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en Effects of eutrophic water flooding on nitrate concentrations in mine wastes -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Effects of eutrophic water flooding on nitrate concentrations in mine wastes
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| 97 | "notes": "Salt marshes near urban, industrial and mining areas are | 107 | "notes": "Salt marshes near urban, industrial and mining areas are | ||
| 98 | often affected both by heavy metals and by eutrophic water. The aim of | 108 | often affected both by heavy metals and by eutrophic water. The aim of | ||
| 99 | this study was to assess and evaluate the main processes involved in | 109 | this study was to assess and evaluate the main processes involved in | ||
| 100 | the decrease of nitrate concentration in pore water of mine wastes | 110 | the decrease of nitrate concentration in pore water of mine wastes | ||
| 101 | flooded with eutrophic water, considering the presence or absence of | 111 | flooded with eutrophic water, considering the presence or absence of | ||
| 102 | plant rhizhosphere. Basic (pH \u223c 7.8) carbonated loam mine wastes | 112 | plant rhizhosphere. Basic (pH \u223c 7.8) carbonated loam mine wastes | ||
| 103 | and free carbonated acidic (pH \u223c 6.2) sandy-loam mine wastes were | 113 | and free carbonated acidic (pH \u223c 6.2) sandy-loam mine wastes were | ||
| 104 | collected from polluted coastal salt marshes of SE Spain which | 114 | collected from polluted coastal salt marshes of SE Spain which | ||
| 105 | regularly receive nutrient-enriched water. The wastes were put in pots | 115 | regularly receive nutrient-enriched water. The wastes were put in pots | ||
| 106 | and flooded for 15weeks with eutrophic water (dissolved organic carbon | 116 | and flooded for 15weeks with eutrophic water (dissolved organic carbon | ||
| 107 | \u223c26 mg L\u22121, PO4 3\u2212 \u223c23 mg L\u22121, NO3\u2212 | 117 | \u223c26 mg L\u22121, PO4 3\u2212 \u223c23 mg L\u22121, NO3\u2212 | ||
| 108 | \u223c180 mg L\u22121). Three treatments were assayed for each type of | 118 | \u223c180 mg L\u22121). Three treatments were assayed for each type of | ||
| 109 | waste: pots withSarcocornia fruticosa, pots withPhragmites australis | 119 | waste: pots withSarcocornia fruticosa, pots withPhragmites australis | ||
| 110 | and unvegetated pots. Soluble organic carbon, nitrate, soluble Cd, Pb | 120 | and unvegetated pots. Soluble organic carbon, nitrate, soluble Cd, Pb | ||
| 111 | and Zn, pH and Eh were monitored. But the 2nd day of flooding, nitrate | 121 | and Zn, pH and Eh were monitored. But the 2nd day of flooding, nitrate | ||
| 112 | concentrations had decreased between 70% and 90% (equivalent to | 122 | concentrations had decreased between 70% and 90% (equivalent to | ||
| 113 | 1.01\u20131.12 g N-NO3 \u2212 m\u22122 day\u22121) with respect to the | 123 | 1.01\u20131.12 g N-NO3 \u2212 m\u22122 day\u22121) with respect to the | ||
| 114 | content in the water used for flooding, except in unvegetated pots | 124 | content in the water used for flooding, except in unvegetated pots | ||
| 115 | with acidic wastes. Denitrification was the main mechanism associated | 125 | with acidic wastes. Denitrification was the main mechanism associated | ||
| 116 | with the removal of nitrate. The role of vegetation in improving the | 126 | with the removal of nitrate. The role of vegetation in improving the | ||
| 117 | rhizospheric environment was relevant in the acidic wastes because | 127 | rhizospheric environment was relevant in the acidic wastes because | ||
| 118 | higher sand content, lower pH and higher soluble metal concentrations | 128 | higher sand content, lower pH and higher soluble metal concentrations | ||
| 119 | might strongly hinder microbial activity Hence, revegetation of salt | 129 | might strongly hinder microbial activity Hence, revegetation of salt | ||
| 120 | marshes polluted by acidic sandy mining wastes might improve the | 130 | marshes polluted by acidic sandy mining wastes might improve the | ||
| 121 | capacity of this type of environment to act as a green filter against | 131 | capacity of this type of environment to act as a green filter against | ||
| 122 | excessive nitrate contents flowing through them.", | 132 | excessive nitrate contents flowing through them.", | ||
| 123 | "notes_translated": { | 133 | "notes_translated": { | ||
| 124 | "es": "Salt marshes near urban, industrial and mining areas are | 134 | "es": "Salt marshes near urban, industrial and mining areas are | ||
| 125 | often affected both by heavy metals and by eutrophic water. The aim of | 135 | often affected both by heavy metals and by eutrophic water. The aim of | ||
| 126 | this study was to assess and evaluate the main processes involved in | 136 | this study was to assess and evaluate the main processes involved in | ||
| 127 | the decrease of nitrate concentration in pore water of mine wastes | 137 | the decrease of nitrate concentration in pore water of mine wastes | ||
| 128 | flooded with eutrophic water, considering the presence or absence of | 138 | flooded with eutrophic water, considering the presence or absence of | ||
| 129 | plant rhizhosphere. Basic (pH \u223c 7.8) carbonated loam mine wastes | 139 | plant rhizhosphere. Basic (pH \u223c 7.8) carbonated loam mine wastes | ||
| 130 | and free carbonated acidic (pH \u223c 6.2) sandy-loam mine wastes were | 140 | and free carbonated acidic (pH \u223c 6.2) sandy-loam mine wastes were | ||
| 131 | collected from polluted coastal salt marshes of SE Spain which | 141 | collected from polluted coastal salt marshes of SE Spain which | ||
| 132 | regularly receive nutrient-enriched water. The wastes were put in pots | 142 | regularly receive nutrient-enriched water. The wastes were put in pots | ||
| 133 | and flooded for 15weeks with eutrophic water (dissolved organic carbon | 143 | and flooded for 15weeks with eutrophic water (dissolved organic carbon | ||
| 134 | \u223c26 mg L\u22121, PO4 3\u2212 \u223c23 mg L\u22121, NO3\u2212 | 144 | \u223c26 mg L\u22121, PO4 3\u2212 \u223c23 mg L\u22121, NO3\u2212 | ||
| 135 | \u223c180 mg L\u22121). Three treatments were assayed for each type of | 145 | \u223c180 mg L\u22121). Three treatments were assayed for each type of | ||
| 136 | waste: pots withSarcocornia fruticosa, pots withPhragmites australis | 146 | waste: pots withSarcocornia fruticosa, pots withPhragmites australis | ||
| 137 | and unvegetated pots. Soluble organic carbon, nitrate, soluble Cd, Pb | 147 | and unvegetated pots. Soluble organic carbon, nitrate, soluble Cd, Pb | ||
| 138 | and Zn, pH and Eh were monitored. But the 2nd day of flooding, nitrate | 148 | and Zn, pH and Eh were monitored. But the 2nd day of flooding, nitrate | ||
| 139 | concentrations had decreased between 70% and 90% (equivalent to | 149 | concentrations had decreased between 70% and 90% (equivalent to | ||
| 140 | 1.01\u20131.12 g N-NO3 \u2212 m\u22122 day\u22121) with respect to the | 150 | 1.01\u20131.12 g N-NO3 \u2212 m\u22122 day\u22121) with respect to the | ||
| 141 | content in the water used for flooding, except in unvegetated pots | 151 | content in the water used for flooding, except in unvegetated pots | ||
| 142 | with acidic wastes. Denitrification was the main mechanism associated | 152 | with acidic wastes. Denitrification was the main mechanism associated | ||
| 143 | with the removal of nitrate. The role of vegetation in improving the | 153 | with the removal of nitrate. The role of vegetation in improving the | ||
| 144 | rhizospheric environment was relevant in the acidic wastes because | 154 | rhizospheric environment was relevant in the acidic wastes because | ||
| 145 | higher sand content, lower pH and higher soluble metal concentrations | 155 | higher sand content, lower pH and higher soluble metal concentrations | ||
| 146 | might strongly hinder microbial activity Hence, revegetation of salt | 156 | might strongly hinder microbial activity Hence, revegetation of salt | ||
| 147 | marshes polluted by acidic sandy mining wastes might improve the | 157 | marshes polluted by acidic sandy mining wastes might improve the | ||
| 148 | capacity of this type of environment to act as a green filter against | 158 | capacity of this type of environment to act as a green filter against | ||
| 149 | excessive nitrate contents flowing through them." | 159 | excessive nitrate contents flowing through them." | ||
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