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en Occurrence of selected endocrine disrupting compounds in Iberian coastal areas and assessment of the environmental risk -
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del recurso Distribución HTML a2026-06-25
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) en Occurrence of selected endocrine disrupting compounds in Iberian coastal areas and assessment of the environmental risk
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| 95 | "notes": "The spatial and temporal distribution of selected | 105 | "notes": "The spatial and temporal distribution of selected | ||
| 96 | endocrine disrupting compounds (4-tert-octylphenol, 4-n-octylphenol, | 106 | endocrine disrupting compounds (4-tert-octylphenol, 4-n-octylphenol, | ||
| 97 | 4-n-nonylphenol, nonylphenol, and bisphenol A) in two coastal areas of | 107 | 4-n-nonylphenol, nonylphenol, and bisphenol A) in two coastal areas of | ||
| 98 | the Iberian Peninsula (Ria de Vigo and Mar Menor lagoon) were | 108 | the Iberian Peninsula (Ria de Vigo and Mar Menor lagoon) were | ||
| 99 | evaluated for the first time. Seawater and sediment samples collected | 109 | evaluated for the first time. Seawater and sediment samples collected | ||
| 100 | during spring and autumn of 2015 were analysed using greener | 110 | during spring and autumn of 2015 were analysed using greener | ||
| 101 | extraction techniques and liquid chromatography-tandem mass | 111 | extraction techniques and liquid chromatography-tandem mass | ||
| 102 | spectrometry. The presence of branched isomers (4-tert-octylphenol and | 112 | spectrometry. The presence of branched isomers (4-tert-octylphenol and | ||
| 103 | nonylphenol) and bisphenol A in almost all seawater and sediment | 113 | nonylphenol) and bisphenol A in almost all seawater and sediment | ||
| 104 | samples demonstrated their importance as pollutants in the frame of | 114 | samples demonstrated their importance as pollutants in the frame of | ||
| 105 | water policy, while no concentrations of linear isomers | 115 | water policy, while no concentrations of linear isomers | ||
| 106 | (4-n-octylphenol and 4-n-nonylphenol) were found. Higher seawater | 116 | (4-n-octylphenol and 4-n-nonylphenol) were found. Higher seawater | ||
| 107 | levels were observed in Mar Menor lagoon, especially in spring, | 117 | levels were observed in Mar Menor lagoon, especially in spring, | ||
| 108 | associated with wastewater treatment plant effluents and nautical, | 118 | associated with wastewater treatment plant effluents and nautical, | ||
| 109 | agricultural and industrial activities. Similar sediment | 119 | agricultural and industrial activities. Similar sediment | ||
| 110 | concentrations were measured in both studied areas, being nonylphenol | 120 | concentrations were measured in both studied areas, being nonylphenol | ||
| 111 | levels five times higher than those measured for the other EDCs. | 121 | levels five times higher than those measured for the other EDCs. | ||
| 112 | Experimental sediment-water partition coefficients showed a moderate | 122 | Experimental sediment-water partition coefficients showed a moderate | ||
| 113 | sorption of target compounds to sediments. Risk quotients for water | 123 | sorption of target compounds to sediments. Risk quotients for water | ||
| 114 | compartment evidenced a moderate risk posed by nonylphenol, | 124 | compartment evidenced a moderate risk posed by nonylphenol, | ||
| 115 | considering the worst-case scenario. For sediments, moderate risk | 125 | considering the worst-case scenario. For sediments, moderate risk | ||
| 116 | related to 4-tert-octylphenol and high risk to nonylphenol were | 126 | related to 4-tert-octylphenol and high risk to nonylphenol were | ||
| 117 | estimated. (C) 2019 Elsevier Ltd. All rights reserved.", | 127 | estimated. (C) 2019 Elsevier Ltd. All rights reserved.", | ||
| 118 | "notes_translated": { | 128 | "notes_translated": { | ||
| 119 | "es": "The spatial and temporal distribution of selected endocrine | 129 | "es": "The spatial and temporal distribution of selected endocrine | ||
| 120 | disrupting compounds (4-tert-octylphenol, 4-n-octylphenol, | 130 | disrupting compounds (4-tert-octylphenol, 4-n-octylphenol, | ||
| 121 | 4-n-nonylphenol, nonylphenol, and bisphenol A) in two coastal areas of | 131 | 4-n-nonylphenol, nonylphenol, and bisphenol A) in two coastal areas of | ||
| 122 | the Iberian Peninsula (Ria de Vigo and Mar Menor lagoon) were | 132 | the Iberian Peninsula (Ria de Vigo and Mar Menor lagoon) were | ||
| 123 | evaluated for the first time. Seawater and sediment samples collected | 133 | evaluated for the first time. Seawater and sediment samples collected | ||
| 124 | during spring and autumn of 2015 were analysed using greener | 134 | during spring and autumn of 2015 were analysed using greener | ||
| 125 | extraction techniques and liquid chromatography-tandem mass | 135 | extraction techniques and liquid chromatography-tandem mass | ||
| 126 | spectrometry. The presence of branched isomers (4-tert-octylphenol and | 136 | spectrometry. The presence of branched isomers (4-tert-octylphenol and | ||
| 127 | nonylphenol) and bisphenol A in almost all seawater and sediment | 137 | nonylphenol) and bisphenol A in almost all seawater and sediment | ||
| 128 | samples demonstrated their importance as pollutants in the frame of | 138 | samples demonstrated their importance as pollutants in the frame of | ||
| 129 | water policy, while no concentrations of linear isomers | 139 | water policy, while no concentrations of linear isomers | ||
| 130 | (4-n-octylphenol and 4-n-nonylphenol) were found. Higher seawater | 140 | (4-n-octylphenol and 4-n-nonylphenol) were found. Higher seawater | ||
| 131 | levels were observed in Mar Menor lagoon, especially in spring, | 141 | levels were observed in Mar Menor lagoon, especially in spring, | ||
| 132 | associated with wastewater treatment plant effluents and nautical, | 142 | associated with wastewater treatment plant effluents and nautical, | ||
| 133 | agricultural and industrial activities. Similar sediment | 143 | agricultural and industrial activities. Similar sediment | ||
| 134 | concentrations were measured in both studied areas, being nonylphenol | 144 | concentrations were measured in both studied areas, being nonylphenol | ||
| 135 | levels five times higher than those measured for the other EDCs. | 145 | levels five times higher than those measured for the other EDCs. | ||
| 136 | Experimental sediment-water partition coefficients showed a moderate | 146 | Experimental sediment-water partition coefficients showed a moderate | ||
| 137 | sorption of target compounds to sediments. Risk quotients for water | 147 | sorption of target compounds to sediments. Risk quotients for water | ||
| 138 | compartment evidenced a moderate risk posed by nonylphenol, | 148 | compartment evidenced a moderate risk posed by nonylphenol, | ||
| 139 | considering the worst-case scenario. For sediments, moderate risk | 149 | considering the worst-case scenario. For sediments, moderate risk | ||
| 140 | related to 4-tert-octylphenol and high risk to nonylphenol were | 150 | related to 4-tert-octylphenol and high risk to nonylphenol were | ||
| 141 | estimated. (C) 2019 Elsevier Ltd. All rights reserved." | 151 | estimated. (C) 2019 Elsevier Ltd. All rights reserved." | ||
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| 252 | "state": "active", | 262 | "state": "active", | ||
| 253 | "study_variables": { | 263 | "study_variables": { | ||
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| 256 | "tag_uri": [ | 266 | "tag_uri": [ | ||
| 257 | 267 | ||||
| 258 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 268 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
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| 260 | "tags": [ | 270 | "tags": [ | ||
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| 262 | "display_name": "contaminacion", | 272 | "display_name": "contaminacion", | ||
| 263 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 273 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 264 | "name": "contaminacion", | 274 | "name": "contaminacion", | ||
| 265 | "state": "active", | 275 | "state": "active", | ||
| 266 | "vocabulary_id": null | 276 | "vocabulary_id": null | ||
| 267 | }, | 277 | }, | ||
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| 269 | "display_name": "diversidad", | 279 | "display_name": "diversidad", | ||
| 270 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | 280 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | ||
| 271 | "name": "diversidad", | 281 | "name": "diversidad", | ||
| 272 | "state": "active", | 282 | "state": "active", | ||
| 273 | "vocabulary_id": null | 283 | "vocabulary_id": null | ||
| 274 | }, | 284 | }, | ||
| 275 | { | 285 | { | ||
| 276 | "display_name": "impacto_ambiental", | 286 | "display_name": "impacto_ambiental", | ||
| 277 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | 287 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | ||
| 278 | "name": "impacto_ambiental", | 288 | "name": "impacto_ambiental", | ||
| 279 | "state": "active", | 289 | "state": "active", | ||
| 280 | "vocabulary_id": null | 290 | "vocabulary_id": null | ||
| 281 | }, | 291 | }, | ||
| 282 | { | 292 | { | ||
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| 284 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 294 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 285 | "name": "marino", | 295 | "name": "marino", | ||
| 286 | "state": "active", | 296 | "state": "active", | ||
| 287 | "vocabulary_id": null | 297 | "vocabulary_id": null | ||
| 288 | }, | 298 | }, | ||
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| 291 | "id": "e10d6086-7221-4a47-95d0-79e65f2a45ef", | 301 | "id": "e10d6086-7221-4a47-95d0-79e65f2a45ef", | ||
| 292 | "name": "restauracion", | 302 | "name": "restauracion", | ||
| 293 | "state": "active", | 303 | "state": "active", | ||
| 294 | "vocabulary_id": null | 304 | "vocabulary_id": null | ||
| 295 | }, | 305 | }, | ||
| 296 | { | 306 | { | ||
| 297 | "display_name": "seguimiento", | 307 | "display_name": "seguimiento", | ||
| 298 | "id": "35753cbf-b84a-487f-80a1-3930d85a73a0", | 308 | "id": "35753cbf-b84a-487f-80a1-3930d85a73a0", | ||
| 299 | "name": "seguimiento", | 309 | "name": "seguimiento", | ||
| 300 | "state": "active", | 310 | "state": "active", | ||
| 301 | "vocabulary_id": null | 311 | "vocabulary_id": null | ||
| 302 | } | 312 | } | ||
| 303 | ], | 313 | ], | ||
| 304 | "thematic_area": [ | 314 | "thematic_area": [ | ||
| 305 | "espacios_protegidos" | 315 | "espacios_protegidos" | ||
| 306 | ], | 316 | ], | ||
| 307 | "theme_es": [ | 317 | "theme_es": [ | ||
| 308 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 318 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 309 | ], | 319 | ], | ||
| 310 | "title": "Occurrence of selected endocrine disrupting compounds in | 320 | "title": "Occurrence of selected endocrine disrupting compounds in | ||
| 311 | Iberian coastal areas and assessment of the environmental risk", | 321 | Iberian coastal areas and assessment of the environmental risk", | ||
| 312 | "title_translated": { | 322 | "title_translated": { | ||
| 313 | "es": "Occurrence of selected endocrine disrupting compounds in | 323 | "es": "Occurrence of selected endocrine disrupting compounds in | ||
| 314 | Iberian coastal areas and assessment of the environmental risk" | 324 | Iberian coastal areas and assessment of the environmental risk" | ||
| 315 | }, | 325 | }, | ||
| 316 | "topic": | 326 | "topic": | ||
| 317 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 327 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 318 | "type": "dataset", | 328 | "type": "dataset", | ||
| 319 | "url": | 329 | "url": | ||
| 320 | //iepnb.es:443/catalogo/dataset/04f6c28d-fd1f-5ced-afeb-50988d38648f", | 330 | //iepnb.es:443/catalogo/dataset/04f6c28d-fd1f-5ced-afeb-50988d38648f", | ||
| 321 | "version_notes": { | 331 | "version_notes": { | ||
| 322 | "es": "" | 332 | "es": "" | ||
| 323 | } | 333 | } | ||
| 324 | } | 334 | } |