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En el instante 23 de junio de 2026, 16:06:51 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 Abandoned mine sites as a source of contamination by heavy metals: A case study in a semi-arid zone
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| 96 | "notes": "Mining and milling operations, including grinding, | 96 | "notes": "Mining and milling operations, including grinding, | ||
| 97 | concentrating ores and disposal of tailings, along with mine and mill | 97 | concentrating ores and disposal of tailings, along with mine and mill | ||
| 98 | waste water, provide obvious sources of contamination in the surface | 98 | waste water, provide obvious sources of contamination in the surface | ||
| 99 | environment. Climatic effects such as heavy rainfall events, have a | 99 | environment. Climatic effects such as heavy rainfall events, have a | ||
| 100 | great impact in the dispersion of metals in semi-arid areas, since | 100 | great impact in the dispersion of metals in semi-arid areas, since | ||
| 101 | soils are typically scarcely vegetated. The dispersion and influence | 101 | soils are typically scarcely vegetated. The dispersion and influence | ||
| 102 | of soluble and particulate metals present in the materials from an | 102 | of soluble and particulate metals present in the materials from an | ||
| 103 | abandoned mine, Cabezo Rajao, in SE Spain, was evaluated. Tailings and | 103 | abandoned mine, Cabezo Rajao, in SE Spain, was evaluated. Tailings and | ||
| 104 | soils were sampled and analysed for pH, EC, CaCO3, grainsize, | 104 | soils were sampled and analysed for pH, EC, CaCO3, grainsize, | ||
| 105 | mineralogical composition and heavy metal content, while water samples | 105 | mineralogical composition and heavy metal content, while water samples | ||
| 106 | were collected and analysed for pH, EC, soluble metals and salts. The | 106 | were collected and analysed for pH, EC, soluble metals and salts. The | ||
| 107 | mean concentrations of Pb, Zn, Cd, Cu and As in solid samples were 8.3 | 107 | mean concentrations of Pb, Zn, Cd, Cu and As in solid samples were 8.3 | ||
| 108 | g kg(-1), 12.5 g kg(-1), 40.9 mg kg(-1), 332.1 mg kg(-1), 314.7 mg | 108 | g kg(-1), 12.5 g kg(-1), 40.9 mg kg(-1), 332.1 mg kg(-1), 314.7 mg | ||
| 109 | kg(-1) respectively, and 1.5 mg l(-1), 50.3 mg l(-1), 13.6 g l(-1), | 109 | kg(-1) respectively, and 1.5 mg l(-1), 50.3 mg l(-1), 13.6 g l(-1), | ||
| 110 | 17.2 mg l(-1), 1.7 mg l(-1) in water samples respectively. These | 110 | 17.2 mg l(-1), 1.7 mg l(-1) in water samples respectively. These | ||
| 111 | metals can be dispersed downstream and downslope from the tailings by | 111 | metals can be dispersed downstream and downslope from the tailings by | ||
| 112 | water after rainfall. Soil samples collected in the surroundings of | 112 | water after rainfall. Soil samples collected in the surroundings of | ||
| 113 | Mar Menor Lagoon were analysed, reflecting the influence of the | 113 | Mar Menor Lagoon were analysed, reflecting the influence of the | ||
| 114 | transport of soluble and particulate materials from Cabezo Rajao, | 114 | transport of soluble and particulate materials from Cabezo Rajao, | ||
| 115 | especially of Pb and Zn. However, the presence of high amounts of | 115 | especially of Pb and Zn. However, the presence of high amounts of | ||
| 116 | carbonate in the soils around the mine area revealed the stabilization | 116 | carbonate in the soils around the mine area revealed the stabilization | ||
| 117 | of all the metals studied. (c) 2007 Elsevier B.V. All rights | 117 | of all the metals studied. (c) 2007 Elsevier B.V. All rights | ||
| 118 | reserved.", | 118 | reserved.", | ||
| 119 | "notes_translated": { | 119 | "notes_translated": { | ||
| 120 | "es": "Mining and milling operations, including grinding, | 120 | "es": "Mining and milling operations, including grinding, | ||
| 121 | concentrating ores and disposal of tailings, along with mine and mill | 121 | concentrating ores and disposal of tailings, along with mine and mill | ||
| 122 | waste water, provide obvious sources of contamination in the surface | 122 | waste water, provide obvious sources of contamination in the surface | ||
| 123 | environment. Climatic effects such as heavy rainfall events, have a | 123 | environment. Climatic effects such as heavy rainfall events, have a | ||
| 124 | great impact in the dispersion of metals in semi-arid areas, since | 124 | great impact in the dispersion of metals in semi-arid areas, since | ||
| 125 | soils are typically scarcely vegetated. The dispersion and influence | 125 | soils are typically scarcely vegetated. The dispersion and influence | ||
| 126 | of soluble and particulate metals present in the materials from an | 126 | of soluble and particulate metals present in the materials from an | ||
| 127 | abandoned mine, Cabezo Rajao, in SE Spain, was evaluated. Tailings and | 127 | abandoned mine, Cabezo Rajao, in SE Spain, was evaluated. Tailings and | ||
| 128 | soils were sampled and analysed for pH, EC, CaCO3, grainsize, | 128 | soils were sampled and analysed for pH, EC, CaCO3, grainsize, | ||
| 129 | mineralogical composition and heavy metal content, while water samples | 129 | mineralogical composition and heavy metal content, while water samples | ||
| 130 | were collected and analysed for pH, EC, soluble metals and salts. The | 130 | were collected and analysed for pH, EC, soluble metals and salts. The | ||
| 131 | mean concentrations of Pb, Zn, Cd, Cu and As in solid samples were 8.3 | 131 | mean concentrations of Pb, Zn, Cd, Cu and As in solid samples were 8.3 | ||
| 132 | g kg(-1), 12.5 g kg(-1), 40.9 mg kg(-1), 332.1 mg kg(-1), 314.7 mg | 132 | g kg(-1), 12.5 g kg(-1), 40.9 mg kg(-1), 332.1 mg kg(-1), 314.7 mg | ||
| 133 | kg(-1) respectively, and 1.5 mg l(-1), 50.3 mg l(-1), 13.6 g l(-1), | 133 | kg(-1) respectively, and 1.5 mg l(-1), 50.3 mg l(-1), 13.6 g l(-1), | ||
| 134 | 17.2 mg l(-1), 1.7 mg l(-1) in water samples respectively. These | 134 | 17.2 mg l(-1), 1.7 mg l(-1) in water samples respectively. These | ||
| 135 | metals can be dispersed downstream and downslope from the tailings by | 135 | metals can be dispersed downstream and downslope from the tailings by | ||
| 136 | water after rainfall. Soil samples collected in the surroundings of | 136 | water after rainfall. Soil samples collected in the surroundings of | ||
| 137 | Mar Menor Lagoon were analysed, reflecting the influence of the | 137 | Mar Menor Lagoon were analysed, reflecting the influence of the | ||
| 138 | transport of soluble and particulate materials from Cabezo Rajao, | 138 | transport of soluble and particulate materials from Cabezo Rajao, | ||
| 139 | especially of Pb and Zn. However, the presence of high amounts of | 139 | especially of Pb and Zn. However, the presence of high amounts of | ||
| 140 | carbonate in the soils around the mine area revealed the stabilization | 140 | carbonate in the soils around the mine area revealed the stabilization | ||
| 141 | of all the metals studied. (c) 2007 Elsevier B.V. All rights | 141 | of all the metals studied. (c) 2007 Elsevier B.V. All rights | ||
| 142 | reserved." | 142 | reserved." | ||
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