SFIREG PREM - aapco.files.wordpress.com · s Luo 5-2090 v 23. Title: SFIREG_PREM.pdf Created Date:...

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Pesticide Registration Evaluation Model (PREM) for Surface Water Protection in California Yuzhuo Luo, Ph.D. Research Scientist IV Surface Water Protection Program (SWPP) California Department of Pesticide Regulation (CDPR)

Transcript of SFIREG PREM - aapco.files.wordpress.com · s Luo 5-2090 v 23. Title: SFIREG_PREM.pdf Created Date:...

Page 1: SFIREG PREM - aapco.files.wordpress.com · s Luo 5-2090 v 23. Title: SFIREG_PREM.pdf Created Date: 9/17/2020 8:44:00 PM

Pesticide Registration Evaluation Model (PREM

) for Surface W

ater Protection in California

Yuzhuo Luo, Ph.D.Research Scientist IV

Surface Water Protection Program

(SWPP)

California Department of Pesticide Regulation (CDPR)

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Pesticide registration evaluation model (PREM

)

•The m

ain modeling tool for surface w

ater registration evaluation•

Historically, SW evaluations have been based on professional

judgment and experience

•A new

methodology has been developed and im

plemented in PREM

for m

ore consistent, transparent, and efficient evaluation•

The first version of PREM w

as released in 2012. It continues to evolve to better fit CA conditions w

ith increasing modeling capabilities

•The latest version: PREM

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Model developm

ent•

Modeling fram

ework w

ith 2-stage evaluation processes

Version 2 (2012)

•Evaluation of urban pesticide uses

Version 3 (2014)

•Evaluation of pesticide degradates

•Exposure potentials to m

arine/estuarine organisms

Version 5 (2017)

•SW

PP continues to improve the m

odel's capabilities and specificity to California conditions: receiving w

ater body; indoor uses and w

astewater, etc.

Under

development

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Scope and limitations

By pesticide use patterns:•

PREM is developed for production agriculture (both upland and

flooded), aquatic application, outdoor impervious surfaces

(residential, comm

ercial, right-of-way), adulticide

application, indoor uses (PO

TW scenario, under developm

ent)

•But N

OT for anti-fouling paint (AFP), inorganic com

pounds (silver, copper), and other biochem

ical and antimicrobial pesticides

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Overview

of PREM evaluation process

Model input data

PREMRegistration

recomm

endations

�Product labels

�Chem

istry data *�

Eco-toxdata *

* DPR-accepted data only

�Support

�Conditionally support

�N

ot support�

Watch-listing, flagging etc.

Evaluation variables

Decision-making

flowchart

Functional modules

Graphical user interface

(GU

I)

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Evaluation variables

VariablesInput param

etersApproaches

Soil-runoffpotential

Adsorption coefficient (KOC), Field

dissipation half-life, Water solubility

USDA W

IN-PST m

odel, modified by DPR

Aquatic persistence

Half-livesin w

ater and sediment

Criticalvalues of 30 and 100 days of half-lives

Aquatictoxicity

Acute aquatic toxicity(LC50 or EC50) for

sensitive species (fish & invertebrates)

USEPA classifications

Use pattern

Use pattern

High-risk usepatterns identified by DPR

Risk quotientChem

ical property, use pattern, labelrate, etc.

USEPA m

odels (PRZM, VVW

M, PFAM

)

Note: variables are presented as descriptive classification, e.g., high (H), low

(L), intermediate (M

)

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Pesticide use pattern

•Pesticide use patterns w

ith high-risk potentials to surface water:

•Aquatic and rice pesticides

•U

rban/residential uses•

Crops with gravity irrigation

•W

inter rain season application•

Pre-emergent application

•Crops w

ith top acreages in California

•O

ther use patterns: low-risk potentials

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Risk quotient (RQ)

•Evaluated for high-risk use patterns only

•EEC (estim

ated environmental concentration) = f(chem

ical property, use pattern, label rate)

•TOX

= the toxicity value (LC50 or EC50) for the most sensitive species

•RQ

is compared to the LO

C (level of concern)•

High RQ: >0.5

•Interm

ediate RQ: 0.1-0.5

TOX

EECRQ

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EEC modeling

•Generally, based on the FIFRA

(Federal Insecticide, Fungicide, and Rodenticide Act) Tier-2 m

odeling framew

ork

Ref: EPA-HQ-O

PP-2015-0424-0036

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EEC modeling

•Generally, based on the FIFRA

(Federal Insecticide, Fungicide, and Rodenticide Act) Tier-2 m

odeling framew

ork•

For applications to an aquatic site (e.g., rice pesticide), modeling for

the treated water body only

USEPA/O

PP 734S16002

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EEC modeling: tools

•Sim

ulation engines (USEPA m

odels)•

Landscape simulation: PRZM

(Pesticide Root-Zone Model)

•In-w

ater simulation: VVW

M (Varying Volum

e Water M

odel), and PFAM

(Pesticide in Flooded Application Model)

•M

odeling scenarios•

USEPA scenarios for agricultural uses

•DPR scenario for urban outdoor uses

•DPR scenario for degradate

evaluation•

USEPA/DPR scenario for rice pesticides

•DPR scenario for dow

n-the-drain pesticides (under development)

•…

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Decision-making flow

chart

Note: L=low, M

=intermediate, H=high, VH=very high

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PREM Results

•Registration recom

mendations (for a product)

•Support registration

•Support conditional registration and request analytical m

ethods•

Do not support registration

•W

atch listing (for an active ingredient)•

Conditional registration: consider the A.I. as a candidate for surface water

monitoring, and w

atchits actual use am

ount and post-use risk•

Low-risk use pattern for the currently evaluated product: Flag the A.I. and

watch

it for new products and label am

endments

13

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Graphical user interface

Chemical-specific data

Product-specific data

Specify the parent compound here

Specify the degradates to be modeled here

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Input data

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High-risk use patterns

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Additional data by pesticide use pattern•

Urban use as an exam

ple

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PREM O

utputs

18From

: PREM5 technical report

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PREM applications

•Registration evaluations for 70+ pesticide products (as of Dec 2019)•

Risk assessment for fipronil(urban) and pyrethroids (urban and ag)

•Com

parison with U

SEPA/OPP residential settings in the ecological risk

assessment (ERA) for pyrethroids (EPA-HQ

-OPP-2010-0384-0045)

•Incorporation w

ith Best Managem

ent Practice (BMP) m

odeling•

Vegetative filter strip (VFS, completed)

•Vegetated drainage ditch (VDD, under developm

ent)

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Summ

ary

•Surface w

ater evaluations with PREM

•Consistently &

reliably identify adverse risks of products to water quality &

aquatic life

•Avoid involved, costly &

protracted post-registration efforts to develop &

implem

ent mitigation or regulations

•Successful resolution betw

een DPR & registrants (data needs, label changes)

reinforces the usefulness & im

portance of SW registration evaluations &

PREM

•PREM

continually evolving for evermore realistic &

CA-centric predictions•

Eventually anyone could run model

Page 21: SFIREG PREM - aapco.files.wordpress.com · s Luo 5-2090 v 23. Title: SFIREG_PREM.pdf Created Date: 9/17/2020 8:44:00 PM

PREM tim

eline

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PREM w

ebsite

ww

w.cdpr.ca.gov/docs/em

on/surfwtr/sw

_models.htm

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Thanks

Yuzhou Luo(916)445-2090Yuzhou.Luo@

cdpr.ca.gov

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