Risk-based Management of PCBs in San Francisco Bay

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Risk-based Management of

PCBs in San Francisco Bay

All the hard work done by

Frank A.P.C. Gobas and Jon A. Arnot

Presentation attempted by

Adrian M.H. deBruyn

October 30, 2008

Workshop on Climate Change Risk Assessments

SFU

1. Problem Definition

•   Contamination of the San Francisco Bay ecosystem poses a threat to the health of wildlife and humans

•   Focus of this analysis is on PCBs

–   Persistent, Bioaccumulative, Toxic

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2. Management Objectives

•   Aspirational objectives

–   Maintain healthy ecosystems & healthy human populations

•   Operational objectives

–   Prevent contaminant levels in wildlife and sportfish from exceeding levels that cause adverse effects

•   Means objectives

–   Manage historical contamination and ongoing contaminant inputs

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3. Indicators of Risk

•   Some combination of magnitudes and probabilities

–   Fraction of a wildlife population exceeding (or probability that an individual within a population will exceed) a particular threshold exposure level associated with a particular type of effect or

–   Probability of a particular level of adverse effects

(e.g., 0.001% increase in lifetime cancer risk) in humans

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4. Management Options

•   Not explicitly addressed, but

–   Focus of assessment is on linking risk to manageable entities (PCB concentrations and loadings)

–   Assessment includes risk-based derivation of management objectives (targets)

–   Management will likely include remediation of portions of SFB and/or key source areas

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7. Conceptual Model

•   Link manageable entities to risk

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7. Conceptual Model

Biological effect levels in seals, bird eggs

Human health risk levels

3. Indicators of Risk

Concentrations in upper trophic level species

Concentrations in sport fish

Concentrations in prey species

Concentrations in water and sediment

Loadings

4. Management Options

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BSAFs

7. Conceptual Model

Biological effect levels in seals, bird eggs

Human health risk levels

3. Indicators of Risk

Concentrations in upper trophic level species

Concentrations in sport fish

Concentrations in prey species

Concentrations in water and sediment

Loadings

4. Management Options

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Biota-Sediment Accumulation Factor (BSAF)

BSAF = C

B

/ C

S

Sediment

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10

C sediment

SFB Food-Web

Bioaccumulation

Model

C biota

Input Model Output

C biota

= BSAF x C sediment

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C sediment

SFB Food-Web

Bioaccumulation

Model

C biota

Output Model Input

C sediment

= C biota

/ BSAF

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C sediment

SFB Food-Web

Bioaccumulation

Model

C biota

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5 & 6. Uncertainty Analysis

•   Characterized variability

–   Sediment concentrations ( n > 1000)

–   Measured BSAFs for sampled species

•   Model Bias

–   Empirical catch-all assessment of ability of model to forecast

•   Monte Carlo Simulation

–   PDFs for various bioaccumulation model parameters

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5 & 6. Uncertainty Analysis

BSAF predicted BSAF observed

Model Bias (MB) = 10 n

Σ Log ( i=1

BSAF predicted,i

BSAF observed,i

) / n

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5 & 6. Uncertainty Analysis

1. Monitoring data

2. Monte Carlo Simulations

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Forward Calculation

+ =

SFB Food-Web

Bioaccumulation

Model

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Forward Calculation

+ =

SFB Food-Web

Bioaccumulation

Model

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Threshold Effect Concentration:

Immunotoxicity

(Kannan et al. 2000)

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Backward Calculation

- =

SFB Food-Web

Bioaccumulation

Model

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Backward Calculation

Female Harbor Seal

Male Harbor Seal

Tern Egg

Cormorant Egg

White croaker

Jacksmelt

Shiner surfperch

Back-calculated sediment targets based on thresholds for toxic effects in fish & wildlife

White croaker

Jacksmelt

Shiner surfperch

Current Mean

Sediment

Concentration

Targets based on 10 -5 excess lifetime cancer risk in human consumers of fish

0 10 20 30 40 50 60 70 80

SFEI Sediment PCB Concentration (ug/kg dw)

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8. Sensitivity Analysis

•   Characterized sensitivity of bioaccumulation model

–   Abiotic state variables (e.g., temperature, suspended solids)

–   Biotic state variables (e.g., lipid content, digestive efficiency)

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8. Sensitivity Analysis

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Key Elements

•   Mechanistic exposure model based on state-of-the-science approaches

•   Combined with empirical data to characterize uncertainty/variability (Model

Bias) in exposure

•   Related to a range of toxicological data

•   Links risk to a manageable entity (C sediment

)

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