Impacts of the Legalization of Marijuana on Emissions and ... · Impacts of the Legalization of...

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ImpactsoftheLegalizationofMarijuanaonEmissionsandAirQualityinUSKirsti Ashworth1 andChristineWiedinmyer2

1UniversityofMichigan,2NationalCenterforAtmosphericResearch

1.INTRODUCTIONRecentchangesinUSstateregulationsallowforlegalmarijuanacultivationfacilities(MCFs,Figure1)anduseinColoradoandWashington.Marijuanaplants(Cannabisspp.)emitprimarilybiologicalparticles(e.g.,Fungi,Pollen[1,2])andahostofbiogenicvolatileorganiccompounds(VOCs).Theemissions,however,areveryuncertainandarenotwellconstrained.Wehypothesizethat,asthenumberofMCFsincreaseacrossthesestates,particularlyinandnearurbanareas,emissionsofbiogenicVOCswillincreaseandpotentiallyresultinimpactsonregionalairquality(O3 andPM).

Questions:WhatcompoundsarebeingemittedbyCannabisspp.andhowmuch?WhatisemittedreleasedtotheatmospherefromindoorandoutdoorMCFs?AretheemissionsfromMCFssignificantonlocalandregionalscales?Dotheseemissionsimpactozoneandparticulatematterformationonlocalandregionalscales?

AstheregulationsonmarijuanagrowingandusechangeacrosstheUS,theimpactsofthesechangesshouldbeevaluated.Byperformingassessmentsoftheemissionsandairqualityimpacts(orlackof)thatresultfromincreasesinMCFsinColoradoandWashingtonstates,wecanprovideaframeworkofforunderstandingtheairqualityimpactsofthechangingregulationsofmarijuanagrowingandusageacrosstheUS.

2.VOLATILESFROMCANNABISSPP.MeasurementsofemissionsfromCannabisspp.arelimited.EmissionfactorsforCannabisspp. forbiogenicVOCemissionsmodelingarenotcurrentlyavailable.

KnownvolatilesfromCannabis spp. includemonoterpenes (a-pinene,b-mycrene,b-pinene,andlimonene),delta-9-tetrahydrocannabinol(THC,C21H30O2),oxygenatedVOCs,andsesquiterpenes (Figure2;[3-6]).

Incultivationfacilities,a-pinene,b-mycrene,b-pinene,andlimonenewerefoundtobepresentinhighconcentrations(50to100ppb)inthegrowingrooms.AlloftheairborneTHClevelswerebelowthedetectionlevel(0.10μg/sample)exceptforonesample(0.70μg/sample)thatwasnearthedetectionlimit[2].

3.QUICKEMISSIONESTIMATESFORCOLORADOCurrently,inColorado,marijuanacultivationfacilitiesmustbeinafullyenclosed,lockedarea.Asof15June2014,thereareontheorderof1,000cultivationsstatewide.Thesizeandlocationofthesearenotknownatthispoint,butthenumberoffacilitiesischangingrapidly(N.Bryant,StateofColorado,Personalcommunications,13June2014).

Jankauskiene andGruzdeviene [7]reportthatthedrybiomassfromtwocultivarsofCannabissativa rangedfrom162– 227g/m2 (average195g/m2).

AssuminganaverageMCFsizeof½hectare(5,000m2),thatequatesto973metrictonsofdrybiomass.Atotalmonoterpene emissionfactorof5mgg-1 hr-1,assumingthatCannabisspp. havetotalmonoterpeneemissionfactorsonthesameorderasotherhighemittingspecies(e.g.,Eucalytpus spp.andArtemisiaspp.(sage))[8].

Giventheseinitialassumptions,totalmonoterpene emissionsfromMCFsareontheorderof43metrictonyr-1.Theseestimationmethodsarevalidforcultivationfacilitiesintheoutdoors.However,inColorado,whereMCFsmustbeenclosed,emissionstotheatmospherewillalsobereduced.There,theamountofbiogenicVOCsreleasedintotheatmospherewillbeafractionofthetotalanddependentontheventilationsystemateachMCF.

4.IMPLICATIONSOverall,thesefirstestimatesarefairlysmallcomparedtootherVOCsourcesinthestateofColorado.However,asthenumberoffacilitiesincreases,thepotentialtoemitsignificantamountsofbiogenicVOCstotheatmospherebecomesapossibility.Thiscouldbeveryimportantwhenevaluatingimpactsonozoneandparticulatematterformation.

IntheFrontRangeregionofColorado,muchoftheDenvermetropolitanareaincludingDenver,Boulder,andpartsofWeldcountieshaveozoneproductionthatisVOC-limited(G.Tonnesson,US.EPARegion08,Personalcommunications,10June2014).Therefore,itispossiblethatincreasesinVOCs,includingemissionsfromMCFs,couldcauseincreasesinozoneconcentrationsincertainareas.

Figure2:VolatilesfromCannabisspp.

alpha-pinene

beta-pinene

myrcene

limonene

beta-caryophellene

ocimene

otherMTs&SQTs

other

oxygenatedVOCs

Figure1:PictureofMarijuanaCultivationFacility

5.FUTUREWORKTheemissionsproposedherearehighlyuncertainduetothelackofdataneededtobetterconstraintheestimationprocess.WerecommendthefollowingforadvancingtheknowledgewithregardtoquantifyingtheatmosphericimpactsofthelegalizationofmarijuanaintheUS:• QuantifyemissionfactorsandbiomassdensitiesassociatedwithCannabis

spp.• Determinethenumber,sizeandlocationofMCFsinlegalizedareas• Performsensitivitysimulationswithchemicaltransportmodelsto

determineif,where,andwhenemissionsfromMCFsareimportanttoozoneandparticulateformation.

References[1]N.Aboulaich,M.M.Trigo,H.Bouziane,B.Cabezudo,M.Recio,M.ElKadiri,andM.Ater,VariationsandoriginoftheatmosphericpollenofCannabisdetectedintheprovinceofTetouan (NWMorocco):2008-2010,inScienceoftheTotalEnvironment,2013,pp.413-419.[2]J.W.Martyny,K.A.Serrano,J.W.Schaeffer,andM.V.VanDyke,PotentialExposuresAssociatedwithIndoorMarijuanaGrowingOperations,inJournalofOccupationalandEnvironmentalHygiene,2013,pp.622-639.[3]L.V.S.Hood,M.E.Dames,andG.T.Barry,HEADSPACEVOLATILESOFMARIHUANA,inNature,1973,pp.402-403.[4]P.Rovellini,L.Folegatti,D.Baglio,S.DeCesarei,P.Fusari,S.Venturini,andA.Cavalieri,ChemicalcharacterizationofoilobtainedbythecoldpressingofCannabissativaL.seeds,inRivista Italiana Delle Sostanze Grasse,2013,pp.139-152.[5]K.W.Hillig,Achemotaxonomicanalysisofterpenoid variationinCannabis,inBiochemicalSystematicsandEcology,2004,pp.875-891.[6]Z.Mehmedic,D.Slade,H.Denham,S.Chandra,D.Stanford,I.A.Khan,andM.A.ElSohly,Indoorandoutdoorcultivationofcannabis:Isthereaneffectonthechemicalcompositionofthevolatileoil?,inPlanta Medica,2008,pp.328-328.[7]Z.Jankauskiene,andE.Gruzdeviene,EvaluationofCannabissativacultivarsinLithuania,inZemdirbyste-Agriculture,2010,pp.87-96.[8]C.Wiedinmyer,A.Guenther,P.Harley,N.Hewitt,C.Geron,P.Artaxo,R.Steinbrecher,andR.Rasmussen,GlobalOrganicEmissionsfromVegetation,inEmissionsofAtmosphericTraceCompounds,C.Granier,P.Artaxo andC.E.Reeveseds.,KluwerAcademicPublishers,Dordrecht,TheNetherlands,2004,pp.115-170.

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