 288 | "vocabulary_id": null | ||
| 318 | }, | 289 | }, | ||
| 319 | { | 290 | { | ||
| 320 | "display_name": "impacto_ambiental", | 291 | "display_name": "impacto_ambiental", | ||
| 321 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | 292 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | ||
| 322 | "name": "impacto_ambiental", | 293 | "name": "impacto_ambiental", | ||
| 323 | "state": "active", | 294 | "state": "active", | ||
| 324 | "vocabulary_id": null | 295 | "vocabulary_id": null | ||
| 325 | }, | 296 | }, | ||
| 326 | { | 297 | { | ||
| 327 | "display_name": "marino", | 298 | "display_name": "marino", | ||
| 328 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 299 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 329 | "name": "marino", | 300 | "name": "marino", | ||
| 330 | "state": "active", | 301 | "state": "active", | ||
| 331 | "vocabulary_id": null | 302 | "vocabulary_id": null | ||
| 332 | }, | 303 | }, | ||
| 333 | { | 304 | { | ||
| 334 | "display_name": "mineria", | 305 | "display_name": "mineria", | ||
| 335 | "id": "5a92f26e-1b91-495c-99a2-dcd469828003", | 306 | "id": "5a92f26e-1b91-495c-99a2-dcd469828003", | ||
| 336 | "name": "mineria", | 307 | "name": "mineria", | ||
| 337 | "state": "active", | 308 | "state": "active", | ||
| 338 | "vocabulary_id": null | 309 | "vocabulary_id": null | ||
| 339 | }, | 310 | }, | ||
| 340 | { | 311 | { | ||
| 341 | "display_name": "suelo", | 312 | "display_name": "suelo", | ||
| 342 | "id": "ddd64fbe-63d9-4624-a38d-30754e273d0a", | 313 | "id": "ddd64fbe-63d9-4624-a38d-30754e273d0a", | ||
| 343 | "name": "suelo", | 314 | "name": "suelo", | ||
| 344 | "state": "active", | 315 | "state": "active", | ||
| 345 | "vocabulary_id": null | 316 | "vocabulary_id": null | ||
| 346 | } | 317 | } | ||
| 347 | ], | 318 | ], | ||
| 348 | "thematic_area": [ | 319 | "thematic_area": [ | ||
| 349 | "espacios_protegidos" | 320 | "espacios_protegidos" | ||
| 350 | ], | 321 | ], | ||
| 351 | "theme_es": [ | 322 | "theme_es": [ | ||
| 352 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 323 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 353 | ], | 324 | ], | ||
| 354 | "title": "Rhizosphere and flooding regime as key factors for the | 325 | "title": "Rhizosphere and flooding regime as key factors for the | ||
| 355 | mobilisation of arsenic and potentially harmful metals in basic, | 326 | mobilisation of arsenic and potentially harmful metals in basic, | ||
| 356 | mining-polluted salt marsh soils", | 327 | mining-polluted salt marsh soils", | ||
| 357 | "title_translated": { | 328 | "title_translated": { | ||
| 358 | "es": "Rhizosphere and flooding regime as key factors for the | 329 | "es": "Rhizosphere and flooding regime as key factors for the | ||
| 359 | mobilisation of arsenic and potentially harmful metals in basic, | 330 | mobilisation of arsenic and potentially harmful metals in basic, | ||
| 360 | mining-polluted salt marsh soils" | 331 | mining-polluted salt marsh soils" | ||
| 361 | }, | 332 | }, | ||
| 362 | "topic": | 333 | "topic": | ||
| 363 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 334 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 364 | "type": "dataset", | 335 | "type": "dataset", | ||
| 365 | "url": | 336 | "url": | ||
| 366 | //iepnb.es:443/catalogo/dataset/67dff52d-05f8-57e0-aaff-fbd6475d5791", | 337 | //iepnb.es:443/catalogo/dataset/67dff52d-05f8-57e0-aaff-fbd6475d5791", | ||
| 367 | "version_notes": { | 338 | "version_notes": { | ||
| 368 | "es": "" | 339 | "es": "" | ||
| 369 | } | 340 | } | ||
| 370 | } | 341 | } |