anne fairbrother, randy wentsel, bill wood, keith sappington, and pam noyes office of research and...
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Anne Fairbrother, Randy Wentsel, Bill Anne Fairbrother, Randy Wentsel, Bill Wood, Keith Sappington, and Pam NoyesWood, Keith Sappington, and Pam Noyes
Office of Research and DevelopmentOffice of Research and Development
SETAC North America Annual ConferenceSETAC North America Annual Conference
November 2006November 2006
Anne Fairbrother, Randy Wentsel, Bill Anne Fairbrother, Randy Wentsel, Bill Wood, Keith Sappington, and Pam NoyesWood, Keith Sappington, and Pam Noyes
Office of Research and DevelopmentOffice of Research and Development
SETAC North America Annual ConferenceSETAC North America Annual Conference
November 2006November 2006
Framework for Inorganic Framework for Inorganic Metals Risk AssessmentMetals Risk AssessmentFramework for Inorganic Framework for Inorganic Metals Risk AssessmentMetals Risk Assessment
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BackgroundBackground
There has been considerable There has been considerable interest in the Agency’s interest in the Agency’s assessments on metals and assessments on metals and metal compoundsmetal compounds
promulgation of the Toxics promulgation of the Toxics Release Inventory (TRI) lead Release Inventory (TRI) lead rulemakingrulemaking
development of the Agency’s development of the Agency’s Waste Minimization Prioritization Waste Minimization Prioritization ToolTool
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PBT framework is based on principles PBT framework is based on principles developed for organic substances developed for organic substances that do not apply to metalsthat do not apply to metals
PBT framework does not distinguish PBT framework does not distinguish between metal elements, metal between metal elements, metal compounds, or particulate sizecompounds, or particulate size
There is a major disconnect between There is a major disconnect between the forms selected for toxicity testing the forms selected for toxicity testing and those in the marketplaceand those in the marketplace
Challenge to the PBT Framework as Challenge to the PBT Framework as Applied to MetalsApplied to Metals
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BCFs for metalsBCFs for metals vary with species and vary with species and
environmental conditionsenvironmental conditions show an inverse relationship with show an inverse relationship with
concentrationconcentration are not a predictor of toxicityare not a predictor of toxicity
Speciation and bioavailability Speciation and bioavailability are more meaningful than are more meaningful than persistence when evaluating persistence when evaluating hazard potentialhazard potential
Challenge to the PBT Framework as Challenge to the PBT Framework as Applied to MetalsApplied to Metals
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Challenge to the PBT Framework as Challenge to the PBT Framework as Applied to MetalsApplied to Metals
PBT framework lacks discriminatory power for metals
All metals would satisfy the All metals would satisfy the criteria to be a PBTcriteria to be a PBT
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Metals FrameworkMetals Framework
Develop a cross-Agency Develop a cross-Agency guidance for assessing metal guidance for assessing metal and metal compoundsand metal compounds
discussions within the Agency, discussions within the Agency, with external stakeholders and with external stakeholders and with Congresswith Congress
provide opportunities for external provide opportunities for external input, peer review and cross-input, peer review and cross-Agency involvement Agency involvement
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Metals FrameworkMetals Framework
Develop a comprehensive Develop a comprehensive framework that could be the framework that could be the basis of future Agency actionsbasis of future Agency actions
Provide a consistent set of key Provide a consistent set of key guiding principles to be guiding principles to be considered in assessing risks considered in assessing risks posed by inorganic metals posed by inorganic metals
Identify available methods, Identify available methods, models, and approaches for use models, and approaches for use in metals risk assessmentsin metals risk assessments
Foster consistency across EPA Foster consistency across EPA programs and regions programs and regions
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Phase I: Metals Phase I: Metals Action Plan Dec 2002 Action Plan Dec 2002
Phase II: Issue PapersPhase II: Issue Papers Aug 2004Aug 2004
ScheduleSchedule
SABSABReviewReview
PeerPeerReviewReview
EnvironEnvironChemistryChemistry
HumanHumanHealthHealth
EcoEcoEffectsEffects
ExposureExposure Bioavail.Bioavail.Bioaccum.Bioaccum.
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Phase III: Draft Metals Phase III: Draft Metals Framework June 2004Framework June 2004
Phase IV: Final Document and AgencyPhase IV: Final Document and Agency Implementation Jan 2007Implementation Jan 2007
ScheduleSchedule
Phase III: Draft Metals Phase III: Draft Metals Framework Dec 2004Framework Dec 2004
Peer Input WorkshopPeer Input WorkshopJuly 2004July 2004
SAB Review Feb 2005 - 2006SAB Review Feb 2005 - 2006
InterAgency Review August 2006InterAgency Review August 2006
IntraAgency Review July 2006IntraAgency Review July 2006
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Metals and Metalloids of Metals and Metalloids of Primary Interest Primary Interest
AluminumAluminum AntimonyAntimony ArsenicArsenic BariumBarium BerylliumBeryllium BoronBoron CadmiumCadmium ChromiumChromium CobaltCobalt CopperCopper IronIron Lead Lead
ManganeseManganese Mercury Mercury
(inorganic)(inorganic) MolybdenumMolybdenum NickelNickel SeleniumSelenium SilverSilver StrontiumStrontium TinTin ThalliumThallium VanadiumVanadium ZincZinc
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Framework TOCFramework TOC
Executive SummaryExecutive Summary
Ch 1 – IntroCh 1 – Intro
Ch 2 – Framework overviewCh 2 – Framework overview
Ch 3 – Environmental Chemistry, Ch 3 – Environmental Chemistry, Transport, and FateTransport, and Fate
Ch 4 – Human HealthCh 4 – Human Health
Ch 5 – Aquatic EcoRiskCh 5 – Aquatic EcoRisk
Ch 6 – Terrestrial EcoRiskCh 6 – Terrestrial EcoRisk
Ch 7 -- ReferencesCh 7 -- References
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Ch 1. IntroductionCh 1. Introduction Purpose and audiencesPurpose and audiences Metals Framework ScopeMetals Framework Scope Metals Assessment ContextMetals Assessment Context
National ranking and categorizationNational ranking and categorization National risk assessmentsNational risk assessments Regional and local risk assessmentsRegional and local risk assessments
Key Principles to ConsiderKey Principles to Consider
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Ch 1. IntroductionCh 1. Introduction Purpose and audiencesPurpose and audiences Metals Framework ScopeMetals Framework Scope Metals Assessment ContextMetals Assessment Context
National ranking and categorizationNational ranking and categorization National risk assessmentsNational risk assessments Regional and local risk assessmentsRegional and local risk assessments
Key Principles to ConsiderKey Principles to Consider
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Categories of Metals Assessments and ApplicableCategories of Metals Assessments and ApplicableEPA Statutory FrameworkEPA Statutory Framework
SiteSite--Specific AssessmentsSpecific Assessments
[CWA, CAA, CERCLA, RCRA][CWA, CAA, CERCLA, RCRA]NationalNational--Scale AssessmentsScale Assessments
ScreeningScreening--LevelLevelAnalysesAnalyses
Criteria/Criteria/Standards DevelopmentStandards Development
[CAA, CWA, SDWA, [CAA, CWA, SDWA, CERCLA, RCRA]CERCLA, RCRA]
Chemical Reviews Chemical Reviews [TSCA, FIFRA, [TSCA, FIFRA, CAA, EPCRA]CAA, EPCRA]
Ranking/Ranking/CategorizationCategorization
[EPCRA, CERCLA, RCRA[EPCRA, CERCLA, RCRATSCA, FIFRA, TSCA, FIFRA,
SDWA, CAA, CWA]SDWA, CAA, CWA]
Complex AnalysesComplex Analyses
ScreeningScreening--LevelLevelAnalysesAnalyses
Complex AnalysesComplex Analyses
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PrinciplesPrinciples
Metals are Metals are naturally occurring naturally occurring constituentsconstituents in the environment in the environment and vary in concentrations and vary in concentrations across geographic regions.across geographic regions.
All environmental media have All environmental media have naturally occurring naturally occurring mixturesmixtures of of metals, and metals often are metals, and metals often are introduced into the introduced into the environment as mixtures. environment as mixtures.
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Natural occurrence of Natural occurrence of baritebarite
Natural occurrence of barite(USGS)
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PrinciplesPrinciples Some metals are Some metals are essentialessential for for
maintaining proper health of maintaining proper health of humans, animals, plants, and humans, animals, plants, and microorganisms.microorganisms.
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PrinciplesPrinciples Unlike organic chemicals, metals are Unlike organic chemicals, metals are
neither created nor destroyedneither created nor destroyed by by biological or chemical processesbiological or chemical processes They can transform from one species to They can transform from one species to
another (valence states) and can convert another (valence states) and can convert them between inorganic and organic forms.them between inorganic and organic forms.
The absorption, distribution, The absorption, distribution, transformation, and excretion of a transformation, and excretion of a metal (metal (toxicokineticstoxicokinetics) within an ) within an organism depends onorganism depends on the metalthe metal the form of the metal or metal compoundthe form of the metal or metal compound the organism’s ability to regulate and/or the organism’s ability to regulate and/or
store the metal. store the metal.
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Ch 2. Framework Over viewCh 2. Framework Over view
Human Health and Ecological Human Health and Ecological Risk Assessment: Planning and Risk Assessment: Planning and Problem FormulationProblem Formulation
Metal Conceptual ModelMetal Conceptual Model Assessment PhaseAssessment Phase
BioavailabilityBioavailability Characterization of ExposureCharacterization of Exposure Characterization of Effects / Hazard Characterization of Effects / Hazard
AnalysisAnalysis Risk CharacterizationRisk Characterization
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Metal Loadings to Media
air
surface water
soil, seds.,
Metal Distribution
in Media
soil, seds., air
Media-based Exposure
Models
ground watersoil, seds., air
Bioaccumulation/TK Models
Metal Distribution
in Tissues
liver, lung,kidney, gill
fur, feather etc.
Residue-based Toxicity Models
Risk (Toxicity)
toOrganism / Individual
mortalitygrowth, repro.
other endpoints
(e.g., mg/kg/d)
diet
Metal Distribution
in Diet
producers1o consumers
BioaccumulationFood Web Model
2o consumers
Dietary ExposureModels
Media-based Toxicity Models
Risks at Higher
Levels of Biological
Organization
populationcommunity
ecosystem
Population, Habitat, Ecosystem
Models
ground watersurface water
ground watersurface water
Dose-basedToxicity Models
Fate & Transport Models
Exposure to Metal
(M1) (M2) (M3) (M4)
(M5)
(M6)
(M7)
(M8)
(M9)
Conceptual Model for Metal Risk AssessmentsConceptual Model for Metal Risk Assessments
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Assessment QuestionsAssessment Questions
Principles are translated into Principles are translated into assessment questions to assist assessment questions to assist in their considerationin their consideration
Questions drafted for all Questions drafted for all phases of the risk assessmentphases of the risk assessment
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Example Assessment Example Assessment QuestionsQuestions
BACKGROUND: How should background BACKGROUND: How should background (natural and anthropogenic) levels for (natural and anthropogenic) levels for metals be characterized for the selected metals be characterized for the selected spatial scale of the assessment? spatial scale of the assessment?
MIXTURES: Are toxicological effects of MIXTURES: Are toxicological effects of metal mixtures being incorporated in the metal mixtures being incorporated in the effects assessment? effects assessment?
ESSENTIALITY: How will both toxicity and ESSENTIALITY: How will both toxicity and deficiencies of essential metals be deficiencies of essential metals be characterized?characterized?
METAL FORMS: Since environmental METAL FORMS: Since environmental chemistry is a primary factor influencing chemistry is a primary factor influencing metal speciation and subsequent metal speciation and subsequent transport, uptake, and toxicity, how will it transport, uptake, and toxicity, how will it be included in the risk assessment?be included in the risk assessment?
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Ch 3. Environmental Chemistry, Ch 3. Environmental Chemistry, Transport, and FateTransport, and Fate
Introduction and TerminologyIntroduction and Terminology Hard and soft acids and basesHard and soft acids and bases TransformationsTransformations Aquatic chemistryAquatic chemistry Ground water and metals mobilityGround water and metals mobility Sediment chemistrySediment chemistry Soil chemistrySoil chemistry Atmospheric behavior / chemistryAtmospheric behavior / chemistry
Metal Transport and FateMetal Transport and Fate Aquatic and terrestrial transport pathwaysAquatic and terrestrial transport pathways Atmospheric fate and transportAtmospheric fate and transport
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Bioavailability IssuesBioavailability Issues
Bioavailability of metals Bioavailability of metals variesvaries widelywidely according to the physical, chemical, according to the physical, chemical, and biological conditions under which and biological conditions under which an organism is exposed. an organism is exposed.
Bioavailability should be Bioavailability should be explicitly explicitly incorporatedincorporated into all risk assessments into all risk assessments
Trophic transfer can be an important Trophic transfer can be an important route of exposure for metalsroute of exposure for metals but biomagnification of inorganic forms of but biomagnification of inorganic forms of
metals in food webs is generally not a metals in food webs is generally not a concern in metals assessments concern in metals assessments
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BAF/BCF IssuesBAF/BCF Issues
Certain metal compounds are Certain metal compounds are known to bioaccumulate in tissues known to bioaccumulate in tissues and this bioaccumulation can be and this bioaccumulation can be related to their toxicity.related to their toxicity.
The latest scientific data on The latest scientific data on bioaccumulation do not currently bioaccumulation do not currently support the use of bioconcentration support the use of bioconcentration factor (BCF) or bioaccumulation factor (BCF) or bioaccumulation factor (BAF) values when applied as factor (BAF) values when applied as generic threshold criteria for the generic threshold criteria for the hazard potential of inorganic metalhazard potential of inorganic metal
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BAF/BCF IssuesBAF/BCF Issues
Single value BAF/BCFs hold the most value for site-specific assessments extrapolation across different exposure
conditions is minimized
For regional and national assessments, BAF/BCFs should be expressed as a function of media chemistry and metal concentration for particular species (or closely related organisms)
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Environmental ChemistryEnvironmental Chemistry Metal speciation affectsMetal speciation affects
toxicity, volatilization, photolysis, toxicity, volatilization, photolysis, sorption, atmospheric deposition, sorption, atmospheric deposition, acid/base equilibria, polymerization, acid/base equilibria, polymerization, complexation, electron-transfer reactions, complexation, electron-transfer reactions, solubility and precipitation equilibria, solubility and precipitation equilibria, microbial transformations, and diffusivitymicrobial transformations, and diffusivity
Speciation includesSpeciation includes free metal ions, metal complexes free metal ions, metal complexes
dissolved in solution and sorbed on solid dissolved in solution and sorbed on solid surfaces, and metal species that have surfaces, and metal species that have been co-precipitated in major metal solids been co-precipitated in major metal solids or that occur in their own solids.or that occur in their own solids.
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Environmental ChemistryEnvironmental Chemistry
pH and redox potential affect pH and redox potential affect speciationspeciation
Kd valuesKd values
limited use of single values limited use of single values
Aging of metals in media reduces Aging of metals in media reduces bioavailabilitybioavailability
Metal sorption behavior affects Metal sorption behavior affects bioavailabilitybioavailability
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Ch 4. Human Health Risk Ch 4. Human Health Risk Assessment for MetalsAssessment for Metals
Metals PrinciplesMetals Principles Human Exposure AssessmentHuman Exposure Assessment
BackgroundBackground BioavailabilityBioavailability Susceptible populationsSusceptible populations Environmental release, transport and fateEnvironmental release, transport and fate Route-specific differences in effectsRoute-specific differences in effects Integrated exposuresIntegrated exposures BiomarkersBiomarkers
Hazard CharacterizationHazard Characterization MixturesMixtures EssentialityEssentiality Forms of metalsForms of metals Toxicokinetics / toxicodynamicsToxicokinetics / toxicodynamics Metal toxicityMetal toxicity Dose-response assessmentDose-response assessment
Risk CharacterizationRisk Characterization
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Human HealthHuman Health
The organ or tissue in which metal The organ or tissue in which metal toxicity occurs may differ from the toxicity occurs may differ from the organ or tissue(s) in which the metal organ or tissue(s) in which the metal bioaccumulates and may be bioaccumulates and may be affected by the metal’s kineticsaffected by the metal’s kinetics
Both the exposure route and the Both the exposure route and the form of a metal can affect the form of a metal can affect the metal’s carcinogenic potential and metal’s carcinogenic potential and its noncancer effects its noncancer effects
Sensitivity to metals varies with Sensitivity to metals varies with age, sex, pregnancy status, age, sex, pregnancy status, nutritional status, and geneticsnutritional status, and genetics
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Human HealthHuman Health
Metals attached to small airborne Metals attached to small airborne particles are of primary particles are of primary importance for inhalation importance for inhalation exposures. exposures.
Because the diets of humans and Because the diets of humans and other animals are diverse, there other animals are diverse, there may be wide variability in the may be wide variability in the dietary intake of some metals dietary intake of some metals (e.g., in seafood)(e.g., in seafood) results in temporal, geographic or results in temporal, geographic or
cultural variability of responses cultural variability of responses
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Essentiality should be viewed Essentiality should be viewed as part of the overall dose-as part of the overall dose-response relationship for response relationship for those metals shown to be those metals shown to be essentialessential Zinc IRIS document is an Zinc IRIS document is an
exampleexample
RFDs should not be below RFDs should not be below RDAsRDAs
Human HealthHuman Health
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Essentiality and ToxicityEssentiality and Toxicity
NutritionallyEssential Metals
with Potential ToxicEffects at Higher
Doses
Toxic Metals WithPossible Beneficial
Effects
Toxic Metals Withno Known
Beneficial Effects
Cobalt Chromium III Copper Iron Manganese Molybdenum Selenium Zinc
Arsenic Boron Nickel Silicon Vanadium
Aluminum Antimony Barium Beryllium Cadmium Chromium VI Lead Mercury Silver Strontium Thallium Tin
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Aquatic Ecological Risk Aquatic Ecological Risk Assessment for MetalsAssessment for Metals
Metals PrinciplesMetals Principles Characterization of ExposureCharacterization of Exposure
BackgroundBackground Forms of metalsForms of metals Exposure pathway analysisExposure pathway analysis Fate and transport of metalsFate and transport of metals Bioavailability and bioaccumulationBioavailability and bioaccumulation
Characterization of EffectsCharacterization of Effects EssentialityEssentiality Toxicokinetics / toxicodynamicsToxicokinetics / toxicodynamics Metal mixturesMetal mixtures Critical body residuesCritical body residues
Risk CharacterizationRisk Characterization
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Terrestrial Ecological Risk Terrestrial Ecological Risk Assessment for MetalsAssessment for Metals
Metals PrinciplesMetals Principles Characterization of ExposureCharacterization of Exposure
Natural occurrence of metalsNatural occurrence of metals Forms of metalsForms of metals Exposure routesExposure routes Soil transport and fate modelsSoil transport and fate models Toxicokinetics / toxicodynamicsToxicokinetics / toxicodynamics Soil invertebrate exposureSoil invertebrate exposure Plant exposurePlant exposure Wildlife exposureWildlife exposure
Characterization of EffectsCharacterization of Effects EssentialityEssentiality Toxicity testsToxicity tests Metal mixturesMetal mixtures Critical body residuesCritical body residues Plant and invertebrate toxicityPlant and invertebrate toxicity Wildlife toxicityWildlife toxicity
Risk CharacterizationRisk Characterization
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EcologicalEcological Background levelsBackground levels refers to those refers to those
concentrations of metals that derive concentrations of metals that derive from natural as well as anthropogenic from natural as well as anthropogenic sources that are not the focus of the sources that are not the focus of the risk assessmentrisk assessment metal concentrations vary widely over metal concentrations vary widely over
space and time space and time are partially responsible for distributions are partially responsible for distributions
of plants and wildlifeof plants and wildlife
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EcologicalEcological
FFor aquatic organisms, routes of or aquatic organisms, routes of exposure includeexposure include absorption across respiratory organs, absorption across respiratory organs,
dermal absorption, sediment ingestion, dermal absorption, sediment ingestion, and food ingestionand food ingestion
For terrestrial organisms, routes of For terrestrial organisms, routes of exposure includeexposure include binding to roots, foliar uptake, dermal binding to roots, foliar uptake, dermal
absorption, food, water, and soil absorption, food, water, and soil ingestion, or inhalationingestion, or inhalation
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EcologicalEcological
For most metals, the free ionic form is most For most metals, the free ionic form is most responsible for toxicityresponsible for toxicity
Free-ion activity models are useful for Free-ion activity models are useful for establishing relative toxicity among metals in establishing relative toxicity among metals in different mediadifferent media BLMBLM FIAMFIAM
Sediment toxicity is reduced by acid volatile Sediment toxicity is reduced by acid volatile sulfides, organic carbon and other factors sulfides, organic carbon and other factors that bind free ions and decrease that bind free ions and decrease bioavailabilitybioavailability
Soil toxicity is affected by pH, CEC, and % Soil toxicity is affected by pH, CEC, and % organic matterorganic matter
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EcologicalEcological
Inorganic metal compounds rarely Inorganic metal compounds rarely biomagnify across three or more biomagnify across three or more trophic levelstrophic levels
Effects addition models are a Effects addition models are a useful first approximation of acute useful first approximation of acute toxicity of metal mixturestoxicity of metal mixtures
Critical body or tissue residues Critical body or tissue residues can be used for effects can be used for effects estimations but few data are estimations but few data are available for metalsavailable for metals
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Metals Framework, January, 2007Metals Framework, January, 2007
http://?http://?
Issue papers August 2004Issue papers August 2004
http://cfpub2.epa.gov/ncea/cfm/http://cfpub2.epa.gov/ncea/cfm/recordisplay.cfm?deid=86119recordisplay.cfm?deid=86119
Web SitesWeb Sites
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Core Technical PanelCore Technical Panel
Co-leads: Anne Fairbrother ORD/NHEERLCo-leads: Anne Fairbrother ORD/NHEERL Randy Wentsel OW/OSTRandy Wentsel OW/OST
Steering Committee:Steering Committee:Bill WoodBill Wood ORD/NCEA/RAFORD/NCEA/RAFSteve DevitoSteve Devito OEI/OIAAOEI/OIAAAlec McBrideAlec McBride OSWER/OSWOSWER/OSWDave MountDave Mount ORD/NHEERLORD/NHEERLKeith SappingtonKeith Sappington ORD/NCEAORD/NCEA
Pam Noyes Pam Noyes ORD/NCEA/RAFORD/NCEA/RAF
Gary Bangs ORD/NCEA/RAFGary Bangs ORD/NCEA/RAF