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HydroQual Capabilities for Pathways Analysis in Support of Natural Resource Damage Assessment

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... Gate Bridge (miles) PREDICTED AVERAGE AND RANGE. BAY-WIDE. WER ... (Data: S.San Francisco Bay RMP, 1993 - 1996) BLM Application Status. Applied to Cu, Ag, Zn ... – PowerPoint PPT presentation

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Title: HydroQual Capabilities for Pathways Analysis in Support of Natural Resource Damage Assessment


1
HydroQual Capabilities for Pathways Analysis in
Support of Natural Resource Damage Assessment
2
Why Consider Models for Pathways Analysis?
  • Models link the sources with observed body
    burdens in organisms
  • Models can add value to data by extending spatial
    and temporal coverage
  • Models have predictive capabilities - what will
    the future of the resource be after remedial
    action?

3
Pathways Analysis Model Components
4
Noted HydroQual Model Component Experts
  • Hydrodynamic Transport Nicholas Kim
  • Organic Carbon Production James Fitzpatrick
  • Chemical Fate and Transport Robin Landeck
    Miller
  • Biotic Ligand Model Robert Santore
  • Food Chain/Bioaccumulation Kevin Farley
  • Toxicity Prediction Joy McGrath

5
Hydrodynamic Transport
  • Rivers, lakes, streams, estuaries, coastal
    ocean, embayments in 1-D, 2-D, or 3-D
  • Landside loadings and atmospheric exchanges and
    fluxes
  • Several model codes (ECOM, EFDC, RRMP, SWMM)
  • Accounts for physical movement of the water and
    dissolved and particulate substances

6
Selected Hydrodynamic Circulation Studies
7
Sediment Transport
  • Directly linked to hydrodynamic model results
  • Can be used to support contaminant fate and
    transport with foc approach
  • Addresses both cohesive and non-cohesive sediment
    types
  • ECOMSED and GLERL codes
  • Provides vertical phase transport terms for
    particulate contaminants (settling, burial,
    resuspension)

8
Organic Carbon Production
  • Directly linked to hydrodynamic model results
  • May also be linked to sediment transport model
    results
  • A refinement over foc approaches (particularly
    for low molecular weight PCB homologs)
  • RCA code
  • Provides direct calculation of the phase to which
    hydrophobic organic contaminants partition with
    independent checks

9
Selected Eutrophication Studies
10
Contaminant Fate and Transport
  • Directly linked to hydrodynamic transport and
    organic carbon production model results
  • Multiple pollutant types (HOCs, metals, methyl
    mercury)
  • Can be modified to support relevant processes
    (volatilization, photolysis, dechlorination,
    phase partitioning)
  • WASTOX, GISTOX, RCATOX codes
  • Provides for the movement and transformation of
    dissolved and particulate phases of contaminants

11
Selected Toxic/Chemical Fate Modeling
Housatonic River NY/NJ Harbor recently completed
12
The Biotic Ligand Model (BLM)
  • Uses standard chemical parameters as inputs (pH,
    DOC, alkalinity, cations, anions)
  • Can predict metal toxicity to aquatic organisms
  • BLM predictions can be used to assess potential
    risk due to environmental metal concentrations
  • Can be used to look at spatial, temporal trends
    in a water body or region

13
Generalized BLM Framework
14
San Francisco Bay Case Study
15
BLM Application Status
  • Applied to Cu, Ag, Zn
  • Cd, Ni, Pb under development
  • No Al or Cr
  • Acute toxicity, aqueous exposures
  • Mostly freshwater

16
Where BLM is Heading
  • Chronic Exposures
  • Multiple routes of exposure (i.e., particulate
    metals)
  • Multiple metals
  • Include sediment pore water effects in addition
    to SEMAVS

17
Toxicity Prediction
  • Answer the question, What level of a contaminant
    causes an effect?
  • Difficult because bioavailability varies over a
    wide range of contaminant concentrations
  • Approaches developed
  • Equilibrium partitioning
  • SEMAVS
  • Narcosis theory/target lipid model
  • Has led to sediment quality criteria

18
Selected Ecological Risk Evaluations
19
Equilibrium Partitioning (EqP)
  • Sediment concentrations normalized to correct for
    varying bioavailability.
  • Published by EPA ORD as Sediment Quality
    Benchmarks (2000)
  • - Nonionic Organics (EPA-822-R-00-001,
    -002)
  • - Dieldrin, Endrin (EPA-822-R-00-003,
    -004)
  • - Cd, Cu, Ni, Pb, Zn and Ag as mixtures
  • (EPA-822-R-00-005)
  • - Total PAHs as mixtures

20
(No Transcript)
21
Pore Water Normalization
22
PAH Criteria
  • Narcotics
  • Based on Universal Narcosis Slope
  • Toxicity is Additive
  • Lipid Based Body Burden

23
Predicted Toxicity for Single PAHs and PAH
Mixtures in Sediments
24
Contact Information
  • Further information on HydroQuals Natural
    Resource Damage Assessment services may be
    obtained from
  • Robin Landeck Miller
  • HydroQual, Inc.
  • 1200 MacArthur Boulevard
  • Mahwah, New Jersey 07430
  • 201-529-5151 ext. 7119
  • rmiller_at_hydroqual.com
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