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Pesticide Risk Assessment

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Title: Pesticide Risk Assessment


1
Pesticide Risk Assessment
2
What is FIFRA?
  • Federal Insecticide, Fungicide, and Rodenticide
    Act
  • Requires pesticides sold or used in U.S. to be
    registered by EPA
  • EPA registration standard will not cause
    unreasonable adverse effects on the environment

3
FIFRA REGISTRATION
  • Section 3 - Authorizes EPA to register new
    pesticide products
  • Section 4 - Reregistration of pesticides by EPA
    to ensure they meet current standards
  • Section 18 - Emergency use requests can be
    granted by EPA for unregistered pesticide uses
  • Section 24(C) - Special local needs requests can
    be granted by EPA for new uses of registered
    products

4
EPA-OPP Standard Evaluation Procedure for
Ecological Risk Assessment
  • Assumes risk is a function of toxicity and
    exposure
  • RQ Estimated Environmental Concentration /
    Toxicity Endpoint
  • RQ compared to levels of concern (LOCs)

5
Toxicity Tests Terrestrial Animals
Test Species Exposure Endpoint
LD50 Bobwhite/ Mallard Single oral Mortality
LC50 Bobwhite/ Mallard 5-d Dietary Mortality
Repro. Bobwhite/ Mallard 10-wk Dietary LOEC, NOEC
6
Toxicity Tests Aquatic Animals
Test Species Exposure Endpoint
LC50 Rainbow, bluegill, sheepshead 96 h Mortality
LC50 Daphnia, mysid, eastern oyster 48-96 h Mortality
ELS Fathead, Rainbow, Sheepshead 30-100 d LOEC, NOEC
Life Cycle Daphnia, mysid, fish spp. 21-300 d LOEC, NOEC
7
Toxicity Tests Terrestrial Invertebrate
  • Honey bee
  • Acute oral LD50
  • Acute dermal LD50
  • Residue studies LD50

8
Toxicity Test Plants
  • Aquatic plants
  • Blue-green and green algae (EC50)
  • Marine and freshwater diatom (EC50)
  • Duckweed (EC50)
  • Terrestrial plants (EC25, NOEC)
  • Six dicots and four monocots (crops)
  • Root-shoot length, weight, visual

9
Other Sources of Toxicity Information
  • Registrant generated test to satisfy registration
    requirements for other countries
  • OECD Studies
  • Beneficial arthropods
  • Soil microorganisms
  • Formulation/mixture studies
  • Metabolite studies

10
Human Health Toxicity Studies
  • Rat LD50
  • 2 generation chronic rat
  • 90-day sub-chronic rat
  • Inhalation (rat/mouse)
  • Dermal (rabbit)

11
Other Sources of Toxicity Information
  • Open Literature
  • Internet Sources (USGS acute toxicity test
    database, EXTOXNET, PAN pesticide database,
    WHO/FAO pesticide data sheets)
  • EPA-OPP One-liner ecotoxicity and environmental
    fate databases
  • www.epa.gov/pesticides/

12
Laboratory Environmental Fate Studies
  • Aerobic Soil Metabolism - rate of degradation by
    soil microorganisms
  • Hydrolysis - chemical reaction with water forming
    new molecule (often pH dependent)
  • Aqueous Photolysis - breakdown of molecules in
    water through the absorption of light
  • Aerobic and Anaerobic Aquatic Metabolism - rate
    of metabolism in aqueous environment with and
    without oxygen.

13
Laboratory Environmental Fate Studies (continued)
  • Kd and Koc - rate of soil adsorption
  • Bioconcentration Factor (BCF) - Ratio of
    concentration in organism (fish) compared to
    surrounding medium (water)

14
Field Environmental Fate Studies
  • Field Dissipation - evaluate pesticide mobility,
    degradation and dissipation under actual use
    conditions
  • agricultural, aquatic, forestry
  • Field Volatility - evaluate pesticide movement
    when volatilization is concern
  • Dislodgeable residue

15
Chemical/Physical Studies
  • Vapor pressure - measure of a chemicals
    volatility
  • Solubility - measure of ability to dissolve in a
    solvent (water)
  • Henrys Law Constant - ratio of vapor pressure to
    water solubility
  • Octanol-water partition coefficient (Kow) - ratio
    of partitioning in octanol to water

16
EPA-OPP Exposure Analysis
  • Terrestrial
  • Kenaga Nomogram
  • Monitoring Data
  • Aquatic
  • GENEEC
  • PRZM/EXAMS
  • Monitoring Data
  • Terrestrial/Aquatic
  • AgDrift

17
Kenaga Nomogram Review
  • Dietary exposure model for liquid broadcast
    applications
  • Determines maximum and median concentrations on
    various food items
  • Residue based on application rate and structure
    of plant/insect
  • Residues independent of application method

18
Granular, Bait, and Treated Seed Exposure
Applications
  • In-furrow applications assume 1 of granules,
    bait or seed unincorporated
  • Incorporated banded treatments assume 15
    material unincorporated
  • Broadcast treatment w/o incorporation assumes
    100 of granules, bait, seed unincorporated

19
Terrestrial Plant Exposure Analysis
  • Runoff based on solubility
  • Drift based on standard assumptions for ground
    (1) and aerial (5) applications
  • Scenario based on runoff from 1-ha to adjacent
    hectare for terrestrial plants
  • Scenario based on runoff from 10-ha to adjacent
    hectare for semi-aquatic plants

20
AgDrift Model Summary
  • Model based on field and wind tunnel studies to
    determine drift from different application
    methods
  • Simulates ground, orchard air blast and aerial
    applications
  • Predicts off-site terrestrial and aquatic
    concentrations into standard or user-defined
    waterbodies

21
Factors that affect drift
  • Droplet size distribution
  • Wind speed/direction
  • Release height
  • Application method
  • Environmental factors (temperature, humidity)

22
GENEEC Input Parameters
  • Application Rate
  • Koc
  • Application Method
  • of applications
  • Application Interval
  • Depth of Incorporation
  • Aerobic Aquatic Metabolism
  • Solubility
  • Aquatic Photolysis
  • Hydrolysis
  • Aerobic Soil Metabolism

23
GENEEC Aquatic Screening Model Assumptions
  • Applications occur on a 10 ha field that drains
    into a one hectare pond 2-m in depth
  • No buffer between the pond and treated field
  • Runoff is from a single large rainfall event over
    a 24-hour period
  • Soil type is considered a high runoff soil (MS
    silt loam)
  • Drift contribution
  • Based on contributions from AgDrift

24
Atrazine estimated environmental concentrations
(1 lb/ai)
25
PRZM/EXAMS Aquatic Exposure Model
  • Site specific model that determines pesticide
    load from agricultural applications
  • Each simulation is conducted using 36 years of
    rainfall data to determine variability in loading
  • Calculates edge of field pesticide loadings in
    surface water and sediment

26
PRZM/EXAMS Aquatic Exposure Model
  • Environmental fate model that simulates the
    process that occur in the water body
  • Steady state model that has a constant volume
  • Calculates peak maximum, 96-hour, 21-day and
    60-day average.
  • The 1 in 10 year maximum value is used in
    calculating risk quotient values

27
Use of Monitoring Data in Pesticide Risk
Assessment
  • Typically used for currently registered
    pesticides (reregistration, special review)
  • Sources
  • NAWQA USGS
  • open literature
  • registrants
  • Considerations for use
  • temporal and spatial sampling
  • storm events vs. base flow

28
Temporal variability of atrazine and chlorpyrifos
in water and sediment
29
Risk Presumption for Terrestrial Animals
Risk Presumption RQ LOC
Acute High Risk EEC/LC50 or LD50/ft2 0.5
Acute Restricted Use EEC/LC50 or LD50/ft2 0.2
Acute Endangered Species EEC/LC50 or LD50/ft2 0.1
Chronic RQ EEC/NOEC 1
30
LOC and Dose Response
31
Risk Presumption for Aquatic Animals
Risk Presumption RQ LOC
Acute High Risk EEC/LC50 or EC50 0.5
Acute Restricted Use EEC/LC50 or EC50 0.1
Acute Endangered Species EEC/LC50 or EC50 0.05
Chronic RQ EEC/NOEC 1
32
Risk Presumption for Terrestrial Plants
Risk Presumption RQ LOC
Terrestrial and semiaquatic plants Terrestrial and semiaquatic plants Terrestrial and semiaquatic plants
Acute high risk EEC/EC25 1
Acute ES EEC/NOEC 1
Aquatic plants Aquatic plants Aquatic plants
Acute high risk EEC/EC50 1
Acute ES EEC/NOEC 1
33
Exceedance of LOCs in the Screening Assessment
  • Request additional effects data
  • Request additional environmental fate data
  • Ex. aerobic aquatic metabolism, foliar
    dissipation
  • Use higher tier modeling/monitoring to refine
    exposure analysis and provide site specific
    exposure distribution

34
NAWQA Maximum Atrazine Concentrations for 40
Agricultural Sites
130
Mortality in Phytoplankton Macrophytes
Estimated to Occur at
120
32 µg/L
110
Invertebrate Populations Likely to be Reduced
at 22 µg/L
100
Mortality to Macrophytes Estimated to Occur at
18 µg/L
Reduction in Primary Production Likely to Occur
at 10 µg/L
90
Reduction in Primary Production Likely to Occur
at 2.62 µg/L and
80
Reductions in Primary Productivity Macrophytes
Estimated to
Occur at 2.3 µg/L
70
Measured Concenrations (ug/L)
60
50
40
30
20
10
0
0
10
20
30
40
50
60
Exceedence
Sites w/ Atrazine Concs gt Y
Source Reregistration Eligibility Decision
Environmental Fate and Effects Chapter. 2002.
35
EPA-OPP Risk Mitigation for Fish and Wildlife
  • Eliminate use on specific crop
  • Buffer zones
  • Time of application
  • Application method and rates
  • Number of applications
  • Spray drift best management practices

36
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37
OPP Endangered Species Protection Program (ESPP)
  • Goal is to implement mitigation measures to
    eliminate adverse impact to listed spp.
  • Currently ESPP defers to county bulletins
  • Program in place since 1989
  • Voluntary BMPs for listed species
  • Very few county bulletins complete
  • Service has not consulted on county bulletins
  • Service currently working with OPP to review ESPP

38
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