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a2026-06-25
en Bioaccumulation and fate of pharmaceuticals in a Mediterranean coastal lagoon: Temporal variation and impact of a flash flood event -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Bioaccumulation and fate of pharmaceuticals in a Mediterranean coastal lagoon: Temporal variation and impact of a flash flood event
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| 96 | "notes": "Coastal ecosystems are particularly vulnerable to | 106 | "notes": "Coastal ecosystems are particularly vulnerable to | ||
| 97 | terrestrial inputs from human-impacted areas. The prevalence of | 107 | terrestrial inputs from human-impacted areas. The prevalence of | ||
| 98 | wastewater treatment plants, unable to remove contaminants such as | 108 | wastewater treatment plants, unable to remove contaminants such as | ||
| 99 | pharmaceuticals (PhACs), leads to their continuous input into the | 109 | pharmaceuticals (PhACs), leads to their continuous input into the | ||
| 100 | marine environment. In this paper, the seasonal occurrence of PhACs in | 110 | marine environment. In this paper, the seasonal occurrence of PhACs in | ||
| 101 | a semi-confined coastal lagoon (the Mar Menor, south-eastern Spain) | 111 | a semi-confined coastal lagoon (the Mar Menor, south-eastern Spain) | ||
| 102 | was studied during 2018 and 2019 by evalu-ating their presence in | 112 | was studied during 2018 and 2019 by evalu-ating their presence in | ||
| 103 | seawater and sediments, and their bioaccumulation in aquatic | 113 | seawater and sediments, and their bioaccumulation in aquatic | ||
| 104 | organisms. Temporal variation in the contamination levels was | 114 | organisms. Temporal variation in the contamination levels was | ||
| 105 | evaluated by comparison to a previous study carried out between 2010 | 115 | evaluated by comparison to a previous study carried out between 2010 | ||
| 106 | and 2011 before the cessation of permanent discharges of treated | 116 | and 2011 before the cessation of permanent discharges of treated | ||
| 107 | wastewater into the lagoon. The impact of a flash flood event | 117 | wastewater into the lagoon. The impact of a flash flood event | ||
| 108 | (September 2019) on PhACs pollution was also assessed. A total of | 118 | (September 2019) on PhACs pollution was also assessed. A total of | ||
| 109 | seven compounds (out of 69 PhACs analysed) were found in seawater | 119 | seven compounds (out of 69 PhACs analysed) were found in seawater | ||
| 110 | during 2018-2019, with a limited detection frequency (<33%) and | 120 | during 2018-2019, with a limited detection frequency (<33%) and | ||
| 111 | concentrations (up to 11 ng/L of clarithromycin). Only carbamazepine | 121 | concentrations (up to 11 ng/L of clarithromycin). Only carbamazepine | ||
| 112 | was found in sediments (ND-1.2 ng/g dw), suggesting an improved | 122 | was found in sediments (ND-1.2 ng/g dw), suggesting an improved | ||
| 113 | environmental quality in comparison to 2010-2011 (when 24 and 13 | 123 | environmental quality in comparison to 2010-2011 (when 24 and 13 | ||
| 114 | compounds were detected in seawater and sediments, respectively). | 124 | compounds were detected in seawater and sediments, respectively). | ||
| 115 | However, the biomonitoring of fish and molluscs showed a still | 125 | However, the biomonitoring of fish and molluscs showed a still | ||
| 116 | remarkable accumulation of analgesic/anti-inflammatory drugs, lipid | 126 | remarkable accumulation of analgesic/anti-inflammatory drugs, lipid | ||
| 117 | regulators, psychiatric drugs and beta-blocking agents, albeit not | 127 | regulators, psychiatric drugs and beta-blocking agents, albeit not | ||
| 118 | higher than in 2010. The flash flood event from 2019 increased the | 128 | higher than in 2010. The flash flood event from 2019 increased the | ||
| 119 | prevalence of PhACs in the lagoon, compared to the 2018-2019 sampling | 129 | prevalence of PhACs in the lagoon, compared to the 2018-2019 sampling | ||
| 120 | campaigns, especially in the upper water layer. After the flash flood | 130 | campaigns, especially in the upper water layer. After the flash flood | ||
| 121 | the antibiotics clarithromycin and sulfapyridine yielded the highest | 131 | the antibiotics clarithromycin and sulfapyridine yielded the highest | ||
| 122 | concentrations ever reported in the lagoon (297 and 145 ng/L, | 132 | concentrations ever reported in the lagoon (297 and 145 ng/L, | ||
| 123 | respectively), alongside azithromycin in 2011 (155 ng/L). Flash flood | 133 | respectively), alongside azithromycin in 2011 (155 ng/L). Flash flood | ||
| 124 | events associated with sewer overflows and soil mobilisation, which | 134 | events associated with sewer overflows and soil mobilisation, which | ||
| 125 | are expected to increase under climate change scenarios, should be | 135 | are expected to increase under climate change scenarios, should be | ||
| 126 | considered when assessing the risks posed by pharmaceuticals to | 136 | considered when assessing the risks posed by pharmaceuticals to | ||
| 127 | vulnerable aquatic eco-systems in the coastal areas.", | 137 | vulnerable aquatic eco-systems in the coastal areas.", | ||
| 128 | "notes_translated": { | 138 | "notes_translated": { | ||
| 129 | "es": "Coastal ecosystems are particularly vulnerable to | 139 | "es": "Coastal ecosystems are particularly vulnerable to | ||
| 130 | terrestrial inputs from human-impacted areas. The prevalence of | 140 | terrestrial inputs from human-impacted areas. The prevalence of | ||
| 131 | wastewater treatment plants, unable to remove contaminants such as | 141 | wastewater treatment plants, unable to remove contaminants such as | ||
| 132 | pharmaceuticals (PhACs), leads to their continuous input into the | 142 | pharmaceuticals (PhACs), leads to their continuous input into the | ||
| 133 | marine environment. In this paper, the seasonal occurrence of PhACs in | 143 | marine environment. In this paper, the seasonal occurrence of PhACs in | ||
| 134 | a semi-confined coastal lagoon (the Mar Menor, south-eastern Spain) | 144 | a semi-confined coastal lagoon (the Mar Menor, south-eastern Spain) | ||
| 135 | was studied during 2018 and 2019 by evalu-ating their presence in | 145 | was studied during 2018 and 2019 by evalu-ating their presence in | ||
| 136 | seawater and sediments, and their bioaccumulation in aquatic | 146 | seawater and sediments, and their bioaccumulation in aquatic | ||
| 137 | organisms. Temporal variation in the contamination levels was | 147 | organisms. Temporal variation in the contamination levels was | ||
| 138 | evaluated by comparison to a previous study carried out between 2010 | 148 | evaluated by comparison to a previous study carried out between 2010 | ||
| 139 | and 2011 before the cessation of permanent discharges of treated | 149 | and 2011 before the cessation of permanent discharges of treated | ||
| 140 | wastewater into the lagoon. The impact of a flash flood event | 150 | wastewater into the lagoon. The impact of a flash flood event | ||
| 141 | (September 2019) on PhACs pollution was also assessed. A total of | 151 | (September 2019) on PhACs pollution was also assessed. A total of | ||
| 142 | seven compounds (out of 69 PhACs analysed) were found in seawater | 152 | seven compounds (out of 69 PhACs analysed) were found in seawater | ||
| 143 | during 2018-2019, with a limited detection frequency (<33%) and | 153 | during 2018-2019, with a limited detection frequency (<33%) and | ||
| 144 | concentrations (up to 11 ng/L of clarithromycin). Only carbamazepine | 154 | concentrations (up to 11 ng/L of clarithromycin). Only carbamazepine | ||
| 145 | was found in sediments (ND-1.2 ng/g dw), suggesting an improved | 155 | was found in sediments (ND-1.2 ng/g dw), suggesting an improved | ||
| 146 | environmental quality in comparison to 2010-2011 (when 24 and 13 | 156 | environmental quality in comparison to 2010-2011 (when 24 and 13 | ||
| 147 | compounds were detected in seawater and sediments, respectively). | 157 | compounds were detected in seawater and sediments, respectively). | ||
| 148 | However, the biomonitoring of fish and molluscs showed a still | 158 | However, the biomonitoring of fish and molluscs showed a still | ||
| 149 | remarkable accumulation of analgesic/anti-inflammatory drugs, lipid | 159 | remarkable accumulation of analgesic/anti-inflammatory drugs, lipid | ||
| 150 | regulators, psychiatric drugs and beta-blocking agents, albeit not | 160 | regulators, psychiatric drugs and beta-blocking agents, albeit not | ||
| 151 | higher than in 2010. The flash flood event from 2019 increased the | 161 | higher than in 2010. The flash flood event from 2019 increased the | ||
| 152 | prevalence of PhACs in the lagoon, compared to the 2018-2019 sampling | 162 | prevalence of PhACs in the lagoon, compared to the 2018-2019 sampling | ||
| 153 | campaigns, especially in the upper water layer. After the flash flood | 163 | campaigns, especially in the upper water layer. After the flash flood | ||
| 154 | the antibiotics clarithromycin and sulfapyridine yielded the highest | 164 | the antibiotics clarithromycin and sulfapyridine yielded the highest | ||
| 155 | concentrations ever reported in the lagoon (297 and 145 ng/L, | 165 | concentrations ever reported in the lagoon (297 and 145 ng/L, | ||
| 156 | respectively), alongside azithromycin in 2011 (155 ng/L). Flash flood | 166 | respectively), alongside azithromycin in 2011 (155 ng/L). Flash flood | ||
| 157 | events associated with sewer overflows and soil mobilisation, which | 167 | events associated with sewer overflows and soil mobilisation, which | ||
| 158 | are expected to increase under climate change scenarios, should be | 168 | are expected to increase under climate change scenarios, should be | ||
| 159 | considered when assessing the risks posed by pharmaceuticals to | 169 | considered when assessing the risks posed by pharmaceuticals to | ||
| 160 | vulnerable aquatic eco-systems in the coastal areas." | 170 | vulnerable aquatic eco-systems in the coastal areas." | ||
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