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Understand Aging in Contaminant Bioavailability and Remediation
Jay Gan and Daniel Schlenk Department of Environmental Sciences UC Riverside
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Outline What did we propose to do? How are we doing it?
Expected results and implications
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Bioaccumulation or toxic effect
Bioavailability Freely dissolved concentration Cfree The potential for a chemical to undergo spontaneous processes, e.g., diffusion and partitioning Accessibility The actual amount of a chemical that is or may become available within a given time and under given conditions Total concentration Bioaccessible Concentration Freely dissolved Concentration Bioaccumulation or toxic effect Bioavailability Reichenberg and Mayer, 2006, Environ. Toxicol. Chem. 25,
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Aged Contaminants Superfund site contaminants:
Released from historical use, misuse, accidents or incidents Have aged extensively e.g., PCBs, DDT, OC pesticides banned in 1970s Residues have “aged” for decades !! 1947 – 1983: Montrose manufactured DDT at its plant near Torrance, California Discharged DDT wastewater into Los Angeles sewers that emptied into the Pacific Ocean off White Point on the Palos Verdes Shelf.
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Benthic invertebrates Dissolved OM
plant roots Non-accessible organic matter microbes Bioaccessible Benthic invertebrates Dissolved OM Freely dissolved
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Aging Decreases Bioavailability
Alexander M., ES&T, 2000 Morrison et al., ES&T, 2000
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Project Aims Optimize a bioavailability method to measure aging effect
Evaluate relationship of age and bioavailability of DDTs in Superfund site sediments Understand effects of black carbon amendment on aging Incorporation of aging effect in risk assessment and remediation monitoring
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Aim 1: Method Optimization
Accessible concentration : Ce (µg/kg) fraction : E (fraction) Isotope Dilution Method Stable isotope analogs Centrifuge Liquid-liquid extraction Sediment extraction Delgado et al., Environ. Poll. 2013 Jia et al., ES&T, 2014
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Approach Delgado et al., 2013 Jia et al., 2014 mixing
2g sediment + 20 mL water centrifuge concentrating extraction GC-MS/MS Delgado et al., 2013 Jia et al., 2014
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Aim 2: Aging Effect in Superfund Site Sediments
Palos Verdes Shelf
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Approach Obtain sediment cores from LACSD:
Archived and new samples 2-cm increments Use 210Pb dating to estimate age of sediment samples Contracted to Prof. M. Brenner, Univ. Florida Measure E values of DDTs in sediment As a function of depth As a function of age Validate bioavailability with bioaccumulation assays Evaluate relationships between age and bioavailability
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Aim 3: Carbon Amendment and Aging
Amendment materials such as carbon are increasingly used in remediation Carbon alters sediment properties by providing more micro/nanopores and aromatic sites Carbon amendment may accelerate “aging” Different carbon materials may exert different influences on aging Information may be used for selecting amendment materials
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Aim 4: Applications Confirm bioavailability estimates
Sediment cores Palos Verdes McGrath Lake sediments Estimate accumulation to food fish Determine BAFs from sediments to biota Calculate risk factors for human consumption of food fish
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IDM validation-2 IDM vs. Bioaccumulation Neanthes Arenaceodentata
California halibut (Paralichthys californicus) Seafood consumption
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McGrath Lake
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Freshwater sediment bioavailability
Chironomus tentans
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Effects of PV sediment treatment on DDT concentrations in Neanthes sp
Effects of PV sediment treatment on DDT concentrations in Neanthes sp. and in Hornyhead Turbot after feeding worms to fish
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Risk Assessment Draft Update of Human Health Ambient Water Criteria (USEPA OW May 2014) BAFs calculated from EPI Suite (Arnot & Gobas model) Trophic level breakdown TL2 benthic filter feeders TL3 forage fish TL4 predatory fish Dietary Exposure (NHANES) Seafood Habits of Recreational Anglers in Santa Monica Bay Southern California Coastal Water Research Project Chemicals in Fish: Consumption of Fish and Shellfish in California and the United States Office of Environmental Health Hazard Assessment (OEHHA) Santa Monica Bay Seafood Consumption study
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Focus of Risk Assessment
Consumption patterns for Subsistence Anglers vs NHANES age groups. Daily, Monthly and Lifetime Dose estimates Non-cancer Hazard Quotient POD Cancer Endpoints Cancer Slope Factor (EPA 2008) Thresholds from CalEPA and OEHHA
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Research Team Collaborators: Joe Gully, Jerry Tang, LACSD
PI Jay Gan PI Dan Schlenk Ph.D. Student Allison Taylor Ph.D. Student Scott Coffin Postdoc Charles Liao Collaborators: Joe Gully, Jerry Tang, LACSD Keith Maruya, Wayne Lao, SCCWRP Prof. M. Brenner, Univ. Florida
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