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En el instante 23 de junio de 2026, 16:11:40 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 Mar Menor lagoon (SE Spain) chlorophyll-a and turbidity estimation with Sentinel-2
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| 93 | "name": "26fd2b61-79aa-5fe3-bcbe-997a2ef4d034", | 93 | "name": "26fd2b61-79aa-5fe3-bcbe-997a2ef4d034", | ||
| 94 | "notes": "Mar Menor is a Mediterranean Coastal lagoon with high | 94 | "notes": "Mar Menor is a Mediterranean Coastal lagoon with high | ||
| 95 | environmental and social value, but has suffered important episodes of | 95 | environmental and social value, but has suffered important episodes of | ||
| 96 | contamination in recent years due to heavy rains, sediment dragging | 96 | contamination in recent years due to heavy rains, sediment dragging | ||
| 97 | and polluting substances mainly from agriculture as well as the entry | 97 | and polluting substances mainly from agriculture as well as the entry | ||
| 98 | of mining waste, causing an increase in eutrophication. Water quality | 98 | of mining waste, causing an increase in eutrophication. Water quality | ||
| 99 | variables such as chlorophyll-a concentration [Chl-a] and turbidity, | 99 | variables such as chlorophyll-a concentration [Chl-a] and turbidity, | ||
| 100 | can be studied through its optical properties by remote sensing | 100 | can be studied through its optical properties by remote sensing | ||
| 101 | techniques. In this work, a methodology is proposed for monitoring | 101 | techniques. In this work, a methodology is proposed for monitoring | ||
| 102 | [Chl-a] and the turbidity of the Mar Menor using Sentinel-2 images. | 102 | [Chl-a] and the turbidity of the Mar Menor using Sentinel-2 images. | ||
| 103 | For this purpose, an extensive database of both variables was used | 103 | For this purpose, an extensive database of both variables was used | ||
| 104 | consisting of data taken on different dates between 2016 and 2019 at | 104 | consisting of data taken on different dates between 2016 and 2019 at | ||
| 105 | 12 points of Mar Menor. The images were atmospherically corrected | 105 | 12 points of Mar Menor. The images were atmospherically corrected | ||
| 106 | using Case 2 Regional Coast Color Processor (C2RCC) version for turbid | 106 | using Case 2 Regional Coast Color Processor (C2RCC) version for turbid | ||
| 107 | waters (C2X) to obtain the water surface reflectance. Then several | 107 | waters (C2X) to obtain the water surface reflectance. Then several | ||
| 108 | arithmetic relations between database and reflectance bands used in | 108 | arithmetic relations between database and reflectance bands used in | ||
| 109 | the bibliography for [Chl-a] and turbidity were analyzed. Comparing | 109 | the bibliography for [Chl-a] and turbidity were analyzed. Comparing | ||
| 110 | the results of each one of these relations with the in situ data, | 110 | the results of each one of these relations with the in situ data, | ||
| 111 | decided that the best index for [Chl-a] estimation is the relation | 111 | decided that the best index for [Chl-a] estimation is the relation | ||
| 112 | (R560 + R705)/(R560 + R665) with an RMSE = 2.6 mg/m(3) and a NRMSE = | 112 | (R560 + R705)/(R560 + R665) with an RMSE = 2.6 mg/m(3) and a NRMSE = | ||
| 113 | 9.1 % and for turbidity R705*R705/R490 with an RMSE = 1.5 NTU and a | 113 | 9.1 % and for turbidity R705*R705/R490 with an RMSE = 1.5 NTU and a | ||
| 114 | NRMSE=10.9 %. Finally, by applying these relationships on different | 114 | NRMSE=10.9 %. Finally, by applying these relationships on different | ||
| 115 | dates, thematic maps of [Chl-a] and turbidity of Mar Menor were | 115 | dates, thematic maps of [Chl-a] and turbidity of Mar Menor were | ||
| 116 | obtained. One of these images was some days after September 2019 | 116 | obtained. One of these images was some days after September 2019 | ||
| 117 | torrential rains, in which a considerable [Chl-a] and turbidity | 117 | torrential rains, in which a considerable [Chl-a] and turbidity | ||
| 118 | increase was observed.", | 118 | increase was observed.", | ||
| 119 | "notes_translated": { | 119 | "notes_translated": { | ||
| 120 | "es": "Mar Menor is a Mediterranean Coastal lagoon with high | 120 | "es": "Mar Menor is a Mediterranean Coastal lagoon with high | ||
| 121 | environmental and social value, but has suffered important episodes of | 121 | environmental and social value, but has suffered important episodes of | ||
| 122 | contamination in recent years due to heavy rains, sediment dragging | 122 | contamination in recent years due to heavy rains, sediment dragging | ||
| 123 | and polluting substances mainly from agriculture as well as the entry | 123 | and polluting substances mainly from agriculture as well as the entry | ||
| 124 | of mining waste, causing an increase in eutrophication. Water quality | 124 | of mining waste, causing an increase in eutrophication. Water quality | ||
| 125 | variables such as chlorophyll-a concentration [Chl-a] and turbidity, | 125 | variables such as chlorophyll-a concentration [Chl-a] and turbidity, | ||
| 126 | can be studied through its optical properties by remote sensing | 126 | can be studied through its optical properties by remote sensing | ||
| 127 | techniques. In this work, a methodology is proposed for monitoring | 127 | techniques. In this work, a methodology is proposed for monitoring | ||
| 128 | [Chl-a] and the turbidity of the Mar Menor using Sentinel-2 images. | 128 | [Chl-a] and the turbidity of the Mar Menor using Sentinel-2 images. | ||
| 129 | For this purpose, an extensive database of both variables was used | 129 | For this purpose, an extensive database of both variables was used | ||
| 130 | consisting of data taken on different dates between 2016 and 2019 at | 130 | consisting of data taken on different dates between 2016 and 2019 at | ||
| 131 | 12 points of Mar Menor. The images were atmospherically corrected | 131 | 12 points of Mar Menor. The images were atmospherically corrected | ||
| 132 | using Case 2 Regional Coast Color Processor (C2RCC) version for turbid | 132 | using Case 2 Regional Coast Color Processor (C2RCC) version for turbid | ||
| 133 | waters (C2X) to obtain the water surface reflectance. Then several | 133 | waters (C2X) to obtain the water surface reflectance. Then several | ||
| 134 | arithmetic relations between database and reflectance bands used in | 134 | arithmetic relations between database and reflectance bands used in | ||
| 135 | the bibliography for [Chl-a] and turbidity were analyzed. Comparing | 135 | the bibliography for [Chl-a] and turbidity were analyzed. Comparing | ||
| 136 | the results of each one of these relations with the in situ data, | 136 | the results of each one of these relations with the in situ data, | ||
| 137 | decided that the best index for [Chl-a] estimation is the relation | 137 | decided that the best index for [Chl-a] estimation is the relation | ||
| 138 | (R560 + R705)/(R560 + R665) with an RMSE = 2.6 mg/m(3) and a NRMSE = | 138 | (R560 + R705)/(R560 + R665) with an RMSE = 2.6 mg/m(3) and a NRMSE = | ||
| 139 | 9.1 % and for turbidity R705*R705/R490 with an RMSE = 1.5 NTU and a | 139 | 9.1 % and for turbidity R705*R705/R490 with an RMSE = 1.5 NTU and a | ||
| 140 | NRMSE=10.9 %. Finally, by applying these relationships on different | 140 | NRMSE=10.9 %. Finally, by applying these relationships on different | ||
| 141 | dates, thematic maps of [Chl-a] and turbidity of Mar Menor were | 141 | dates, thematic maps of [Chl-a] and turbidity of Mar Menor were | ||
| 142 | obtained. One of these images was some days after September 2019 | 142 | obtained. One of these images was some days after September 2019 | ||
| 143 | torrential rains, in which a considerable [Chl-a] and turbidity | 143 | torrential rains, in which a considerable [Chl-a] and turbidity | ||
| 144 | increase was observed." | 144 | increase was observed." | ||
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| 346 | ], | 317 | ], | ||
| 347 | "title": "Mar Menor lagoon (SE Spain) chlorophyll-a and turbidity | 318 | "title": "Mar Menor lagoon (SE Spain) chlorophyll-a and turbidity | ||
| 348 | estimation with Sentinel-2", | 319 | estimation with Sentinel-2", | ||
| 349 | "title_translated": { | 320 | "title_translated": { | ||
| 350 | "es": "Mar Menor lagoon (SE Spain) chlorophyll-a and turbidity | 321 | "es": "Mar Menor lagoon (SE Spain) chlorophyll-a and turbidity | ||
| 351 | estimation with Sentinel-2" | 322 | estimation with Sentinel-2" | ||
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| 358 | "version_notes": { | 329 | "version_notes": { | ||
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| 360 | } | 331 | } | ||
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