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En el instante 23 de junio de 2026, 16:13:56 UTC,
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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 Input of pharmaceuticals through coastal surface watercourses into a Mediterranean lagoon (Mar Menor, SE Spain): Sources and seasonal variations
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| 92 | "notes": "The seasonal occurrence and distribution of 69 | 92 | "notes": "The seasonal occurrence and distribution of 69 | ||
| 93 | pharmaceuticals along coastal watercourses during 6 sampling campaigns | 93 | pharmaceuticals along coastal watercourses during 6 sampling campaigns | ||
| 94 | and their input through El Albujon watercourse to the Mar Menor lagoon | 94 | and their input through El Albujon watercourse to the Mar Menor lagoon | ||
| 95 | were determined by UPLC-MS-MS, considering a total of 115 water | 95 | were determined by UPLC-MS-MS, considering a total of 115 water | ||
| 96 | samples. The major source of pharmaceuticals running into this | 96 | samples. The major source of pharmaceuticals running into this | ||
| 97 | watercourse was an effluent from the Los Alcazares WWTP, although | 97 | watercourse was an effluent from the Los Alcazares WWTP, although | ||
| 98 | other sources were also present (runoffs, excess water from | 98 | other sources were also present (runoffs, excess water from | ||
| 99 | irrigation, etc.). In this urban and agriculturally influenced | 99 | irrigation, etc.). In this urban and agriculturally influenced | ||
| 100 | watercourse different pharmaceutical distribution profiles were | 100 | watercourse different pharmaceutical distribution profiles were | ||
| 101 | detected according to their attenuation, which depended on | 101 | detected according to their attenuation, which depended on | ||
| 102 | physicochemical water conditions, pollutant input variation, | 102 | physicochemical water conditions, pollutant input variation, | ||
| 103 | biodegradation and photodegradation rates of pollutants, etc. The less | 103 | biodegradation and photodegradation rates of pollutants, etc. The less | ||
| 104 | recalcitrant compounds in this study (macrolides, beta-blockers, etc.) | 104 | recalcitrant compounds in this study (macrolides, beta-blockers, etc.) | ||
| 105 | showed a relevant seasonal variability as a consequence of dissipation | 105 | showed a relevant seasonal variability as a consequence of dissipation | ||
| 106 | processes (degradation, sorption, etc.). Attenuation was lower, | 106 | processes (degradation, sorption, etc.). Attenuation was lower, | ||
| 107 | however, for diclofenac, carbamazepine, lorazepam, valsartan, | 107 | however, for diclofenac, carbamazepine, lorazepam, valsartan, | ||
| 108 | sulfamethoxazole among others, due to their known lower degradability | 108 | sulfamethoxazole among others, due to their known lower degradability | ||
| 109 | and sorption onto particulate matter, according to previous studies. | 109 | and sorption onto particulate matter, according to previous studies. | ||
| 110 | The maximum concentrations detected were higher than 1000 ng L-1 for | 110 | The maximum concentrations detected were higher than 1000 ng L-1 for | ||
| 111 | azithromycin, clarithromycin, valsartan, acetaminophen and ibuprofen. | 111 | azithromycin, clarithromycin, valsartan, acetaminophen and ibuprofen. | ||
| 112 | These high concentration levels were favored by the limited dilution | 112 | These high concentration levels were favored by the limited dilution | ||
| 113 | in this low flow system, and consequently some of them could pose an | 113 | in this low flow system, and consequently some of them could pose an | ||
| 114 | acute risk to the biota of this watercourse. Considering data from | 114 | acute risk to the biota of this watercourse. Considering data from | ||
| 115 | 2009 to 2010, it has been estimated that a total of 11.3 kg of | 115 | 2009 to 2010, it has been estimated that a total of 11.3 kg of | ||
| 116 | pharmaceuticals access the Mar Menor lagoon annually through the El | 116 | pharmaceuticals access the Mar Menor lagoon annually through the El | ||
| 117 | Albujon watercourse. The highest proportion of this input corresponded | 117 | Albujon watercourse. The highest proportion of this input corresponded | ||
| 118 | to antibiotics (46%), followed by antihypertensives (20%) and | 118 | to antibiotics (46%), followed by antihypertensives (20%) and | ||
| 119 | diuretics (18%). (C) 2014 Elsevier B.V. All rights reserved.", | 119 | diuretics (18%). (C) 2014 Elsevier B.V. All rights reserved.", | ||
| 120 | "notes_translated": { | 120 | "notes_translated": { | ||
| 121 | "es": "The seasonal occurrence and distribution of 69 | 121 | "es": "The seasonal occurrence and distribution of 69 | ||
| 122 | pharmaceuticals along coastal watercourses during 6 sampling campaigns | 122 | pharmaceuticals along coastal watercourses during 6 sampling campaigns | ||
| 123 | and their input through El Albujon watercourse to the Mar Menor lagoon | 123 | and their input through El Albujon watercourse to the Mar Menor lagoon | ||
| 124 | were determined by UPLC-MS-MS, considering a total of 115 water | 124 | were determined by UPLC-MS-MS, considering a total of 115 water | ||
| 125 | samples. The major source of pharmaceuticals running into this | 125 | samples. The major source of pharmaceuticals running into this | ||
| 126 | watercourse was an effluent from the Los Alcazares WWTP, although | 126 | watercourse was an effluent from the Los Alcazares WWTP, although | ||
| 127 | other sources were also present (runoffs, excess water from | 127 | other sources were also present (runoffs, excess water from | ||
| 128 | irrigation, etc.). In this urban and agriculturally influenced | 128 | irrigation, etc.). In this urban and agriculturally influenced | ||
| 129 | watercourse different pharmaceutical distribution profiles were | 129 | watercourse different pharmaceutical distribution profiles were | ||
| 130 | detected according to their attenuation, which depended on | 130 | detected according to their attenuation, which depended on | ||
| 131 | physicochemical water conditions, pollutant input variation, | 131 | physicochemical water conditions, pollutant input variation, | ||
| 132 | biodegradation and photodegradation rates of pollutants, etc. The less | 132 | biodegradation and photodegradation rates of pollutants, etc. The less | ||
| 133 | recalcitrant compounds in this study (macrolides, beta-blockers, etc.) | 133 | recalcitrant compounds in this study (macrolides, beta-blockers, etc.) | ||
| 134 | showed a relevant seasonal variability as a consequence of dissipation | 134 | showed a relevant seasonal variability as a consequence of dissipation | ||
| 135 | processes (degradation, sorption, etc.). Attenuation was lower, | 135 | processes (degradation, sorption, etc.). Attenuation was lower, | ||
| 136 | however, for diclofenac, carbamazepine, lorazepam, valsartan, | 136 | however, for diclofenac, carbamazepine, lorazepam, valsartan, | ||
| 137 | sulfamethoxazole among others, due to their known lower degradability | 137 | sulfamethoxazole among others, due to their known lower degradability | ||
| 138 | and sorption onto particulate matter, according to previous studies. | 138 | and sorption onto particulate matter, according to previous studies. | ||
| 139 | The maximum concentrations detected were higher than 1000 ng L-1 for | 139 | The maximum concentrations detected were higher than 1000 ng L-1 for | ||
| 140 | azithromycin, clarithromycin, valsartan, acetaminophen and ibuprofen. | 140 | azithromycin, clarithromycin, valsartan, acetaminophen and ibuprofen. | ||
| 141 | These high concentration levels were favored by the limited dilution | 141 | These high concentration levels were favored by the limited dilution | ||
| 142 | in this low flow system, and consequently some of them could pose an | 142 | in this low flow system, and consequently some of them could pose an | ||
| 143 | acute risk to the biota of this watercourse. Considering data from | 143 | acute risk to the biota of this watercourse. Considering data from | ||
| 144 | 2009 to 2010, it has been estimated that a total of 11.3 kg of | 144 | 2009 to 2010, it has been estimated that a total of 11.3 kg of | ||
| 145 | pharmaceuticals access the Mar Menor lagoon annually through the El | 145 | pharmaceuticals access the Mar Menor lagoon annually through the El | ||
| 146 | Albujon watercourse. The highest proportion of this input corresponded | 146 | Albujon watercourse. The highest proportion of this input corresponded | ||
| 147 | to antibiotics (46%), followed by antihypertensives (20%) and | 147 | to antibiotics (46%), followed by antihypertensives (20%) and | ||
| 148 | diuretics (18%). (C) 2014 Elsevier B.V. All rights reserved." | 148 | diuretics (18%). (C) 2014 Elsevier B.V. All rights reserved." | ||
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