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CESMTutorial2016,Chemistry
AtmosphericModelingwithInterac5veChemistry
PresentedbySimoneTilmesACOM/CGD• Runningwithfully-coupledchemistry,differentchemical
mechanismversions• DescripJonofsecondaryorganicaerosolsasparameterizedin
CAM-chem• EvaluaJon• OtherapplicaJonsofCAMchem
CESMTutorial2016,Chemistry
TroposphericChemistryandAerosols
Photo-chemistryGas-phasechemistryHeterogeneouschemistryAerosolformaJonOHdeterminesthelifeJmeofMethane
CESMTutorial2016,Chemistry
ModelingwithChemistryAvailablechemicalmechanismsinCAM-ChemSuperfastChemistry(CAM4/5):
12species,simplechemistrymechanism,CH4prescribedLINOZ+Cariolleinstratosphere,fullycoupled
BulkAerosolModel(BAM)(CAM4/5):IncludesBlackCarbon,OrganicCarbon,SeaSalt,Dust(prescribedmonthlyfieldsofCO2,CH4,O3,OH,HO2,NO2,N2O,SO2/SO4)
Troposphericchemistry(trop_mozart)(CAM4/5):Troposphericmechanism,over100species(MOZART:Emmonsetal.,2010)Stratosphericchemistryisprescribedabout50hPa:(O3,HNO3,CH4,CO)Emissions,Dry/WetDeposiJonSecondaryOrganicaerosols
Plusstratosphericchemistry(trop-stratmozart)(CAM4/5):TroposphericandStratosphericmechanism(~122species)includingstratosphericheterogeneousreacJons,about300reacJons(similartoWACCM)(Lamarqueetal.,2012,Tilmesetal.,2015)
CESMTutorial2016,Chemistry
ChemistryinCESMCAM5
EmissionsofSO2AndAerosolsAnthropogenicBiomassburningBiogenic
Removal:Wet/DryDeposiJon
Land/OceanBiosphere
Radia5onClouds(indirecteffect)Dynamics/H2O
Snow/Ice
SimpleChemistry
AerosolformaJon(MAM)
CESMTutorial2016,Chemistry
ChemistryinCESMCAM5-Chem
ComplexChemicalReacJons
(chemicalmechanism)AerosolformaJon
EmissionsAnthropogenicBiomassburningBiogenic
Removal:Wet/DryDeposiJon
Land/OceanBiosphere
Radia5onClouds(indirecteffect)Dynamics/H2O
Snow/Ice
MEG
AN
CAM4-chemdoesnotincludecouplingbetweenaerosolsandclouds
CESMTutorial2016,Chemistry
1.SoluJons:listsallchemicalconsJtuenciesanddefineswhattheyare,e.g.• IncludesFixedSpecies:listsofchemicalspeciesthatdonotchange• AndNon-transportedComponents(veryshortlifeJme)2.SoluJonclasses,dividessoluJonspeciesintoexplicitandimplicit(shorterJmestepinthesolver)4.Chemistry:• Photolysis:[jo3_a]O3+hv->O1D+O2• Gas-phasechemistry:[O_O3]O+O3->2*O2;8.00e-12,-2060.• HeterogeneousReacJon[usr_N2O5_aer]N2O5->2*HNO3
ModelingwithChemistryChemicalMechanism:includessetofequaJonsThechemistrypreprocessor:toolthatgeneratesCAMFortransourcecode;numericallysolveasetofdifferenJalequaJonswhichrepresentthechemicalreacJons->temporalevoluJonofthechemicaltracers
rates(temperaturedependenceetc.)
ISOP -> C5H8,BIGENE->C4H8,BIGALK->C5H12,MEK->C4H8O
UserdefinedreacJons:aredefinedinthemodelcode:mo_usrrxt.F90
CESMTutorial2016,Chemistry
Emissions:aredefinedintheuser_nl_camnamelistvariable• Dependingonmechanism,differentspeciesneedtobeemiled
Emissions
• Chemicalcomponentsarecurrentlyemiledatthesurface.
• Includeanthropogenic,biomassburningandfireemissions.
• BiogenicemissionscanbecalculatedbyMEGAN(makesuretonotdouble-count)
• Comingsoon:fireemissionsmaybecalculatedbythelandmodel
->Carefulifchangingemissions,tomatchyourmodelsetup
CESMTutorial2016,Chemistry
Emissions:surfaceemissionsfields,fixedboundarycondiJons,calculatedusingvegetaJontype(biogenic,VOC)
Lamarqueetal.,2010
CESMTutorial2016,Chemistry
OrganicAerosols(simulatedinCAM4-Chem)
FromC.Heald,MITCambridge
Forma5onofSOA• Emissionsof
volaJleorganiccarbons
• FormaJonofSemi-VolaJles
• EmissionsofPOM->SOA
CESMTutorial2016,Chemistry
WaterSolub
ility
log(H)(M
/atm
)
Vola=lity,log(C*),μg/m3
COCO2
Oxidative Chemistry
Fragmentation
SVOCi
SVOCn
SOA
dry & wet depo.
of SOA and soluble SVOC Emissions
S/IVOC,VOC
Removal by photolysis
+Ox
Simplis=cwaysoftrea=ngthecomplexSOAlifecycle
Fi0edtochamberdata
VOCSOASOAyield:netconversion
Vola;lityBasisSet VOC+OH,O3
2-productsBAM VOC+OH,O3
WithSolubilityaxis
VOCCAM5BASE SOG directlyemitsSOG
MorephysicalapproachDirectcouplingtobiogenicemissionschangesfromMEGAN->couplesSOAforma5ontolanduseandclimatechange->onlyworksinfullchemistryversionatthispoint
NewSOAapproachinCESM2CAM5-Chem/WACCM(nextyear)
CESMTutorial2016,Chemistry
Aerosols:CAM5ModalAerosolModel(MAM3/7)
Liuetal.,2011
a2 a1 a3
a2 a1
a3 a6
a5a4
a7
MAM3
MAM7
712 X. Liu et al.: Toward a minimal representation of aerosols in climate models
Table 1. Geometric standard deviations (�g) and dry diameter sizeranges for MAM3 and MAM7 modes. The size range values arethe 10th and 90th percentiles of the global annual average numberdistribution for the modes (from simulations presented in Sect. 3).
Mode �g Size range (µm)
MAM3
Aitken 1.6 0.015–0.053Accumulation 1.8 0.058–0.27Coarse 1.8 0.80–3.65
MAM7
Aitken 1.6 0.015–0.052Accumulation 1.8 0.056–0.26Primary Carbon 1.6 0.039–0.13Fine Sea Salt 2.0 0.095–0.56Fine Dust 1.8 0.14–0.62Coarse Sea Salt 2.0 0.63–3.70Coarse Dust 1.8 0.59–2.75
single coarse mode based on the recognition that sources ofdust and sea salt are geographically separated. Although dustis much less soluble than sea salt, it readily absorbs water(Koretsky et al., 1997) and activates similarly as CCN (Ku-mar et al., 2009), particularly when coated by species likesulfate and organic. So dust is likely to be removed by wetdeposition almost as easily as sea salt, and the merging ofdust and sea salt in a single mode is unlikely to introducesubstantial error into our simulations; (3) the fine dust andsea salt modes are similarly merged with the accumulationmode; (4) sulfate is partially neutralized by ammonium inthe form of NH4HSO4, so that ammonium is effectively pre-scribed and NH3 is not simulated. The total number of trans-ported aerosol tracers in MAM3 is 15. The transported gasspecies are SO2, H2O2, DMS, H2SO4, and a lumped semi-volatile organic species. The prescribed standard deviationand the typical size range for each mode are given in Table 1.
3 Aerosol distributions and budgets
All simulations are performed with the stand-alone versionCAM5.1, using climatological sea surface temperature andsea ice and anthropogenic aerosol and precursor gas emis-sions for the year 2000. The model is integrated for 6 yr, andresults from the last 5 yr are used in this study. In this sectionmodel-simulated global distributions and budgets for differ-ent aerosol species are analyzed and comparisons are madebetween MAM3 and MAM7.
65
Figure 2. Predicted species for interstitial and cloud-borne component of each aerosol
mode in MAM3.
Fig. 2. Predicted species for interstitial and cloud-borne componentof each aerosol mode in MAM3.
3.1 Simulated global aerosol distributions
Figures 3a and b show annual mean vertically integrated (col-umn burden) mass concentrations of sulfate, BC, POM, SOA,dust and sea salt from MAM3, and the relative difference ofthese concentrations between MAM7 and MAM3, respec-tively. These aerosol species concentrations are summationsover all available modes (e.g., the POM concentration inMAM7 includes contributions from the primary carbon andaccumulation modes). Sulfate has maximum concentrationsin the industrial regions (e.g., East Asia, Europe, and NorthAmerica). The distribution patterns and absolute values ofsulfate concentration are very similar (mostly within 10%)between MAM3 andMAM7 (Fig. 3b). This is expected sincemost of sulfate burden (⇠90%) is in the accumulation mode(see sulfate budget in Sect. 3.2). This is also the case forSOA, which has high concentrations over the industrial re-gions and tropical regions with strong biogenic emissions(e.g., Central Africa and South America). The differencesbetween MAM3 and MAM7 are generally small (mostlywithin 10%). POM column concentrations have spatial dis-tributions and magnitudes similar to SOA, but are lower inEurope, Northeastern US and South America, and higher inCentral Africa. The distribution patterns of BC burden con-centrations are similar to those of POM, but have relativelylarger contributions from the industrial regions because ofdifferent emission factors of BC/POM from different sectors.Dust burden concentrations have maxima over strong sourceregions (e.g., Northern Africa, Southwest and Central Asia,and Australia) and over the outflow regions (e.g., in the At-lantic and in the western Pacific). Sea salt burden concentra-tions are high over the storm track regions (e.g., the SouthernOcean) where wind speeds and emissions are higher, and inthe subtropics of both hemispheres where precipitation scav-enging is weaker.One major difference between MAM3 and MAM7 is the
treatment of primary carbonaceous aerosols (POM and BC).These aerosols are instantaneously mixed with sulfate andother components in the accumulation mode in MAM3 oncethey are emitted, and thus are subject to wet removal byprecipitation due to the high hygroscopicity of sulfate. InMAM7, carbonaceous aerosols are emitted in the primary
Geosci. Model Dev., 5, 709–739, 2012 www.geosci-model-dev.net/5/709/2012/
CESMTutorial2016,Chemistry
DifferencesinAerosols,CAM4andCAM5Annual SummerWinter
Sulfate:SO4SO4(a1,a2,a3)SO4(a1,a2,a4-7)
BC:CB1,CB2BC(a1)BC(a1,a3)
OC:CB1,CB2,SOApom(a1,a3),soa(a1,a2)pom(a1,a3),soa(a1,a2) SurfacelayerconcentraJon(mg/m3)
IMPROVECAM4-BAMCAM5-MAM3CAM5-MAM7
CESMTutorial2016,Chemistry
Scien5ficallyValidatedChemistryVersionshZp://www.cesm.ucar.edu/models/scien5fically-supported.htmlTilmes,Setal.,2015:DescripJonandevaluaJonoftroposphericchemistryandaerosolsintheCommunityEarthSystemModel(CESM1.2),Geosci.ModelDev.,8,1395-1426,doi:10.5194/gmd-8-1395-2015,2015.(hlp://www.geosci-model-dev.net/8/1395/2015/gmd-8-1395-2015.html)
CESMTutorial2016,Chemistry
Evalua5onoftheModel
AMWGDiagnos5cPackageincludesChemistryEvalua5on
CESMTutorial2016,Chemistry
Evalua5onoftheModelAMWGDiagnos5cPackageincludesChemistryEvalua5on
CESMTutorial2016,Chemistry
CCMISimula5onsinComparisontoOzonesondeData:Mid-La5tudes,500hPa
EasternUS900hPa
50hPa250hPa
500hPa
WACCMREFC1CAM-ChemREFC1 1995-2004average
CESMTutorial2016,Chemistry
PerformanceoftheModels:CarbonMonoxideinComparisontoMOPITT
CESMTutorial2016,Chemistry
ChangingChemistryChemicalMechanism:addorchangetracersandreacJons(e.g.Taggingoftracers)Emissions:includerequiredemissionsDeposi5on:adddryandwetdeposiJoncomponentstothemodelcode
RunningwithMEGANEmissions:hlp://www.cesm.ucar.edu/working_groups/Chemistry/running_CESM1_MEGANNv0408.pdfRoadmaptorunandchangechemistry(CESM1.2.0)hlp://www.cesm.ucar.edu/working_groups/Chemistry/roadmap_cesm120.pdf
CESMTutorial2016,Chemistry
TheModelforOzoneandRelatedchemicalTracers(MOZART4)Emissions:StreetsARCTASemissions+dailyfires(C.Wiedinmyer)VerJcalInjecJonofFireEmissionbetween0-6km
South Asia
O3,CO,BCtagswithOfflineMeteorologyEmmonsetal.,2012,GMD
CESMTutorial2016,Chemistry
ImportanceofAnthropogenicCOEmissionswithout South Asia and SH South Asia and SH only
April
COaveragedcolumnbetweensurf.and200hPa
CESMTutorial2016,Chemistry
without South Asia and SH South Asia and SH only April
ImportanceofAnthropogenicCOEmissions
COaveragedcolumnbetweensurf.and200hPa
CESMTutorial2016,Chemistry
without South Asia and SH South Asia and SH only April
ImportanceofAnthropogenicCOEmissions
COaveragedcolumnbetweensurf.and200hPa
CESMTutorial2016,Chemistry
ObservationsØ MOPITT-CO, IASI-CO, MODIS AODØ Meteorological observations
Observations, plus errors
Ensemble of optimized initial conditions every 6 hours
DARTAssimilation
-> update CO concentrationAnd Meteorology
Weighted mean of observations and model knowing respective errors
CESMCommunityAtmosphereModel(CAMandCAM-Chem)Ensembleofatmosphericstatewithchemistry
Ø Ensemble of emissions (+CO tags)
Ø Ensemble of transportØ Ensemble of
deposition (land model)
Ø Ensemble of Chemistry
CESMTutorial2016,Chemistry
CAM-chemforecas5ng
FortheNASAKORUS-AQexperiment,CAM-chem/DARTforecastswererun
MOPITTCOretrievalswereassimilatedeachday(30-memberensemble)
GEOS-5meteorologywasusedtodriveasingleCAM-chemforecastsimulaJon
TaggedCOtracerswereincludedtotracksourcecontribuJonstoKorea
hlp://www.acom.ucar.edu/acresp/korus-aq/
CESMTutorial2016,Chemistry
WACCMandCAM-ChemCustomerSupport
CGD Forum: http://bb.cgd.ucar.edu/ Mike Mills WACCM Liaison [email protected] (303) 497-1425 Simone Tilmes CAM-Chem Liaison [email protected] (303) 497-1445