4.8 Article

Activated Carbon Mitigates Mercury and Methylmercury Bioavailability in Contaminated Sediments

Journal

ENVIRONMENTAL SCIENCE & TECHNOLOGY
Volume 47, Issue 22, Pages 13001-13010

Publisher

AMER CHEMICAL SOC
DOI: 10.1021/es4021074

Keywords

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Funding

  1. U.S. Department of Defense ESTCP Program [08 EB-ER4-017]
  2. Dow Chemical Company
  3. I.E. DuPont de Nemours

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There are few available in situ remediation options for Hg contaminated sediments, short of capping. Here we present the first tests of activated carbon and other sorbents as potential in situ amendments for remediation of mercury and methylmercury (MeHg), using a study design that combined 2 L sediment/water microcosms with 14 day bioaccumulation assays. Our key key end points were pore water concentrations, and bioaccumulation of total Hg and MeHg by a deposit-feeding oligo-chaete Lumbriculus variegatus. Four amendments were tested: an activated carbon (AG); CETCO Organoclay MRM (MRM); Thiol-SAMMS (TS), a thiol-functionalized mesoporous silica; and A/VIBERSEP GT74, an ion-exchange resin. Amendments were tested in four separate microcosm assays using Hg-contaminated sediments from two freshwater and two estuarine sites. AC and TS amendments, added at 2-7% of the dry weight of sediments significantly reduced both MeHg concentrations in pore waters, relative to unamended controls (by 45-95%) and bioaccumulation of MeHg by Lumbriculus (by between 30 and 90%). Both amendments had only small impacts on microcosm surface water, sediment and pore water chemistry, with the exception of significant reductions in pore water dissolved organic matter. The effectiveness of amendments in reducing bioaccumulation was well-correlated with their effectiveness in increasing sediment:water partitioning, especially of MeHg. Sediments with low native sediment:water MeHg partition coefficients were most effectively treated. Thus, in situ sediment sorbent amendments may be able to reduce the risk of biotic Hg and MeHg uptake in contaminated sediments, and subsequent contamination of food webs.

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