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a2026-06-25
en Impact assessment of agricultural inputs into a Mediterranean coastal lagoon (Mar Menor, SE Spain) on transplanted clams (Ruditapes decussatus) by biochemical and physiological responses -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Impact assessment of agricultural inputs into a Mediterranean coastal lagoon (Mar Menor, SE Spain) on transplanted clams (Ruditapes decussatus) by biochemical and physiological responses
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| 96 | "notes": "The Mar Menor is a coastal lagoon threatened by the | 106 | "notes": "The Mar Menor is a coastal lagoon threatened by the | ||
| 97 | development of intensive agriculture in the sur\u0002rounding areas. | 107 | development of intensive agriculture in the sur\u0002rounding areas. | ||
| 98 | Large amounts of pesticides from these areas are discharged into El | 108 | Large amounts of pesticides from these areas are discharged into El | ||
| 99 | Albuj\u00f3n, a permanent watercourse flowing into the lagoon. We have | 109 | Albuj\u00f3n, a permanent watercourse flowing into the lagoon. We have | ||
| 100 | used a multi-biomarker approach to assess the biological effects of | 110 | used a multi-biomarker approach to assess the biological effects of | ||
| 101 | agricultural pollution on a bivalve species. Biomarkers indicative of | 111 | agricultural pollution on a bivalve species. Biomarkers indicative of | ||
| 102 | neurotoxicity (acetylcholinesterase, AChE), oxidative stress | 112 | neurotoxicity (acetylcholinesterase, AChE), oxidative stress | ||
| 103 | (catalase, CAT; glutathione reductase, GR and lipid peroxidation, | 113 | (catalase, CAT; glutathione reductase, GR and lipid peroxidation, | ||
| 104 | LPO), phase II biotransformation of xenobiotics (glutathione | 114 | LPO), phase II biotransformation of xenobiotics (glutathione | ||
| 105 | S-transferase, GST) and physiological stress (scope for growth, SFG) | 115 | S-transferase, GST) and physiological stress (scope for growth, SFG) | ||
| 106 | were mea\u0002sured in clams transplanted to four sites of the lagoon | 116 | were mea\u0002sured in clams transplanted to four sites of the lagoon | ||
| 107 | (two reference sites and two sites affected by the dispersion of the | 117 | (two reference sites and two sites affected by the dispersion of the | ||
| 108 | effluent of the El Albuj\u00f3n), for exposure periods of 7 and 22 | 118 | effluent of the El Albuj\u00f3n), for exposure periods of 7 and 22 | ||
| 109 | days. The hazards of this effluent were also examined by | 119 | days. The hazards of this effluent were also examined by | ||
| 110 | simultaneously measuring up to 83 contaminants (pesticides, PCBs, PAHs | 120 | simultaneously measuring up to 83 contaminants (pesticides, PCBs, PAHs | ||
| 111 | and others) in samples of fresh water from the watercourse mouth and | 121 | and others) in samples of fresh water from the watercourse mouth and | ||
| 112 | seawater from the deployed sites, as well as the bioaccumulation of | 122 | seawater from the deployed sites, as well as the bioaccumulation of | ||
| 113 | organochlorinated compounds and PAHs in the transplanted animals. | 123 | organochlorinated compounds and PAHs in the transplanted animals. | ||
| 114 | Biomarker responses showed marked differences between reference and | 124 | Biomarker responses showed marked differences between reference and | ||
| 115 | affected sites after 7 and 22 days. However it was only after 22 days | 125 | affected sites after 7 and 22 days. However it was only after 22 days | ||
| 116 | that principal component analysis (PCA) of the biomarker responses | 126 | that principal component analysis (PCA) of the biomarker responses | ||
| 117 | distinguished between clams deployed in sites affected by the | 127 | distinguished between clams deployed in sites affected by the | ||
| 118 | dispersion of the effluent of the watercourse and those from the | 128 | dispersion of the effluent of the watercourse and those from the | ||
| 119 | reference sites. The chemical analysis of water showed high | 129 | reference sites. The chemical analysis of water showed high | ||
| 120 | concentra\u0002tions of pesticides close to El Albuj\u00f3n | 130 | concentra\u0002tions of pesticides close to El Albuj\u00f3n | ||
| 121 | watercourse mouth, with the greatest input flux corresponding to the | 131 | watercourse mouth, with the greatest input flux corresponding to the | ||
| 122 | organophosphate chlorpyrifos, followed by pendimethalin and | 132 | organophosphate chlorpyrifos, followed by pendimethalin and | ||
| 123 | naphthalene, and at lower levels ace\u0002naphthene, | 133 | naphthalene, and at lower levels ace\u0002naphthene, | ||
| 124 | terbuthylazine-desethyl and chlorpyrifos-methyl. In this regard, PCA | 134 | terbuthylazine-desethyl and chlorpyrifos-methyl. In this regard, PCA | ||
| 125 | analysis showed that the biological effects of the mixture of | 135 | analysis showed that the biological effects of the mixture of | ||
| 126 | pesticides in caged clams after 22 days were reduced levels of AchE | 136 | pesticides in caged clams after 22 days were reduced levels of AchE | ||
| 127 | and SFG and increased levels of GR and phase II GST activity. An | 137 | and SFG and increased levels of GR and phase II GST activity. An | ||
| 128 | integrated biomarker response index was calculated from the | 138 | integrated biomarker response index was calculated from the | ||
| 129 | combination of these biomarkers, proving useful for the assessment of | 139 | combination of these biomarkers, proving useful for the assessment of | ||
| 130 | the impact of agricultural pollution in caged clams.", | 140 | the impact of agricultural pollution in caged clams.", | ||
| 131 | "notes_translated": { | 141 | "notes_translated": { | ||
| 132 | "es": "The Mar Menor is a coastal lagoon threatened by the | 142 | "es": "The Mar Menor is a coastal lagoon threatened by the | ||
| 133 | development of intensive agriculture in the sur\u0002rounding areas. | 143 | development of intensive agriculture in the sur\u0002rounding areas. | ||
| 134 | Large amounts of pesticides from these areas are discharged into El | 144 | Large amounts of pesticides from these areas are discharged into El | ||
| 135 | Albuj\u00f3n, a permanent watercourse flowing into the lagoon. We have | 145 | Albuj\u00f3n, a permanent watercourse flowing into the lagoon. We have | ||
| 136 | used a multi-biomarker approach to assess the biological effects of | 146 | used a multi-biomarker approach to assess the biological effects of | ||
| 137 | agricultural pollution on a bivalve species. Biomarkers indicative of | 147 | agricultural pollution on a bivalve species. Biomarkers indicative of | ||
| 138 | neurotoxicity (acetylcholinesterase, AChE), oxidative stress | 148 | neurotoxicity (acetylcholinesterase, AChE), oxidative stress | ||
| 139 | (catalase, CAT; glutathione reductase, GR and lipid peroxidation, | 149 | (catalase, CAT; glutathione reductase, GR and lipid peroxidation, | ||
| 140 | LPO), phase II biotransformation of xenobiotics (glutathione | 150 | LPO), phase II biotransformation of xenobiotics (glutathione | ||
| 141 | S-transferase, GST) and physiological stress (scope for growth, SFG) | 151 | S-transferase, GST) and physiological stress (scope for growth, SFG) | ||
| 142 | were mea\u0002sured in clams transplanted to four sites of the lagoon | 152 | were mea\u0002sured in clams transplanted to four sites of the lagoon | ||
| 143 | (two reference sites and two sites affected by the dispersion of the | 153 | (two reference sites and two sites affected by the dispersion of the | ||
| 144 | effluent of the El Albuj\u00f3n), for exposure periods of 7 and 22 | 154 | effluent of the El Albuj\u00f3n), for exposure periods of 7 and 22 | ||
| 145 | days. The hazards of this effluent were also examined by | 155 | days. The hazards of this effluent were also examined by | ||
| 146 | simultaneously measuring up to 83 contaminants (pesticides, PCBs, PAHs | 156 | simultaneously measuring up to 83 contaminants (pesticides, PCBs, PAHs | ||
| 147 | and others) in samples of fresh water from the watercourse mouth and | 157 | and others) in samples of fresh water from the watercourse mouth and | ||
| 148 | seawater from the deployed sites, as well as the bioaccumulation of | 158 | seawater from the deployed sites, as well as the bioaccumulation of | ||
| 149 | organochlorinated compounds and PAHs in the transplanted animals. | 159 | organochlorinated compounds and PAHs in the transplanted animals. | ||
| 150 | Biomarker responses showed marked differences between reference and | 160 | Biomarker responses showed marked differences between reference and | ||
| 151 | affected sites after 7 and 22 days. However it was only after 22 days | 161 | affected sites after 7 and 22 days. However it was only after 22 days | ||
| 152 | that principal component analysis (PCA) of the biomarker responses | 162 | that principal component analysis (PCA) of the biomarker responses | ||
| 153 | distinguished between clams deployed in sites affected by the | 163 | distinguished between clams deployed in sites affected by the | ||
| 154 | dispersion of the effluent of the watercourse and those from the | 164 | dispersion of the effluent of the watercourse and those from the | ||
| 155 | reference sites. The chemical analysis of water showed high | 165 | reference sites. The chemical analysis of water showed high | ||
| 156 | concentra\u0002tions of pesticides close to El Albuj\u00f3n | 166 | concentra\u0002tions of pesticides close to El Albuj\u00f3n | ||
| 157 | watercourse mouth, with the greatest input flux corresponding to the | 167 | watercourse mouth, with the greatest input flux corresponding to the | ||
| 158 | organophosphate chlorpyrifos, followed by pendimethalin and | 168 | organophosphate chlorpyrifos, followed by pendimethalin and | ||
| 159 | naphthalene, and at lower levels ace\u0002naphthene, | 169 | naphthalene, and at lower levels ace\u0002naphthene, | ||
| 160 | terbuthylazine-desethyl and chlorpyrifos-methyl. In this regard, PCA | 170 | terbuthylazine-desethyl and chlorpyrifos-methyl. In this regard, PCA | ||
| 161 | analysis showed that the biological effects of the mixture of | 171 | analysis showed that the biological effects of the mixture of | ||
| 162 | pesticides in caged clams after 22 days were reduced levels of AchE | 172 | pesticides in caged clams after 22 days were reduced levels of AchE | ||
| 163 | and SFG and increased levels of GR and phase II GST activity. An | 173 | and SFG and increased levels of GR and phase II GST activity. An | ||
| 164 | integrated biomarker response index was calculated from the | 174 | integrated biomarker response index was calculated from the | ||
| 165 | combination of these biomarkers, proving useful for the assessment of | 175 | combination of these biomarkers, proving useful for the assessment of | ||
| 166 | the impact of agricultural pollution in caged clams." | 176 | the impact of agricultural pollution in caged clams." | ||
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| 352 | responses", | 362 | responses", | ||
| 353 | "title_translated": { | 363 | "title_translated": { | ||
| 354 | "es": "Impact assessment of agricultural inputs into a | 364 | "es": "Impact assessment of agricultural inputs into a | ||
| 355 | Mediterranean coastal lagoon (Mar Menor, SE Spain) on transplanted | 365 | Mediterranean coastal lagoon (Mar Menor, SE Spain) on transplanted | ||
| 356 | clams (Ruditapes decussatus) by biochemical and physiological | 366 | clams (Ruditapes decussatus) by biochemical and physiological | ||
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