*3 Before HARRY PREGERSON IKUTA, Judges, SANDRA S. Circuit MOSKOWITZ,* BARRY T. District Judge. PREGERSON;
Opinion Judge Partial Concurrence and Partial Dissent by Judge IKUTA.
PREGERSON, Judge: Circuit environmental Petitioners two groups challenging the Environmental (“EPA”) Agency’s Protection establish- pesticides ment of tolerances for seven mostly vegetable crops. used on fruit and grant petition deny it in part, We part, and remand to the EPA. BACKGROUND Olsen, Colangelo and Erik D. Na- Aaron Council, Washing- Resource Defense tional I. D.C.; Davis, ton, Shelley Farm-worker regulates two pesticides The under D.C.; Fund, Washington, Patti Justice Insecticide, Fungi- statutes: the Federal Seattle, WA, Goldman, Earthjustice, cide, (“FIFRA”), 7 and Rodenticide Act petitioners-appellants Northwest Coalition Food, 136-136y, § U.S.C. and the Federal for Aternatives to Pesticides and National (“FDCA”), 21 Drug, and Cosmetic Act Resources Defense Council. § U.S.C. 346a. Fleuchaus, Environmental Jonathan J. FIFRA, in the Under sold D.C.; Agency, Washington, Protection Sue registered by the United States must be General, Woodridge, Attorney Ellen John may § EPA. 7 The EPA U.S.C. 136a. Cruden, Deputy Attorney Assistant C. register pesticide pesticide unless the Hanson, General, E. and Kent Environ- function perform will intended without Division, and Natural Resources ment causing “any unreasonable adverse effects Justice, Department States United environment.” U.S.C. D.C., Washington, respondent-appellee 136a(e)(5)(C). § Agency. Environmental Protection Weinstein, The authorizes the EPA to set FDCA Kenneth W. Claudia M. O’Brien, Sturkie, in food. pesticide Latham “tolerances” for residues and Cassandra * Moskowitz, Barry sitting by designation. The T. District Honorable California, Judge for the Southern District of 346a(b). II. § “A tolerance is the U.S.C. pesticide maximum allowable amount of Congress amended FDCA commodity.” may remain in or on a by enacting Quality the Food Protection (9th EPA, Nader v. 104-170, (“FQPA”), Pub.L. No. Act Cir.1988). “establish key provisions Stat. 1489. One leave in effect a tolerance for FQPA requires give spe- the EPA to only in or on a food if chemical residue posed cial consideration to risks to infants determines that the tolerance is [the EPA] establishing pesticide and children when 346a(b)(2)(A)(i). safe.” FQPA Specifically, tolerances. directs to mean that “there term “safe” is defined *4 EPA “an additional1 tenfold to use certainty a that no harm will is reasonable margin safety ... to take into account aggregate exposure result from to the potential pre-and post-natal toxicity and residue, all pesticide including chemical respect completeness data with anticipated dietary exposures and all other toxicity and chil- exposure and to infants exposures for which there is reliable infor- 346a(b)(2)(A)(ii). 346a(b)(2)(C). § § mation.” 21 U.S.C. 21 dren.” U.S.C. This Any (or “10x”) tolerance that is not “safe” must be safety tenfold child factor is 21 modified or revoked. U.S.C. all presumptively tolerances. applied 346a(b)(2)(A)(i). § decisions, Thus, making in tolerance EPA must assume risk to children Tolerances are established rulemak- 346a(d). particular pesticide § from the use of a ing. 21 Pesticide man- U.S.C. rulemaking process ufacturers initiate the greater food is ten times than for adults. by petitioning the EPA to a tolerance. set may margin EPA a “use different 346a(d)(l). § pub- 21 U.S.C. The EPA safety for the chemical residue in petitions lishes notices of these the Fed- data, only if, on the basis reliable such 346a(d)(3). § Register. eral 21 U.S.C. margin will be safe for infants and chil- reviewing petition any After a com- added). (emphasis dren.” Id. it, EPA ments received on issue: Unfortunately, FQPA does not de- (1) (2) tolerance, establishing a final rule a dispute fine “reliable data.” The before us (3) rule, proposed denying a an order turns on the definition of this term. 346a(d)(4). petition. § 21 U.S.C. 2002, April Between 2001 and December EPA Once the takes final action on a published regulations seven es- any days petition, party sixty affected has tablishing pesticides tolerances for the ace- objections EPA to file with the and to seek fenhexamid, tamiprid, halosulfuron-methyl, evidentiary objections. hearing on those isoxadifen-ethyl, mepiquat, pymetrozine, § 346a(g)(2). U.S.C. The EPA’s final foods, zetacypermethrin many used on objections in response order to those fruits, nuts, including vegetables, subject judicial cereal review. 346a(h)(l). milk, § grains, eggs.2 regulation Each margin, safety range popula- 1. This is "additional” to two of sensitivities in the human tion). long factors that the has used to account for other a fac- uncertainties: tenfold rulings, 2. For the EPA’s individual tolerance (to interspecies tor for differences account for Tolerance, Acetamiprid; see Pesticide 67 Fed. possibility people suscepti- are more 14,649 27, Fenhexamid; (Mar. 2002); Reg. laboratory experi- ble than in animals studied Tolerance, 19,114 Fed.Reg. (Apr. Pesticide ments), tenfold factor for intra- 18, 2002); Halosulfuron-methyl; Pesticide (to species differences account for the wide Tolerance, 66,333 (Dec. Fed.Reg. objections response in to an indus- NRDC filed administrative promulgated was try petition to establish tolerances. publish- the tolerances in 2002. denying objec- ed its Final Order those presumptive apply The EPA did not August days, tions on Within any lOx child factor to of these petition filed a NRDC review The EPA reduced the pesticides. seven Circuit, petition Second and NCAP filed a lOx child factor to 3x for four of the fenhexamid, review this court. The Judicial Pan- (acetamiprid, isoxa- pesticides difen-ethyl, pymetrozine). Litigation For the re- el on Multidistrict transferred (halosulfuron, me- maining three petition for NRDC’s this court piquat, zeta-cypermethrin), pursuant to 28 U.S.C. and NRDC at all. apply did not joint appeal. and NCAP filed briefs on Natural Resources Defense STANDARD OF REVIEW (“NRDC”) Council, objections Inc. filed each of the tolerances based on the EPA’s does not The FDCA establish stan- to reduce or remove the child decision reviewing pesticide dard for tolerances *5 safety argued factor.3 NRDC public that are without a established evi- allowing EPA not have “reliable data” did 21 dentiary hearing. See U.S.C. it to deviate from the child 346a(h)(2). § In the absence of such a 10, 2005, EPA August On issued its standard, governed by our review is sec- objections. final rejecting order NRDC’s tion 706 of the Administrative Procedure Denying Objections to Issu- See Order (“APA”). 706; § Act 5 City See U.S.C. Tolerances, 46,706 Fed.Reg. 70 ances of O’Neill, Sausalito v. 1205- 2005) (hereinafter (Aug. “Final Or- (9th Cir.2004). 06 der”). upheld The Final the 3x Order APA, Under the we must set aside acetamiprid, factor for fenhex- agency’s “arbitrary, an decision if it is amid, isoxadifenethyl, pymetrozine, discretion, capricious, an abuse of or other (i.e., and a lx child no wise not in accordance with law.” 5 U.S.C. factor) halosulfuron, mepiquat, and ze- 706(2)(A). agency § An decision would 46,711-13, 46,736. taeypermethrin. Id. at if normally arbitrary capricious be NRDC and the Northwest Coalition for has relied on factors which agency “the (“NCAP”) Alternatives to Pesticides each consider, Congress has not intended it to petitioned for review of the Final Order. entirely important failed to consider an JURISDICTION aspect problem, explana of the offered an decision that runs counter to tion for its FDCA, jurisdiction have under the We or is so agency, the evidence before the “any provides person which who will that it not implausible could be ascribed adversely be affected” an order product a difference in view or the denying objections may tolerance file a agency expertise.” Ass’n v. State petition Appeals for review in the Court of Mfrs’ Co., 29, 43, Mut. Auto. Ins. 463 U.S. 21 Farm days within 60 of the EPA’s order. (1983). 346a(h)(l). § 77 L.Ed.2d 103 S.Ct. 443 Tolerance, 6,422 Tolerance, ers; 2001); Fed.Reg. Isoxadifenethyl; Pesticide Pesticide 12,875 (Mar. 2002); 15, 2002). Fed.Reg. Mepi- (Feb. Tolerance, 3,113 quat; Fed.Reg. Pesticide (Jan. 23, 2002); Pymetrozine; Pesticide Tol- request evidentiary hear- 3. NRDC did not erance, 66,786 27, 2001); (Dec. Fed.Reg. ing objections. on its Zeta-cypermethrin and R-isonom- its Inactive FQPA, required under the As scope “The of review standard is nar will ‘arbitrary capricious’ whether infants and children monitors a court is not to substitute row and in unsafe levels of exposed be agency.” Id. judgment for that of However, the EPA lacks drinking water. “Nevertheless, agency must examine data for drinking exposure water sufficient and articulate a satisfac the relevant data including pesticides, several the ones including its action tory explanation for Therefore, issue this case. the facts ‘rational connection between computer modeling to determine used ” (cita made.’ Id. found and the choice pes- drinking exposure water seven omitted). explana “In reviewing tion modeling results re- Because the ticides. tion, must consider whether court] [the pesticide expo- little-to-no risk of vealed decision was based on consideration water, drinking reduced sure and whether there has the relevant factors safety factor for each or removed the child (cita judgment.” Id. been a clear error pesticide tolerances. omitted). tion argue that because the EPA Petitioners “uphold a decision Although we will modeling sampling instead of actual used clarity agency’s than if the of less ideal drinking data to determine discerned,” reasonably path be the EPA does not have pesticides, to these “may supply not a reasoned basis for justifying its use of a lower “reliable data” agency’s action that the itself has margin than lOx for the (citations omitted). given.” Id. 346a(b)(2)(C). tolerances. See U.S.C. *6 short, argue modeling In Petitioners ANALYSIS can never constitute reliable data results challenge Petitioners seven tolerances FQPA. meaning within the fenhexamid, (acetamiprid, halosulfuron- methyl, isoxadifen-ethyl, mepiquat, pyme- disagree. have We Petitioners trozine, zeta-cypermethrin) based presented modeling no evidence that does gather drinking the EPA’s failure to water nothing yield not reliable data. There is exposure analysis. Peti- part data as its inherently unreliable about the use of mod challenge tioners also three tolerances See, e.g., els in scientific assessments. (acetamiprid, mepiquat, pymetrozine) Small Lead Phase-Down Task Refiner toxicity the absence of certain based on (D.C.Cir. Force v. EPA studies, and based on the EPA’s failure to 1983) (“[Administrative agencies have un explain why it had reliable data in the models.”). power predictive doubted to use toxicity absence of those studies.4 We ad- Moreover, difficulty in because of the sam challenges in turn. dress these pling supply, the entire nation’s water
I. necessary modeling is to determine wheth drinking er water has been contaminated FQPA EPA directs the to use an Topography, geology, and pesticides. margin additional tenfold to take hydrology greatly differ across the nation completeness into account of data with re- cases, constantly change. many spect pesticide “exposure to infants and 346a(b)(2)(C) (em- accurately computer modeling can more children.” 21 added). phasis incorporate provide these elements and however, knowledge, subsequent agency initially challenged 4. Petitioners also the tol- halosulfuronmethyl zeta-cy- erances for challenges moot. actions have rendered those permethrin grounds. They on these now ac- reliable data than actual water pesticides more sam- from likely to result in pling data can provide.5 exposures. such accomplish To this goal, the models are based on data from
Therefore, unwilling adopt we are studies at highly sites that are vulnera- narrow construction of “reliable data” that pesticides ble runoff of to surface Although FQPA Petitioners advance. data,” water leaching does not define “reliable we are ground modeling satisfy confident that results can water. If a fails this conserva- statutory requirement. (health-protective) screen, tive EPA would investigate whether the model is Furthermore, case, in this significantly overstating the residue lev- provided specific, explanation detailed els that actually occur. drinking water models do yield reliable developed data. The Final Order has models for esti- states: mating exposure in both surface water ground Lack comprehensive drinking wa- water. EPA uses two- (DW) monitoring
ter data. NRDC con- tiered approach to modeling pesticide that, tends because used a model exposure in water. In the initial surface for calculating drinking exposure, tier, EPA FQPA uses the Index Reser- have, EPA does not aas definitional (FIRST) voir Screening Tool model. matter, choosing “reliable data” for replaces FIRST the Generic Estimated factor different than the 10X default val- (GEN- Environmental Concentrations ue. Similar comments were made dur- EEC) model that was used as the first ing development of EPA’s Children’s tier screen EPA from 1995-1999. If Safety Policy. This issue was addressed suggests first tier model pesti- length response to the imida- cide levels water unacceptably be objections. eloprid That in- response is high, a more refined model is used as a corporated herein and is summarized be- second tier assessment. The second tier low. actually model is a combination of the Although availability drinking models, Pesticide Root Zone Model *7 monitoring water data has increased (PRZM) Exposure Analysis and the dramatically in years, the last several (EXAMS). System Model For estimat- EPA still it necessary rely finds for ing pesticide in groundwater, residues most pesticides upon exposure various EPA uses the Screening Concentration models to exposure estimate levels in (SCI-GROW) In Ground Water model. drinking water. These models are Currently, EPA has no second tier based on generic data regarding fate groundwater model. transport and in pesticides the envi- Whether EPA pesticide expo- assesses ronment, they operate by combining drinking sure in water through moni- generic data with pesticide-specific toring modeling, data or EPA uses the data on chemical properties to estimate higher the two values exposure. primarily EPA has used its from surface ground drinking assessing water in overall water models to “screen” those exposure pose unacceptable pesticide. to the In most exposures cases, risks due to in drinking water pesticide residues in wa- surface Panel, Assessment, (Dec. Advisory 1997), See FIFRA etary Scientific A Set Risk 4-7 avail- Being of Scientific Issues Considered http://epa.gov/scipoly/sap/meetings/ able at Agency Estimating in Connection with Drink- 1997/december/finaldec.pdf. ing Exposure Component Water as a of Di- II. higher in significantly are than ter ground water. challenge to the to NRDC’s addition data, exposure Petitioners completeness of Order, EPA ana- Imidacloprid
In the
wheth-
arguments regarding
also raise two
models extensive-
lyzed each
its water
toxicity
supported
data
a reduc-
er reliable
design
Based on the results of
char-
ly.
tion in
factor.
models,
peer
outside
acteristics of the
models,
validation of
A.
models,
comparison
between the
challenges
first
the EPA’s
NRDC
water
predictions
models’
and extensive
failure
for the
of certain
to wait
results
data,
monitoring
EPA concluded that
developmental
neurotoxicity
studies
on reliable data
the models are based
studies”)
(“DNT
establishing
before
toler
that are un-
produce
and will
estimates
py
acetamiprid, mepiquat,
ances for
likely
exposure
pes-
underestimate
specifically required
metrozine. The EPA
drinking
water.
ticides
pesticides to con
registrants
of these
Accordingly, EPA reaffirms its earlier
However,
EPA did
duct DNT studies.
drinking water mod-
conclusion that its
studies
not wait for the results
the DNT
finding
provide
reliable basis
els
making its
determina
before
tolerance
exposure
residues
tions.
are not
underestimated.
contend that DNT studies
Petitioners
(internal
46,726-29
Final Order
citations
ef-
assessing pesticide
are essential for
added).
omitted)
Thus,
(emphasis
explain
fects.
that DNT stud-
Petitioners
length
reliability
EPA addressed at
ies are
best available studies for ex-
explained
models.
that the
amining neurological
in children
effects
yield
data because the
models
conservative
sensitive
because DNT studies
more
incorporate
higher
of the two
models
studies,
that are
than other
address areas
ground
from
water in
values
surface
studies,
not covered
other
and some-
assessing
risk of
overall
developmental
times
harm that
reveal
pesticides.
Petitioners have not estab-
require
significant enough to
more strin-
explanation regard-
lished
EPA’s
gent
argue that
regulation. Petitioners
reliability
faulty
models is
ing the
of its
arbitrarily
capriciously
the EPA acted
suspect.
by requesting
failing
DNT studies but
wait
the results of those studies before
Accordingly,
we conclude
the com-
removing the child
modeling
by the EPA
puter
used
to calcu-
*8
safety
however,
drinking
late the
water was nei-
position,
Petitioners’
is incon
contrary
arbitrary
Supreme
ther
to law nor
and
decision
sistent with the
Court’s
capricious.6
aspect
We affirm this
of the
in
Ass’n
Home Builders v.
National
— U.S. -,
Wildlife,
Final Order.
Defenders of
course,
conclusion,
6. Our
is not
ensure that the first result was accurate. The
meant
however,
test,
suggest that
are
the EPA’s models
flawless.
EPA
run a
if
does not
second
Petitioners have raised some concerns about
expo-
acceptable
the initial test results reveal
may
exposure
the EPA's
models that
Although
required
we
de-
sure
are
levels.
give
scrutiny.
further
exam-
warrant
To
one
expertise
fer to
in this
the EPA’s technical
ple,
performs
the EPA
first
model-based
area,
EPA,
see,
Ctr.,
e.g., Envtl
Inc. v.
Def.
exposure
using
water
ria;
test
conservative crite-
832,
(9th Cir.2003),
F.3d
we
that the
note
unacceptable
the
reveal
if
test results
methodology.
EPA
to revisit
wish
levels,
exposure
EPA runs a second test to
the
(2007).
B.
Home
also
that
disputes
NRDC
the
“arbitrary
capri-
and
order
EPA as
EPA’s decision
deviate from the lOx
EPA
relied on
the
had
“le-
cious” because
imposed
presumptive
factor
contradictory
before
gally
positions”
arriv- Congress
supported by reliable
was
data
decision.
ing at
its final administrative
establishing,
certainty,
with reasonable
Court,
Supreme
2529. The
127 S.Ct. at
margin
that the
for aceta
lower
however,
opinion.
our
The Court
reversed
miprid,
pymetrozine
and
would
mepiquat,
mere fact that
held that
the
not harm infants and children.
“internally
adopted
inconsis-
might have
(C).
346a(b)(2)(A),
though
Even
throughout
the decision-
positions
tent”
EPA
necessarily required
was not
to wait
making process did not render
EPA’s
studies,
the results
the DNT
arbitrary
capricious.
final decision
and
decision to reduce the lOx child
explained
dren’s
toxicological
the
information to demonstrate
enough
to 3X because
vide
reduced
sen-
greater
no evidence of
data showed
connection
the factors
rational
between
was no
the
and there
sitivity
young
to
EPA examined and the conclu-
that
in the devel-
of abnormalities
Farm,
evidence
463
it reached. See State
sions
system.
the fetal nervous
opment
43,
are there-
at
tions, challenged the NRDC basis for the PART, GRANTED IN DENIED IN safety reduced inadequate. levels as PART, AND REMANDED. particular, that, argued NRDC absent the studies, DNT the EPA had no reliable IKUTA, Circuit Judge, concurring safety data to reduce the lOx child factor. part dissenting in part: objection NRDC’s challenge was direct I agree to the lower child with by majority’s levels set conclusion justify EPA. To that “the computer its decision to set a 3x or modeling used lx EPA to factor without calculate the safety DNT of drinking studies, the EPA needed to was neither explain why contrary to law nor arbitrary possession the data and capricious.” Maj. was reliable and Op. at 1050; supported such see also reductions. As noted The Lands Council v. McNair, above, (9th the EPA explained why the 537 F.3d absence 989-94 Cir. 2008) (en banc). of the DNT necessarily studies does not I agree also with the majority’s mean that holding there is a lack of reliable data National Ass’n of justifying a Home downward deviation from Builders v. Wildlife, Defenders of — U.S. -, However, lOx child 2529-30, 127 S.Ct. (2007), explain why, EPA failed to L.Ed.2d 467 in the petitioners’ case of forecloses issue, argument the three “that the EPA arbitrarily available acted justified capriciously information specific safety establishing pesti re- cide ductions. Because the tolerances for challenged acetamiprid, mepiquat, NRDC pymetrozine provide that explanation, receiving before ... DNT Maj. EPA’s failure to do so studies.” properly Op. is before at 1051. us for review. however, I disagree, majority’s with the conclusion that regulations the tolerance
CONCLUSION acetamiprid, for mepiquat, and pymetro- Because the EPA failed to adequately zine must be remanded to be- explain the basis for its deviations from cause “it entirely is unclear the lOx child factor for acetamiprid, chose factors of 3x pymetrozine for mepiquat, pymetrozine, grant we and acetamiprid, lx mepiquat,” petitions for part review in and remand to and therefore “the Final Order [did] the EPA for further proceedings provide enough consis- information to demon- tent opinion. issues, with this allOn other strate a rational connection between the deny we petitions for review. factors the EPA examined and the eonclu- quately explained. (internal The mere fact that an quotation citations and marks omit operating expertise is in a field ted). of its Riverkeeper, See also Inc. v. United customary does not excuse us from our Agency, States Environmental Protection And, responsibilities. where the (2d Cir.2007) ("In F.3d 103-04 a technical agency's reasoning, although complex, is sort, area judges of this it is difficult for rational, clear, complete, we must af- parties propriety interested to determine the Contrarily, agency's firm. where the rea- Agency's justification action without a irrational, unclear, soning sup- or not supported by clearly for the action identified ported by purports interpret, the data it import substantial evidence whose is ex disapprove agency’s must action. plained.”). Peck, Safety Center Auto v. (D.C.Cir. 1985) J., (Wright, dissenting) *11 1054 A The Maj. at 1052. Op. it reached.”
sions argument raise this failed to petitioners tolerance majority, the noted the As to the prior objections to their have substan- appeal in this rules at issue De Order Final Rule. See issuance the devel- While tially similar histories.2 Toler Objections to Issuances nying inwas policy factor of its opment 2005) 46,706 (Aug. ances, Fed.Reg. 70 pesticide peti- the EPA received process, Rule], therefore the [hereinafter, Final of tolerances issuance requesting tions the explain no given opportunity was EPA lx pesticides 3x and three adopting the for the rationale for under the FFDCA its may FFDCA, safety factors. Because the required in the As issue. EPA, the raised before objections only the and other the data EPA reviewed scientific 346a(g)-(h); § 40 C.F.R. 21 U.S.C. see information, completeness their evaluated 180.30(b), 178.25(a)(2), is not the issue §§ “the rela- reliability, considered petition if the Even before us. properly of such studies tionship of the results objection, there is no raised this ers had risk.” human infor provided the EPA could have doubt 346a(b)(2)(D)(iii); see, e.g., Pymetrozine; a rational sufficient mation demonstrate 66,786, Tolerance, Fed.Reg. Pesticide safety factors. selecting these for basis 2001). (Dec. 27, EPA 66,787 deter- Indeed, the record establishes safety factor was not that the child mined expertise to select upon drew 3x, for necessary, or be reduced could principles on uncertainty factors based analysis based on its pesticides each of the communi in the scientific established well given exposure levels for potential majority’s no basis for ty. There is extent to which pesticide, the not path is agency’s conclusion effects, and the development, affected fetal See, case. reasonably discernable in multi- infants as observed any, if Ass’n v. State Motor Vehicle e.g., Mfrs. mammals. In each generational studies Co., 29, 43, Ins. 463 U.S. Mut. Auto. Farm case, expla- a reasoned provided (1983). 77 L.Ed.2d 103 S.Ct. eliminating reducing or nation for IIB the I from Part Accordingly, dissent factor.3 majority opinion.1 Tolerance, 27, 2002); Mepiquat; Pesticide majori- 6 of the 1. I also dissent from footnote 3,113 (Jan. 2002); Pymetrozine; Fed.Reg. majority’s suggestion that the ty opinion. 66,786 (Dec. Tolerance, Fed.Reg. Pesticide methodology” revisit[its] wish to "EPA 27, 2001). exposure regarding its "model-based teaching directly with the conflicts testfs]” establishing tolerance for 3.In its order Lands panel in Council. en banc Lands our explained: acetamiprid, proper not a emphasized it "is Council appellate to "act as a a federal court” for role to 3x could be reduced [T]he [agency] of scientists that instructs panel toxicology acetamiprid da- because hypotheses,” "chooses to validate its how quantitative complete; there is no tabase is studies,” requires among scientific suscep- of increased qualitative evidence every possible "explain scientific following rat tibility in útero majority uncertainty.” 537 at 988. The F.3d fetuses; (food dietary rabbit by doing that which Lands in this case errs water) exposure assess- and residential expressly forbids. Council potential ments will underestimate infants, children, exposures and/or childbearing age; and the re- are acetami- at issue women of 2. The three neurotoxicity developmental pymetrozine. quirement For the of a mepiquat, and prid, reflecting Acetamiprid; study on criteria rulings, is not based see tolerance individual 14,649 Tolerance, (Mar. developing fetuses Fed.Reg. special concern for Pesticide *12 objections study pesticide, In NRDC filed to for each and the because the for each EPA drinking exposure the final rules relied on water to reduce than based on the EPA’s decision the models rather on pesticide-specific or lx. safety drinking monitoring lOx to 3x The data.4 Notably, on the the objections object NRDC’s were based the- NRDC did not the ground on that ory justify that did not have “reliable the EPA failed to its choice of a safety data” which allow it to reduce the factor of 3x or lx would relative to some factor, other safety child factor because the had such or 5x as “4x or 8x a or yet Maj. Op. received the results of DNT 9x.” at 1052.5 The EPA generally establishing young pymetro- or which are used for re- for tolerance zine, quiring study a DNT and a Tolerance, the EPA stated: Acetamiprid; complete Pesticide 67 Fed. toxicity There is a database for 14,655. Reg. at pymetrozine exposure and data are com- The EPA removed additional safe- plete or are estimated on data based lx) (reducing ty mepiquat it to factor for reasonably potential expo- accounts for already itself of because it had satisfied sures. EPA determined that 10X mepiquat "salt” that it of another of protect factor to infants and children could was identical in its envi- determined terms of FQPA be reduced to 3. The factor is re- toxicology. Mepi- ronmental distribution assessing potential duced after for addi- Tolerance, quat; Fed.Reg. Pesticide sensitivity of tional infants and children to 3,115-16. explained: It pymetrozine following residues of published Agency The a assessment risk for developmental toxicity studies: studies in 12, 2000, mepiquat January chloride on two-generation repro- rabbit and rat and use on as well as all discusses cotton study duction in the rat. There was no registered mepiquat other uses of chloride. susceptibility evidence of increased in these analysis exposure In that risk for estimates FQPA safety studies. The factor was not Agen- mepiquat chloride were below reduced due to one to the need for devel- cy’s Agency level concern. The has re- of opmental neurotoxicity study. mepiquat study viewed a dissociation for Tolerance, Pymetrozine; Pesticide 66 Fed. pentaborate mepi- that demonstrates that 66,791. Reg. at quat pentaborate in an dissociates identical Council, Objec- 4. Natural Resources Defense physical mepiquat manner to chloride in Therefore, tions to the Establishment performed Tolerances analysis water. of for Pesticide Chemical Residues: mepiquat for salt,” chloride the "chloride or Halosulfuron- (filed methyl Pymetrozine mepiquat "penta- pertains also to this Tolerances rate, 25, 2002); borate use use Feb. salt” because the maxi- Natural Resources Defense Council, pertinent Objections mum seasonal use rate and other to the Establishment mepiquat use remain the for factors same Tolerances Pesticide Chemical Residues: for chloride the "chloride ... or salt.” Imidacloprid, Mepiquat, Bifenazate, Zetacy- Margins incorporated into permetkrin, and Tolerances Diflubenzuron directly EPA risk assessments either (filed 19, 2002); May Natural De- Resources (MOE) through margin aof use Council, Objections fense Establish- (safe- analysis through using uncertainty ment Tolerances Pesticide Chemical for ty) calculating a dose level that factors in Isoxadifen-ethyl, Acetamiprid, Residues: Pro- poses appreciable no risk to humans. Furilazole, Fenhexamid, piconazole, Agency has determined that (filed 2002). May Tolerances Fluazinam FQPA safety mepiquat factor for is IX. See objected 5. The three NRDC also to the toler- Agency’s mepiquat risk assessment for grounds, ances a number of other includ- on January chloride dated for details. ing the ad- failure consider farm children pentaborate mepiquat are that facts equately, worker risk failure consider mepiquat mepi- another “salt” adequately, inadequate aggregate an risk as- quat pentaborate mepiquat disassociates to sessment, improper on a toxicology reliance "lowest the basic data base therefore (LOAEL) mepiquat pertains mepiquat observed adverse effect level” rath- chloride pentaborate. er than a "no observed adverse effect level” (NOAEL), assumption "percentile” Id. a residue agency to an give notice quirement is to Final objections NRDC’s rejected issues, can so the errors or specific explanation Rule, detailed provided experience bear Agency’s “bring had reli- that it concluding of its basis *13 EPA, 859 Nader v. question,” a contested absence of notwithstanding the data able (9th Cir.1988), either and F.2d expo- the use of and DNT studies certain a reasoned provide the error or correct reliable data models, why such and sure explanation. it that conclusion the EPA’s supported child the safely reduce could EPA’s deci- objected to the The NRDC 46,706. The Fed.Reg. generally re- See was not factor that a lOx sion safety fac- child 3x upheld Rule the Final toler- three each of the quired for and pymetrozine, and acetamiprid objection for on the ances, tor based mepiquat. for factor data the lx child lacked reliable the EPA ground that 46,736. 46,711-13, a DNT at to obtain Id. it had failed because drinking water study and had relied
B
rests its
majority
models. The
required
remand is
concluding that
for acetami-
that
the tolerances
decision
why it
explain
the EPA failed
must be
pymetrozine
mepiquat,
because
prid,
acetami-
uncertainty factor for
a different
EPA on
chose a 3x
to the
remanded
uncertainty
failed to
and a lx
namely that
pymetrozine
ground,
prid
uncertainty
“4x
or
fac-
or 5x
it chose a 3x
mepiquat instead
explain
factor for
and a
1052, majority
pymetrozine
9x,”
acetamiprid
the
tor
Maj. Op. at
or
8x
instead
uncertainty
mepiquat
lx
factor
properly
before
argument
an
reaching
9x,” Maj. Op. at 1052.
or
“4x or 5x or 8x
to the
applicable
regulations
The
us.
object to the
did not
Because the NRDC
of administra-
exhaustion
require
FFDCA
that
the
ground
the
180.30(b) EPA’s decision on
§
40 C.F.R.
tive remedies. See
explanation
a clear
give
EPA had failed to
is not avail-
“judicial
that
(providing
“4x
in lieu of
or lx
of the 3x
adversely
party
affected
an
unless
able
id.,
9x,”
identified
the issue
or 5x or 8x or
objection procedures,
the[]
exhausts
exhausted, and we
majority
by the
is not
there-
procedures preliminary
any petition
reviewing it.
from
precluded
to”).
objection
the
In order to exhaust
FFDCA, peti-
by the
provided
procedure
justify
ad-
majority attempts
The
to the
objections
must raise their
tioners
did not
the NRDC
dressing issues that
See
specificity.
with
adminis-
by turning
raise to the
objections to an
(requiring
346a(g)(2)(A)
§
on its head.
requirement
trative exhaustion
establishing a tolerance to
above,
regulations re-
EPA order
As noted
under
provisions
reme-
particularity
“with
administrative
specify
quiring exhaustion of
objectiona- dies,
proposed regula-
order deemed
regulation
objecting
or
parties
178.25(a)(2) (“To
burden,
be
and must
ble”); 40 C.F.R.
tions bear the initial
Administrator,
objec-
objections
agen-
to the
by
specific
considered
raise their
are waived and
particularity
cy; any issues not raised
Specify
tion must:
with
order,
agency or
considered
regulation,
need not be
provision(s) of
appeal.
40 C.F.R.
to,
objee- by
the court on
objected
basis for
denial
Here,
178.25(a)(2),
majori-
pur-
§§
The
180.30.
tion(s),
sought.”).
the relief
EPA to identi-
to the
ty
re-
shifts
burden
exhaustion
of this administrative
pose
to us on
these issues
did not raise
inadequately protected infants and chil-
NRDC
Rule,
4;
supra
Final
dren,
appeal. See
Note
improper assessment of chron-
and an
46,717-36.
46,713-14,
Fed.Reg. at
among
dietary exposure,
others.
ic
raise,
fy,
and resolve additional
ly”
issues
to the agency.). Nor would it be rea-
all,
petitioners
failed
raise at
let alone
sonable or consistent with the purpose of
requisite “particularity.”
frame with the
the administrative
requirement
exhaustion
178.25(a)(2).
§Id.
Here,
to do so.
responded
to the
NRDC’s specific objection by carefully ex-
majority
first
*14
specific objection
recharacterizes
short,
as
we have no authority to re-
being
general
a
“challenge
more
to the
verse an agency decision based on an ob-
lower child
levels
jection
set
the EPA.”
that was not raised.
Supreme
Maj. Op. at
generaliza
1053.6 From this
Court
long
has
warned us not to invent
tion,
majority leaps
to the conclusion new issues
part
as
of our
objec-
review of
specific
that the
objection places
NRDC’s
tions raised to an administrative agency.
a burden on the EPA to “explain why the
“A reviewing
usurps
court
agency’s
possession”
data in its
supported its deci
function when it sets aside the administra-
sion to set a 3x or lx
factor for
tive determination upon
ground
a
not
opposed
issue “as
4x
to
or
presented
theretofore
and deprives the
5x
Maj.
1052,
or 8x or 9x.”
Op. at
agency]
[administrative
an opportunity
of
There is no basis in our case law for taking
matter,
to consider the
make
ruling,
such a leap
placing
or
such a burden on and state the reasons for its action.” Un-
the EPA. We have never required an
employment Comp. Com’n v. Aragon, 329
interpret
a specific objection
143, 155,
245,
as U.S.
67 S.Ct.
C for us to conclude basis adequate us to address proper were it Even uncertainty lx a 3x EPA’s selection of EPA’s consideration of the adequacy IIHS, Though Farm and State be used?” validity [data] disregarded because others, responded with substantial agency’s among validity of the curves essential case, suggestion how- not even simply not the there was isIt comments conclusion. ever, represented a postulates for curves the essential effectiveness that all of methodology. fundamentally must be contained agency rule invalid any why peti- conse- Every judgment of of reasons provides record. list dissent upon an infinitude objec- quence is constructed these might not have raised tioners greater lesser certi- judgments, rulemaking proceeding. other during the tions tude, logical dependen- progression of in a down all of which boil at 1387-88 Dissent equiv- principle the cy in a first terminating upset probable petitioners' reluctance They possibly all cannot 1 + alent of 1=2. Even if determinations. favorable in the statement basis be included consideration, would be of only it were the rulemaking. have We do not purpose for a tacti- reward their questionable wisdom to under- authority require that all elements agency in the to leave the cal decision *15 “un- forth in a fashion lying a rule set be agen- encourage benighted thus dark —and layman,” Vermont a see to derstandable event, any in future. But cy in the action Corp. v. Natural Re- Power Yankee Nuclear explain speculations do not the dissent's Inc., 519, Council, 435 U.S. sources Defense mph standard proponents of the 2.5 1218, 1197, 557, 460 55 L.Ed.2d S.Ct. 98 fact, arguments. these did not raise (1978). well be disclosed And it as June 1979 Final on the commenters some judges we fields ourselves that in scientific (which mph supported the 5.0 Assessment equipped to laymen, ill determine are standard) object "effectiveness did that the expla- requisite where the falls between line systems to mph are overstated for 5.0 ratios analysis problematic useless nation of extent,” objection that but considerable cognoscenti replication of what for correspondence upon the lack was of based physics. basic textbook on amounts to a repair data than theoretical with cost rather Thus, adequacy of an for the our "feel” curves. inadequacy of the effectiveness necessarily gov- analysis in cases is such were consid- conclude curves We from that it elicits erned the reaction ground expert of part of the common ered knowledgeable commenters. From explana- required analysis no further that ground point at which it reaches common objections on this score Petitioners' tion. reasonably further assume that no we can Supreme Court’s put us in mind required. We will hear on explication is adminis- injunction in Vermont Yankee appeal that needful assertions elaborations game proceedings not be a should trative requested provided; but fairly were engage unjustified obstruc- in a forum skeptical rec- implacably of belated must be making cryptic ref- and obscure tionism appellate stage that ele- ognition at the "ought to be” consid- to matters erence analysis unchallenged ments scientific then, failing to do more after ered proceeding are incom- during a contested attention, agency’s the matter to the bring explanation. further prehensible without agency seeking have that determination post-appeal pleas inade- To credit such ground on the vacated integri- quate is to threaten the information "forcefully pre- to consider matters failed beyond rulemaking our ty in fields of all sented.” present ken. The limited scientific own 553-54, S.Ct. at 1217. U.S. at pres- challenge curves to the effectiveness appropri- more instructions even These flagrant particularly in a ents the threat reference to cryptic and ate when obscure peti- specifically asked the NHTSA form. fact, even less inadequacy theoretical (and rulemaking participants) tioners other —or that, explana- lack of than mere assertion of existing analyses repre- in 1979: "Do adequacy first made theoretical ap- tion of appropriate sent the most methods —is on appeal. study bumper at proaching a standards original, (emphases internal at Id. 1361-62 impact speeds and levels of dam- different omitted). not, the record age If what should citations resistance? method arbitrary, majority factor was not as the ance documents selecting FQPA erroneously Maj. Op. concludes. at factor different from the default lOx FQPA See, safety factor. e.g., Fenari- The record in this case contains the mol; Tolerance, Pesticide 32,- 71 Fed.Reg. published guidance EPA’s for determina- 841, 32,844-45 (June 2006) (noting that an appropriate FQPA safety tion of the EPA originally FQPA reduced the EPA, Programs, See Office of Pesticide Safety factor from lOx to subject 3x Appropriate FQPA Determination receiving data, additional subsequent- Factor(s) Safety in Tolerance Assessment ly recommended reducing the FQPA 3x (Feb. 2002). explained in As Safety factor lx when it obtained ade- guidance document, “when evaluating data); quate Thiacloprid; Pesticide Toler- whether reliable data are available to sup- ances, Fed.Reg. 55,503, 55,509 (Sept. port FQPA safety factor different from 2003) (“Although the lack morpho- FQPA default lOx factor and metric assessments in the DNT raised FQPA what level of ‘different’ safety fac- some uncertainty, EPA determined that children,” tor would be safe for infants and there were sufficient reliable data id. at to select inmay, the exercise of additional factor of 3X instead of judgment, scientific consider the 3x un- 10X.”). certainty relied on this traditionally long-es- factor that has been approach tablished in setting evaluating posed by used pesti- risks factors for the three at cide in a related issue context. See id. here, 26; supra see at nn. & 3. see also id. at (noting 9-10 that in evaluating the posed by pesticide risks ex- Because petitioners did not chal- *16 posure, a “often value of 3x is used to lenge the absence an explanation of as to ”). address database deficiencies.... why picked a 3x or lx factor However, in “the optimal case” in “which rather than a “4x or factor, 5x or 8x or 9x” high is a there level of that confidence the we are deprived of the EPA’s more de- hazard and assessments are suf- tailed explanation toas the scientific ficiently conservative!,] and there are no community relies uncertainty on the 3x assessment,” residual uncertainties in the factor when database deficiencies are iden- factor, i.e., EPA will remove the Nevertheless, tified. the record indicates apply “safety IX,” it a will factor of deem- that use of uncertainty the 3x factor is existing ing threshold “sufficient to generally accepted by the scientific com- protect infants and children.” at Id. 51- munity. al., See L. Michael Dourson et 52. See also Office of Programs, Pesticide Evolution Uncertainty Science-Based of EPA, Programs’ Policy Pesticide Office Assessment, Factors in Noncancer Risk on The Appropriate Determination 24 Regulatory Toxicology and Pharmacolo- FQPA Factor(s) Safety For Use in The (1996) gy (generally discussing the sci- Tolerance-setting Response Process: to ence underlying the use of lOx and 3x Public Comments OPP Docket OPP-00610 factors). Indeed, default uncertainty (Feb. 2002) (internal citation omit- any lack of controversy regarding ra- ted) (further explaining long-standing tionale underlying the selection aof 3x for “imposing basis uncertainty database safety factor rather “4x than a or 5x or 8x factor of 3X if study one is key missing or 9x” may explain why the NRDC from the database and a factor of 10X if argue objections did not in its to the EPA than more one is missing.”). agency justifica- a special needed EPA tolerance-setting factor,
Other regulations selecting tion for 3x once the approach reflect guid- described determined additional light required. factor was not lOx BARRETT, Henry Jacob long-established aon EPA’s reliance Plaintiff-Appellant, majori protocol, widely accepted these “the EPA chose ty’s statement v. arbitrarily” sup is not safety levels lower record, contrary to and is Nofziger; BELLEQUE; Rebec- ported J. Brian the scientific Taylor; defer to obligation Russell; Prinslow; Gary our J. ca agen made judgments analysis Defendants-Appellees. Parker, Kent special ex its area of within cy operating No. 06-35667. Co., 462 U.S. and Elec. Balt. Gas pertise. 103, 103 2246. S.Ct. Appeals, States Court United Ninth Circuit. recently emphasized, “[w]e we have
As agen- when most are to be deferential March and Submitted Argued within its area cy making predictions, sci- the frontiers of expertise, at special 22, 2008. Sept. Filed Council, at 993 Lands ence.”
(internal marks alterations quotation
omitted). from prohibits us Lands Council panel “act temptation to as
indulging the Nor can we at 988. Id.
of scientists.” always “to demonstrate
require methodology its scientific reliability underlying [agen- hypotheses
or the (internal Id. at 990
cy’s] methodology.” omitted). Lands Council marks
quotation simply role is proper that our
teaches expertise, in its agency,
ensure *17 rendering judgment
made no clear error id. arbitrary capricious. See
its action case The EPA’s choices
at 992-94. arbitrary capricious nor neither
were judgment. See must defer to 706(2)(A); Elec. Balt. Gas and 103-05,
Co., 103 S.Ct. 462 U.S. deny petition
Accordingly, I would entirety. in its notes “the plaining why the absence of DNT studies that, argued NRDC absent the DNT stud did not require the retention of the lOx ies, had no reliable data to reduce safety factor. The EPA satisfied its bur- the lOx Maj. Op. factor.” den, and had no obligation additional specific objection 1053. This is indeed the make a further response. raised majority NRDC. The then
