temporal scale analysis of airpact5 performance for o...
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Temporal scale analysis of AIRPACT5 Performance for O3 and PM2.5 in the Pacific Northwest
Tsengel Nergui, Serena Chung*, Yunha Lee, Joseph Vaughan, and Brian Lamb
Laboratory for Atmospheric Research, Washington State University*U.S. Environmental Protection Agency
NW-AIRQUEST Annual Meeting, June 14-16, 2017, Richland, WA
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OperationalEvaluationfor2016:Summer(49sites):Goodagreement(MFBs>± 30%at11sites)Winter(28sites):Overestimation(MFBs>± 30%at21sites)
Ozone: Mean Fractional Error (MFE) and Mean Fractional Bias (MFB)
BenchmarkforO3:NME<±15%andNME<35%(aboutsameasMFB<±30%andMFE<50%)
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PM2.5 : Mean Fractional Error (MFE) and Mean Fractional Bias (MFB)
OperationalEvaluationfor2016:Summer(103sites):Underestimationatmostsites(~60%MFBs)Winter(129sites):Overestimatedinurban(~70%MFBs),underestimatedinruralareas(~60%MFBs)
BenchmarkforPM2.5:MFB<±30%andMFE<50%
Objective
To assess the AIRPACT-5 ability for reproducing the important temporal scale components embedded in observed O3 and PM2.5 concentrations
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DataandMethod
• HourlyO3 concentrations,~50AQSsites
• HourlyPM2.5 concentrations,~140AQSsites
• TheAIRPACT-5outputsfor2016
• Spectralanalysis(temporalscaleseparation)usingtheKolmogorov–Zurbenko(KZ)filtering
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Analyzingatimeseriesindistincttemporalscales
Kolmogorov–Zurbenko(KZ)filter(Zurbenko,1986)
Atimeseries=Mean+Varioustemporalscalefluctuations+Trend
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Example:O3 timeseriesdecomposition(Site#530090013,RURAL/Forest,WA)
Baselin
e(>21
days)
— Seasonalvariationofsolarradiation
— Depositionduetochangesinsurfaceproperties
— Slowchangingprecursors’emissions
Syno
ptic
(3-21days) — Changesinweatherconditions
(stagnanthighpressuresystem,frontalpassage)
— Associatedchangesinmixingheights,cloudcover,andcirculationpatterns
Diurna
l(11-36
hrs) — Diurnalpatternofsolarradiation
— Differencebetweendaytimeproduction&nighttimeremovalfor O3
Intrad
ay(<11
hrs) —Convectivemixing
— Localemissionschanges— Photolysisratesassociatedwith
theactinicflux
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Variance Contributions Component Correlations(7sites)
(25sites)
Summertime O3:
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Findings for summertime O3:
• VariancecontributionsforobservedO3:― Diurnal(~67%),Synoptic(~15%),Baseline(~12%),and
Intraday(~5%)components.― Diurnalcomponentishigherinurbanvs.ruralareas(72%vs.
64%).― Thebaseline/synopticcomponentstendtobehigherinruralvs.
urbanareas(18%vs.12%).• Modelunderestimatedvariancecontributionfordiurnal(~16%less)
andoverestimatedforsynoptic(~15%more)andbaseline(~6%more)components.
• DiurnalcomponentwasthebestcorrelatedbecauseofinherentcyclicalnatureofthediurnalprocessforO3production/destruction.
• Correlationsatthebaselinescalearebetterthanthoseforsynopticandintradaytimescales,butvarybysite(medianr =0.6,MAD= 0.3).
HOURLYPM2.5CONCENTRATIONS(88101:FRM/FEM~40SITES)(88502:NON-FRM/FEM~100SITES)
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Variance Contributions Component Correlations(45sites)
(39sites)
Wintertime PM2.5:
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• VariancecontributionsforobservedPM2.5:― Diurnal(~30%),baseline(~26%),synoptic(~25%),and
Intraday(~15%)components.― Contributionofintradaycomponentincreasesfromurbanto
ruralsites(13%to18%).• Modeltendstogiveslightlyhighermeanforurban/suburbansites
andlowerforruralsites.• Themodelunderestimatedvariancesoftheintraday,diurnal,and
baselinecomponents(~10%lessforeach)andoverestimatedforsynopticcomponent(~7%more).
• Correlationsbetweenmodeledvs.observedcomponentsincreasefromdiurnaltobaseline,butdisplayalargevariability(medianR=0.2-0.8,MAD= 0.3).
Findings for wintertime PM2.5:
Spectral analysis shows…• The diurnal and baseline components
are the most important temporal scales for O3 and PM2.5 concentrations.
• Improving the baseline component:
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Baseline (>21 days)— Seasonal variation of solar radiation— Deposition due to changes in surface
properties— Seasonal allocation of O3 precursors’
emissions
Variancecontributionsfromdifferenttemporalscalesbasedonentiretimeseries
What next?
THANKYOU.
FEEDBACKSANDQUESTIONS?
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