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En el instante 23 de junio de 2026, 16:09:20 UTC,
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Modificado el valor del campo
spatial_coverage
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en Estimating groundwater use patterns of perennial and seasonal crops in a Mediterranean irrigation scheme, using remoto sensing
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| 95 | "notes": "This work explores the use of satellite-based vegetation | 95 | "notes": "This work explores the use of satellite-based vegetation | ||
| 96 | indices (VI) to study groundwater use in a semi\u0002arid agricultural | 96 | indices (VI) to study groundwater use in a semi\u0002arid agricultural | ||
| 97 | irrigated area. The objective is to obtain insight in spatial and | 97 | irrigated area. The objective is to obtain insight in spatial and | ||
| 98 | temporal patterns and differences in groundwater usage of perennial | 98 | temporal patterns and differences in groundwater usage of perennial | ||
| 99 | (mainly fruit trees) and seasonal crops (mainly row veg\u0002etable | 99 | (mainly fruit trees) and seasonal crops (mainly row veg\u0002etable | ||
| 100 | crops) under varying climatic conditions. Cropping intensities of | 100 | crops) under varying climatic conditions. Cropping intensities of | ||
| 101 | seasonal crops are derived for each sector and irrigation water | 101 | seasonal crops are derived for each sector and irrigation water | ||
| 102 | applied (IWA) is calculated using VI-based (NDVI from MODIS) actual | 102 | applied (IWA) is calculated using VI-based (NDVI from MODIS) actual | ||
| 103 | evapotranspiration estimates and local efficiency factors. Groundwater | 103 | evapotranspiration estimates and local efficiency factors. Groundwater | ||
| 104 | use is then derived as the residual of total IWA and surface water | 104 | use is then derived as the residual of total IWA and surface water | ||
| 105 | supplies for each sector and crop type. The results of IWA following | 105 | supplies for each sector and crop type. The results of IWA following | ||
| 106 | this methodology were compared with survey-based results for two crop | 106 | this methodology were compared with survey-based results for two crop | ||
| 107 | types. Results correlated well, but deviate most during drought | 107 | types. Results correlated well, but deviate most during drought | ||
| 108 | period, likely due to salt leaching practices. Monthly groundwater use | 108 | period, likely due to salt leaching practices. Monthly groundwater use | ||
| 109 | pat\u0002terns and spatial and temporal differences during normal | 109 | pat\u0002terns and spatial and temporal differences during normal | ||
| 110 | water availability and drought conditions are reported. On average, | 110 | water availability and drought conditions are reported. On average, | ||
| 111 | about 50% of irrigation water is extracted from aquifers, but during | 111 | about 50% of irrigation water is extracted from aquifers, but during | ||
| 112 | droughts this percentage increases considerably. Perennial crops show | 112 | droughts this percentage increases considerably. Perennial crops show | ||
| 113 | sharper increases in groundwater use under such conditions than | 113 | sharper increases in groundwater use under such conditions than | ||
| 114 | seasonal crops. Overall, seasonal crops put more pressure on the | 114 | seasonal crops. Overall, seasonal crops put more pressure on the | ||
| 115 | groundwater resource than perennial crops. Our results and methodology | 115 | groundwater resource than perennial crops. Our results and methodology | ||
| 116 | will be useful for water resource managers, and policy makers | 116 | will be useful for water resource managers, and policy makers | ||
| 117 | concerned with the role of groundwater resources on the sustainability | 117 | concerned with the role of groundwater resources on the sustainability | ||
| 118 | of semiarid agricultural regions.", | 118 | of semiarid agricultural regions.", | ||
| 119 | "notes_translated": { | 119 | "notes_translated": { | ||
| 120 | "es": "This work explores the use of satellite-based vegetation | 120 | "es": "This work explores the use of satellite-based vegetation | ||
| 121 | indices (VI) to study groundwater use in a semi\u0002arid agricultural | 121 | indices (VI) to study groundwater use in a semi\u0002arid agricultural | ||
| 122 | irrigated area. The objective is to obtain insight in spatial and | 122 | irrigated area. The objective is to obtain insight in spatial and | ||
| 123 | temporal patterns and differences in groundwater usage of perennial | 123 | temporal patterns and differences in groundwater usage of perennial | ||
| 124 | (mainly fruit trees) and seasonal crops (mainly row veg\u0002etable | 124 | (mainly fruit trees) and seasonal crops (mainly row veg\u0002etable | ||
| 125 | crops) under varying climatic conditions. Cropping intensities of | 125 | crops) under varying climatic conditions. Cropping intensities of | ||
| 126 | seasonal crops are derived for each sector and irrigation water | 126 | seasonal crops are derived for each sector and irrigation water | ||
| 127 | applied (IWA) is calculated using VI-based (NDVI from MODIS) actual | 127 | applied (IWA) is calculated using VI-based (NDVI from MODIS) actual | ||
| 128 | evapotranspiration estimates and local efficiency factors. Groundwater | 128 | evapotranspiration estimates and local efficiency factors. Groundwater | ||
| 129 | use is then derived as the residual of total IWA and surface water | 129 | use is then derived as the residual of total IWA and surface water | ||
| 130 | supplies for each sector and crop type. The results of IWA following | 130 | supplies for each sector and crop type. The results of IWA following | ||
| 131 | this methodology were compared with survey-based results for two crop | 131 | this methodology were compared with survey-based results for two crop | ||
| 132 | types. Results correlated well, but deviate most during drought | 132 | types. Results correlated well, but deviate most during drought | ||
| 133 | period, likely due to salt leaching practices. Monthly groundwater use | 133 | period, likely due to salt leaching practices. Monthly groundwater use | ||
| 134 | pat\u0002terns and spatial and temporal differences during normal | 134 | pat\u0002terns and spatial and temporal differences during normal | ||
| 135 | water availability and drought conditions are reported. On average, | 135 | water availability and drought conditions are reported. On average, | ||
| 136 | about 50% of irrigation water is extracted from aquifers, but during | 136 | about 50% of irrigation water is extracted from aquifers, but during | ||
| 137 | droughts this percentage increases considerably. Perennial crops show | 137 | droughts this percentage increases considerably. Perennial crops show | ||
| 138 | sharper increases in groundwater use under such conditions than | 138 | sharper increases in groundwater use under such conditions than | ||
| 139 | seasonal crops. Overall, seasonal crops put more pressure on the | 139 | seasonal crops. Overall, seasonal crops put more pressure on the | ||
| 140 | groundwater resource than perennial crops. Our results and methodology | 140 | groundwater resource than perennial crops. Our results and methodology | ||
| 141 | will be useful for water resource managers, and policy makers | 141 | will be useful for water resource managers, and policy makers | ||
| 142 | concerned with the role of groundwater resources on the sustainability | 142 | concerned with the role of groundwater resources on the sustainability | ||
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| 288 | 259 | ||||
| 289 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 260 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 290 | ], | 261 | ], | ||
| 291 | "tags": [ | 262 | "tags": [ | ||
| 292 | { | 263 | { | ||
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| 294 | "id": "34809f0c-ffb1-4169-a701-6e9b9b10278b", | 265 | "id": "34809f0c-ffb1-4169-a701-6e9b9b10278b", | ||
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| 301 | "id": "7af4b5b1-a152-48cb-b581-a321fbe3ff88", | 272 | "id": "7af4b5b1-a152-48cb-b581-a321fbe3ff88", | ||
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| 308 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | 279 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | ||
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| 315 | "id": "615f969b-9f23-4c8a-b31d-82fef513bfbc", | 286 | "id": "615f969b-9f23-4c8a-b31d-82fef513bfbc", | ||
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| 329 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 300 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
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| 333 | } | 304 | } | ||
| 334 | ], | 305 | ], | ||
| 335 | "thematic_area": [ | 306 | "thematic_area": [ | ||
| 336 | "espacios_protegidos" | 307 | "espacios_protegidos" | ||
| 337 | ], | 308 | ], | ||
| 338 | "theme_es": [ | 309 | "theme_es": [ | ||
| 339 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 310 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 340 | ], | 311 | ], | ||
| 341 | "title": "Estimating groundwater use patterns of perennial and | 312 | "title": "Estimating groundwater use patterns of perennial and | ||
| 342 | seasonal crops in a Mediterranean irrigation scheme, using remoto | 313 | seasonal crops in a Mediterranean irrigation scheme, using remoto | ||
| 343 | sensing", | 314 | sensing", | ||
| 344 | "title_translated": { | 315 | "title_translated": { | ||
| 345 | "es": "Estimating groundwater use patterns of perennial and | 316 | "es": "Estimating groundwater use patterns of perennial and | ||
| 346 | seasonal crops in a Mediterranean irrigation scheme, using remoto | 317 | seasonal crops in a Mediterranean irrigation scheme, using remoto | ||
| 347 | sensing" | 318 | sensing" | ||
| 348 | }, | 319 | }, | ||
| 349 | "topic": | 320 | "topic": | ||
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| 351 | "type": "dataset", | 322 | "type": "dataset", | ||
| 352 | "url": | 323 | "url": | ||
| 353 | //iepnb.es:443/catalogo/dataset/45181a31-73ab-504f-b476-adb1664d0895", | 324 | //iepnb.es:443/catalogo/dataset/45181a31-73ab-504f-b476-adb1664d0895", | ||
| 354 | "version_notes": { | 325 | "version_notes": { | ||
| 355 | "es": "" | 326 | "es": "" | ||
| 356 | } | 327 | } | ||
| 357 | } | 328 | } |