S1‐1
SummaryoftheupdatedRegulatoryImpactAnalysis(RIA)fortheReconsiderationofthe
2008OzoneNationalAmbientAirQualityStandard(NAAQS)
OnSeptember16,2009,EPAcommittedtoreconsideringtheozoneNAAQSstandard
promulgatedinMarch2008.TheozoneNAAQSwillbeselectedfromtheproposedrangeof
0.060to0.070ppm,basedonthisreconsiderationoftheevidenceavailableatthetimethelast
standardwasset.Today’sproposedrulealsoincludesaseparatesecondaryNAAQS,forwhich
thisRIAprovidesonlyqualitativeanalysisduetothelimitednatureofavailableEPAguidance
forattainingthisstandard
ThissupplementtotheRIAcontainsanupdatedillustrativeanalysisofthepotential
costsandhumanhealthandwelfarebenefitsofnationallyattaininga
newprimaryozone
standard.ThebasisforthisupdatedeconomicanalysisistheRIApublishedinMarch2008with
afewsignificantchanges.Thesechangesreflectthemorestringentrangeofoptionsbeing
proposedbytheAdministrator.Italsoreflectssomesignificantmethodologicalimprovements
toairpollutionbenefitsestimation,whichEPAhasadoptedsincetheozonestandardwaslast
promulgated.Thesesignificantchangesincludethefollowing:
InMarch2008,theAdministratorloweredtheprimaryozoneNAAQSfrom0.084
ppmto0.075ppm.TheRIAwhichaccompaniedthatruleanalyzedalessstringent
alternativestandardof0.079ppm,andtwomorestringentstandardsof0.065and
0.070ppm.ThisRIAsupplementpresentsananalysisofthreealternativestandards
withintheproposedrange:0.060,0.065and0.070ppm.Becausetoday’sproposed
ruleisareconsideration,eachalternativestandardiscomparedagainsttheprior
standardof0.084ppm.PerExecutiveOrder12866andtheguidelinesofOMB
CircularA‐4,thisRegulatoryImpactAnalysis(RIA)alsopresentsanalysesoftwo
alternativestandards,0.075ppmand0.055ppm.Itisimportanttonotethatasthe
stringencyofthestandardsincreases,webelievethattheuncertaintyinthe
estimatesofthecostsandbenefitsalso
increases.Thisisexplainedinmoredetailin
sections2and3ofthissupplement.
Wehaveadoptedseveralkeymethodologicalupdatestobenefitsassessmentsince
the2008OzoneNAAQSRIA.Theseupdateshavealreadybeenincorporatedinto
previousRIAsfortheproposedPortlandcementNESHAP,proposedNO
2
NAAQS,
andCategory3MarineDieselEngineRule,andarethereforenowincorporatedin
thisanalysis.Significantupdatesinclude:
o Weremovedtheassumptionofnocausalityforozonemortality,as
recommendedbytheNationalAcademyofScience(NAS).
S1‐2
o Weincludedtwomoreozonemulti‐citystudies,perNASrecommendation.
o WerevisedtheValueofaStatisticalLife(VSL)tobeconsistentwiththevalue
usedincurrentEPAanalyses.
o Weremovedthresholdsfromtheconcentration‐responsefunctionsforPM
2.5
,
consistentwithEPA’sIntegratedScienceAssessmentforParticulateMatter.
StructureofthisUpdatedRIA
AspartoftheozoneNAAQSreconsideration,thisRIAsupplementtakesasits
foundationthe2008ozoneNAAQSRIA.Detailedexplanationofthemajorityofassumptions
andmethodsarecontainedwithinthatdocumentandshouldbereliedupon,exceptasnoted
inthissummary.
Thissupplementitselfconsistsoffourparts:
Section1providesanoverviewofthechangestotheanalysisandsummarytablesof
theillustrativecostandbenefitsofobtainingarevisedstandardandseveral
alternatives.
Section2containsasupplementalbenefitandcostanalysisforstandardalternatives
at0.055and0.060ppm.
Section3containsasupplementalbenefitsanalysisoutliningtheadoptedchangesin
themethodology,updatedresultsforstandardalternatives0.065,0.070and0.075
ppmusingtherevisedmethodologyandassumptions.
Section4containssupplementalevaluationofaseparatesecondaryozoneNAAQSin
therangeof7to15ppm‐hr,aswellasalessstringentof21ppm‐hr.This
supplementalprovidesanexplanationoftheextremedifficultyofquantifyingthe
costsandbenefitsofasecondarystandardatthistime.
S1.1ResultsofBenefit‐CostAnalysis
ThisupdatedRIAconsistsofmultipleanalyses,includinganassessmentofthenature
andsourcesofambientozone;estimatesofcurrentandfutureemissionsofrelevant
ozoneprecursors;airqualityanalysesofbaselineandalternativecontrolstrategies;
illustrativecontrolstrategiestoattainthestandardalternativesinfutureyears;
estimatesoftheincrementalcostsandbenefitsofattainingthealternativestandards,
S1‐3
togetherwithanexaminationofkeyuncertaintiesandlimitations;andaseriesof
conclusionsandinsightsgainedfromtheanalysis.ItisimportanttorecallthatthisRIA
restsontheanalysisdonein2008;nonewairqualitymodelingorotherassessments
werecompletedexceptthoseoutlinedabove.
Thesupplementincludesapresentationofthebenefitsandcostsofattainingvarious
alternativeozoneNationalAmbientAirQualityStandardsintheyear2020.Theseestimates
onlyincludeareasassumedtomeetthecurrentstandardby2020.Theydonotincludethe
costsorbenefitsofattainingthealternatestandardsintheSanJoaquinValleyandSouthCoast
airbasinsinCalifornia,becauseweexpectthatnonattainmentdesignationsundertheCleanAir
Actfortheseareaswouldplacethemincategoriesaffordedextratimebeyond2020toattain
theozoneNAAQS.
InTableS1.1below,theindividualrowestimatesreflectthedifferentstudiesavailableto
describetherelationshipofozoneexposuretoprematuremortality.Thesemonetizedbenefits
includereducedhealtheffectsfromreducedexposuretoozone,reducedhealtheffectsfrom
reducedexposuretoPM
2.5
,andimprovementsinvisibility.Therangeswithineachrowreflect
twoPMmortalitystudies(i.e.PopeandLaden).
Rangesinthetotalcostscolumnreflectdifferentassumptionsabouttheextrapolation
ofcostsasdiscussedinChapter5ofthe2008OzoneNAAQSRIA.Thelowendoftherangeof
netbenefitsisconstructedbysubtractingthehighestcostfromthelowestbenefit,whilethe
highendoftherangeisconstructedbysubtractingthelowestcostfromthehighestbenefit.
Thepresentationofthenetbenefitestimatesrepresentsthewidestpossiblerangefromthis
analysis.
TableS1.2presentstheestimateoftotalozoneandPM
2.5
‐relatedprematuremortalities
andmorbiditiesavoidednationwidein2020asaresultofthisregulation.
S1‐4
TableS1.1:TotalMonetizedCostswithOzoneBenefitsandPM
2.5
Co‐Benefitsin2020
(inBillionsof2006$)*
Ozone
Mortality
Function
Reference
TotalBenefits** TotalCosts*** NetBenefits
3% 7% 7% 3% 7%
0.075ppm
Multi‐city
Belletal.2004 $6.9to$15 $6.4to$13 $7.6to$8.8 $‐1.9to$7.4 $‐2.4to$5.4
Schwartz2005 $7.2to$16 $6.8to$13 $7.6to$8.8 $‐1.6to$8.4 $‐2.1to$5.4
Huang2005 $7.3to$16 $6.9to$13 $7.6to$8.8 $‐1.5to$8.4 $‐2.0to$5.4
Meta‐
analysis
Belletal.2005 $8.3to$17 $7.9to$14 $7.6to$8.8 $‐0.50to
$9.4 $‐1.0to$6.4
Itoetal.2005 $9.1to$18 $8.7to$15 $7.6to$8.8 $0.30to$10 $‐0.20to$7.4
Levyetal.2005 $9.2to$18 $8.8to$15 $7.6to$8.8 $0.40to$10 $‐0.10to$7.4
0.070ppm
Multi‐city
Belletal.2004 $13to$29 $11to$24 $19to$25 $‐12to$10 $‐14to$5.0
Schwartz2005 $15to$30 $12to$25 $19to$25 $‐10to$11 $‐13to$6.0
Huang2005 $15to$30 $13to$26 $19to$25 $‐10to$11 $‐12to$7.0
Meta‐
analysis
Belletal.2005 $18to$34 $16to$29 $19to$25 $‐7.0to$15 $‐9.0to$10
Itoetal.2005 $21to$37 $18to$31 $19to$25 $‐4.0to$18 $‐6.0to$12
Levyetal.2005 $21to$37 $18to$31 $19to$25 $‐4.0to$18 $‐6.0to$12
Multi‐city
Belletal.2004 $22to$47 $19 to$40 $32to$44 $‐22to$15 $‐25to$7.0
0.065ppm
Schwartz2005 $24to$49 $21to$42 $32to$44 $‐20to$17 $‐23to$9.0
Huang2005 $25to$50 $22to$42 $32to$44 $‐19to$18 $‐23to$10
Meta‐
analysis
Belletal.2005 $31to$56 $27to$48 $32to$44 $‐13to
$24 $‐17to$16
Itoetal.2005 $36to$61 $32to$53 $32to$44 $‐8.0to$29 $‐13to$20
Levyetal.2005 $36to$61 $32to$53 $32to$44 $‐7.0to$29 $‐12to$20
0.060ppm
Multi‐city
Belletal.2004 $35to$73 $30to$61 $52to$90 $‐55to$21 $‐60to$9.0
Schwartz2005 $39to$78 $34to$66 $52to$90 $‐51to$26 $‐56to$14
Huang2005 $41to$78 $35to$66 $52to$90 $‐49to$26 $‐55to$14
Meta‐
analysis
Belletal.2005 $53to$91 $46to$78 $52to$90 $‐37to
$39 $‐44to$26
Itoetal.2005 $63to$100 $55to$87 $52to$90 $‐27to$48 $‐35to$35
Levyetal.2005 $63to$100 $56to$87 $52to$90 $‐27to$48 $‐34to$35
0.055ppm
Multi‐city
Belletal.2004 $53to$110 $45to$90 $78to$130 $‐77to$32 $‐85to$12
Schwartz2005 $61to$120 $52to$100 $78to$130 $‐69to$42 $‐78to$22
Huang2005 $63to$120 $54to$100 $78to$130 $‐67to$42 $‐76to$22
Meta‐
analysis
Belletal.2005 $84to$140 $74to$120 $78to$130 $‐46to
$62 $‐56to$42
Itoetal.2005 $100to$160 $90to$140 $78to$130 $‐30to82 $‐40to$62
Levyetal.2005 $100to$160 $91to$140 $78to$130 $‐30to$82 $‐39to$62
*Allestimatesroundedtotwosignificantfigures.Assuch,theymaynotsumacrosscolumns.Onlyincludesareas
requiredtomeetthecurrentstandardby2020,doesnotincludeSanJoaquinandSouthCoastareasinCalifornia.
**Includesozonebenefits,andPM
2.5
co‐benefits.Rangewasdevelopedbyaddingtheestimatefromtheozone
prematuremortalityfunctiontoestimatesfromthePM
2.5
prematuremortalityfunctionsfromPopeetal.and
Ladenetal.Tablesexcludeunquantifiedandnonmonetizedbenefits.
***Rangereflectslowerandupperboundcostestimates.Dataforcalculatingcostsata3%discountratewasnot
availableforallsectors,andthereforetotalannualizedcostsat3%arenotpresentedhere.
Additionally,these
estimatesassumeaparticulartrajectoryofaggressivetechnologicalchange.Analternativestorylinemight
hypothesizeamuchlessoptimistictechnologicaltrajectory,withincreasedcosts,orwithdecreasedbenefitsin
2020duetoalaterattainmentdate.
S1‐5
TableS1.2:SummaryofTotalNumberofAnnualOzoneandPM
2.5
‐RelatedPremature
MortalitiesandPrematureMorbidityAvoided:2020NationalBenefits
A
CombinedEstimateofMortality 0.075ppm 0.070ppm 0.065ppm 0.060ppm 0.055ppm
NMMAPS
Belletal.(2004) 760 to 1,900 1,500 to 3,500 2,500 to 5,600 4,000 to 8,700 5,900 to 13,000
Schwartz 800 to 1,900 1,600 to 3,600 2,700 to 5 ,800 4,500 to 9,200 6,700 to 13,000
Huang 820 to 1,900 1,600 to 3,600 2,800 to 5,900 4,600 to 9,300 6,900 to 14,000
Meta‐analysis
Belletal.(2005) 930 to 2,000 2,000 to 4,000 3,500 to 6,600 6,000 to 11,000 9,400 to 16,000
Itoetal. 1,000 to 2,100 2,300 to 4,300 4,000 to 7,100 7,100 to 12,000 11,000 to 18,000
Levyetal. 1,000 to 2,100 2,300 to 4,300 4,100 to 7,200 7,100 to 12,000 12,000 to 18,000
CombinedEstimateofMorbidity 0.075ppm 0.070ppm 0.065ppm 0.060ppm 0.055ppm
AcuteMyocardialInfarction
B
1,300 2,200 3,500 5,300 7,500
UpperRespiratorySymptoms
B
9,900 19,000 31,000 48,000 69,000
LowerRespiratorySymptoms
B
13,000 25,000 41,000 63,000 91,000
ChronicBronchitis
B
470 880 1,400 2,200 3,200
AcuteBronchitis
B
1,100 2,100 3,400 5,300 7,600
AsthmaExacerbation
B
12,000 23,000 38,000 58,000 83,000
WorkLossDays
B
88,000 170,000 270,000 420,000 600,000
SchoolLossDays
C
190,000 600,000 1,100,000 2,100,000 3,700,000
HospitalandERVisits 2,600 6,700 11,000 21,000 35,000
MinorRestrictedActivityDays 1,000,000 2,600,000 4,500,000 8,100,000 13,000,000
A
Onlyincludesareasrequiredtomeetthecurrentstandardby2020,doesnotincludeSanJoaquin
ValleyandSouthCoastairbasinsinCalifornia.Includesozonebenefits,andPM
2.5
co‐benefits.Range
wasdevelopedbyaddingtheestimatefromtheozoneprematuremortalityfunctiontoboththelower
andupperendsoftherangeofthePM
2.5
prematuremortalityfunctionscharacterizedintheexpert
elicitationdescribedinChapter6ofthe2008RIA.
B
EstimatedreductioninprematuremortalityduetoPM
2.5
reductionsonly.
C
Estimatedreductioninprematuremortalityduetoozonereductionsonly.
Thefollowingsetofgraphsisincludedtoprovidethereaderwitharicherpresentation
oftherangeofcostsandbenefitsofthealternativestandards.Thegraphssupplementthe
tablesbydisplayingallpossiblecombinationsofnetbenefits,utilizingthesixdifferentozone
functions,thefourteendifferentPMfunctions,andthetwocostmethods.Eachofthe168bars
ineachgraphrepresentsaseparatepointestimateofnetbenefitsunderacertaincombination
ofcostandbenefitestimationmethods.Becauseitisnotadistribution,itisnotpossibleto
inferthelikelihoodofanysinglenetbenefitestimate.Thebluebarsindicatecombinations
wherethenetbenefitsarenegative,whereasthegreenbarsindicatecombinationswherenet
benefitsarepositive.FiguresS1.1throughS1.5showsallofthesecombinationsforall
standardsanalyzed.FigureS1.6showsthecomparisonoftotalmonetizedbenefitswithcosts
usingthetwobenefits
anchorpointsbasedonPope/Bell2004andLaden/Levy.
S1‐6
FigureS1.1:
FigureS1.2:
$(100)
$(80)
$(60)
$(40)
$(20)
$‐
$20
$40
$60
$80
$100
Billionsof2006$
Combin atio nsof6Ozonebenefitsestimateswith14PM
2.5
co‐benefitsestimateswith2costsestimates
NetBe nefitsforanAlternateStandardof0. 075pp m(7%discountrate)
Benefitsaregreaterthan
costs
Costsaregreaterthan
benefits
Median
=$3.1b
$(100)
$(80)
$(60)
$(40)
$(20)
$‐
$20
$40
$60
$80
$100
Billionsof2006$
Combination sof6Ozonebenefitsestimateswith14PM
2.5
co‐benefitsestimateswith2costsestimates
NetBenefitsforanAlternateStandardof 0.070ppm (7%discountrate)
Benefits aregreaterthan
costs
Costsaregreaterthan
benefits
Median
=$1.4b
Thesegraphsshowall168combinationsofthe6differentozonemortalityfunctionsandassumptions,the14differentPM
mortalityfunctions,andthe2costmethods.Thesecombinationsdonotrepresentadistribution.
S1‐7
FigureS1.3:
FigureS1.4:
$(100)
$(80)
$(60)
$(40)
$(20)
$‐
$20
$40
$60
$80
$100
Billion sof2006$
C ombinationsof6Ozonebenefitsestimateswith14PM
2.5
co‐benefitsestimateswith2costsestimates
NetBenefitsforanAlternateStandardof0.065ppm(7%discountrate)
Benefitsaregreaterthan
costs
Costsar egreaterthan
benefits
Median
=$0.7b
$(100)
$(80)
$(60)
$(40)
$(20)
$‐
$20
$40
$60
$80
$100
Billion sof2006$
Combination sof6Ozonebenefitsestimateswith14PM
2.5
co‐benefitsestimateswith2costsestimates
NetBenefitsforanAlternateStandardof0.060ppm(7%discountrate)
Benefitsaregreaterthan
costs
Costsar egreaterthan
benefits
Median
=$‐4.8b
Thesegraphsshowall168combinationsofthe6differentozonemortalityfunctionsandassumptions,the14differentPM
mortalityfunctions,andthe2costmethods.Thesecombinationsdonotrepresentadistribution.
S1‐8
FigureS1.5:
FigureS1.6:
$(100)
$(80)
$(60)
$(40)
$(20)
$‐
$20
$40
$60
$80
$100
Billionsof2006$
Combinationsof6Ozonebenefitses timateswith14PM
2.5
co‐benefitsestimateswith2costsestimates
NetBenefitsforanAlternateStandardof0.055ppm(7%discountrate)
Benefitsaregreaterthan
costs
Costsaregreaterthan
benefits
Median
=$‐2.8b
$0
$20
$40
$60
$80
$100
$120
$140
$160
0.075
ppm
0.070
ppm
0.065
ppm
0.060
ppm
0.055
ppm
Billions of 2006$
Alternative Standard Level
ComparisonofTotalMonetizedBenefits toCos ts forAlternative
StandardLevelsin2020(Updatedresults,7%discountrate)
Thisgraphshowsall168combinationsofthe6differentozonemortalityfunctionsandassumptions,the14differentPM
mortalityfunctions,andthe2costmethods.Thesecombinationsdonotrepresentadistribution.
ThelowbenefitsestimateisbasedonPope/Bell2004andthehighbenefitsestimateisbasedonLaden/Levy.Thetwocostestimates
arebasedontwodifferentextrapolatedcostmethodologies.Theseendpointsrepresentseparateestimatesbasedonseparate
methodologies.Thedottedlinesareavisualcueonly,andtheselinesdonotimplyauniformrangebetweentheseendpoints.
S‐9
S1.2AnalysisoftheProposedSecondaryNAAQSforOzone
Exposurestoozonehavebeenassociatedwithawidearrayofvegetationand
ecosystemeffects,includingthosethatdamageorimpairtheintendeduseoftheplantor
ecosystem.Sucheffectsareconsideredadversetothepublicwelfare.
Today’sproposedrulecontainsacumulativeseasonalsecondarystandard,expressedas
anindexoftheannualsumofweightedhourlyconcentrations(usingtheW126form),setata
levelintherangeof7to15ppm‐hours,andrequestscommentonalevelof21ppm‐hours.
Theindexwould
becumulatedoverthe12‐hourdaylightwindow(8:00a.m.to8:00p.m.)
duringtheconsecutive3‐monthperiodduringtheozoneseasonwiththemaximumindexvalue
(hereafter,referredtoasthe12‐hour,maximum3‐monthW126).Forreasonsdetailedin
section4ofthissupplement,wewerenotabletocalculatemonetizedcostsandbenefitsof
attainmentoftheselevels.However,section4containsadetaileddiscussionoftherelevant
welfareeffects,andestimatesofthenumberofcountiesnationwidewhichwouldnotattain
eachalternativesecondaryNAAQS,bothcurrentlyandin2020.
S1.3 CaveatsandConclusions
Ofcriticalimportancetounderstandingtheseestimatesoffuturecostsandbenefitsis
thattheyarenotintendedtobeforecastsoftheactualcostsandbenefitsofimplementing
revisedstandards.Therearemanychallengesinestimatingthecostsandbenefitsofattaininga
tighterozonestandard,whicharefullydiscussed
in2008OzoneNAAQSRIAandthe
supplementtothisanalysisaccompanyingtoday’sproposedrule.
Theestimatedcostsandbenefitsofattainingalternateozonestandardsof0.060ppmor0.055
ppmarehighlyspeculativeandsubjecttolimitationsanduncertaintiesthatareuniquetothis
analysis. Wefirstsummarizethesekeyuncertainties:
Theestimatednumberofpotentialnon‐attainmentareasisuncertain.Basedon
present‐dayozoneconcentrationsitisclearthatmanyareascurrentlyexceedtheozone
targetsof0.055and0.060.Itisalsoclearthattherewillbesubstantialimprovementsin
ozoneairqualitybetweennowand2020duetoexistingandrecentlypromulgated
emissionsreductionrules.Wehaveusedanairqualitymodeltoprojectozonelevelsin
2020basedoncertainestimatesofhowemissionswillincreaseordecreaseoverthat
timeperiod.Theseassumptionsaboutforecastedemissionsgrowthorreductionare
S‐10
highlyuncertainandwilldependuponeconomicoutcomesandfuturepolicydecisions.
Additionally,themethodologyforprojectingfuturenonattainmentreliesuponbaseline
observationsfromtheexistingozonemonitoringnetwork.Thisnetworkmaynot
includesomecountiesthateasilyattainhigherozonestandards,butmaynotattain
ozonestandardssofarbelowthecurrentNAAQS.Weestimatehumanhealthbenefits
byadjustingmonitoredozonevaluestojustattainalternatestandardlevels;wecan
onlyperformthisextrapolationincountiescontaininganozonemonitor.
Thepredictedemissionreductionsnecessarytoattainthesetwoalternativestandards
arealsohighlyuncertain.BecausethehypotheticalRIAcontrolscenarioleftasignificant
portionofthecountryexceedingthe0.055and0.060targets,wehadtoextrapolatethe
rateofozonereductionseeninpreviousairqualitymodelingexercisestoestimatethe
additionalemissionsreductionsneededtomeetthelowertargets.Thedetailsofthe
approachareexplainedbelow,butformostareasoftheanalysisweusedsimpleimpact
ratiostoprojecttheozoneimprovementsasarateofNOxemissionsreduced.Useof
non‐site‐specific,linearimpactratiostodeterminethenon‐linear,spatially‐varying,
ozoneresponsewasanecessarylimitationwhichresultsinconsiderableuncertaintyin
theextrapolatedairqualitytargets.
Thecostsofidentifiedcontrolmeasuresaccountsforanincreasinglysmallerquantityof
thetotalcostsofattainment.Thisisamajorlimitationofthecostanalysis.Weassume
amajorityofthecostsofattainingthetighteralternativestandardswillbeincurred
throughtechnologieswedonotyetknowabout.Thereforecostingfutureattainment
baseduponunspecifiedemissionreductionsisinherentlydifficultandspeculative.
Theuncertaintiesandlimitationssummarizedabovearegenerallymoreextensivethan
thoseforthe0.075ppm,0.070ppm,and0.065ppmanalyses.However,there
aresignificant
uncertaintiesinbothcostandbenefitestimatesforthefullrangeofstandardalternatives.
Belowwesummarizesomeofthemoresignificantsourcesofuncertaintycommontoalllevel
analyzedinthe2008ozoneNAAQSRIAandthissupplementalanalysis:
Benefitsestimatesareinfluencedbyourabilitytoaccuratelymodelrelationships
betweenozoneandPMandtheirassociatedhealtheffects(e.g.,premature
mortality).
Benefitsestimatesarealsoheavilydependentuponthechoiceofthestatistical
modelchosenforeachhealthbenefit.
S‐11
PMco‐benefitsarederivedprimarilyfromreductionsinnitrates(associatedwith
NOxcontrols).Assuch,theseestimatesarestronglyinfluencedbytheassumption
thatallPMcomponentsareequallytoxic.Co‐benefitestimatesarealsoinfluenced
bytheextenttowhichaparticularareachoosestouseNOxcontrolsratherthan
VOCcontrols.
Thereareseveralnonquantifiedbenefits(e.g.,effectsofreducedozoneonforest
healthandagriculturalcropproduction)anddisbenefits(e.g.,decreasesin
troposphericozoneleadtoreducedscreeningofUV‐Braysandreducednitrogen
fertilizationofforestsandcropland)discussedinthisanalysisinChapter6ofthe
2008OzoneNAAQSRIA.
Changesinairqualityasaresultofcontrolsarenotexpectedtobeuniformoverthe
country.Inourhypotheticalcontrolscenariosomeincreasesinozonelevelsoccurin
areasalreadyinattainment,thoughnotenoughtopushtheareasinto
nonattainment
AsexplainedinChapter5ofthe2008OzoneNAAQSRIA,thereareseveral
uncertaintiesinourcostestimates.Forexample,thestatesarelikelytousedifferent
approachesforreducingNOxandVOCsintheirstateimplementationplanstoreach
atighterstandard.Inaddition,sinceourmodelingofknowncontrolsdoesnotgetall
areasintoattainment,weneededtomakeassumptionsaboutthecostsofcontrol
technologiesthatmightbedevelopedinthefutureandusedtomeetthetighter
alternative.Forexample,forthe21counties(infourgeographicareas)thatarenot
expectedtoattain0.075ppm
1
in2020
2
,assumedcostsofunspecifiedcontrols
representasubstantialfraction,ofthecostsestimatedinthisanalysisrangingfrom
50%to89%oftotalcostsdependingonthestandardbeinganalyzed.
AsdiscussedinChapter5ofthe2008OzoneNAAQSRIA,advicefromEPA’s
ScienceAdvisoryBoardhasquestionedtheappropriatenessofanapproach
similartooneofthoseusedhereforestimatingextrapolatedcosts.Forbalance,
EPAalsoappliedamethodologyrecommendedbytheScienceAdvisoryBoardin
aneffort
tobestapproximatethecostsofcontroltechnologiesthatmightbe
developedinthefuture.
1
Areasthatdonotmeet0.075ppmareChicago,Houston,theNortheasternCorridor,and
Sacramento.Formoreinformationseechapter4section4.1.1ofthe2008OzoneNAAQSRIA.
2
ThislistofareasdoesnotincludetheSanJoaquinandSouthCoastairbasinswhoarenot
expectedtoattainthecurrent0.084ppmstandarduntil2024.
S‐12
Bothextrapolatedcostsandbenefitshaveadditionaluncertaintyrelativeto
modeledcostsandbenefits.Theextrapolatedcostsandbenefitswillonlybe
realizedtotheextentthatunknownextrapolatedcontrolsareeconomically
feasibleandareimplemented.Technologicaladvancesovertimewilltendto
increasetheeconomicfeasibilityofreducingemissions,andwilltendtoreduce
thecostsofreducingemissions.Ourestimatesofcostsofattainmentin2020
assumeaparticulartrajectoryofaggressivetechnologicalchange.This
trajectoryleadstoaparticularlevelofemissionsreductionsandcostswhichwe
haveestimatedbasedontwodifferentapproaches,thefixedcostandhybrid
approaches.Analternativestorylinemighthypothesizeamuchlessoptimistic
technologicalchangepath,suchthatemissionsreductionstechnologiesfor
industrialsourceswouldbemoreexpensiveorwouldbeunavailable,sothat
emissionsreductionsfrommanysmallersourcesmightberequiredfor2020
attainment,atapotentiallygreatercostperton.Underthisalternative
storyline,twooutcomesarehypotheticallypossible:Underonescenario,total
costsassociatedwithfullattainmentmightbesubstantiallyhigher.Underthe
secondscenario,statesmaychoosetotakeadvantageofflexibilityintheClean
AirActtoadoptplanwithlaterattainmentdatestoallowforadditional
technologiestobedevelopedandforexistingprogramslikeEPA’sOnroadDiesel,
NonroadDiesel,andLocomotiveandMarinerulestobefullyimplemented.If
statesweretosubmitplanswithattainmentdatesbeyondour2020analysis
year,benefitswouldclearlybelowerthanwehaveestimatedunderour
analyticalstoryline.However,inthiscase,statedecisionmakersseekingto
maximizeeconomicefficiencywouldnotimposecosts,includingpotential
opportunitycostsofnotmeetingtheirattainmentdate,whentheyexceedthe
expectedhealthbenefitsthatstateswouldrealizefrommeetingtheirmodeled
2020attainmentdate.Inthiscase,upperboundcostsare
difficulttoestimate
becausewedonothaveanestimateofthepointwheremarginalcostsareequal
tomarginalbenefitsplusthecostsofnonattainment.Clearly,thesecondstage
analysisisahighlyspeculativeexercise,becauseitisbasedonestimating
emissionreductionsandairqualityimprovementswithoutanyinformation
aboutthespecificcontrolsthatwouldbeavailabletodoso.
S2‐1
S2:SupplementalRegulatoryImpactAnalysisofAlternativeStandards
0.055and0.060ppmfortheOzoneNAAQSReconsideration
Synopsis
Thissupplementalchapterpresentsthecostsandbenefitsoftwoadditionalalternative
standards
1
,0.055ppmand0.060ppm.
S2.1 UncertaintiesandLimitations
Theestimatedcostsandbenefitsofattainingalternateozonestandardsof0.060ppmor
0.055ppmarehighlyspeculativeandsubjecttolimitationsanduncertaintiesthatareuniqueto
thisanalysis.Wefirstsummarizethesekeyuncertaintiesbeforedescribinghowbestto
interprettheseresults.
Theestimatednumberofpotentialnon‐attainmentareasisuncertain.Basedon
present‐dayozoneconcentrationsitisclearthatmanyareascurrentlyexceedtheozone
targetsof0.055and0.060.Itisalsoclearthattherewillbesubstantialimprovementsin
ozoneairqualitybetweennowand2020duetoexistingandrecentlypromulgated
emissionsreductionrules.
2
Wehaveusedanairqualitymodeltoprojectozonelevelsin
2020basedoncertainestimatesofhowemissionswillincreaseordecreaseoverthat
timeperiod.Theseassumptionsaboutforecastedemissionsgrowthorreductionare
highlyuncertainandwilldependuponeconomicoutcomesandfuturepolicydecisions.
Additionally,themethodologyforprojectingfuturenonattainmentreliesuponbaseline
observationsfromtheexistingozonemonitoringnetwork.Thisnetworkmaynot
includesomecountiesthateasilyattainhigherozonestandards,butmaynotattain
ozonestandardssofarbelowthecurrentNAAQS.Weestimatehumanhealthbenefits
byadjustingmonitoredozonevalues
tojustattainalternatestandardlevels;wecan
onlyperformthisextrapolationincountiescontaininganozonemonitor.
Thepredictedemissionreductionsnecessarytoattainthesetwoalternativestandards
arealsohighlyuncertain.BecausethehypotheticalRIAcontrolscenarioleftasignificant
portionofthecountryexceedingthe0.055
and0.060targets,wehadtoextrapolatethe
1
Forbenefitsresultsofthealternativestandardsanalysesfor0.065,0.070,and0.075,pleaseseeSection3ofthis
supplement.Forthecostresultsofthealternativestandardsanalysesfor0.065,0.070,and0.075,pleaseseethe
2008OzoneNAAQSRIA,whichcanbefoundat< />2
Thisimprovementinozoneairqualityisanticipateddespiteotherfactorsthatmayworsenozoneairquality,such
asincreasedpopulation,increasedtraffic,orotherfederalpolicies.
S2‐2
rateofozonereductionseeninpreviousairqualitymodelingexercisestoestimatethe
additionalemissionsreductionsneededtomeetthelowertargets.Thedetailsofthe
approachareexplainedbelow,butformostareasoftheanalysisweusedsimpleimpact
ratiostoprojecttheozoneimprovementsasarateofNOxemissionsreduced.Useof
non‐site‐specific,linearimpactratiostodeterminethenon‐linear,spatially‐varying,
ozoneresponsewasanecessarylimitationwhichresultsinconsiderableuncertaintyin
theextrapolatedairqualitytargets.
Thecostsofidentifiedcontrolmeasuresaccountsforanincreasinglysmallerquantityof
thetotalcostsofattainment.Thisisamajorlimitationofthecostanalysis.Weassume
amajorityofthecostsofattainingthetighteralternativestandardswillbeincurred
throughtechnologieswedonotyetknowabout.Thereforecostingfutureattainment
baseduponunspecifiedemissionreductionsisinherentlydifficultandspeculative.
Theuncertaintiesandlimitationssummarizedabovearegenerallymoreextensivethan
thoseforthe0.075ppm,0.070ppm,and0.065ppmanalyses.Thetablebelowcontrastsour
levelofconfidenceineachofthekeyresults.
TableS2.1:Keyuncertaintiesandlimitationsintheanalysisfor
0.060ppmand0.055ppm
Analyticalquestion StandardAlternativesAnalyzed
0.055ppm&0.060ppm 0.065ppm,0.070ppm&
0.075ppm
Airqualityestimates
Numberofcountiesattainingeachstandard
alternative
Medium Higher
Airqualityincrementnecessarytoattain
standard
Lower Medium
Costs
Totalcostestimate Lower Medium
Distributionofcostsbysector Lower Medium
Levelofextrapolatedcosts Lower Medium
Benefits
Sizeofozone‐relatedhumanhealthbenefits Lower Higher
SizeofPM
2.5
‐relatedhumanhealthco‐benefits Lower Higher
Distributionofbenefitsacrossthepopulation Lower Higher
Giventhepervasiveuncertaintiesinthe55ppband60ppbanalysis,thetypesof
conclusionsthatreadersmaydrawisnecessarilylimited.Conclusionsofthissupplemental
analysisareprovidedinSectionS2.6.
S2‐3
S2.2 EstimatingAQTargets
Themethodologyusedtodeveloptheestimatesofadditionalemissionsreductions
neededtomeetthe0.055ppmand0.060ppmstandardsisbasedonestimationtechniques
previouslysummarizedinthe2008OzoneNAAQSRIASection4.1,includingapplicationofthe
samecontrolmeasurereductionsandcosts.Theproceduresusedtoextendthatoriginal
analysistothetwolowerozonetargetsisexplainedbelow.
Ofthe659countiesthatarepartoftheanalysis,thereare565and385countiesthat
areprojectednottomeetthe0.055ppmand0.060ppmozonetargetsin2020,evenafter
implementationofthecontrolsinthehypotheticalRIAscenario.Asdescribedintheearlier
documentation,these“extrapolatedcontrolareas”wereseparatedintothreegroupsforthe
purposesofdeterminingwhatadditionalemissionsreductionswouldbenecessaryfor
projectedattainment.
Phase1areasweredefinedasthefourareaswiththelargestexpectedextrapolated
costs:SouthernCalifornia,westernLakeMichigan,Houston,andpartsoftheNortheast
Corridor.Fortheselocations,wehaveanavailablesetofsensitivitymodelingresultswhich
allowsforanassessmentoftheimpactsofadditionalNOxandNOx+VOCcontrolsofupto90
percentbeyondtheRIAcase.Unliketheoriginalanalysis,therewerenoareasforwhichan
equalcombinationofNOxandVOCcontrolswasdeterminedtobeamorecosteffectivecontrol
pathtoattainthelowerozonetargetsthanNOxcontrolexclusively.Therefore,forthis
supplementalanalysis,weassumedthatalladditionalextrapolatedemissionsreductionswould
comefromNOxcontrols.TableS2.2presentstheadditionalNOxreductionsestimatedtobe
neededtomeetthe0.055and0.060ppmtargets,aboveandbeyondthehypotheticalRIA
controlcase.Itshouldbenotedthatbecausethesensitivitymodelingdidnotconsidercontrols
beyonda
90percentreduction,itisnotpossibletoestimatethenecessary“extrapolatedtons”
foranyareathatdoesnotmeetthetargetinthesensitivitymodelingevenafter90percent
control.Theemissionstargetsfortheseareasaresimplylistedas“greaterthan90%”.
S2‐4
TableS2.2:EstimatedPercentageReductionsofNOxbeyondtheRIAControlScenario
NecessarytoMeettheSupplementalAnalysisTargetsinthePhase1Areas
0.055 0.060
Amador and Calaveras Cos., CA 0.071 65% 47%
Chico, CA 0.068 58% 37%
Imperial Co., CA 0.071 70% 51%
Inyo Co., CA 0.068 87% 56%
Los Angeles South Coast Air Basin, CA 0.122 > 90% > 90%
Mariposa and Tuolumne Cos., CA 0.072 72% 52%
Nevada Co., CA 0.075 74% 58%
Sacramento Metro, CA 0.080 82% 69%
San Benito Co., CA 0.066 54% 29%
San Diego, CA 0.076 80% 67%
San Francisco Bay Area, CA 0.069 64% 45%
San Joaquin Valley, CA 0.096 > 90% 87%
Santa Barbara Co., CA 0.068 55% 35%
Sutter Co., CA 0.067 56% 35%
Ventura Co, CA 0.077 73% 59%
Northeast Corridor, CT-DE-MD-NJ-NY-PA 0.077 > 90% 70%
Eastern Lake Michigan, IL-IN-WI 0.080 > 90% > 90%
Houston, TX 0.087 > 90% > 90%
Additional local control needed to
meet various standards
Phase 1 Area (NOx only)
2020 Design Value after RIA
Control Scenario (ppm)
Phase2areasweredefinedasanyareaoutsideaPhase1areawhoseprojected2020
designvalueexceeded0.070ppminthehypotheticalRIAscenario.Theimpactsofadditional
hypotheticalemissionsreductionsinupwindPhase1areaswereaccountedforinthe
calculationofneededextrapolatedtonsinPhase2areas.Afterthoseupwindreductionswere
accountedfor,weutilizedsimple“impactratios”(ppmimprovement/%emissionsreduced)to
determinetheremainingadditionalreductionsneededtomeetthe0.055and0.060ppm
targets.Asite‐specificimpactratiowasusedforeachPhase2areabasedonthelocalized
ozonechangesintheRIAcontrolscenariomodeling.TableS2.3presentstheextrapolated
percentreductionsestimatedforthePhase2areas.
S2‐5
TableS2.3:EstimatedPercentageReductionsofNOxbeyondtheRIAControlScenario
NecessarytoMeettheSupplementalAnalysisTargetsinthePhase2Areas
Allotherlocationsthatdidnotmeetthe0.055or0.060ppmtargetsafterthe2020RIA
controlscenariowereconsideredasaPhase3area.Ahighlysimplifiedapproachwasusedto
determine theextrapolatedtons neededintheseareas.First, insteadofexplicitly accounting
fortheimpactsofthe Phase1andPhase2upwind emissionsreductionsonPhase3areas,we
assumedthatthedesignvaluesfromthe60%NOxreductionrunweretheappropriatestarting
pointforestimatingtheadditionalemissionsreductionsinthePhase3areas.Sincethetargets
forthePhase1areasaregenerallygreaterthan60%andsincewe havenotaccountedforthe
Phase2reductions,theseestimatesshouldprovidea conservativeestimateofthepercentage
emissions reductions needed for full attainment.Secondly, we did not develop site‐specific
impactratiosforthe multiplePhase3areas.Instead,weusedastandardrelationshipof0.150
ppb / 1% NOx reduction for calculating the emissions reductions needed to attain 0.055 and
0.060 ppm in these areas.This value was the average site‐specific relationship calculated for
the Phase 2 areas, as described above.As a result of these assumptions, the estimated
emissions reductions needed to attain the supplemental standards in the Phase 3 should be
consideredtobehighlyuncertain.TheresultsofthePhase3analysisareshowninTableS2.4.
S2‐6
TableS2.4:EstimatedPercentageReductionsofNOxbeyondtheRIAControlScenario
NecessarytoMeettheSupplementalAnalysisTargetsinthePhase3Areas
S2‐7
S2‐8
FiguresS2.1andS2.2showwhichcountiesarepartoftheextrapolatedcostareasas
wellastheestimatedpercentreductionneededbeyondtheRIAcontrolcasetomeetthe
alternativestandardsof0.055and0.060ppmwithineachofthoseareas.Theconversionof
theseadditionalpercentagereductionstoactualextrapolatedtonsisdescribedinSectionsS2.3
ofthissupplement.
S2‐9
FigureS2.1:MapofExtrapolatedCostCountiesforthe0.055ppmAlternateStandardand
EstimatedPercentageNOxControlsNeededtoMeetthatStandardin2020
S2‐10
FigureS2.2:MapofExtrapolatedCostCountiesforthe0.060ppmAlternateStandardand
EstimatedPercentageNOxControlsNeededtoMeetthatStandardin2020
S2.3 EstimatingEmissionTargets
ThemethodologytodevelopairqualityNOxreductiontargetsforestimating
extrapolatedtonsreducedforthealternativestandardsispresentedinthe2008OzoneNAAQS
RIA
3
Section4.1.5.Nomethodologicalchangesweremadetoextendtheanalysistotargetsfor
the0.055ppmand0.060ppmalternativestandards.DiscussiononthecreationoftheNOx
targetsforthe0.055ppmand0.060ppmstandardsisinsectionS1.1.TheseNOxtargetswere
appliedtotheremainingemissionsfromtheRIAcontrolscenariobygeographicarea.Table
S2.5providestheextrapolatedreductionsbygeographicareaneededtoobtainthetwo
alternativestandardspost‐RIAcontrolscenarioemissions.TheextrapolatedNOxtonsare
obtainedbymultiplyingtheNOxtargetsinTablesS2.2throughS2.4bytheremainingemissions
for
eachareaaftertheRIAcontrolscenario.
3
/>S2‐11
Itisimportanttorepeatthattheextrapolatedcostareasarepotentiallystandard‐
specificbecausethelocationofcountiesinanextrapolatedareadependsonwhetherthe
particularstandardisbeingviolatedbyagreaterorlessernumberofmonitorsinthearea.For
example,asseeninFigures4.3aand4.3bofthe2008OzoneNAAQSRIA
3
theBoiseIdahoarea
extendsfurthereastforthe0.055ppmalternatestandardwhereareaslikeNewOrleans
attainedthe0.060standardbutnot0.055ppmalternatestandard.
TableS2.5:ExtrapolatedEmissionReductions(post‐RIAcontrolscenario)NeededtoMeet
the0.055ppmand0.060ppmAlternateStandardsin2020
a
ExtrapolatedCostArea AdditionalNOxEmissionReductionsNeeded
(annualtons/year)
0.055ppm 0.060ppm
Albuquerque,NM 7,800 3,100
Appleton‐Oshkosh,WI 3,600
Atlanta,GA 140,000 80,000
Augusta,GA‐SC 4,900
Austin,TX 41
BatonRouge,LA 250,000 250,000
BentonHarbor,MI 3,500 200
BenzieCo,MI 1,800
BerkeleyandJeffersonCounties,WV 1,200
Birmingham,AL 72,000 17,000
Boise,ID 32,000 17,000
Boston‐Lawrence‐Worcester,MA 62,000 40,000
Buffalo‐NiagaraFalls,NY 50,000 35,000
Burlington,V
T
3,100
CampbellCo,WY 26,000 14,000
CanyonlandsNP 1,500 530
Carlsbad,NM 20,000 6,800
CedarCo,MO 1,400 2,200
CedarRapids,IA 160
Charleston,WV 220
Charlotte‐Gastonia‐RockHill,NC‐SC 210,000 150,000
Chattanooga,TN‐GA 12,000 1,600
Chico,CA 3,000 1,900
Cincinnati‐Hamilton,OH‐KY‐IN 110,000 59,000
ClearfieldandIndianaCos,PA 410 33
Cleveland,MS 180
Cleveland‐Akron‐Lorain,OH 190,000 160,000
Clinton,IA 24,000
CochiseCo,AZ 4,800 2,100
ColoradoSprings,CO 500
Columbia,SC 24,000 8,700
CorpusChristi,TX 31,000
Dallas‐FortWorth,TX 220,000 120,000
Davenport,IA 150
Denver‐Boulder‐Greeley‐FtCollins‐Love., 80,000 43,000
Detroit‐AnnArbor,MI 180,000 180,000
S2‐12
ExtrapolatedCostArea AdditionalNOxEmissionReductionsNeeded
(annualtons/year)
0.055ppm 0.060ppm
ElPaso,TX‐NM 20,000 12,000
Eugene‐Springfield,OR 450
Farmington,NM 86,000 52,000
FranklinCo,PA 630 100
GrandCanyonNP 22,000 1,800
GrandRapids,MI 90
GreatBasinNP 470
GreatSmokyMountainsNP 560 180
GreenBay,WI 420 11,000
Gulfport‐Biloxi,AL‐MS 25,000 6,600
Hancock,Knox,Lincoln&WaldoCo,ME 17,000
Houston‐Galveston‐Brazoria,TX 260,000 310,000
Huntington‐Ashland,WV‐KY 170,000 100,000
HuronCo,MI 15,000 7,500
JeffersonCo,NY 26,000 17,000
JohnsonCity‐Kingsport‐Bristol,TN 45,000 21,000
KansasCity,MO‐KS 100,000 37,000
Knoxville,TN 22,000 9,200
LaCrosse,WI 290
LakeCharles,LA 6,900 1,100
Lansing‐EastLansing,MI 1,900
LasVegas,NV 23,000 14,500
LittleRock,AR 18,000 1,500
Longview,TX 950 360
LosAngelesSouthCoastAirBasin,CA
b
270,000 230,000
Louisville,KY‐IN 59,000 29,000
Macon,GA 7,500 4,200
MadisonandPageCos(ShenandoahNP),VA 350
McAlester,OK 800
Medford,OR 5,200 300
Memphis,TN‐AR‐MS 160,000 98,000
MesaVerdeNP 4,600 390
Minneapolis‐St.Paul,MN‐WI 6,300
Mobile,AL 25,000 9,900
Monroe,LA 9,300
Muskegon,MI 160
Nashville,TN 1,900 210
Natchez,MS 6 ,100 960
NevadaCo,CA 1,200
NewOrleans,LA 2,800
Newton,AR 2,300
Norfolk‐VirginiaBeach‐NewportNews(HR) 130,000 79,000
NortheastCorridor,CT‐DE‐MD‐NJ‐NY‐PA 550,000 430,000
OklahomaCity,OK 18,600
Omaha,NE‐IA 62,000 11,000
Orlando,FL 1,300
Owensboro,KY‐IN 18,000 5,400
S2‐13
ExtrapolatedCostArea AdditionalNOxEmissionReductionsNeeded
(annualtons/year)
0.055ppm 0.060ppm
Paducah,KY‐IL 590 620
PanamaCity,FL 3,400 850
Parkersburg‐Marietta,WV‐OH 13,000 380
Pascagoula,MS 59,000 33,000
Pensacola,FL 24,000 10,000
Phoenix‐Mesa,AZ 51,000 28,000
Pittsburgh‐BeaverValley,PA 82,000 49,000
Portland,OR‐WA 37,000 11,000
Providence(AllRI),RI 310
Raleigh‐Durham‐ChapelHill,NC 25,000 6,200
RapidCity,SD 4,400 700
Reno,NV 9,700 1,300
Richmond‐Petersburg,VA 30,000 15,000
Roanoke,VA 7,700
RockyMount,NC 710 20
SacramentoMetro,CA 11,000 8,900
SaltLakeCity‐Ogden‐Provo,UT 43,000 24,000
SanAntonio,TX 39,000 19,000
SanJoaquinValley,CA
b
180,000 150,000
SchoolcraftCo,MI 1,000
Seattle,WA 98,000 48,000
Somerset,KY 450
Spokane,WA 2 ,700
Springfield,MO 90
StLouis,MO‐IL 230,000 120,000
Steubenville‐Weirton,OH‐WV 260
TampaBay‐St.Petersburg,FL 140,000 52,000
Toledo,OH 2,000 1,000
Tulsa,OK 130,000 55,000
Tupelo,MS 1,600
Washington,DC‐MD‐VA 2,500 1,000
Waterloo,IA 19
WesternLakeMichigan,IL‐IN‐WI 420,000 420,000
Wheeling,WV‐OH 130
Wichita,KS 26,000 11,000
Williston,ND 620
Wytheville,VA 240
a
Estimatesareroundedtotwosignificantfigures.Assuch,totalswillnotsumdowncolumns.
b
TheLosAngelesSouthCoastAirBasinandSanJoaquinValleyareasofCAwillbereducingemissionstomeetthe
0.08ppmstandardintheyear2020.Theyareincludedinthisanalysisduetotheirinfluenceontheattainmentof
theSacramentogeographicarea.