Cambios
En el instante 23 de junio de 2026, 16:06:01 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Liming and vegetation favor Fe-mobilization in eutrophic wetland soils affected by mine wastes
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| 93 | "notes": "The aim of this study was to evaluate the effects of | 93 | "notes": "The aim of this study was to evaluate the effects of | ||
| 94 | liming and vegetation on the dynamic of Fe in eutrophic wetland soils | 94 | liming and vegetation on the dynamic of Fe in eutrophic wetland soils | ||
| 95 | affected by mine wastes, under different flooding regimes. Simulated | 95 | affected by mine wastes, under different flooding regimes. Simulated | ||
| 96 | soil profiles were constructed with two types of wastes (pH \u223c 3.1 | 96 | soil profiles were constructed with two types of wastes (pH \u223c 3.1 | ||
| 97 | and \u223c6.4) collected from polluted salt marshes and four | 97 | and \u223c6.4) collected from polluted salt marshes and four | ||
| 98 | treatments were assayed: without liming + without plant, without | 98 | treatments were assayed: without liming + without plant, without | ||
| 99 | liming + with plant, with liming + without plant, and with liming + | 99 | liming + with plant, with liming + without plant, and with liming + | ||
| 100 | with plant. The plant species was the halophyte Sarcocornia fruticosa. | 100 | with plant. The plant species was the halophyte Sarcocornia fruticosa. | ||
| 101 | Three horizons were differentiated in the profiles: A horizons (never | 101 | Three horizons were differentiated in the profiles: A horizons (never | ||
| 102 | underwater), C1 (alternat ing flooding\u2013drying conditions), and C2 | 102 | underwater), C1 (alternat ing flooding\u2013drying conditions), and C2 | ||
| 103 | (always underwater). The pH, Eh, salinity, and the concentrations of | 103 | (always underwater). The pH, Eh, salinity, and the concentrations of | ||
| 104 | DOC and soluble Fe were measured regularly at each horizon for 18 | 104 | DOC and soluble Fe were measured regularly at each horizon for 18 | ||
| 105 | weeks. Liming decreased Fe sol ubility, mainly in the acidic waste | 105 | weeks. Liming decreased Fe sol ubility, mainly in the acidic waste | ||
| 106 | (maximum average concentrations \u223c18 mg L\u22121 without liming | 106 | (maximum average concentrations \u223c18 mg L\u22121 without liming | ||
| 107 | and \u223c6 mg L\u22121 with liming). However, liming also facilitated | 107 | and \u223c6 mg L\u22121 with liming). However, liming also facilitated | ||
| 108 | a drop in Eh, increasing soluble Fe content. Plant rhizosphere | 108 | a drop in Eh, increasing soluble Fe content. Plant rhizosphere | ||
| 109 | re-distributed this Fe, which was accumulated in the upper horizons of | 109 | re-distributed this Fe, which was accumulated in the upper horizons of | ||
| 110 | the treat ments with liming + with plant, particularly in the acidic | 110 | the treat ments with liming + with plant, particularly in the acidic | ||
| 111 | waste (average concentrations \u223c10 mg L\u22121 in the A horizon | 111 | waste (average concentrations \u223c10 mg L\u22121 in the A horizon | ||
| 112 | and \u223c5 mg L\u22121 in the C1 and C2 horizons). Therefore, we | 112 | and \u223c5 mg L\u22121 in the C1 and C2 horizons). Therefore, we | ||
| 113 | conclude that the combined use of liming and vegetation enhance the | 113 | conclude that the combined use of liming and vegetation enhance the | ||
| 114 | mobilization of Fe in eutrophic wetland soils polluted by mine wastes | 114 | mobilization of Fe in eutrophic wetland soils polluted by mine wastes | ||
| 115 | under alternating flooding\u2013drying conditions. This should be | 115 | under alternating flooding\u2013drying conditions. This should be | ||
| 116 | considered for the envi ronmental management of these sites due to the | 116 | considered for the envi ronmental management of these sites due to the | ||
| 117 | role of Fe-minerals as sink for potentially-harmful compounds", | 117 | role of Fe-minerals as sink for potentially-harmful compounds", | ||
| 118 | "notes_translated": { | 118 | "notes_translated": { | ||
| 119 | "es": "The aim of this study was to evaluate the effects of liming | 119 | "es": "The aim of this study was to evaluate the effects of liming | ||
| 120 | and vegetation on the dynamic of Fe in eutrophic wetland soils | 120 | and vegetation on the dynamic of Fe in eutrophic wetland soils | ||
| 121 | affected by mine wastes, under different flooding regimes. Simulated | 121 | affected by mine wastes, under different flooding regimes. Simulated | ||
| 122 | soil profiles were constructed with two types of wastes (pH \u223c 3.1 | 122 | soil profiles were constructed with two types of wastes (pH \u223c 3.1 | ||
| 123 | and \u223c6.4) collected from polluted salt marshes and four | 123 | and \u223c6.4) collected from polluted salt marshes and four | ||
| 124 | treatments were assayed: without liming + without plant, without | 124 | treatments were assayed: without liming + without plant, without | ||
| 125 | liming + with plant, with liming + without plant, and with liming + | 125 | liming + with plant, with liming + without plant, and with liming + | ||
| 126 | with plant. The plant species was the halophyte Sarcocornia fruticosa. | 126 | with plant. The plant species was the halophyte Sarcocornia fruticosa. | ||
| 127 | Three horizons were differentiated in the profiles: A horizons (never | 127 | Three horizons were differentiated in the profiles: A horizons (never | ||
| 128 | underwater), C1 (alternat ing flooding\u2013drying conditions), and C2 | 128 | underwater), C1 (alternat ing flooding\u2013drying conditions), and C2 | ||
| 129 | (always underwater). The pH, Eh, salinity, and the concentrations of | 129 | (always underwater). The pH, Eh, salinity, and the concentrations of | ||
| 130 | DOC and soluble Fe were measured regularly at each horizon for 18 | 130 | DOC and soluble Fe were measured regularly at each horizon for 18 | ||
| 131 | weeks. Liming decreased Fe sol ubility, mainly in the acidic waste | 131 | weeks. Liming decreased Fe sol ubility, mainly in the acidic waste | ||
| 132 | (maximum average concentrations \u223c18 mg L\u22121 without liming | 132 | (maximum average concentrations \u223c18 mg L\u22121 without liming | ||
| 133 | and \u223c6 mg L\u22121 with liming). However, liming also facilitated | 133 | and \u223c6 mg L\u22121 with liming). However, liming also facilitated | ||
| 134 | a drop in Eh, increasing soluble Fe content. Plant rhizosphere | 134 | a drop in Eh, increasing soluble Fe content. Plant rhizosphere | ||
| 135 | re-distributed this Fe, which was accumulated in the upper horizons of | 135 | re-distributed this Fe, which was accumulated in the upper horizons of | ||
| 136 | the treat ments with liming + with plant, particularly in the acidic | 136 | the treat ments with liming + with plant, particularly in the acidic | ||
| 137 | waste (average concentrations \u223c10 mg L\u22121 in the A horizon | 137 | waste (average concentrations \u223c10 mg L\u22121 in the A horizon | ||
| 138 | and \u223c5 mg L\u22121 in the C1 and C2 horizons). Therefore, we | 138 | and \u223c5 mg L\u22121 in the C1 and C2 horizons). Therefore, we | ||
| 139 | conclude that the combined use of liming and vegetation enhance the | 139 | conclude that the combined use of liming and vegetation enhance the | ||
| 140 | mobilization of Fe in eutrophic wetland soils polluted by mine wastes | 140 | mobilization of Fe in eutrophic wetland soils polluted by mine wastes | ||
| 141 | under alternating flooding\u2013drying conditions. This should be | 141 | under alternating flooding\u2013drying conditions. This should be | ||
| 142 | considered for the envi ronmental management of these sites due to the | 142 | considered for the envi ronmental management of these sites due to the | ||
| 143 | role of Fe-minerals as sink for potentially-harmful compounds" | 143 | role of Fe-minerals as sink for potentially-harmful compounds" | ||
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