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En el instante 23 de junio de 2026, 16:11:25 UTC,
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Modificado el valor del campo
spatial_coverage
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en Assessing the effectiveness of potential best management practices for science-informed decision support at the watershed scale: The case of the Mar Menor coastal lagoon, Spain
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| 94 | "notes": "Coastal lagoons are ecosystems of high environmental | 94 | "notes": "Coastal lagoons are ecosystems of high environmental | ||
| 95 | importance but are quite vulnerable to human activities. The | 95 | importance but are quite vulnerable to human activities. The | ||
| 96 | continuous inflow of pollutant loads can trigger negative impacts on | 96 | continuous inflow of pollutant loads can trigger negative impacts on | ||
| 97 | the ecological status of these water bodies, which is contrary to the | 97 | the ecological status of these water bodies, which is contrary to the | ||
| 98 | European Green Deal. One example is the Mar Menor coastal lagoon in | 98 | European Green Deal. One example is the Mar Menor coastal lagoon in | ||
| 99 | Spain, which has experienced significant environmental degradation in | 99 | Spain, which has experienced significant environmental degradation in | ||
| 100 | recent years due to excessive external nutrient input, especially from | 100 | recent years due to excessive external nutrient input, especially from | ||
| 101 | non-point source (NPS) pollution. Mar Menor is one of the largest | 101 | non-point source (NPS) pollution. Mar Menor is one of the largest | ||
| 102 | coastal lagoons of the Mediterranean region and a site of great | 102 | coastal lagoons of the Mediterranean region and a site of great | ||
| 103 | ecological and socio-economic value. In this study, the highly | 103 | ecological and socio-economic value. In this study, the highly | ||
| 104 | anthropogenic and complex watershed of Mar Menor, known as Campo de | 104 | anthropogenic and complex watershed of Mar Menor, known as Campo de | ||
| 105 | Cartagena (1244 km2), was modelled with the Soil and Water Assessment | 105 | Cartagena (1244 km2), was modelled with the Soil and Water Assessment | ||
| 106 | Tool (SWAT) to analyse potential options for recovery of this unique | 106 | Tool (SWAT) to analyse potential options for recovery of this unique | ||
| 107 | system. The model was used to simulate several best management | 107 | system. The model was used to simulate several best management | ||
| 108 | practices (BMP) proposed by recent MarMenor regulations, such as | 108 | practices (BMP) proposed by recent MarMenor regulations, such as | ||
| 109 | vegetative filter strips, shoreline buffers, contour farming, removal | 109 | vegetative filter strips, shoreline buffers, contour farming, removal | ||
| 110 | of illegal agriculture, crop rotation management, waterway vegetation | 110 | of illegal agriculture, crop rotation management, waterway vegetation | ||
| 111 | restoration, fertiliser management and greenhouse rainwater | 111 | restoration, fertiliser management and greenhouse rainwater | ||
| 112 | harvesting. Sixteen scenarios of individual and combined BMPs were | 112 | harvesting. Sixteen scenarios of individual and combined BMPs were | ||
| 113 | analysed in this study. We found that, as individual measures, | 113 | analysed in this study. We found that, as individual measures, | ||
| 114 | vegetative filter strips and contour farming were most effective in | 114 | vegetative filter strips and contour farming were most effective in | ||
| 115 | nutrient reduction: approximately 30% for total nitrogen (TN) and 40 % | 115 | nutrient reduction: approximately 30% for total nitrogen (TN) and 40 % | ||
| 116 | for total phosphorus (TP). Moreover, waterway vegetation restoration | 116 | for total phosphorus (TP). Moreover, waterway vegetation restoration | ||
| 117 | showed the highest sediment (S) reduction at approximately 20 %. | 117 | showed the highest sediment (S) reduction at approximately 20 %. | ||
| 118 | However, the combination of BMPs demonstrated clear synergistic | 118 | However, the combination of BMPs demonstrated clear synergistic | ||
| 119 | effects, reducing S export by 38 %, TN by 67 %, and TP by 75 %. | 119 | effects, reducing S export by 38 %, TN by 67 %, and TP by 75 %. | ||
| 120 | Selecting the most appropriate BMPs to be implemented at a watershed | 120 | Selecting the most appropriate BMPs to be implemented at a watershed | ||
| 121 | scale requires a holistic approach considering effectiveness in | 121 | scale requires a holistic approach considering effectiveness in | ||
| 122 | reducing NPS pollution loads andBMP implementation costs. Thus, we | 122 | reducing NPS pollution loads andBMP implementation costs. Thus, we | ||
| 123 | have demonstrated a way forward for enabling science-informed | 123 | have demonstrated a way forward for enabling science-informed | ||
| 124 | decision-makingwhen choosing strategies to control NPS contamination | 124 | decision-makingwhen choosing strategies to control NPS contamination | ||
| 125 | at the watershed scale.", | 125 | at the watershed scale.", | ||
| 126 | "notes_translated": { | 126 | "notes_translated": { | ||
| 127 | "es": "Coastal lagoons are ecosystems of high environmental | 127 | "es": "Coastal lagoons are ecosystems of high environmental | ||
| 128 | importance but are quite vulnerable to human activities. The | 128 | importance but are quite vulnerable to human activities. The | ||
| 129 | continuous inflow of pollutant loads can trigger negative impacts on | 129 | continuous inflow of pollutant loads can trigger negative impacts on | ||
| 130 | the ecological status of these water bodies, which is contrary to the | 130 | the ecological status of these water bodies, which is contrary to the | ||
| 131 | European Green Deal. One example is the Mar Menor coastal lagoon in | 131 | European Green Deal. One example is the Mar Menor coastal lagoon in | ||
| 132 | Spain, which has experienced significant environmental degradation in | 132 | Spain, which has experienced significant environmental degradation in | ||
| 133 | recent years due to excessive external nutrient input, especially from | 133 | recent years due to excessive external nutrient input, especially from | ||
| 134 | non-point source (NPS) pollution. Mar Menor is one of the largest | 134 | non-point source (NPS) pollution. Mar Menor is one of the largest | ||
| 135 | coastal lagoons of the Mediterranean region and a site of great | 135 | coastal lagoons of the Mediterranean region and a site of great | ||
| 136 | ecological and socio-economic value. In this study, the highly | 136 | ecological and socio-economic value. In this study, the highly | ||
| 137 | anthropogenic and complex watershed of Mar Menor, known as Campo de | 137 | anthropogenic and complex watershed of Mar Menor, known as Campo de | ||
| 138 | Cartagena (1244 km2), was modelled with the Soil and Water Assessment | 138 | Cartagena (1244 km2), was modelled with the Soil and Water Assessment | ||
| 139 | Tool (SWAT) to analyse potential options for recovery of this unique | 139 | Tool (SWAT) to analyse potential options for recovery of this unique | ||
| 140 | system. The model was used to simulate several best management | 140 | system. The model was used to simulate several best management | ||
| 141 | practices (BMP) proposed by recent MarMenor regulations, such as | 141 | practices (BMP) proposed by recent MarMenor regulations, such as | ||
| 142 | vegetative filter strips, shoreline buffers, contour farming, removal | 142 | vegetative filter strips, shoreline buffers, contour farming, removal | ||
| 143 | of illegal agriculture, crop rotation management, waterway vegetation | 143 | of illegal agriculture, crop rotation management, waterway vegetation | ||
| 144 | restoration, fertiliser management and greenhouse rainwater | 144 | restoration, fertiliser management and greenhouse rainwater | ||
| 145 | harvesting. Sixteen scenarios of individual and combined BMPs were | 145 | harvesting. Sixteen scenarios of individual and combined BMPs were | ||
| 146 | analysed in this study. We found that, as individual measures, | 146 | analysed in this study. We found that, as individual measures, | ||
| 147 | vegetative filter strips and contour farming were most effective in | 147 | vegetative filter strips and contour farming were most effective in | ||
| 148 | nutrient reduction: approximately 30% for total nitrogen (TN) and 40 % | 148 | nutrient reduction: approximately 30% for total nitrogen (TN) and 40 % | ||
| 149 | for total phosphorus (TP). Moreover, waterway vegetation restoration | 149 | for total phosphorus (TP). Moreover, waterway vegetation restoration | ||
| 150 | showed the highest sediment (S) reduction at approximately 20 %. | 150 | showed the highest sediment (S) reduction at approximately 20 %. | ||
| 151 | However, the combination of BMPs demonstrated clear synergistic | 151 | However, the combination of BMPs demonstrated clear synergistic | ||
| 152 | effects, reducing S export by 38 %, TN by 67 %, and TP by 75 %. | 152 | effects, reducing S export by 38 %, TN by 67 %, and TP by 75 %. | ||
| 153 | Selecting the most appropriate BMPs to be implemented at a watershed | 153 | Selecting the most appropriate BMPs to be implemented at a watershed | ||
| 154 | scale requires a holistic approach considering effectiveness in | 154 | scale requires a holistic approach considering effectiveness in | ||
| 155 | reducing NPS pollution loads andBMP implementation costs. Thus, we | 155 | reducing NPS pollution loads andBMP implementation costs. Thus, we | ||
| 156 | have demonstrated a way forward for enabling science-informed | 156 | have demonstrated a way forward for enabling science-informed | ||
| 157 | decision-makingwhen choosing strategies to control NPS contamination | 157 | decision-makingwhen choosing strategies to control NPS contamination | ||
| 158 | at the watershed scale." | 158 | at the watershed scale." | ||
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