In situ experiment to evaluate biochemical responses in the freshwater mussel Diplodon chilensis under anthropogenic eutrophication conditions

An in-situ experiment was performed to study metabolic responses of the freshwater mussel Diplodon chilensis to water contaminated by leachates from an open dump and cattle activity, in order to analyze both the effects of those contaminants on aquatic environments and the potential use of a native...

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Veröffentlicht in:Ecotoxicology and environmental safety 2020-04, Vol.193, p.110341, Article 110341
Hauptverfasser: Yusseppone, M.S., Bianchi, V.A., Castro, J.M., Noya Abad, T., Minaberry, Y.S., Sabatini, S.E., Luquet, C.M., Rios de Molina, M.C., Rocchetta, I.
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container_start_page 110341
container_title Ecotoxicology and environmental safety
container_volume 193
creator Yusseppone, M.S.
Bianchi, V.A.
Castro, J.M.
Noya Abad, T.
Minaberry, Y.S.
Sabatini, S.E.
Luquet, C.M.
Rios de Molina, M.C.
Rocchetta, I.
description An in-situ experiment was performed to study metabolic responses of the freshwater mussel Diplodon chilensis to water contaminated by leachates from an open dump and cattle activity, in order to analyze both the effects of those contaminants on aquatic environments and the potential use of a native bivalve to evaluate the effects of anthropic influence and eutrophication. Bivalves from a reference site were cage-transplanted to a control site (site A) and to a temporal water pond (site B) over 30 and 60 periods. Water quality analyses revealed that the site B was affected by anthropogenic influence. Mussel's hemocytes from site B showed 50% lower reactive oxygen species production and 130% higher lysosomal membrane stability in the site B mussels. In addition, no oxidative stress was evident in gills, despite the elevated copper and iron concentrations recorded in the site B water samples (CuB = 0.3350 ± 0.0636 mg. L−1vs. CuA = 0.0045 ± 0.0007 mg. L−1; FeB = 3.8650 ± 0.4031 mg. L−1vs. FeA = 0.0365 ± 0.0049 mg. L−1). In contrast, the adductor muscle accumulated more Fe (~10–20-fold) than the gills and showed signs of oxidative stress, e.g. superoxide dismutase activity and TBARS levels were increased by 10% were 34%, respectively, in the site B compared with the site A after 60 days of exposure. Additionally, the adductor muscle showed signs of anaerobic metabolism activation. Cu is accumulated in gills from both sites’ individuals, at 60 days, in concordance with the increase in the activity of the cu-containing enzyme cytochrome-c-oxidase. There was a reduction in the overall condition and digestive gland index in bivalves exposed at site B, associated with diminished levels of lipid and protein contents. Metal-pollution and eutrophication affects D. chilensis metabolism and is associated to tissue-specific exposure, anaerobic metabolism and general energetic condition depletion. •Metal-pollution and eutrophication affects D. chilensis metabolism.•There are evidences of a tissue-specific response with different metal accumulation.•There is an association between tissue-specific exposure and anaerobic metabolism.•The general energetic condition suffers depletion.
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Bivalves from a reference site were cage-transplanted to a control site (site A) and to a temporal water pond (site B) over 30 and 60 periods. Water quality analyses revealed that the site B was affected by anthropogenic influence. Mussel's hemocytes from site B showed 50% lower reactive oxygen species production and 130% higher lysosomal membrane stability in the site B mussels. In addition, no oxidative stress was evident in gills, despite the elevated copper and iron concentrations recorded in the site B water samples (CuB = 0.3350 ± 0.0636 mg. L−1vs. CuA = 0.0045 ± 0.0007 mg. L−1; FeB = 3.8650 ± 0.4031 mg. L−1vs. FeA = 0.0365 ± 0.0049 mg. L−1). In contrast, the adductor muscle accumulated more Fe (~10–20-fold) than the gills and showed signs of oxidative stress, e.g. superoxide dismutase activity and TBARS levels were increased by 10% were 34%, respectively, in the site B compared with the site A after 60 days of exposure. Additionally, the adductor muscle showed signs of anaerobic metabolism activation. Cu is accumulated in gills from both sites’ individuals, at 60 days, in concordance with the increase in the activity of the cu-containing enzyme cytochrome-c-oxidase. There was a reduction in the overall condition and digestive gland index in bivalves exposed at site B, associated with diminished levels of lipid and protein contents. Metal-pollution and eutrophication affects D. chilensis metabolism and is associated to tissue-specific exposure, anaerobic metabolism and general energetic condition depletion. •Metal-pollution and eutrophication affects D. chilensis metabolism.•There are evidences of a tissue-specific response with different metal accumulation.•There is an association between tissue-specific exposure and anaerobic metabolism.•The general energetic condition suffers depletion.</description><identifier>ISSN: 0147-6513</identifier><identifier>EISSN: 1090-2414</identifier><identifier>DOI: 10.1016/j.ecoenv.2020.110341</identifier><identifier>PMID: 32092582</identifier><language>eng</language><publisher>Netherlands: Elsevier Inc</publisher><subject>anaerobiosis ; Animals ; anthropogenic activities ; aquatic environment ; biochemical pathways ; Bivalve caging ; Bivalvia - drug effects ; Bivalvia - enzymology ; Bivalvia - metabolism ; Cattle ; copper ; Copper - metabolism ; cytochrome-c oxidase ; Diplodon chilensis ; Dipolodon chilensis ; enzyme activity ; Eutrophication ; Fresh Water ; freshwater mussels ; gills ; Gills - drug effects ; Gills - metabolism ; hemocytes ; Hemocytes - drug effects ; Hemocytes - metabolism ; indigenous species ; iron ; leachates ; lipids ; Metabolism ; Metals, Heavy - metabolism ; Metals, Heavy - toxicity ; muscles ; Oxidative Stress ; Pollution ; protein content ; reactive oxygen species ; Reactive Oxygen Species - metabolism ; superoxide dismutase ; Superoxide Dismutase - metabolism ; Thiobarbituric Acid Reactive Substances - metabolism ; thiobarbituric acid-reactive substances ; Water Pollutants, Chemical - metabolism ; Water Pollutants, Chemical - toxicity ; water pollution ; Water Quality ; water quality analysis</subject><ispartof>Ecotoxicology and environmental safety, 2020-04, Vol.193, p.110341, Article 110341</ispartof><rights>2020 Elsevier Inc.</rights><rights>Copyright © 2020 Elsevier Inc. 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Bivalves from a reference site were cage-transplanted to a control site (site A) and to a temporal water pond (site B) over 30 and 60 periods. Water quality analyses revealed that the site B was affected by anthropogenic influence. Mussel's hemocytes from site B showed 50% lower reactive oxygen species production and 130% higher lysosomal membrane stability in the site B mussels. In addition, no oxidative stress was evident in gills, despite the elevated copper and iron concentrations recorded in the site B water samples (CuB = 0.3350 ± 0.0636 mg. L−1vs. CuA = 0.0045 ± 0.0007 mg. L−1; FeB = 3.8650 ± 0.4031 mg. L−1vs. FeA = 0.0365 ± 0.0049 mg. L−1). In contrast, the adductor muscle accumulated more Fe (~10–20-fold) than the gills and showed signs of oxidative stress, e.g. superoxide dismutase activity and TBARS levels were increased by 10% were 34%, respectively, in the site B compared with the site A after 60 days of exposure. Additionally, the adductor muscle showed signs of anaerobic metabolism activation. Cu is accumulated in gills from both sites’ individuals, at 60 days, in concordance with the increase in the activity of the cu-containing enzyme cytochrome-c-oxidase. There was a reduction in the overall condition and digestive gland index in bivalves exposed at site B, associated with diminished levels of lipid and protein contents. 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Bianchi, V.A. ; Castro, J.M. ; Noya Abad, T. ; Minaberry, Y.S. ; Sabatini, S.E. ; Luquet, C.M. ; Rios de Molina, M.C. ; Rocchetta, I.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c441t-bb78ddf57dc378009d6933ed5f5c321350a3ac11c51fc68b8ebdb07a7bf453923</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2020</creationdate><topic>anaerobiosis</topic><topic>Animals</topic><topic>anthropogenic activities</topic><topic>aquatic environment</topic><topic>biochemical pathways</topic><topic>Bivalve caging</topic><topic>Bivalvia - drug effects</topic><topic>Bivalvia - enzymology</topic><topic>Bivalvia - metabolism</topic><topic>Cattle</topic><topic>copper</topic><topic>Copper - metabolism</topic><topic>cytochrome-c oxidase</topic><topic>Diplodon chilensis</topic><topic>Dipolodon chilensis</topic><topic>enzyme activity</topic><topic>Eutrophication</topic><topic>Fresh Water</topic><topic>freshwater mussels</topic><topic>gills</topic><topic>Gills - drug effects</topic><topic>Gills - metabolism</topic><topic>hemocytes</topic><topic>Hemocytes - drug effects</topic><topic>Hemocytes - metabolism</topic><topic>indigenous species</topic><topic>iron</topic><topic>leachates</topic><topic>lipids</topic><topic>Metabolism</topic><topic>Metals, Heavy - metabolism</topic><topic>Metals, Heavy - toxicity</topic><topic>muscles</topic><topic>Oxidative Stress</topic><topic>Pollution</topic><topic>protein content</topic><topic>reactive oxygen species</topic><topic>Reactive Oxygen Species - metabolism</topic><topic>superoxide dismutase</topic><topic>Superoxide Dismutase - metabolism</topic><topic>Thiobarbituric Acid Reactive Substances - metabolism</topic><topic>thiobarbituric acid-reactive substances</topic><topic>Water Pollutants, Chemical - metabolism</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>water pollution</topic><topic>Water Quality</topic><topic>water quality analysis</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Yusseppone, M.S.</creatorcontrib><creatorcontrib>Bianchi, V.A.</creatorcontrib><creatorcontrib>Castro, J.M.</creatorcontrib><creatorcontrib>Noya Abad, T.</creatorcontrib><creatorcontrib>Minaberry, Y.S.</creatorcontrib><creatorcontrib>Sabatini, S.E.</creatorcontrib><creatorcontrib>Luquet, C.M.</creatorcontrib><creatorcontrib>Rios de Molina, M.C.</creatorcontrib><creatorcontrib>Rocchetta, I.</creatorcontrib><collection>ScienceDirect Open Access Titles</collection><collection>Elsevier:ScienceDirect:Open Access</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>AGRICOLA</collection><collection>AGRICOLA - Academic</collection><jtitle>Ecotoxicology and environmental safety</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Yusseppone, M.S.</au><au>Bianchi, V.A.</au><au>Castro, J.M.</au><au>Noya Abad, T.</au><au>Minaberry, Y.S.</au><au>Sabatini, S.E.</au><au>Luquet, C.M.</au><au>Rios de Molina, M.C.</au><au>Rocchetta, I.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>In situ experiment to evaluate biochemical responses in the freshwater mussel Diplodon chilensis under anthropogenic eutrophication conditions</atitle><jtitle>Ecotoxicology and environmental safety</jtitle><addtitle>Ecotoxicol Environ Saf</addtitle><date>2020-04-15</date><risdate>2020</risdate><volume>193</volume><spage>110341</spage><pages>110341-</pages><artnum>110341</artnum><issn>0147-6513</issn><eissn>1090-2414</eissn><abstract>An in-situ experiment was performed to study metabolic responses of the freshwater mussel Diplodon chilensis to water contaminated by leachates from an open dump and cattle activity, in order to analyze both the effects of those contaminants on aquatic environments and the potential use of a native bivalve to evaluate the effects of anthropic influence and eutrophication. Bivalves from a reference site were cage-transplanted to a control site (site A) and to a temporal water pond (site B) over 30 and 60 periods. Water quality analyses revealed that the site B was affected by anthropogenic influence. Mussel's hemocytes from site B showed 50% lower reactive oxygen species production and 130% higher lysosomal membrane stability in the site B mussels. In addition, no oxidative stress was evident in gills, despite the elevated copper and iron concentrations recorded in the site B water samples (CuB = 0.3350 ± 0.0636 mg. L−1vs. CuA = 0.0045 ± 0.0007 mg. L−1; FeB = 3.8650 ± 0.4031 mg. L−1vs. FeA = 0.0365 ± 0.0049 mg. L−1). In contrast, the adductor muscle accumulated more Fe (~10–20-fold) than the gills and showed signs of oxidative stress, e.g. superoxide dismutase activity and TBARS levels were increased by 10% were 34%, respectively, in the site B compared with the site A after 60 days of exposure. Additionally, the adductor muscle showed signs of anaerobic metabolism activation. Cu is accumulated in gills from both sites’ individuals, at 60 days, in concordance with the increase in the activity of the cu-containing enzyme cytochrome-c-oxidase. There was a reduction in the overall condition and digestive gland index in bivalves exposed at site B, associated with diminished levels of lipid and protein contents. Metal-pollution and eutrophication affects D. chilensis metabolism and is associated to tissue-specific exposure, anaerobic metabolism and general energetic condition depletion. •Metal-pollution and eutrophication affects D. chilensis metabolism.•There are evidences of a tissue-specific response with different metal accumulation.•There is an association between tissue-specific exposure and anaerobic metabolism.•The general energetic condition suffers depletion.</abstract><cop>Netherlands</cop><pub>Elsevier Inc</pub><pmid>32092582</pmid><doi>10.1016/j.ecoenv.2020.110341</doi><oa>free_for_read</oa></addata></record>
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subjects anaerobiosis
Animals
anthropogenic activities
aquatic environment
biochemical pathways
Bivalve caging
Bivalvia - drug effects
Bivalvia - enzymology
Bivalvia - metabolism
Cattle
copper
Copper - metabolism
cytochrome-c oxidase
Diplodon chilensis
Dipolodon chilensis
enzyme activity
Eutrophication
Fresh Water
freshwater mussels
gills
Gills - drug effects
Gills - metabolism
hemocytes
Hemocytes - drug effects
Hemocytes - metabolism
indigenous species
iron
leachates
lipids
Metabolism
Metals, Heavy - metabolism
Metals, Heavy - toxicity
muscles
Oxidative Stress
Pollution
protein content
reactive oxygen species
Reactive Oxygen Species - metabolism
superoxide dismutase
Superoxide Dismutase - metabolism
Thiobarbituric Acid Reactive Substances - metabolism
thiobarbituric acid-reactive substances
Water Pollutants, Chemical - metabolism
Water Pollutants, Chemical - toxicity
water pollution
Water Quality
water quality analysis
title In situ experiment to evaluate biochemical responses in the freshwater mussel Diplodon chilensis under anthropogenic eutrophication conditions
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