Differential tolerance of two Gammarus pulex populations transplanted from different metallogenic regions to a polymetal gradient

The River Hayle, Cornwall, UK exhibits pronounced Cu and Zn concentration gradients which were used to compare the metal handling abilities of two populations of Gammarus pulex (Crustacea: Amphipoda). One population was native to the Hayle region (Drym) and presumably has been historically impacted...

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Veröffentlicht in:Aquatic toxicology 2011-03, Vol.102 (1), p.95-103
Hauptverfasser: Khan, Farhan R., Irving, Jennifer R., Bury, Nicolas R., Hogstrand, Christer
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creator Khan, Farhan R.
Irving, Jennifer R.
Bury, Nicolas R.
Hogstrand, Christer
description The River Hayle, Cornwall, UK exhibits pronounced Cu and Zn concentration gradients which were used to compare the metal handling abilities of two populations of Gammarus pulex (Crustacea: Amphipoda). One population was native to the Hayle region (Drym) and presumably has been historically impacted by elevated Cu and Zn levels, whilst naïve gammarids were collected from the River Cray, Kent, UK. Both populations were subject to a 32 day in situ exposure at four R. Hayle sites (Drym, Godolphin, Relubbus and St. Erth). Mortality (LT50), Cu and Zn accumulation and sub-cellular distribution, and oxidative stress (malondialdehyde production) increased with the expected Cu and Zn bioavailabilities at the four sites (i.e. Godolphin > Relubbus > St. Erth > Drym). The naïve population experienced greater metal induced effects in terms of Cu and Zn accumulation, oxidative stress responses and lower LT50s. Analysis of Cu and Zn sub-cellular distribution, however, revealed no significant differences in metal handling. In both populations each metal was localised predominantly to the sub-cellular fraction containing metal bound to metallothionein-like proteins (MTLP) or that holding both metal-rich granules (MRG) and exoskeleton, MTLP and MRG binding being indicative of metal detoxification. However, a greater capacity for detoxified metal storage is not a mechanism implicated in the perceived tolerance of the historically impacted gammarids. Instead our results suggest that the historically impacted population was adapted for lower uptake of Cu and Zn leading to lower bioaccumulation, stress response and ultimately mortality. These results demonstrate not only the usefulness of the in situ methodology, but also that differences in population exposure history can cause significant differences in metal responses during exposure at higher concentrations.
doi_str_mv 10.1016/j.aquatox.2011.01.001
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One population was native to the Hayle region (Drym) and presumably has been historically impacted by elevated Cu and Zn levels, whilst naïve gammarids were collected from the River Cray, Kent, UK. Both populations were subject to a 32 day in situ exposure at four R. Hayle sites (Drym, Godolphin, Relubbus and St. Erth). Mortality (LT50), Cu and Zn accumulation and sub-cellular distribution, and oxidative stress (malondialdehyde production) increased with the expected Cu and Zn bioavailabilities at the four sites (i.e. Godolphin &gt; Relubbus &gt; St. Erth &gt; Drym). The naïve population experienced greater metal induced effects in terms of Cu and Zn accumulation, oxidative stress responses and lower LT50s. Analysis of Cu and Zn sub-cellular distribution, however, revealed no significant differences in metal handling. In both populations each metal was localised predominantly to the sub-cellular fraction containing metal bound to metallothionein-like proteins (MTLP) or that holding both metal-rich granules (MRG) and exoskeleton, MTLP and MRG binding being indicative of metal detoxification. However, a greater capacity for detoxified metal storage is not a mechanism implicated in the perceived tolerance of the historically impacted gammarids. Instead our results suggest that the historically impacted population was adapted for lower uptake of Cu and Zn leading to lower bioaccumulation, stress response and ultimately mortality. 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Psychology ; Gammarus pulex ; General aspects ; Inactivation, Metabolic ; Malondialdehyde - analysis ; Malondialdehyde - metabolism ; Metal bioaccumulation ; Mortality ; Oxidative Stress ; Population differences ; Rivers ; Sub-cellular distribution ; Toxicity Tests - methods ; Water Pollutants, Chemical - toxicity ; Zinc - analysis ; Zinc - pharmacokinetics ; Zinc - toxicity</subject><ispartof>Aquatic toxicology, 2011-03, Vol.102 (1), p.95-103</ispartof><rights>2011 Elsevier B.V.</rights><rights>2015 INIST-CNRS</rights><rights>Copyright © 2011 Elsevier B.V. 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One population was native to the Hayle region (Drym) and presumably has been historically impacted by elevated Cu and Zn levels, whilst naïve gammarids were collected from the River Cray, Kent, UK. Both populations were subject to a 32 day in situ exposure at four R. Hayle sites (Drym, Godolphin, Relubbus and St. Erth). Mortality (LT50), Cu and Zn accumulation and sub-cellular distribution, and oxidative stress (malondialdehyde production) increased with the expected Cu and Zn bioavailabilities at the four sites (i.e. Godolphin &gt; Relubbus &gt; St. Erth &gt; Drym). The naïve population experienced greater metal induced effects in terms of Cu and Zn accumulation, oxidative stress responses and lower LT50s. Analysis of Cu and Zn sub-cellular distribution, however, revealed no significant differences in metal handling. In both populations each metal was localised predominantly to the sub-cellular fraction containing metal bound to metallothionein-like proteins (MTLP) or that holding both metal-rich granules (MRG) and exoskeleton, MTLP and MRG binding being indicative of metal detoxification. However, a greater capacity for detoxified metal storage is not a mechanism implicated in the perceived tolerance of the historically impacted gammarids. Instead our results suggest that the historically impacted population was adapted for lower uptake of Cu and Zn leading to lower bioaccumulation, stress response and ultimately mortality. 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Psychology</subject><subject>Gammarus pulex</subject><subject>General aspects</subject><subject>Inactivation, Metabolic</subject><subject>Malondialdehyde - analysis</subject><subject>Malondialdehyde - metabolism</subject><subject>Metal bioaccumulation</subject><subject>Mortality</subject><subject>Oxidative Stress</subject><subject>Population differences</subject><subject>Rivers</subject><subject>Sub-cellular distribution</subject><subject>Toxicity Tests - methods</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>Zinc - analysis</subject><subject>Zinc - pharmacokinetics</subject><subject>Zinc - toxicity</subject><issn>0166-445X</issn><issn>1879-1514</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkU2PFCEQhonRuOPoT1C5GE89QgP9cTKbVVeTTTzoJt4IA8WECd30Aq27R_-5tD2rxyWV1KGeqnqpF6GXlOwooc27407dzCqH211NKN2REoQ-QhvatX1FBeWP0aZwTcW5-HGGnqV0JOXVvH-KzmrKWtrQdoN-f3DWQoQxO-VxDh6iGjXgYHH-FfClGgYV54Sn2cMtnkLJKrswJpwLmCavxgwG2xgGbO5H4QGy8j4cYHQaRzisDQGrMsHf_a3iQ1TGFfg5emKVT_DilLfo-tPH7xefq6uvl18uzq8qzQXJlRFs31gDPTFMaOhAG6KZ7W3bM2oMcNsaWjea6LbtbA0NCOi0UYLXZG8tZVv0dp07xXAzQ8pycEmDLz-AMCfZNbxvWM_ah0khalIz3hdSrKSOIaUIVk7RlYPdSUrkYpM8ypNNcrFJkhJk0fLqtGHeD2D-dd37UoA3J0AlrbxdTHHpP8cJa0XRsEWvV86qINUhFub6W9nECO0FbdqFeL8SUG7700GUSZezazAugs7SBPeA2D_OO8Dx</recordid><startdate>20110301</startdate><enddate>20110301</enddate><creator>Khan, Farhan R.</creator><creator>Irving, Jennifer R.</creator><creator>Bury, Nicolas R.</creator><creator>Hogstrand, Christer</creator><general>Elsevier B.V</general><general>Amsterdam; New York: Elsevier Science</general><general>Elsevier</general><scope>FBQ</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope><scope>7QH</scope><scope>7ST</scope><scope>7TV</scope><scope>7U7</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H95</scope><scope>H97</scope><scope>L.G</scope><scope>SOI</scope></search><sort><creationdate>20110301</creationdate><title>Differential tolerance of two Gammarus pulex populations transplanted from different metallogenic regions to a polymetal gradient</title><author>Khan, Farhan R. ; Irving, Jennifer R. ; Bury, Nicolas R. ; Hogstrand, Christer</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c450t-d53b6fde90d35ce8ecd0c3f9f7931dde4f7d126c0c778f2e6e5e8cda5420bff13</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>Adaptation, Physiological</topic><topic>Amphipoda</topic><topic>Amphipoda - drug effects</topic><topic>Amphipoda - metabolism</topic><topic>Animal Population Groups</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Biological and medical sciences</topic><topic>Biological Availability</topic><topic>Copper - analysis</topic><topic>Copper - pharmacokinetics</topic><topic>Copper - toxicity</topic><topic>Crustacea</topic><topic>Cytotoxins</topic><topic>Detoxification</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>England</topic><topic>Environmental Exposure - adverse effects</topic><topic>Fundamental and applied biological sciences. 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One population was native to the Hayle region (Drym) and presumably has been historically impacted by elevated Cu and Zn levels, whilst naïve gammarids were collected from the River Cray, Kent, UK. Both populations were subject to a 32 day in situ exposure at four R. Hayle sites (Drym, Godolphin, Relubbus and St. Erth). Mortality (LT50), Cu and Zn accumulation and sub-cellular distribution, and oxidative stress (malondialdehyde production) increased with the expected Cu and Zn bioavailabilities at the four sites (i.e. Godolphin &gt; Relubbus &gt; St. Erth &gt; Drym). The naïve population experienced greater metal induced effects in terms of Cu and Zn accumulation, oxidative stress responses and lower LT50s. Analysis of Cu and Zn sub-cellular distribution, however, revealed no significant differences in metal handling. In both populations each metal was localised predominantly to the sub-cellular fraction containing metal bound to metallothionein-like proteins (MTLP) or that holding both metal-rich granules (MRG) and exoskeleton, MTLP and MRG binding being indicative of metal detoxification. However, a greater capacity for detoxified metal storage is not a mechanism implicated in the perceived tolerance of the historically impacted gammarids. Instead our results suggest that the historically impacted population was adapted for lower uptake of Cu and Zn leading to lower bioaccumulation, stress response and ultimately mortality. These results demonstrate not only the usefulness of the in situ methodology, but also that differences in population exposure history can cause significant differences in metal responses during exposure at higher concentrations.</abstract><cop>Amsterdam</cop><pub>Elsevier B.V</pub><pmid>21371617</pmid><doi>10.1016/j.aquatox.2011.01.001</doi><tpages>9</tpages></addata></record>
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subjects Adaptation, Physiological
Amphipoda
Amphipoda - drug effects
Amphipoda - metabolism
Animal Population Groups
Animal, plant and microbial ecology
Animals
Applied ecology
Biological and medical sciences
Biological Availability
Copper - analysis
Copper - pharmacokinetics
Copper - toxicity
Crustacea
Cytotoxins
Detoxification
Ecotoxicology, biological effects of pollution
England
Environmental Exposure - adverse effects
Fundamental and applied biological sciences. Psychology
Gammarus pulex
General aspects
Inactivation, Metabolic
Malondialdehyde - analysis
Malondialdehyde - metabolism
Metal bioaccumulation
Mortality
Oxidative Stress
Population differences
Rivers
Sub-cellular distribution
Toxicity Tests - methods
Water Pollutants, Chemical - toxicity
Zinc - analysis
Zinc - pharmacokinetics
Zinc - toxicity
title Differential tolerance of two Gammarus pulex populations transplanted from different metallogenic regions to a polymetal gradient
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