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en Influence of soil properties on trace element availability and plant accumulation in a Mediterranean salt marsh polluted by mining wastes: Implications for phytomanagement -
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del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Influence of soil properties on trace element availability and plant accumulation in a Mediterranean salt marsh polluted by mining wastes: Implications for phytomanagement
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| 93 | "notes": "The aims of this study were to determine the factors which | 103 | "notes": "The aims of this study were to determine the factors which | ||
| 94 | control metal and As phytoavailability in the different | 104 | control metal and As phytoavailability in the different | ||
| 95 | microenvironments (Sand Dunes, Salt Flat, Dry River and Shrubs) | 105 | microenvironments (Sand Dunes, Salt Flat, Dry River and Shrubs) | ||
| 96 | present at a Mediterranean salt marsh polluted by mining wastes. We | 106 | present at a Mediterranean salt marsh polluted by mining wastes. We | ||
| 97 | performed a field study following a plot sampling survey. The analyses | 107 | performed a field study following a plot sampling survey. The analyses | ||
| 98 | of soil parameters (pH, electrical conductivity (EC), organic carbon | 108 | of soil parameters (pH, electrical conductivity (EC), organic carbon | ||
| 99 | contents, etc.), total metal and As concentrations and their | 109 | contents, etc.), total metal and As concentrations and their | ||
| 100 | phytoavailability assessed with EDTA were related to each | 110 | phytoavailability assessed with EDTA were related to each | ||
| 101 | microenvironment and the corresponding plant species uptake. The | 111 | microenvironment and the corresponding plant species uptake. The | ||
| 102 | averages of pH and EC were slightly alkaline (pH\u22487.5) and saline | 112 | averages of pH and EC were slightly alkaline (pH\u22487.5) and saline | ||
| 103 | (\u22482.2 to 17.1 dS m\u22121) respectively. The soil samples from | 113 | (\u22482.2 to 17.1 dS m\u22121) respectively. The soil samples from | ||
| 104 | the Salt Flat subzone showed the highest metal concentrations (e.g. 51 | 114 | the Salt Flat subzone showed the highest metal concentrations (e.g. 51 | ||
| 105 | mg kg\u22121 Cd, 11,600 mg kg\u22121 Pb) while for As, the highest | 115 | mg kg\u22121 Cd, 11,600 mg kg\u22121 Pb) while for As, the highest | ||
| 106 | concentrations occurred in the Dry River (380 mg kg\u22121 As). The | 116 | concentrations occurred in the Dry River (380 mg kg\u22121 As). The | ||
| 107 | total metal and EDTA-extractable concentrations occurred as it | 117 | total metal and EDTA-extractable concentrations occurred as it | ||
| 108 | follows: Salt FlatNDry RiverNDegraded DunesNShrubs. In relation to | 118 | follows: Salt FlatNDry RiverNDegraded DunesNShrubs. In relation to | ||
| 109 | plant metal and As accumulation, the highest root concentrations were | 119 | plant metal and As accumulation, the highest root concentrations were | ||
| 110 | obtained in the species from the Salt Flat subzone: ~17 mg kg\u22121 | 120 | obtained in the species from the Salt Flat subzone: ~17 mg kg\u22121 | ||
| 111 | As, ~620 mg kg\u22121 Pb, for both, Juncus maritimus and Arthrocnemum | 121 | As, ~620 mg kg\u22121 Pb, for both, Juncus maritimus and Arthrocnemum | ||
| 112 | macrostachyum. However the highest metal and As shoot concentrations | 122 | macrostachyum. However the highest metal and As shoot concentrations | ||
| 113 | occurred in species from the Sand Dunes: ~23 mg kg\u22121 As ~270 mg | 123 | occurred in species from the Sand Dunes: ~23 mg kg\u22121 As ~270 mg | ||
| 114 | kg\u22121 Pb for Dittrichia viscosa; ~23 mg kg\u22121 As, ~390 mg | 124 | kg\u22121 Pb for Dittrichia viscosa; ~23 mg kg\u22121 As, ~390 mg | ||
| 115 | kg\u22121 Zn for Crucianella maritima. The occurrence of edaphic | 125 | kg\u22121 Zn for Crucianella maritima. The occurrence of edaphic | ||
| 116 | gradients including salinity and texture determined the vegetation | 126 | gradients including salinity and texture determined the vegetation | ||
| 117 | distribution. However, it cannot be concluded that there was a | 127 | distribution. However, it cannot be concluded that there was a | ||
| 118 | disturbance due to metal(loid)s soil concentrations in terms of | 128 | disturbance due to metal(loid)s soil concentrations in terms of | ||
| 119 | vegetation composition except in the Degraded Dunes and Dry River. The | 129 | vegetation composition except in the Degraded Dunes and Dry River. The | ||
| 120 | higher EDTA-extractable concentrations were coincidental with the most | 130 | higher EDTA-extractable concentrations were coincidental with the most | ||
| 121 | saline soils but this did not result in higher metal(loid)s plant | 131 | saline soils but this did not result in higher metal(loid)s plant | ||
| 122 | accumulation", | 132 | accumulation", | ||
| 123 | "notes_translated": { | 133 | "notes_translated": { | ||
| 124 | "es": "The aims of this study were to determine the factors which | 134 | "es": "The aims of this study were to determine the factors which | ||
| 125 | control metal and As phytoavailability in the different | 135 | control metal and As phytoavailability in the different | ||
| 126 | microenvironments (Sand Dunes, Salt Flat, Dry River and Shrubs) | 136 | microenvironments (Sand Dunes, Salt Flat, Dry River and Shrubs) | ||
| 127 | present at a Mediterranean salt marsh polluted by mining wastes. We | 137 | present at a Mediterranean salt marsh polluted by mining wastes. We | ||
| 128 | performed a field study following a plot sampling survey. The analyses | 138 | performed a field study following a plot sampling survey. The analyses | ||
| 129 | of soil parameters (pH, electrical conductivity (EC), organic carbon | 139 | of soil parameters (pH, electrical conductivity (EC), organic carbon | ||
| 130 | contents, etc.), total metal and As concentrations and their | 140 | contents, etc.), total metal and As concentrations and their | ||
| 131 | phytoavailability assessed with EDTA were related to each | 141 | phytoavailability assessed with EDTA were related to each | ||
| 132 | microenvironment and the corresponding plant species uptake. The | 142 | microenvironment and the corresponding plant species uptake. The | ||
| 133 | averages of pH and EC were slightly alkaline (pH\u22487.5) and saline | 143 | averages of pH and EC were slightly alkaline (pH\u22487.5) and saline | ||
| 134 | (\u22482.2 to 17.1 dS m\u22121) respectively. The soil samples from | 144 | (\u22482.2 to 17.1 dS m\u22121) respectively. The soil samples from | ||
| 135 | the Salt Flat subzone showed the highest metal concentrations (e.g. 51 | 145 | the Salt Flat subzone showed the highest metal concentrations (e.g. 51 | ||
| 136 | mg kg\u22121 Cd, 11,600 mg kg\u22121 Pb) while for As, the highest | 146 | mg kg\u22121 Cd, 11,600 mg kg\u22121 Pb) while for As, the highest | ||
| 137 | concentrations occurred in the Dry River (380 mg kg\u22121 As). The | 147 | concentrations occurred in the Dry River (380 mg kg\u22121 As). The | ||
| 138 | total metal and EDTA-extractable concentrations occurred as it | 148 | total metal and EDTA-extractable concentrations occurred as it | ||
| 139 | follows: Salt FlatNDry RiverNDegraded DunesNShrubs. In relation to | 149 | follows: Salt FlatNDry RiverNDegraded DunesNShrubs. In relation to | ||
| 140 | plant metal and As accumulation, the highest root concentrations were | 150 | plant metal and As accumulation, the highest root concentrations were | ||
| 141 | obtained in the species from the Salt Flat subzone: ~17 mg kg\u22121 | 151 | obtained in the species from the Salt Flat subzone: ~17 mg kg\u22121 | ||
| 142 | As, ~620 mg kg\u22121 Pb, for both, Juncus maritimus and Arthrocnemum | 152 | As, ~620 mg kg\u22121 Pb, for both, Juncus maritimus and Arthrocnemum | ||
| 143 | macrostachyum. However the highest metal and As shoot concentrations | 153 | macrostachyum. However the highest metal and As shoot concentrations | ||
| 144 | occurred in species from the Sand Dunes: ~23 mg kg\u22121 As ~270 mg | 154 | occurred in species from the Sand Dunes: ~23 mg kg\u22121 As ~270 mg | ||
| 145 | kg\u22121 Pb for Dittrichia viscosa; ~23 mg kg\u22121 As, ~390 mg | 155 | kg\u22121 Pb for Dittrichia viscosa; ~23 mg kg\u22121 As, ~390 mg | ||
| 146 | kg\u22121 Zn for Crucianella maritima. The occurrence of edaphic | 156 | kg\u22121 Zn for Crucianella maritima. The occurrence of edaphic | ||
| 147 | gradients including salinity and texture determined the vegetation | 157 | gradients including salinity and texture determined the vegetation | ||
| 148 | distribution. However, it cannot be concluded that there was a | 158 | distribution. However, it cannot be concluded that there was a | ||
| 149 | disturbance due to metal(loid)s soil concentrations in terms of | 159 | disturbance due to metal(loid)s soil concentrations in terms of | ||
| 150 | vegetation composition except in the Degraded Dunes and Dry River. The | 160 | vegetation composition except in the Degraded Dunes and Dry River. The | ||
| 151 | higher EDTA-extractable concentrations were coincidental with the most | 161 | higher EDTA-extractable concentrations were coincidental with the most | ||
| 152 | saline soils but this did not result in higher metal(loid)s plant | 162 | saline soils but this did not result in higher metal(loid)s plant | ||
| 153 | accumulation" | 163 | accumulation" | ||
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