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a2026-06-25
en Assessment of bioaccessible As in a wetland with mining influence (Mar Menor, SE Spain). -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Assessment of bioaccessible As in a wetland with mining influence (Mar Menor, SE Spain).
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| 95 | "notes": "Mining areas are so complex that it is sometimes difficult | 105 | "notes": "Mining areas are so complex that it is sometimes difficult | ||
| 96 | to differentiate between anthropogenic contamination and geogenic | 106 | to differentiate between anthropogenic contamination and geogenic | ||
| 97 | anomalies. This is the case in the so-called Sierra de Cartagena-La | 107 | anomalies. This is the case in the so-called Sierra de Cartagena-La | ||
| 98 | Uni\u00f3n, which constitutes a mining district of Ag, Pb, Zn, Fe in | 108 | Uni\u00f3n, which constitutes a mining district of Ag, Pb, Zn, Fe in | ||
| 99 | stratabound sulphide deposits that have been exploited for more than | 109 | stratabound sulphide deposits that have been exploited for more than | ||
| 100 | three thousand years. Since the closure programme was implemented in | 110 | three thousand years. Since the closure programme was implemented in | ||
| 101 | 1991, the area has remained abandoned. This results in runoff from | 111 | 1991, the area has remained abandoned. This results in runoff from | ||
| 102 | extreme rainfall events, as well as wind action, allowing the | 112 | extreme rainfall events, as well as wind action, allowing the | ||
| 103 | transport of dissolved or suspended particles and pollutants from | 113 | transport of dissolved or suspended particles and pollutants from | ||
| 104 | mining areas to the plain of Campo de Cartagena, the Mar Menor and the | 114 | mining areas to the plain of Campo de Cartagena, the Mar Menor and the | ||
| 105 | Mediterranean Sea. In this area, arsenic pollution is one of the main | 115 | Mediterranean Sea. In this area, arsenic pollution is one of the main | ||
| 106 | environmental and public health problems. In general, arsenic levels | 116 | environmental and public health problems. In general, arsenic levels | ||
| 107 | in uncontaminated soils rarely exceed 10 mg/kg, the proposed Generic | 117 | in uncontaminated soils rarely exceed 10 mg/kg, the proposed Generic | ||
| 108 | Reference Level (GRL) being 7.84 mg/kg for the Region of Murcia. In | 118 | Reference Level (GRL) being 7.84 mg/kg for the Region of Murcia. In | ||
| 109 | exclusion zones, As concentrations exceed 300 mg/kg, reaching in some | 119 | exclusion zones, As concentrations exceed 300 mg/kg, reaching in some | ||
| 110 | cases 5000 mg/kg (coinciding with accumulations of mining waste, | 120 | cases 5000 mg/kg (coinciding with accumulations of mining waste, | ||
| 111 | ponds, dumps, etc.). The main objective of this work was to evaluate | 121 | ponds, dumps, etc.). The main objective of this work was to evaluate | ||
| 112 | the potential risk to humans, through the main route of entry, | 122 | the potential risk to humans, through the main route of entry, | ||
| 113 | ingestion, represented by the soils of the Rambla del Beal basin (SE | 123 | ingestion, represented by the soils of the Rambla del Beal basin (SE | ||
| 114 | Spain) and its mouth in the Lopoyo Wetland (Mar Menor, SE Spain), | 124 | Spain) and its mouth in the Lopoyo Wetland (Mar Menor, SE Spain), | ||
| 115 | taking into account: - Total As content in four different soil | 125 | taking into account: - Total As content in four different soil | ||
| 116 | fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | 126 | fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | ||
| 117 | \u02c263\u00b5m).\n - Bioaccessible arsenic content in four different | 127 | \u02c263\u00b5m).\n - Bioaccessible arsenic content in four different | ||
| 118 | soil fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | 128 | soil fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | ||
| 119 | \u02c263\u00b5m).\n - Two possible adult land uses (agricultural and | 129 | \u02c263\u00b5m).\n - Two possible adult land uses (agricultural and | ||
| 120 | residential) and one possible child land use\n (residential).\n For | 130 | residential) and one possible child land use\n (residential).\n For | ||
| 121 | the determination of As bioaccessible, in vitro extraction methods | 131 | the determination of As bioaccessible, in vitro extraction methods | ||
| 122 | were used. Among the various in vitro methods to assess the relative | 132 | were used. Among the various in vitro methods to assess the relative | ||
| 123 | bioavailability of existing metals, the Solubility Bioaccessibility | 133 | bioavailability of existing metals, the Solubility Bioaccessibility | ||
| 124 | Research Consortium (SBRC) method was selected, as it provides an | 134 | Research Consortium (SBRC) method was selected, as it provides an | ||
| 125 | adequate relationship between bioavailability and bioaccessibility of | 135 | adequate relationship between bioavailability and bioaccessibility of | ||
| 126 | arsenic, with a high correlation with the results obtained in vivo | 136 | arsenic, with a high correlation with the results obtained in vivo | ||
| 127 | experiments, distinguishing two phases, stomach and intestinal.", | 137 | experiments, distinguishing two phases, stomach and intestinal.", | ||
| 128 | "notes_translated": { | 138 | "notes_translated": { | ||
| 129 | "es": "Mining areas are so complex that it is sometimes difficult | 139 | "es": "Mining areas are so complex that it is sometimes difficult | ||
| 130 | to differentiate between anthropogenic contamination and geogenic | 140 | to differentiate between anthropogenic contamination and geogenic | ||
| 131 | anomalies. This is the case in the so-called Sierra de Cartagena-La | 141 | anomalies. This is the case in the so-called Sierra de Cartagena-La | ||
| 132 | Uni\u00f3n, which constitutes a mining district of Ag, Pb, Zn, Fe in | 142 | Uni\u00f3n, which constitutes a mining district of Ag, Pb, Zn, Fe in | ||
| 133 | stratabound sulphide deposits that have been exploited for more than | 143 | stratabound sulphide deposits that have been exploited for more than | ||
| 134 | three thousand years. Since the closure programme was implemented in | 144 | three thousand years. Since the closure programme was implemented in | ||
| 135 | 1991, the area has remained abandoned. This results in runoff from | 145 | 1991, the area has remained abandoned. This results in runoff from | ||
| 136 | extreme rainfall events, as well as wind action, allowing the | 146 | extreme rainfall events, as well as wind action, allowing the | ||
| 137 | transport of dissolved or suspended particles and pollutants from | 147 | transport of dissolved or suspended particles and pollutants from | ||
| 138 | mining areas to the plain of Campo de Cartagena, the Mar Menor and the | 148 | mining areas to the plain of Campo de Cartagena, the Mar Menor and the | ||
| 139 | Mediterranean Sea. In this area, arsenic pollution is one of the main | 149 | Mediterranean Sea. In this area, arsenic pollution is one of the main | ||
| 140 | environmental and public health problems. In general, arsenic levels | 150 | environmental and public health problems. In general, arsenic levels | ||
| 141 | in uncontaminated soils rarely exceed 10 mg/kg, the proposed Generic | 151 | in uncontaminated soils rarely exceed 10 mg/kg, the proposed Generic | ||
| 142 | Reference Level (GRL) being 7.84 mg/kg for the Region of Murcia. In | 152 | Reference Level (GRL) being 7.84 mg/kg for the Region of Murcia. In | ||
| 143 | exclusion zones, As concentrations exceed 300 mg/kg, reaching in some | 153 | exclusion zones, As concentrations exceed 300 mg/kg, reaching in some | ||
| 144 | cases 5000 mg/kg (coinciding with accumulations of mining waste, | 154 | cases 5000 mg/kg (coinciding with accumulations of mining waste, | ||
| 145 | ponds, dumps, etc.). The main objective of this work was to evaluate | 155 | ponds, dumps, etc.). The main objective of this work was to evaluate | ||
| 146 | the potential risk to humans, through the main route of entry, | 156 | the potential risk to humans, through the main route of entry, | ||
| 147 | ingestion, represented by the soils of the Rambla del Beal basin (SE | 157 | ingestion, represented by the soils of the Rambla del Beal basin (SE | ||
| 148 | Spain) and its mouth in the Lopoyo Wetland (Mar Menor, SE Spain), | 158 | Spain) and its mouth in the Lopoyo Wetland (Mar Menor, SE Spain), | ||
| 149 | taking into account: - Total As content in four different soil | 159 | taking into account: - Total As content in four different soil | ||
| 150 | fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | 160 | fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | ||
| 151 | \u02c263\u00b5m).\n - Bioaccessible arsenic content in four different | 161 | \u02c263\u00b5m).\n - Bioaccessible arsenic content in four different | ||
| 152 | soil fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | 162 | soil fractions (\u02c22mm; \u02c2250\u00b5m; \u02c2100\u00b5m; | ||
| 153 | \u02c263\u00b5m).\n - Two possible adult land uses (agricultural and | 163 | \u02c263\u00b5m).\n - Two possible adult land uses (agricultural and | ||
| 154 | residential) and one possible child land use\n (residential).\n For | 164 | residential) and one possible child land use\n (residential).\n For | ||
| 155 | the determination of As bioaccessible, in vitro extraction methods | 165 | the determination of As bioaccessible, in vitro extraction methods | ||
| 156 | were used. Among the various in vitro methods to assess the relative | 166 | were used. Among the various in vitro methods to assess the relative | ||
| 157 | bioavailability of existing metals, the Solubility Bioaccessibility | 167 | bioavailability of existing metals, the Solubility Bioaccessibility | ||
| 158 | Research Consortium (SBRC) method was selected, as it provides an | 168 | Research Consortium (SBRC) method was selected, as it provides an | ||
| 159 | adequate relationship between bioavailability and bioaccessibility of | 169 | adequate relationship between bioavailability and bioaccessibility of | ||
| 160 | arsenic, with a high correlation with the results obtained in vivo | 170 | arsenic, with a high correlation with the results obtained in vivo | ||
| 161 | experiments, distinguishing two phases, stomach and intestinal." | 171 | experiments, distinguishing two phases, stomach and intestinal." | ||
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| 305 | "name": "impacto_ambiental", | 315 | "name": "impacto_ambiental", | ||
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| 314 | "vocabulary_id": null | 324 | "vocabulary_id": null | ||
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| 318 | "id": "5a92f26e-1b91-495c-99a2-dcd469828003", | 328 | "id": "5a92f26e-1b91-495c-99a2-dcd469828003", | ||
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| 328 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 338 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 329 | ], | 339 | ], | ||
| 330 | "title": "Assessment of bioaccessible As in a wetland with mining | 340 | "title": "Assessment of bioaccessible As in a wetland with mining | ||
| 331 | influence (Mar Menor, SE Spain).", | 341 | influence (Mar Menor, SE Spain).", | ||
| 332 | "title_translated": { | 342 | "title_translated": { | ||
| 333 | "es": "Assessment of bioaccessible As in a wetland with mining | 343 | "es": "Assessment of bioaccessible As in a wetland with mining | ||
| 334 | influence (Mar Menor, SE Spain)." | 344 | influence (Mar Menor, SE Spain)." | ||
| 335 | }, | 345 | }, | ||
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