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En el instante 23 de junio de 2026, 15:59:50 UTC,
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Modificado el valor del campo
spatial_coverage
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en When liming and revegetation contribute to the mobilisation of metals: Learning lessons for the phytomanagement of metal-polluted wetlands
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| 95 | "notes": "The aim of this study was to identify the effectiveness of | 95 | "notes": "The aim of this study was to identify the effectiveness of | ||
| 96 | liming in combination with vegetation for the recovery of slightly | 96 | liming in combination with vegetation for the recovery of slightly | ||
| 97 | acidic, saline soils of eutrophic wetlands affected by mine wastes, | 97 | acidic, saline soils of eutrophic wetlands affected by mine wastes, | ||
| 98 | under fluctuating flooding conditions. Simulated soil profiles were | 98 | under fluctuating flooding conditions. Simulated soil profiles were | ||
| 99 | constructed and four treatments were assayed under greenhouse | 99 | constructed and four treatments were assayed under greenhouse | ||
| 100 | conditions: control, only plant, only liming, and liming and plant. | 100 | conditions: control, only plant, only liming, and liming and plant. | ||
| 101 | The plant species was the halophyte Sarcocornia fruticosa. Three | 101 | The plant species was the halophyte Sarcocornia fruticosa. Three | ||
| 102 | horizons were differentiated: A (never under water), C1 (alter nating | 102 | horizons were differentiated: A (never under water), C1 (alter nating | ||
| 103 | flooding-drying conditions), and C2 (always under water). The pH, Eh, | 103 | flooding-drying conditions), and C2 (always under water). The pH, Eh, | ||
| 104 | salinity, and the concen trations of dissolved organic carbon and | 104 | salinity, and the concen trations of dissolved organic carbon and | ||
| 105 | soluble metals were measured regularly for 18 weeks. Liming favoured | 105 | soluble metals were measured regularly for 18 weeks. Liming favoured | ||
| 106 | the growth of S. fruticosa, an increase in pH and a fall in Eh. The | 106 | the growth of S. fruticosa, an increase in pH and a fall in Eh. The | ||
| 107 | amendment was effective for reducing Mn, Zn, and Cd in pore water of | 107 | amendment was effective for reducing Mn, Zn, and Cd in pore water of | ||
| 108 | bare soils, but not Cu and Pb. In the treatment with liming and plant, | 108 | bare soils, but not Cu and Pb. In the treatment with liming and plant, | ||
| 109 | the growth of S. fruticosa counteracted the effect of the amendment, | 109 | the growth of S. fruticosa counteracted the effect of the amendment, | ||
| 110 | strongly increasing the concentrations of metals in pore water and | 110 | strongly increasing the concentrations of metals in pore water and | ||
| 111 | distributing them along the soil profile. Hence, the combined use of | 111 | distributing them along the soil profile. Hence, the combined use of | ||
| 112 | liming and plants may increase the risk of metals mobilisation.", | 112 | liming and plants may increase the risk of metals mobilisation.", | ||
| 113 | "notes_translated": { | 113 | "notes_translated": { | ||
| 114 | "es": "The aim of this study was to identify the effectiveness of | 114 | "es": "The aim of this study was to identify the effectiveness of | ||
| 115 | liming in combination with vegetation for the recovery of slightly | 115 | liming in combination with vegetation for the recovery of slightly | ||
| 116 | acidic, saline soils of eutrophic wetlands affected by mine wastes, | 116 | acidic, saline soils of eutrophic wetlands affected by mine wastes, | ||
| 117 | under fluctuating flooding conditions. Simulated soil profiles were | 117 | under fluctuating flooding conditions. Simulated soil profiles were | ||
| 118 | constructed and four treatments were assayed under greenhouse | 118 | constructed and four treatments were assayed under greenhouse | ||
| 119 | conditions: control, only plant, only liming, and liming and plant. | 119 | conditions: control, only plant, only liming, and liming and plant. | ||
| 120 | The plant species was the halophyte Sarcocornia fruticosa. Three | 120 | The plant species was the halophyte Sarcocornia fruticosa. Three | ||
| 121 | horizons were differentiated: A (never under water), C1 (alter nating | 121 | horizons were differentiated: A (never under water), C1 (alter nating | ||
| 122 | flooding-drying conditions), and C2 (always under water). The pH, Eh, | 122 | flooding-drying conditions), and C2 (always under water). The pH, Eh, | ||
| 123 | salinity, and the concen trations of dissolved organic carbon and | 123 | salinity, and the concen trations of dissolved organic carbon and | ||
| 124 | soluble metals were measured regularly for 18 weeks. Liming favoured | 124 | soluble metals were measured regularly for 18 weeks. Liming favoured | ||
| 125 | the growth of S. fruticosa, an increase in pH and a fall in Eh. The | 125 | the growth of S. fruticosa, an increase in pH and a fall in Eh. The | ||
| 126 | amendment was effective for reducing Mn, Zn, and Cd in pore water of | 126 | amendment was effective for reducing Mn, Zn, and Cd in pore water of | ||
| 127 | bare soils, but not Cu and Pb. In the treatment with liming and plant, | 127 | bare soils, but not Cu and Pb. In the treatment with liming and plant, | ||
| 128 | the growth of S. fruticosa counteracted the effect of the amendment, | 128 | the growth of S. fruticosa counteracted the effect of the amendment, | ||
| 129 | strongly increasing the concentrations of metals in pore water and | 129 | strongly increasing the concentrations of metals in pore water and | ||
| 130 | distributing them along the soil profile. Hence, the combined use of | 130 | distributing them along the soil profile. Hence, the combined use of | ||
| 131 | liming and plants may increase the risk of metals mobilisation." | 131 | liming and plants may increase the risk of metals mobilisation." | ||
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| 277 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 248 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
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| 290 | "name": "eutrofizacion", | 261 | "name": "eutrofizacion", | ||
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| 310 | "id": "6e4b1d4d-e9a1-4e79-9f81-387ce2265097", | 281 | "id": "6e4b1d4d-e9a1-4e79-9f81-387ce2265097", | ||
| 311 | "name": "nutrientes", | 282 | "name": "nutrientes", | ||
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| 317 | "id": "f76a3cbe-6d1e-43dd-8c8b-d901aedbbb4a", | 288 | "id": "f76a3cbe-6d1e-43dd-8c8b-d901aedbbb4a", | ||
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| 320 | "vocabulary_id": null | 291 | "vocabulary_id": null | ||
| 321 | }, | 292 | }, | ||
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| 324 | "id": "ddd64fbe-63d9-4624-a38d-30754e273d0a", | 295 | "id": "ddd64fbe-63d9-4624-a38d-30754e273d0a", | ||
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| 326 | "state": "active", | 297 | "state": "active", | ||
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| 328 | } | 299 | } | ||
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| 331 | "espacios_protegidos" | 302 | "espacios_protegidos" | ||
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| 334 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 305 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 335 | ], | 306 | ], | ||
| 336 | "title": "When liming and revegetation contribute to the | 307 | "title": "When liming and revegetation contribute to the | ||
| 337 | mobilisation of metals: Learning lessons for the phytomanagement of | 308 | mobilisation of metals: Learning lessons for the phytomanagement of | ||
| 338 | metal-polluted wetlands", | 309 | metal-polluted wetlands", | ||
| 339 | "title_translated": { | 310 | "title_translated": { | ||
| 340 | "es": "When liming and revegetation contribute to the mobilisation | 311 | "es": "When liming and revegetation contribute to the mobilisation | ||
| 341 | of metals: Learning lessons for the phytomanagement of metal-polluted | 312 | of metals: Learning lessons for the phytomanagement of metal-polluted | ||
| 342 | wetlands" | 313 | wetlands" | ||
| 343 | }, | 314 | }, | ||
| 344 | "topic": | 315 | "topic": | ||
| 345 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 316 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 346 | "type": "dataset", | 317 | "type": "dataset", | ||
| 347 | "url": | 318 | "url": | ||
| 348 | //iepnb.es:443/catalogo/dataset/c5cef28d-26ae-5ed1-af19-f542ca4ae2ac", | 319 | //iepnb.es:443/catalogo/dataset/c5cef28d-26ae-5ed1-af19-f542ca4ae2ac", | ||
| 349 | "version_notes": { | 320 | "version_notes": { | ||
| 350 | "es": "" | 321 | "es": "" | ||
| 351 | } | 322 | } | ||
| 352 | } | 323 | } |