2020
DOI: 10.1016/j.ecoenv.2020.110341
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In situ experiment to evaluate biochemical responses in the freshwater mussel Diplodon chilensis under anthropogenic eutrophication conditions

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Cited by 7 publications
(3 citation statements)
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References 72 publications
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“…An increase in soft tissues was previously reported in mussels and clams exposed to municipal effluent in the laboratory ( Nobles and Zhang, 2015 ). In another study, mussel caging was used to determine the ecotoxicological impacts of leachates from an open dump site ( Yusseppone et al, 2020 ). Mussels were caged for over 30 days at these sites and showed signs of stress in the form of lysosome membrane destabilization in the hemocytes; additionally, certain tissues (gills and adductor muscles) exhibited elevated copper and iron levels.…”
Section: Discussionmentioning
confidence: 99%
“…An increase in soft tissues was previously reported in mussels and clams exposed to municipal effluent in the laboratory ( Nobles and Zhang, 2015 ). In another study, mussel caging was used to determine the ecotoxicological impacts of leachates from an open dump site ( Yusseppone et al, 2020 ). Mussels were caged for over 30 days at these sites and showed signs of stress in the form of lysosome membrane destabilization in the hemocytes; additionally, certain tissues (gills and adductor muscles) exhibited elevated copper and iron levels.…”
Section: Discussionmentioning
confidence: 99%
“…It is noteworthy that the gills of D. chilensis accumulated iron but not Cu 2+ and showed increased GST activity after 30 and 60 days of exposure to a polluted medium with elevated concentrations of both metals (Yusseppone et al, 2020). Together with our results, this finding suggests that the gills of this species respond to Cu 2+ with the induction of GST and CAT activity but do not accumulate Cu 2+ , independently of the route and time of exposure.…”
Section: Discussionmentioning
confidence: 99%
“…There are reports on the decline of D. chilensis populations due to eutrophication and contamination in both countries (see Parada & Peredo, 2005; Parada et al, 2009; Rocchetta et al, 2014). In Argentina, this species is abundant in pristine lakes protected in national parks, but its distribution extends to areas contaminated by sewage effluents and leachates from garbage dumps (Sabatini, Rocchetta, Luquet et al, 2011; Yusseppone et al, 2019, 2020).…”
Section: Introductionmentioning
confidence: 99%