Cambios
En el instante 23 de junio de 2026, 16:08:36 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-2.34, 37.38], [-0.69, 37.38], [-0.69, 38.76], [-2.34, 38.76], [-2.34, 37.38]]]}', 'centroid': '{"type": "Point", "coordinates": [-1.515, 38.07]}', 'text': 'Región de Murcia', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia'}]
en Nutrient and particulate inputs into the Mar Menor lagoon (Se Spain) from an intensive agricultural watershed
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| 8 | "author": "Velasco, J., Lloret, J., Millan, A., Marin, A., Barahona, | 8 | "author": "Velasco, J., Lloret, J., Millan, A., Marin, A., Barahona, | ||
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| 63 | "nutrientes", | 63 | "nutrientes", | ||
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| 83 | "miteco_data_population": { | 83 | "miteco_data_population": { | ||
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| 89 | "miteco_dataset_type": | 89 | "miteco_dataset_type": | ||
| 90 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 90 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 91 | "miteco_geo_level": "1", | 91 | "miteco_geo_level": "1", | ||
| 92 | "modified": "2026-06-23", | 92 | "modified": "2026-06-23", | ||
| 93 | "name": "501637c7-ffa1-5ef9-b93f-213e651de602", | 93 | "name": "501637c7-ffa1-5ef9-b93f-213e651de602", | ||
| 94 | "notes": "The Mar Menor is a Mediterranean coastal lagoon of high | 94 | "notes": "The Mar Menor is a Mediterranean coastal lagoon of high | ||
| 95 | conservation interest, but highly threatened by non-point pollution | 95 | conservation interest, but highly threatened by non-point pollution | ||
| 96 | derived from agricultural lands. This is the first comprehensive study | 96 | derived from agricultural lands. This is the first comprehensive study | ||
| 97 | that evaluates the inputs into the Mar Menor from a drainage channel | 97 | that evaluates the inputs into the Mar Menor from a drainage channel | ||
| 98 | and the Albujon wadi, the main watercourse, and their influence on the | 98 | and the Albujon wadi, the main watercourse, and their influence on the | ||
| 99 | trophic state of the lagoon. Discharge variation during the study | 99 | trophic state of the lagoon. Discharge variation during the study | ||
| 100 | period was closely related to the precipitation pattern. Suspended | 100 | period was closely related to the precipitation pattern. Suspended | ||
| 101 | sediments and particulate organic matter loads greatly increased with | 101 | sediments and particulate organic matter loads greatly increased with | ||
| 102 | flash floods. Nitrate concentrations, too, increased after heavy | 102 | flash floods. Nitrate concentrations, too, increased after heavy | ||
| 103 | autumn rains through washing of the nitrates accumulated in soils, | 103 | autumn rains through washing of the nitrates accumulated in soils, | ||
| 104 | although no significant correlations were found between nitrate | 104 | although no significant correlations were found between nitrate | ||
| 105 | concentrations and precipitation or discharge. The nitrate load | 105 | concentrations and precipitation or discharge. The nitrate load | ||
| 106 | depended on several factors including the intensity and frequency of | 106 | depended on several factors including the intensity and frequency of | ||
| 107 | precipitation, and the nitrates accumulated in soils as a result of | 107 | precipitation, and the nitrates accumulated in soils as a result of | ||
| 108 | fertilisation. Phosphate concentrations decreased with higher flows. | 108 | fertilisation. Phosphate concentrations decreased with higher flows. | ||
| 109 | The total input into the lagoon from the two discharges estimated for | 109 | The total input into the lagoon from the two discharges estimated for | ||
| 110 | the period September 2002-October 2003 were 10,142 t.yr(-1) of | 110 | the period September 2002-October 2003 were 10,142 t.yr(-1) of | ||
| 111 | suspended sediments, 389 t.yr(-1)supercript stop of particulate | 111 | suspended sediments, 389 t.yr(-1)supercript stop of particulate | ||
| 112 | organic matter, 2,010 t.yr(-1) of dissolved inorganic nitrogen (93 % | 112 | organic matter, 2,010 t.yr(-1) of dissolved inorganic nitrogen (93 % | ||
| 113 | as NO3-) and 178 t.yr(-1) of soluble reactive phosphorus. The Albujon | 113 | as NO3-) and 178 t.yr(-1) of soluble reactive phosphorus. The Albujon | ||
| 114 | wadi exported about 80% of the N load and 70% of the P load. Higher | 114 | wadi exported about 80% of the N load and 70% of the P load. Higher | ||
| 115 | flows contributed approximately 80% of the total discharge and | 115 | flows contributed approximately 80% of the total discharge and | ||
| 116 | nutrient loads, 99% of suspended sediment and 88% of the particulate | 116 | nutrient loads, 99% of suspended sediment and 88% of the particulate | ||
| 117 | organic matter. Mean suspended solids and nutrient concentrations in | 117 | organic matter. Mean suspended solids and nutrient concentrations in | ||
| 118 | the lagoon followed a spatial pattern, decreasing with distance from | 118 | the lagoon followed a spatial pattern, decreasing with distance from | ||
| 119 | the mouth of the Albujon wadi. Water nitrate and phosphate | 119 | the mouth of the Albujon wadi. Water nitrate and phosphate | ||
| 120 | concentrations in the Mar Menor lagoon were lower than reference | 120 | concentrations in the Mar Menor lagoon were lower than reference | ||
| 121 | limits for eutrophic conditions, except after heavy rains. Nutrient | 121 | limits for eutrophic conditions, except after heavy rains. Nutrient | ||
| 122 | concentrations were positively correlated with precipitation variables | 122 | concentrations were positively correlated with precipitation variables | ||
| 123 | and particulate and nutrient inputs. Phosphorus was the most limiting | 123 | and particulate and nutrient inputs. Phosphorus was the most limiting | ||
| 124 | nutrient in the Mar Menor, the DIN:SRP ratios found being higher than | 124 | nutrient in the Mar Menor, the DIN:SRP ratios found being higher than | ||
| 125 | the Redfield ratio on all sampling dates. Phytoplankton bloom in the | 125 | the Redfield ratio on all sampling dates. Phytoplankton bloom in the | ||
| 126 | lagoon was only found next to the Albujon mouth during late summer and | 126 | lagoon was only found next to the Albujon mouth during late summer and | ||
| 127 | extending 5000 m into the lagoon in autumn as a consequence of large | 127 | extending 5000 m into the lagoon in autumn as a consequence of large | ||
| 128 | freshwater discharge caused by flash floods. Around 53.6% of the | 128 | freshwater discharge caused by flash floods. Around 53.6% of the | ||
| 129 | variation in chlorophyll a in the lagoon was explained by the NH4 and | 129 | variation in chlorophyll a in the lagoon was explained by the NH4 and | ||
| 130 | NO3 inputs and distance from the Albujon mouth. A good deal of P input | 130 | NO3 inputs and distance from the Albujon mouth. A good deal of P input | ||
| 131 | into the lagoon is retained in the sediments, supporting a high | 131 | into the lagoon is retained in the sediments, supporting a high | ||
| 132 | biomass of the benthic macroalga Caulerpa prolifera in spring and | 132 | biomass of the benthic macroalga Caulerpa prolifera in spring and | ||
| 133 | summer.", | 133 | summer.", | ||
| 134 | "notes_translated": { | 134 | "notes_translated": { | ||
| 135 | "es": "The Mar Menor is a Mediterranean coastal lagoon of high | 135 | "es": "The Mar Menor is a Mediterranean coastal lagoon of high | ||
| 136 | conservation interest, but highly threatened by non-point pollution | 136 | conservation interest, but highly threatened by non-point pollution | ||
| 137 | derived from agricultural lands. This is the first comprehensive study | 137 | derived from agricultural lands. This is the first comprehensive study | ||
| 138 | that evaluates the inputs into the Mar Menor from a drainage channel | 138 | that evaluates the inputs into the Mar Menor from a drainage channel | ||
| 139 | and the Albujon wadi, the main watercourse, and their influence on the | 139 | and the Albujon wadi, the main watercourse, and their influence on the | ||
| 140 | trophic state of the lagoon. Discharge variation during the study | 140 | trophic state of the lagoon. Discharge variation during the study | ||
| 141 | period was closely related to the precipitation pattern. Suspended | 141 | period was closely related to the precipitation pattern. Suspended | ||
| 142 | sediments and particulate organic matter loads greatly increased with | 142 | sediments and particulate organic matter loads greatly increased with | ||
| 143 | flash floods. Nitrate concentrations, too, increased after heavy | 143 | flash floods. Nitrate concentrations, too, increased after heavy | ||
| 144 | autumn rains through washing of the nitrates accumulated in soils, | 144 | autumn rains through washing of the nitrates accumulated in soils, | ||
| 145 | although no significant correlations were found between nitrate | 145 | although no significant correlations were found between nitrate | ||
| 146 | concentrations and precipitation or discharge. The nitrate load | 146 | concentrations and precipitation or discharge. The nitrate load | ||
| 147 | depended on several factors including the intensity and frequency of | 147 | depended on several factors including the intensity and frequency of | ||
| 148 | precipitation, and the nitrates accumulated in soils as a result of | 148 | precipitation, and the nitrates accumulated in soils as a result of | ||
| 149 | fertilisation. Phosphate concentrations decreased with higher flows. | 149 | fertilisation. Phosphate concentrations decreased with higher flows. | ||
| 150 | The total input into the lagoon from the two discharges estimated for | 150 | The total input into the lagoon from the two discharges estimated for | ||
| 151 | the period September 2002-October 2003 were 10,142 t.yr(-1) of | 151 | the period September 2002-October 2003 were 10,142 t.yr(-1) of | ||
| 152 | suspended sediments, 389 t.yr(-1)supercript stop of particulate | 152 | suspended sediments, 389 t.yr(-1)supercript stop of particulate | ||
| 153 | organic matter, 2,010 t.yr(-1) of dissolved inorganic nitrogen (93 % | 153 | organic matter, 2,010 t.yr(-1) of dissolved inorganic nitrogen (93 % | ||
| 154 | as NO3-) and 178 t.yr(-1) of soluble reactive phosphorus. The Albujon | 154 | as NO3-) and 178 t.yr(-1) of soluble reactive phosphorus. The Albujon | ||
| 155 | wadi exported about 80% of the N load and 70% of the P load. Higher | 155 | wadi exported about 80% of the N load and 70% of the P load. Higher | ||
| 156 | flows contributed approximately 80% of the total discharge and | 156 | flows contributed approximately 80% of the total discharge and | ||
| 157 | nutrient loads, 99% of suspended sediment and 88% of the particulate | 157 | nutrient loads, 99% of suspended sediment and 88% of the particulate | ||
| 158 | organic matter. Mean suspended solids and nutrient concentrations in | 158 | organic matter. Mean suspended solids and nutrient concentrations in | ||
| 159 | the lagoon followed a spatial pattern, decreasing with distance from | 159 | the lagoon followed a spatial pattern, decreasing with distance from | ||
| 160 | the mouth of the Albujon wadi. Water nitrate and phosphate | 160 | the mouth of the Albujon wadi. Water nitrate and phosphate | ||
| 161 | concentrations in the Mar Menor lagoon were lower than reference | 161 | concentrations in the Mar Menor lagoon were lower than reference | ||
| 162 | limits for eutrophic conditions, except after heavy rains. Nutrient | 162 | limits for eutrophic conditions, except after heavy rains. Nutrient | ||
| 163 | concentrations were positively correlated with precipitation variables | 163 | concentrations were positively correlated with precipitation variables | ||
| 164 | and particulate and nutrient inputs. Phosphorus was the most limiting | 164 | and particulate and nutrient inputs. Phosphorus was the most limiting | ||
| 165 | nutrient in the Mar Menor, the DIN:SRP ratios found being higher than | 165 | nutrient in the Mar Menor, the DIN:SRP ratios found being higher than | ||
| 166 | the Redfield ratio on all sampling dates. Phytoplankton bloom in the | 166 | the Redfield ratio on all sampling dates. Phytoplankton bloom in the | ||
| 167 | lagoon was only found next to the Albujon mouth during late summer and | 167 | lagoon was only found next to the Albujon mouth during late summer and | ||
| 168 | extending 5000 m into the lagoon in autumn as a consequence of large | 168 | extending 5000 m into the lagoon in autumn as a consequence of large | ||
| 169 | freshwater discharge caused by flash floods. Around 53.6% of the | 169 | freshwater discharge caused by flash floods. Around 53.6% of the | ||
| 170 | variation in chlorophyll a in the lagoon was explained by the NH4 and | 170 | variation in chlorophyll a in the lagoon was explained by the NH4 and | ||
| 171 | NO3 inputs and distance from the Albujon mouth. A good deal of P input | 171 | NO3 inputs and distance from the Albujon mouth. A good deal of P input | ||
| 172 | into the lagoon is retained in the sediments, supporting a high | 172 | into the lagoon is retained in the sediments, supporting a high | ||
| 173 | biomass of the benthic macroalga Caulerpa prolifera in spring and | 173 | biomass of the benthic macroalga Caulerpa prolifera in spring and | ||
| 174 | summer." | 174 | summer." | ||
| 175 | }, | 175 | }, | ||
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| 360 | "id": "84335733-0721-4020-983e-6887954016ee", | 331 | "id": "84335733-0721-4020-983e-6887954016ee", | ||
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| 369 | "theme_es": [ | 340 | "theme_es": [ | ||
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| 371 | ], | 342 | ], | ||
| 372 | "title": "Nutrient and particulate inputs into the Mar Menor lagoon | 343 | "title": "Nutrient and particulate inputs into the Mar Menor lagoon | ||
| 373 | (Se Spain) from an intensive agricultural watershed", | 344 | (Se Spain) from an intensive agricultural watershed", | ||
| 374 | "title_translated": { | 345 | "title_translated": { | ||
| 375 | "es": "Nutrient and particulate inputs into the Mar Menor lagoon | 346 | "es": "Nutrient and particulate inputs into the Mar Menor lagoon | ||
| 376 | (Se Spain) from an intensive agricultural watershed" | 347 | (Se Spain) from an intensive agricultural watershed" | ||
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