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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 Phosphorus fractionation and distribution in salt marsh soils affected by mine wastes and eutrophicated water: A case study in SE Spain
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| 95 | "notes": "The study aimed to establish the distribution and fate of | 95 | "notes": "The study aimed to establish the distribution and fate of | ||
| 96 | phosphorus in the soils of a coastal salt marsh affected by mine | 96 | phosphorus in the soils of a coastal salt marsh affected by mine | ||
| 97 | wastes and wastewater effluents. Water samples from two watercourses | 97 | wastes and wastewater effluents. Water samples from two watercourses | ||
| 98 | were analysed for soluble phosphorus and dissolved organic carbon and | 98 | were analysed for soluble phosphorus and dissolved organic carbon and | ||
| 99 | soil samples within the marsh were analysed for total P, Fe, N and | 99 | soil samples within the marsh were analysed for total P, Fe, N and | ||
| 100 | CaCO3. In addition, a fractionation of the phosphorus was performed. | 100 | CaCO3. In addition, a fractionation of the phosphorus was performed. | ||
| 101 | The results indicate that high concentrations of soluble phosphorus | 101 | The results indicate that high concentrations of soluble phosphorus | ||
| 102 | (up to 12.3 mg PO43\u2212P L\u22121) and dissolved organic carbon (up | 102 | (up to 12.3 mg PO43\u2212P L\u22121) and dissolved organic carbon (up | ||
| 103 | to 36.5 mg L\u22121) flowed from one of the watercourses into the salt | 103 | to 36.5 mg L\u22121) flowed from one of the watercourses into the salt | ||
| 104 | marsh. Organic residual P was the most abundant P form in the soils, | 104 | marsh. Organic residual P was the most abundant P form in the soils, | ||
| 105 | constituting between 38.6 and 76.6% of the total P, whereas P | 105 | constituting between 38.6 and 76.6% of the total P, whereas P | ||
| 106 | associated with humic acids was less abundant (less than 3%). Among | 106 | associated with humic acids was less abundant (less than 3%). Among | ||
| 107 | the mineral soil components, Ca and Mg compounds were the most active | 107 | the mineral soil components, Ca and Mg compounds were the most active | ||
| 108 | in phosphorus retention (up to 50% of the total P), except in the | 108 | in phosphorus retention (up to 50% of the total P), except in the | ||
| 109 | plots most affected by mine wastes. In the latter sites, the highest | 109 | plots most affected by mine wastes. In the latter sites, the highest | ||
| 110 | Fe(up to 247 g kg\u22121) and the lowest CaCO3 (8.9 g kg\u22121) | 110 | Fe(up to 247 g kg\u22121) and the lowest CaCO3 (8.9 g kg\u22121) | ||
| 111 | concentrations were obtained, and Fe- and Al-bound P was the most | 111 | concentrations were obtained, and Fe- and Al-bound P was the most | ||
| 112 | abundant fraction, reaching 23.9% of the total P. Unusually low total | 112 | abundant fraction, reaching 23.9% of the total P. Unusually low total | ||
| 113 | nitrogen/total phosphorus ratios (between 5.4 and 5.7) showed that | 113 | nitrogen/total phosphorus ratios (between 5.4 and 5.7) showed that | ||
| 114 | marsh areas affected by wastewater effluents are acting as phosphorus | 114 | marsh areas affected by wastewater effluents are acting as phosphorus | ||
| 115 | sinks.", | 115 | sinks.", | ||
| 116 | "notes_translated": { | 116 | "notes_translated": { | ||
| 117 | "es": "The study aimed to establish the distribution and fate of | 117 | "es": "The study aimed to establish the distribution and fate of | ||
| 118 | phosphorus in the soils of a coastal salt marsh affected by mine | 118 | phosphorus in the soils of a coastal salt marsh affected by mine | ||
| 119 | wastes and wastewater effluents. Water samples from two watercourses | 119 | wastes and wastewater effluents. Water samples from two watercourses | ||
| 120 | were analysed for soluble phosphorus and dissolved organic carbon and | 120 | were analysed for soluble phosphorus and dissolved organic carbon and | ||
| 121 | soil samples within the marsh were analysed for total P, Fe, N and | 121 | soil samples within the marsh were analysed for total P, Fe, N and | ||
| 122 | CaCO3. In addition, a fractionation of the phosphorus was performed. | 122 | CaCO3. In addition, a fractionation of the phosphorus was performed. | ||
| 123 | The results indicate that high concentrations of soluble phosphorus | 123 | The results indicate that high concentrations of soluble phosphorus | ||
| 124 | (up to 12.3 mg PO43\u2212P L\u22121) and dissolved organic carbon (up | 124 | (up to 12.3 mg PO43\u2212P L\u22121) and dissolved organic carbon (up | ||
| 125 | to 36.5 mg L\u22121) flowed from one of the watercourses into the salt | 125 | to 36.5 mg L\u22121) flowed from one of the watercourses into the salt | ||
| 126 | marsh. Organic residual P was the most abundant P form in the soils, | 126 | marsh. Organic residual P was the most abundant P form in the soils, | ||
| 127 | constituting between 38.6 and 76.6% of the total P, whereas P | 127 | constituting between 38.6 and 76.6% of the total P, whereas P | ||
| 128 | associated with humic acids was less abundant (less than 3%). Among | 128 | associated with humic acids was less abundant (less than 3%). Among | ||
| 129 | the mineral soil components, Ca and Mg compounds were the most active | 129 | the mineral soil components, Ca and Mg compounds were the most active | ||
| 130 | in phosphorus retention (up to 50% of the total P), except in the | 130 | in phosphorus retention (up to 50% of the total P), except in the | ||
| 131 | plots most affected by mine wastes. In the latter sites, the highest | 131 | plots most affected by mine wastes. In the latter sites, the highest | ||
| 132 | Fe(up to 247 g kg\u22121) and the lowest CaCO3 (8.9 g kg\u22121) | 132 | Fe(up to 247 g kg\u22121) and the lowest CaCO3 (8.9 g kg\u22121) | ||
| 133 | concentrations were obtained, and Fe- and Al-bound P was the most | 133 | concentrations were obtained, and Fe- and Al-bound P was the most | ||
| 134 | abundant fraction, reaching 23.9% of the total P. Unusually low total | 134 | abundant fraction, reaching 23.9% of the total P. Unusually low total | ||
| 135 | nitrogen/total phosphorus ratios (between 5.4 and 5.7) showed that | 135 | nitrogen/total phosphorus ratios (between 5.4 and 5.7) showed that | ||
| 136 | marsh areas affected by wastewater effluents are acting as phosphorus | 136 | marsh areas affected by wastewater effluents are acting as phosphorus | ||
| 137 | sinks." | 137 | sinks." | ||
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| 271 | "uri": | 242 | "uri": | ||
| 272 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | 243 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | ||
| 273 | } | 244 | } | ||
| 274 | ], | 245 | ], | ||
| 275 | "spatial_uri": | 246 | "spatial_uri": | ||
| 276 | tos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia", | 247 | tos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia", | ||
| 277 | "state": "active", | 248 | "state": "active", | ||
| 278 | "study_variables": { | 249 | "study_variables": { | ||
| 279 | "es": "" | 250 | "es": "" | ||
| 280 | }, | 251 | }, | ||
| 281 | "tag_uri": [ | 252 | "tag_uri": [ | ||
| 282 | 253 | ||||
| 283 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 254 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 284 | ], | 255 | ], | ||
| 285 | "tags": [ | 256 | "tags": [ | ||
| 286 | { | 257 | { | ||
| 287 | "display_name": "contaminacion", | 258 | "display_name": "contaminacion", | ||
| 288 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 259 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 289 | "name": "contaminacion", | 260 | "name": "contaminacion", | ||
| 290 | "state": "active", | 261 | "state": "active", | ||
| 291 | "vocabulary_id": null | 262 | "vocabulary_id": null | ||
| 292 | }, | 263 | }, | ||
| 293 | { | 264 | { | ||
| 294 | "display_name": "eutrofizacion", | 265 | "display_name": "eutrofizacion", | ||
| 295 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | 266 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | ||
| 296 | "name": "eutrofizacion", | 267 | "name": "eutrofizacion", | ||
| 297 | "state": "active", | 268 | "state": "active", | ||
| 298 | "vocabulary_id": null | 269 | "vocabulary_id": null | ||
| 299 | }, | 270 | }, | ||
| 300 | { | 271 | { | ||
| 301 | "display_name": "marino", | 272 | "display_name": "marino", | ||
| 302 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 273 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 303 | "name": "marino", | 274 | "name": "marino", | ||
| 304 | "state": "active", | 275 | "state": "active", | ||
| 305 | "vocabulary_id": null | 276 | "vocabulary_id": null | ||
| 306 | }, | 277 | }, | ||
| 307 | { | 278 | { | ||
| 308 | "display_name": "nutrientes", | 279 | "display_name": "nutrientes", | ||
| 309 | "id": "6e4b1d4d-e9a1-4e79-9f81-387ce2265097", | 280 | "id": "6e4b1d4d-e9a1-4e79-9f81-387ce2265097", | ||
| 310 | "name": "nutrientes", | 281 | "name": "nutrientes", | ||
| 311 | "state": "active", | 282 | "state": "active", | ||
| 312 | "vocabulary_id": null | 283 | "vocabulary_id": null | ||
| 313 | }, | 284 | }, | ||
| 314 | { | 285 | { | ||
| 315 | "display_name": "suelo", | 286 | "display_name": "suelo", | ||
| 316 | "id": "ddd64fbe-63d9-4624-a38d-30754e273d0a", | 287 | "id": "ddd64fbe-63d9-4624-a38d-30754e273d0a", | ||
| 317 | "name": "suelo", | 288 | "name": "suelo", | ||
| 318 | "state": "active", | 289 | "state": "active", | ||
| 319 | "vocabulary_id": null | 290 | "vocabulary_id": null | ||
| 320 | } | 291 | } | ||
| 321 | ], | 292 | ], | ||
| 322 | "thematic_area": [ | 293 | "thematic_area": [ | ||
| 323 | "espacios_protegidos" | 294 | "espacios_protegidos" | ||
| 324 | ], | 295 | ], | ||
| 325 | "theme_es": [ | 296 | "theme_es": [ | ||
| 326 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 297 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 327 | ], | 298 | ], | ||
| 328 | "title": "Phosphorus fractionation and distribution in salt marsh | 299 | "title": "Phosphorus fractionation and distribution in salt marsh | ||
| 329 | soils affected by mine wastes and eutrophicated water: A case study in | 300 | soils affected by mine wastes and eutrophicated water: A case study in | ||
| 330 | SE Spain", | 301 | SE Spain", | ||
| 331 | "title_translated": { | 302 | "title_translated": { | ||
| 332 | "es": "Phosphorus fractionation and distribution in salt marsh | 303 | "es": "Phosphorus fractionation and distribution in salt marsh | ||
| 333 | soils affected by mine wastes and eutrophicated water: A case study in | 304 | soils affected by mine wastes and eutrophicated water: A case study in | ||
| 334 | SE Spain" | 305 | SE Spain" | ||
| 335 | }, | 306 | }, | ||
| 336 | "topic": | 307 | "topic": | ||
| 337 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 308 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 338 | "type": "dataset", | 309 | "type": "dataset", | ||
| 339 | "url": | 310 | "url": | ||
| 340 | //iepnb.es:443/catalogo/dataset/51b89a3a-18a9-58e2-a09b-796a0a670540", | 311 | //iepnb.es:443/catalogo/dataset/51b89a3a-18a9-58e2-a09b-796a0a670540", | ||
| 341 | "version_notes": { | 312 | "version_notes": { | ||
| 342 | "es": "" | 313 | "es": "" | ||
| 343 | } | 314 | } | ||
| 344 | } | 315 | } |