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en Spatial distribution and pollution evaluation in dry riverbeds affected by mine tailings -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Spatial distribution and pollution evaluation in dry riverbeds affected by mine tailings
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| 94 | "notes": "The objective of this study was to evaluate the level of | 104 | "notes": "The objective of this study was to evaluate the level of | ||
| 95 | pollution, sources and potential risk of heavy metals (Zn, Cu, Mn, Cd, | 105 | pollution, sources and potential risk of heavy metals (Zn, Cu, Mn, Cd, | ||
| 96 | Cr, Ni, Fe and Pb) and arsenic (As) in four dry riverbeds affected by | 106 | Cr, Ni, Fe and Pb) and arsenic (As) in four dry riverbeds affected by | ||
| 97 | mine tailing, which drain into one of the biggest coastal lagoon of | 107 | mine tailing, which drain into one of the biggest coastal lagoon of | ||
| 98 | Europe (Mar Menor). El Beal, La Carrasquilla, Las Matildes and Ponce | 108 | Europe (Mar Menor). El Beal, La Carrasquilla, Las Matildes and Ponce | ||
| 99 | dry riverbeds sediments were sampled along its course (20, 18, 13, 19 | 109 | dry riverbeds sediments were sampled along its course (20, 18, 13, 19 | ||
| 100 | samples were collected, respectively), and total/soluble metal(loid)s, | 110 | samples were collected, respectively), and total/soluble metal(loid)s, | ||
| 101 | water soluble ions, nitrogen, and organic/inorganic carbon contents | 111 | water soluble ions, nitrogen, and organic/inorganic carbon contents | ||
| 102 | were analyzed. Spatial distribution, principal component analysis | 112 | were analyzed. Spatial distribution, principal component analysis | ||
| 103 | (PCA), hierarchical cluster analysis (HCA), contamination factor (Cf), | 113 | (PCA), hierarchical cluster analysis (HCA), contamination factor (Cf), | ||
| 104 | pollution load index (PLI) and potential ecological risk index (RI) | 114 | pollution load index (PLI) and potential ecological risk index (RI) | ||
| 105 | were used to identify the possible sources of metal(loid)s and to | 115 | were used to identify the possible sources of metal(loid)s and to | ||
| 106 | assess the sediment pollution status. The results showed that the mean | 116 | assess the sediment pollution status. The results showed that the mean | ||
| 107 | total concentrations of As, Cu, Cd, Mn, Zn and Pb exceeded the natural | 117 | total concentrations of As, Cu, Cd, Mn, Zn and Pb exceeded the natural | ||
| 108 | background levels of the study area, with the highest values located | 118 | background levels of the study area, with the highest values located | ||
| 109 | close to the mining areas. Correlation and cluster analysis identified | 119 | close to the mining areas. Correlation and cluster analysis identified | ||
| 110 | that Cd and Zn were associated mainly with anthropogenic activities | 120 | that Cd and Zn were associated mainly with anthropogenic activities | ||
| 111 | for all riverbeds, while Cr and Ni come from parent. PLI graded the | 121 | for all riverbeds, while Cr and Ni come from parent. PLI graded the | ||
| 112 | four riverbeds as contaminated by heavy metals, while RI manifested | 122 | four riverbeds as contaminated by heavy metals, while RI manifested | ||
| 113 | that 100% of samples located in El Beal, La Carrasquilla and Las | 123 | that 100% of samples located in El Beal, La Carrasquilla and Las | ||
| 114 | Matildes had a significantly high ecological risk. Therefore, this | 124 | Matildes had a significantly high ecological risk. Therefore, this | ||
| 115 | study suggests that mine wastes are the main source of metal(loids) | 125 | study suggests that mine wastes are the main source of metal(loids) | ||
| 116 | contamination in the dry riverbeds, which results can be used to | 126 | contamination in the dry riverbeds, which results can be used to | ||
| 117 | design actions and measures to reduce the environmental impact of | 127 | design actions and measures to reduce the environmental impact of | ||
| 118 | metal(loid)s in the Mar Menor coastal lagoon.", | 128 | metal(loid)s in the Mar Menor coastal lagoon.", | ||
| 119 | "notes_translated": { | 129 | "notes_translated": { | ||
| 120 | "es": "The objective of this study was to evaluate the level of | 130 | "es": "The objective of this study was to evaluate the level of | ||
| 121 | pollution, sources and potential risk of heavy metals (Zn, Cu, Mn, Cd, | 131 | pollution, sources and potential risk of heavy metals (Zn, Cu, Mn, Cd, | ||
| 122 | Cr, Ni, Fe and Pb) and arsenic (As) in four dry riverbeds affected by | 132 | Cr, Ni, Fe and Pb) and arsenic (As) in four dry riverbeds affected by | ||
| 123 | mine tailing, which drain into one of the biggest coastal lagoon of | 133 | mine tailing, which drain into one of the biggest coastal lagoon of | ||
| 124 | Europe (Mar Menor). El Beal, La Carrasquilla, Las Matildes and Ponce | 134 | Europe (Mar Menor). El Beal, La Carrasquilla, Las Matildes and Ponce | ||
| 125 | dry riverbeds sediments were sampled along its course (20, 18, 13, 19 | 135 | dry riverbeds sediments were sampled along its course (20, 18, 13, 19 | ||
| 126 | samples were collected, respectively), and total/soluble metal(loid)s, | 136 | samples were collected, respectively), and total/soluble metal(loid)s, | ||
| 127 | water soluble ions, nitrogen, and organic/inorganic carbon contents | 137 | water soluble ions, nitrogen, and organic/inorganic carbon contents | ||
| 128 | were analyzed. Spatial distribution, principal component analysis | 138 | were analyzed. Spatial distribution, principal component analysis | ||
| 129 | (PCA), hierarchical cluster analysis (HCA), contamination factor (Cf), | 139 | (PCA), hierarchical cluster analysis (HCA), contamination factor (Cf), | ||
| 130 | pollution load index (PLI) and potential ecological risk index (RI) | 140 | pollution load index (PLI) and potential ecological risk index (RI) | ||
| 131 | were used to identify the possible sources of metal(loid)s and to | 141 | were used to identify the possible sources of metal(loid)s and to | ||
| 132 | assess the sediment pollution status. The results showed that the mean | 142 | assess the sediment pollution status. The results showed that the mean | ||
| 133 | total concentrations of As, Cu, Cd, Mn, Zn and Pb exceeded the natural | 143 | total concentrations of As, Cu, Cd, Mn, Zn and Pb exceeded the natural | ||
| 134 | background levels of the study area, with the highest values located | 144 | background levels of the study area, with the highest values located | ||
| 135 | close to the mining areas. Correlation and cluster analysis identified | 145 | close to the mining areas. Correlation and cluster analysis identified | ||
| 136 | that Cd and Zn were associated mainly with anthropogenic activities | 146 | that Cd and Zn were associated mainly with anthropogenic activities | ||
| 137 | for all riverbeds, while Cr and Ni come from parent. PLI graded the | 147 | for all riverbeds, while Cr and Ni come from parent. PLI graded the | ||
| 138 | four riverbeds as contaminated by heavy metals, while RI manifested | 148 | four riverbeds as contaminated by heavy metals, while RI manifested | ||
| 139 | that 100% of samples located in El Beal, La Carrasquilla and Las | 149 | that 100% of samples located in El Beal, La Carrasquilla and Las | ||
| 140 | Matildes had a significantly high ecological risk. Therefore, this | 150 | Matildes had a significantly high ecological risk. Therefore, this | ||
| 141 | study suggests that mine wastes are the main source of metal(loids) | 151 | study suggests that mine wastes are the main source of metal(loids) | ||
| 142 | contamination in the dry riverbeds, which results can be used to | 152 | contamination in the dry riverbeds, which results can be used to | ||
| 143 | design actions and measures to reduce the environmental impact of | 153 | design actions and measures to reduce the environmental impact of | ||
| 144 | metal(loid)s in the Mar Menor coastal lagoon." | 154 | metal(loid)s in the Mar Menor coastal lagoon." | ||
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