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en Influence of an intensive agricultural drainage basin on the seasonal distribution of organic pollutants in seawater from a Mediterranean coastal lagoon (Mar Menor, SE Spain) -
Modificado el valor del campo
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del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Influence of an intensive agricultural drainage basin on the seasonal distribution of organic pollutants in seawater from a Mediterranean coastal lagoon (Mar Menor, SE Spain)
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| 96 | hydrocarbons, polychlorinated biphenyls, organochlorine pesticides, | 106 | hydrocarbons, polychlorinated biphenyls, organochlorine pesticides, | ||
| 97 | organophosphorus pesticides, triazines and other organic pollutants in | 107 | organophosphorus pesticides, triazines and other organic pollutants in | ||
| 98 | surface seawater from the Mar Menor lagoon (SE Spain) was | 108 | surface seawater from the Mar Menor lagoon (SE Spain) was | ||
| 99 | characterized from spring 2009 to winter 2010 by stir bar sorptive | 109 | characterized from spring 2009 to winter 2010 by stir bar sorptive | ||
| 100 | extraction and thermal desorption followed by capillary gas | 110 | extraction and thermal desorption followed by capillary gas | ||
| 101 | chromatography coupled to mass spectrometry (SBSE-GC-MS). The most | 111 | chromatography coupled to mass spectrometry (SBSE-GC-MS). The most | ||
| 102 | ubiquitous pollutants were chlorpyrifos, chlortal-dimethyl, | 112 | ubiquitous pollutants were chlorpyrifos, chlortal-dimethyl, | ||
| 103 | terbuthylazine, naphthalene and propyzamide throughout the year. | 113 | terbuthylazine, naphthalene and propyzamide throughout the year. | ||
| 104 | Insecticides and herbicides were predominant in summer and spring, and | 114 | Insecticides and herbicides were predominant in summer and spring, and | ||
| 105 | fungicides were more abundant in autumn and winter. Chlorpyrifos was | 115 | fungicides were more abundant in autumn and winter. Chlorpyrifos was | ||
| 106 | predominant in autumn and spring; herbicides (propyzamide, | 116 | predominant in autumn and spring; herbicides (propyzamide, | ||
| 107 | terbuthyldzine and terbuthylazinedesethyl) in autumn and fungicides | 117 | terbuthyldzine and terbuthylazinedesethyl) in autumn and fungicides | ||
| 108 | (flutolanil, boscalid, cyprodinil) in autumn and winter. The highest | 118 | (flutolanil, boscalid, cyprodinil) in autumn and winter. The highest | ||
| 109 | concentrations for the majority of pollutants were detected in autumn | 119 | concentrations for the majority of pollutants were detected in autumn | ||
| 110 | as consequence of air and surface/ground water inputs, and above all | 120 | as consequence of air and surface/ground water inputs, and above all | ||
| 111 | of desorption from terrigenous materials deposited in sediments by two | 121 | of desorption from terrigenous materials deposited in sediments by two | ||
| 112 | intense flash flood events (September 2009). (C) 2013 Elsevier Ltd. | 122 | intense flash flood events (September 2009). (C) 2013 Elsevier Ltd. | ||
| 113 | All rights reserved.", | 123 | All rights reserved.", | ||
| 114 | "notes_translated": { | 124 | "notes_translated": { | ||
| 115 | "es": "The seasonal distribution of polycyclic aromatic | 125 | "es": "The seasonal distribution of polycyclic aromatic | ||
| 116 | hydrocarbons, polychlorinated biphenyls, organochlorine pesticides, | 126 | hydrocarbons, polychlorinated biphenyls, organochlorine pesticides, | ||
| 117 | organophosphorus pesticides, triazines and other organic pollutants in | 127 | organophosphorus pesticides, triazines and other organic pollutants in | ||
| 118 | surface seawater from the Mar Menor lagoon (SE Spain) was | 128 | surface seawater from the Mar Menor lagoon (SE Spain) was | ||
| 119 | characterized from spring 2009 to winter 2010 by stir bar sorptive | 129 | characterized from spring 2009 to winter 2010 by stir bar sorptive | ||
| 120 | extraction and thermal desorption followed by capillary gas | 130 | extraction and thermal desorption followed by capillary gas | ||
| 121 | chromatography coupled to mass spectrometry (SBSE-GC-MS). The most | 131 | chromatography coupled to mass spectrometry (SBSE-GC-MS). The most | ||
| 122 | ubiquitous pollutants were chlorpyrifos, chlortal-dimethyl, | 132 | ubiquitous pollutants were chlorpyrifos, chlortal-dimethyl, | ||
| 123 | terbuthylazine, naphthalene and propyzamide throughout the year. | 133 | terbuthylazine, naphthalene and propyzamide throughout the year. | ||
| 124 | Insecticides and herbicides were predominant in summer and spring, and | 134 | Insecticides and herbicides were predominant in summer and spring, and | ||
| 125 | fungicides were more abundant in autumn and winter. Chlorpyrifos was | 135 | fungicides were more abundant in autumn and winter. Chlorpyrifos was | ||
| 126 | predominant in autumn and spring; herbicides (propyzamide, | 136 | predominant in autumn and spring; herbicides (propyzamide, | ||
| 127 | terbuthyldzine and terbuthylazinedesethyl) in autumn and fungicides | 137 | terbuthyldzine and terbuthylazinedesethyl) in autumn and fungicides | ||
| 128 | (flutolanil, boscalid, cyprodinil) in autumn and winter. The highest | 138 | (flutolanil, boscalid, cyprodinil) in autumn and winter. The highest | ||
| 129 | concentrations for the majority of pollutants were detected in autumn | 139 | concentrations for the majority of pollutants were detected in autumn | ||
| 130 | as consequence of air and surface/ground water inputs, and above all | 140 | as consequence of air and surface/ground water inputs, and above all | ||
| 131 | of desorption from terrigenous materials deposited in sediments by two | 141 | of desorption from terrigenous materials deposited in sediments by two | ||
| 132 | intense flash flood events (September 2009). (C) 2013 Elsevier Ltd. | 142 | intense flash flood events (September 2009). (C) 2013 Elsevier Ltd. | ||
| 133 | All rights reserved." | 143 | All rights reserved." | ||
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| 229 | 37.38]]]}", | 239 | 37.38]]]}", | ||
| 230 | "spatial_coverage": [ | 240 | "spatial_coverage": [ | ||
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| 236 | 38.07]}", | 246 | 38.07]}", | ||
| 237 | "text": "Regi\u00f3n de Murcia", | 247 | "text": "Regi\u00f3n de Murcia", | ||
| 238 | "uri": | 248 | "uri": | ||
| 239 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | 249 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | ||
| 240 | } | 250 | } | ||
| 241 | ], | 251 | ], | ||
| 242 | "spatial_uri": | 252 | "spatial_uri": | ||
| 243 | tos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia", | 253 | tos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia", | ||
| 244 | "state": "active", | 254 | "state": "active", | ||
| 245 | "study_variables": { | 255 | "study_variables": { | ||
| 246 | "es": "" | 256 | "es": "" | ||
| 247 | }, | 257 | }, | ||
| 248 | "tag_uri": [ | 258 | "tag_uri": [ | ||
| 249 | 259 | ||||
| 250 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 260 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 251 | ], | 261 | ], | ||
| 252 | "tags": [ | 262 | "tags": [ | ||
| 253 | { | 263 | { | ||
| 254 | "display_name": "agricultura", | 264 | "display_name": "agricultura", | ||
| 255 | "id": "34809f0c-ffb1-4169-a701-6e9b9b10278b", | 265 | "id": "34809f0c-ffb1-4169-a701-6e9b9b10278b", | ||
| 256 | "name": "agricultura", | 266 | "name": "agricultura", | ||
| 257 | "state": "active", | 267 | "state": "active", | ||
| 258 | "vocabulary_id": null | 268 | "vocabulary_id": null | ||
| 259 | }, | 269 | }, | ||
| 260 | { | 270 | { | ||
| 261 | "display_name": "contaminacion", | 271 | "display_name": "contaminacion", | ||
| 262 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 272 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 263 | "name": "contaminacion", | 273 | "name": "contaminacion", | ||
| 264 | "state": "active", | 274 | "state": "active", | ||
| 265 | "vocabulary_id": null | 275 | "vocabulary_id": null | ||
| 266 | }, | 276 | }, | ||
| 267 | { | 277 | { | ||
| 268 | "display_name": "infraestructuras", | 278 | "display_name": "infraestructuras", | ||
| 269 | "id": "9e9a574a-6ae9-49b0-adf2-5929c130581d", | 279 | "id": "9e9a574a-6ae9-49b0-adf2-5929c130581d", | ||
| 270 | "name": "infraestructuras", | 280 | "name": "infraestructuras", | ||
| 271 | "state": "active", | 281 | "state": "active", | ||
| 272 | "vocabulary_id": null | 282 | "vocabulary_id": null | ||
| 273 | }, | 283 | }, | ||
| 274 | { | 284 | { | ||
| 275 | "display_name": "lagunas-costeras-salobres-saladas", | 285 | "display_name": "lagunas-costeras-salobres-saladas", | ||
| 276 | "id": "92dd4d50-2752-4df9-8eeb-64128064bda8", | 286 | "id": "92dd4d50-2752-4df9-8eeb-64128064bda8", | ||
| 277 | "name": "lagunas-costeras-salobres-saladas", | 287 | "name": "lagunas-costeras-salobres-saladas", | ||
| 278 | "state": "active", | 288 | "state": "active", | ||
| 279 | "vocabulary_id": null | 289 | "vocabulary_id": null | ||
| 280 | }, | 290 | }, | ||
| 281 | { | 291 | { | ||
| 282 | "display_name": "marino", | 292 | "display_name": "marino", | ||
| 283 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 293 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 284 | "name": "marino", | 294 | "name": "marino", | ||
| 285 | "state": "active", | 295 | "state": "active", | ||
| 286 | "vocabulary_id": null | 296 | "vocabulary_id": null | ||
| 287 | }, | 297 | }, | ||
| 288 | { | 298 | { | ||
| 289 | "display_name": "monitorizacion", | 299 | "display_name": "monitorizacion", | ||
| 290 | "id": "08630ee4-23ef-407b-84cb-934e9ce058d1", | 300 | "id": "08630ee4-23ef-407b-84cb-934e9ce058d1", | ||
| 291 | "name": "monitorizacion", | 301 | "name": "monitorizacion", | ||
| 292 | "state": "active", | 302 | "state": "active", | ||
| 293 | "vocabulary_id": null | 303 | "vocabulary_id": null | ||
| 294 | } | 304 | } | ||
| 295 | ], | 305 | ], | ||
| 296 | "thematic_area": [ | 306 | "thematic_area": [ | ||
| 297 | "espacios_protegidos" | 307 | "espacios_protegidos" | ||
| 298 | ], | 308 | ], | ||
| 299 | "theme_es": [ | 309 | "theme_es": [ | ||
| 300 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 310 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 301 | ], | 311 | ], | ||
| 302 | "title": "Influence of an intensive agricultural drainage basin on | 312 | "title": "Influence of an intensive agricultural drainage basin on | ||
| 303 | the seasonal distribution of organic pollutants in seawater from a | 313 | the seasonal distribution of organic pollutants in seawater from a | ||
| 304 | Mediterranean coastal lagoon (Mar Menor, SE Spain)", | 314 | Mediterranean coastal lagoon (Mar Menor, SE Spain)", | ||
| 305 | "title_translated": { | 315 | "title_translated": { | ||
| 306 | "es": "Influence of an intensive agricultural drainage basin on | 316 | "es": "Influence of an intensive agricultural drainage basin on | ||
| 307 | the seasonal distribution of organic pollutants in seawater from a | 317 | the seasonal distribution of organic pollutants in seawater from a | ||
| 308 | Mediterranean coastal lagoon (Mar Menor, SE Spain)" | 318 | Mediterranean coastal lagoon (Mar Menor, SE Spain)" | ||
| 309 | }, | 319 | }, | ||
| 310 | "topic": | 320 | "topic": | ||
| 311 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 321 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 312 | "type": "dataset", | 322 | "type": "dataset", | ||
| 313 | "url": | 323 | "url": | ||
| 314 | //iepnb.es:443/catalogo/dataset/8734e271-2006-53c0-8f68-c8ea7b7fda3f", | 324 | //iepnb.es:443/catalogo/dataset/8734e271-2006-53c0-8f68-c8ea7b7fda3f", | ||
| 315 | "version_notes": { | 325 | "version_notes": { | ||
| 316 | "es": "" | 326 | "es": "" | ||
| 317 | } | 327 | } | ||
| 318 | } | 328 | } |