? ? The goal of this project is to develop activated carbon (AC) amendment as a multifunctional, in-situ sediment remediation technique to reduce the bioavailability of both mercury (Hg) and polychlorinated biphenyls (PCBs) at contaminated sediment sites. Activated carbon particles will be impregnated with nanoscale zero-valent iron (nZVI) to induce Hg reduction and sequestration, and PCB dechlorination. Successful application of this innovative technology may significantly reduce the human health risks posed by Hg and PCBs at many hazardous waste sites, while minimizing negative impact to sensitive habitats. The project will accomplish its main goal through a combination of spectroscopic, physicochemical, and biological tests. State-of-the-art microspectroscopy will be used to understand contaminant binding to AC at the particle scale. Physicochemical tests will probe the partitioning of Hg and PCBs to AC particles, and provide insight into sequestration and dechlorination rates, including mechanistic understanding of the role of nZVI on these processes. Finally, biological tests with a relevant clam species will document the effectiveness of AC amendment in reducing Hg and PCB bioavailability to sediment-dwelling macro- invertebrates. Sediment from Stege Marsh (San Francisco Bay, CA), a toxic """"""""hot spot"""""""" contaminated with both Hg and PCBs, will be used in these tests. In-situ treatment with (nZVI-) AC may protect sensitive habitats and endangered species, such as the California clapper rail in the case of Stege Marsh. Combined, Hg and PCB contamination are responsible for the vast majority of fish consumption advisories currently in effect in the US. In addition, public use of Hg- and PCB-contaminated sites is limited due to human health risks associated with these often co-occurring contaminants. This research advances AC amendment as a remediation strategy that will lower both types of human health risks by (1) reducing the level of Hg and PCBs entering the food chain, and (2) decreasing the availability of Hg and PCBs to the local environment. ? ? ? ?

Agency
National Institute of Health (NIH)
Institute
National Institute of Environmental Health Sciences (NIEHS)
Type
Research Project (R01)
Project #
1R01ES016143-01
Application #
7340327
Study Section
Special Emphasis Panel (ZES1-SET-D (R1))
Program Officer
Thompson, Claudia L
Project Start
2007-09-28
Project End
2010-07-31
Budget Start
2007-09-28
Budget End
2008-07-31
Support Year
1
Fiscal Year
2007
Total Cost
$306,425
Indirect Cost
Name
Stanford University
Department
Engineering (All Types)
Type
Schools of Engineering
DUNS #
009214214
City
Stanford
State
CA
Country
United States
Zip Code
94305
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Kim, Eun-Ah; Masue-Slowey, Yoko; Fendorf, Scott et al. (2012) Intra-particle migration of mercury in granular polysulfide-rubber-coated activated carbon (PSR-AC). Chemosphere 86:648-54
Kim, Eun-Ah; Seyfferth, Angelia L; Fendorf, Scott et al. (2011) Immobilization of Hg(II) in water with polysulfide-rubber (PSR) polymer-coated activated carbon. Water Res 45:453-60
Kim, Eun-Ah; Luthy, Richard G (2011) Partitioning of dissolved organic matter-bound mercury between a hydrophobic surface and polysulfide-rubber polymer. Water Res 45:5441-8
Zhuang, Yuan; Ahn, Sungwoo; Seyfferth, Angelia L et al. (2011) Dehalogenation of polybrominated diphenyl ethers and polychlorinated biphenyl by bimetallic, impregnated, and nanoscale zerovalent iron. Environ Sci Technol 45:4896-903
Zhuang, Yuan; Ahn, Sungwoo; Luthy, Richard G (2010) Debromination of polybrominated diphenyl ethers by nanoscale zerovalent iron: pathways, kinetics, and reactivity. Environ Sci Technol 44:8236-42
Ahn, Sungwoo; Werner, David; Luthy, Richard G (2008) Modeling PAH mass transfer in a slurry of contaminated soil or sediment amended with organic sorbents. Water Res 42:2931-42