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En el instante 23 de junio de 2026, 16:12:23 UTC,
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Modificado el valor del campo
spatial_coverage
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en Impact of flash flood events on the distribution of organic pollutants in surface sediments from a Mediterranean coastal lagoon (Mar Menor, SE Spain)
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| 95 | "notes": "The influence of flash flood events on the input and | 95 | "notes": "The influence of flash flood events on the input and | ||
| 96 | distribution of polycyclic aromatic hydrocarbons (PAHs), | 96 | distribution of polycyclic aromatic hydrocarbons (PAHs), | ||
| 97 | polychlorinated biphenyls (PCBs), and organochlorinated pesticides | 97 | polychlorinated biphenyls (PCBs), and organochlorinated pesticides | ||
| 98 | (OCPs) in surface sediments from the Mar Menor lagoon were | 98 | (OCPs) in surface sediments from the Mar Menor lagoon were | ||
| 99 | characterized in this study. These contaminants were analyzed in | 99 | characterized in this study. These contaminants were analyzed in | ||
| 100 | surface water samples collected during two flash flood events in the | 100 | surface water samples collected during two flash flood events in the | ||
| 101 | main surface watercourse which flow into the Mar Menor lagoon. Surface | 101 | main surface watercourse which flow into the Mar Menor lagoon. Surface | ||
| 102 | sediments were sampled semiannually before and after flash flood | 102 | sediments were sampled semiannually before and after flash flood | ||
| 103 | events. The total input of PAHs, OCPs, and PCBs (sorbed + dissolved) | 103 | events. The total input of PAHs, OCPs, and PCBs (sorbed + dissolved) | ||
| 104 | during two flash flood events was estimated at 0.98, 1.32, and 0.34 | 104 | during two flash flood events was estimated at 0.98, 1.32, and 0.34 | ||
| 105 | kg, respectively, the main input corresponding to p, p'-DDE (1.00 kg). | 105 | kg, respectively, the main input corresponding to p, p'-DDE (1.00 kg). | ||
| 106 | The distribution of organic contaminants in surface sediments was not | 106 | The distribution of organic contaminants in surface sediments was not | ||
| 107 | homogeneous as a consequence of the presence of many simultaneous | 107 | homogeneous as a consequence of the presence of many simultaneous | ||
| 108 | sources and different meteorological, hydrodynamic, and | 108 | sources and different meteorological, hydrodynamic, and | ||
| 109 | physicochemical conditions. As a consequence of flash flood events, p, | 109 | physicochemical conditions. As a consequence of flash flood events, p, | ||
| 110 | p'-DDE concentrations in surface sediments increased significantly in | 110 | p'-DDE concentrations in surface sediments increased significantly in | ||
| 111 | the central and south zones of the lagoon. However, in the case of | 111 | the central and south zones of the lagoon. However, in the case of | ||
| 112 | PCBs, a dilution effect was observed in the south zone after such | 112 | PCBs, a dilution effect was observed in the south zone after such | ||
| 113 | events, reducing the environmental risk. These changes in the | 113 | events, reducing the environmental risk. These changes in the | ||
| 114 | pollutant distribution persisted at least 1 year later (autumn 2010), | 114 | pollutant distribution persisted at least 1 year later (autumn 2010), | ||
| 115 | showing that the impact of flood events in the distribution of | 115 | showing that the impact of flood events in the distribution of | ||
| 116 | persistent organic contaminants in Mediterranean coastal lagoons is of | 116 | persistent organic contaminants in Mediterranean coastal lagoons is of | ||
| 117 | relevance according to the ecological risk assessment carried out. The | 117 | relevance according to the ecological risk assessment carried out. The | ||
| 118 | impact of these events should be also considered in other coastal | 118 | impact of these events should be also considered in other coastal | ||
| 119 | systems, especially in semiarid and semiconfined areas.", | 119 | systems, especially in semiarid and semiconfined areas.", | ||
| 120 | "notes_translated": { | 120 | "notes_translated": { | ||
| 121 | "es": "The influence of flash flood events on the input and | 121 | "es": "The influence of flash flood events on the input and | ||
| 122 | distribution of polycyclic aromatic hydrocarbons (PAHs), | 122 | distribution of polycyclic aromatic hydrocarbons (PAHs), | ||
| 123 | polychlorinated biphenyls (PCBs), and organochlorinated pesticides | 123 | polychlorinated biphenyls (PCBs), and organochlorinated pesticides | ||
| 124 | (OCPs) in surface sediments from the Mar Menor lagoon were | 124 | (OCPs) in surface sediments from the Mar Menor lagoon were | ||
| 125 | characterized in this study. These contaminants were analyzed in | 125 | characterized in this study. These contaminants were analyzed in | ||
| 126 | surface water samples collected during two flash flood events in the | 126 | surface water samples collected during two flash flood events in the | ||
| 127 | main surface watercourse which flow into the Mar Menor lagoon. Surface | 127 | main surface watercourse which flow into the Mar Menor lagoon. Surface | ||
| 128 | sediments were sampled semiannually before and after flash flood | 128 | sediments were sampled semiannually before and after flash flood | ||
| 129 | events. The total input of PAHs, OCPs, and PCBs (sorbed + dissolved) | 129 | events. The total input of PAHs, OCPs, and PCBs (sorbed + dissolved) | ||
| 130 | during two flash flood events was estimated at 0.98, 1.32, and 0.34 | 130 | during two flash flood events was estimated at 0.98, 1.32, and 0.34 | ||
| 131 | kg, respectively, the main input corresponding to p, p'-DDE (1.00 kg). | 131 | kg, respectively, the main input corresponding to p, p'-DDE (1.00 kg). | ||
| 132 | The distribution of organic contaminants in surface sediments was not | 132 | The distribution of organic contaminants in surface sediments was not | ||
| 133 | homogeneous as a consequence of the presence of many simultaneous | 133 | homogeneous as a consequence of the presence of many simultaneous | ||
| 134 | sources and different meteorological, hydrodynamic, and | 134 | sources and different meteorological, hydrodynamic, and | ||
| 135 | physicochemical conditions. As a consequence of flash flood events, p, | 135 | physicochemical conditions. As a consequence of flash flood events, p, | ||
| 136 | p'-DDE concentrations in surface sediments increased significantly in | 136 | p'-DDE concentrations in surface sediments increased significantly in | ||
| 137 | the central and south zones of the lagoon. However, in the case of | 137 | the central and south zones of the lagoon. However, in the case of | ||
| 138 | PCBs, a dilution effect was observed in the south zone after such | 138 | PCBs, a dilution effect was observed in the south zone after such | ||
| 139 | events, reducing the environmental risk. These changes in the | 139 | events, reducing the environmental risk. These changes in the | ||
| 140 | pollutant distribution persisted at least 1 year later (autumn 2010), | 140 | pollutant distribution persisted at least 1 year later (autumn 2010), | ||
| 141 | showing that the impact of flood events in the distribution of | 141 | showing that the impact of flood events in the distribution of | ||
| 142 | persistent organic contaminants in Mediterranean coastal lagoons is of | 142 | persistent organic contaminants in Mediterranean coastal lagoons is of | ||
| 143 | relevance according to the ecological risk assessment carried out. The | 143 | relevance according to the ecological risk assessment carried out. The | ||
| 144 | impact of these events should be also considered in other coastal | 144 | impact of these events should be also considered in other coastal | ||
| 145 | systems, especially in semiarid and semiconfined areas." | 145 | systems, especially in semiarid and semiconfined areas." | ||
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