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Ocean acidification increases the toxicity of contaminated sediments
Author(s) -
Roberts David A.,
Birchenough Silva. R.,
Lewis Ceri,
Sanders Matthew B.,
Bolam Thi,
Sheahan Dave
Publication year - 2013
Publication title -
global change biology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 4.146
H-Index - 255
eISSN - 1365-2486
pISSN - 1354-1013
DOI - 10.1111/gcb.12048
Subject(s) - environmental chemistry , sediment , contamination , bioavailability , zinc , water column , amphipoda , metal , flux (metallurgy) , chemistry , toxicity , environmental science , geology , ecology , biology , paleontology , bioinformatics , crustacean , organic chemistry
Ocean acidification ( OA ) may alter the behaviour of sediment‐bound metals, modifying their bioavailability and thus toxicity. We provide the first experimental test of this hypothesis with the amphipod C orophium volutator . Amphipods were exposed to two test sediments, one with relatively high metals concentrations (Σ metals 239 mg kg −1 ) and a reference sediment with lower contamination (Σ metals 82 mg kg −1 ) under conditions that mimic current and projected conditions of OA (390–1140 μatm p CO 2 ). Survival and DNA damage was measured in the amphipods, whereas the flux of labile metals was measured in the sediment and water column ( WC ) using D iffusive G radients in T hin‐films. The contaminated sediments became more acutely toxic to C . volutator under elevated p CO 2 (1140 μatm). There was also a 2.7‐fold increase in DNA damage in amphipods exposed to the contaminated sediment at 750 μatm p CO 2 , as well as increased DNA damage in organisms exposed to the reference sediment, but only at 1140 μatm p CO 2 . The projected p CO 2 concentrations increased the flux of nickel and zinc to labile states in the WC and pore water. However, the increase in metal flux at elevated p CO 2 was equal between the reference and contaminated sediments or, occasionally, greater from reference sediments. Hence, the toxicological interaction between OA and contaminants could not be explained by e ffects of pH on metal speciation. We propose that the additive physiological effects of OA and contaminants will be more important than changes in metal speciation in determining the responses of benthos to contaminated sediments under OA . Our data demonstrate clear potential for near‐future OA to increase the susceptibility of benthic ecosystems to contaminants. Environmental policy should consider contaminants within the context of changing environmental conditions. Specifically, sediment metals guidelines may need to be reevaluated to afford appropriate environmental protection under future conditions of OA .