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1.NitrousOxide:TheThirdLargestGreenhouseGasinTheWorld
Emissionsofnitrousoxide(N₂O),amajorGHG,aregainingincreasedattention.DatafromtheGlobalAtmosphericResearchEmissionsDatabase(EDGAR)indicatesthatglobalN₂Oemissionsin2023reachedapproximately2.5billiontonsofcarbondioxideequivalent(CO2e),accountingfor5%ofglobalGHGemissions.ThismakesN₂OthethirdlargestGHGaftercarbondioxideandmethane.1AlthoughN₂Oemissionsarerelativelylowercomparedtocarbondioxide,ithasastrongwarmingeffect,withawarmingpotentialofabout273timesgreaterthancarbondioxideovera100-yearperiod—andlongatmosphericlifespanofaround120years.2The2024globalN₂ObudgetalsorevealsthatN₂Oemissionsfromhumanactivitieshaveincreasedby40%between1980and2020.3Inaddition,researchshowsthat,withoutadditionalmeasures,N₂Oemissionsareexpectedtorisebyapproximately30%by2050comparedto2020.4Therefore,takingearlyactiontoreduceN₂Oemissionsisessentialtomitigateclimatechange.
Inadditiontocontributingtoglobalwarming,N₂Oemissionssignificantlydepletetheozonelayer,increasinghumanexposuretoharmfulradiation.WhiletheMontrealProtocolhasmadesubstantialprogressinrestoringtheozonelayerbyregulatingmajorozone-depletingsubstances,N₂Oemissionsremainoutsideitsscope.Asaresult,N₂Ohasbecometheprimarygasesdepletingtheozonelayer.5TheUnitedNationsEnvironmentProgramme(UNEP)highlightedthisissueinits2022scientificassessmentofozonedepletion.ThereportfoundthatN₂Oemissions(usingCFC-11equivalent)fromhumanactivitiesbetween2016and2020weretwiceashighasglobalemissionsofCFCsin2020.6Furthermore,theseN₂Oemissionsareexpectedtodelaytheozonelayer’srecovery,underscoringtheneedfortargetedmitigationefforts.
1Crippa,M.,Guizzardi,D.,Pagani,F.,Banja,M.,Muntean,M.,Schaaf,E.,Monforti-Ferrario,F.,Becker,W.E.,Quadrelli,R.,RisquezMartin,A.,Taghavi-Moharamli,P.,Köykkä,J.,Grassi,G.,Rossi,S.,Melo,J.,Oom,D.,Branco,A.,San-Miguel,J.,Manca,G.,Pisoni,E.,Vignati,E.,&Pekar,F.(2024).GHGemissionsofallworldcountries.PublicationsOfficeoftheEuropeanUnion.
/10.2760/4002897
2TheGWPvaluesusedintheIPCCSixthAssessmentReportareusedhere
3Tian,H.,Pan,N.,Thompson,R.L.,Canadell,J.G.,Suntharalingam,P.,Regnier,P.,...&Zhu,Q.(2023).Globalnitrousoxidebudget1980–2020.EarthSystemScienceDataDiscussions,2023,1-98.
4ValerieVolcovici.(October31,2024).WorldwillmissParisclimatetargetasnitrousoxiderises,reportsays.Reuters.
/business/environment/world-will-miss-paris-climate-target-nitrous-oxide-rises-report-says-2024-10-31/
5Alcamo,J.,&Bouwman,L.(2013).DrawingdownN₂Otoprotectclimateandtheozonelayer.UnitedNationsEnvironmentProgramme.
6UNEP.(2023).ScientificAssessmentoftheOzoneLayerDepletion:2022.
/system/files/documents/Scientific-Assessment-of-Ozone-Depletion-2022.pdf
ReducingN₂Oemissionscanalsoofferadditionalenvironmentalbenefits,asnitrogenoxides(NOx),acommonairpollutantfromstationarysources,containsmallamountsofN₂O.LoweringN₂Oemissionsnotonlyhelpswithclimatemitigationbutalsocontributestoimprovingairqualitybyreducingphotochemicalsmogandminimizingsoilacidification.
2.CurrentStatusandTrendsofN₂OEmissions
2.1.GlobalN₂OEmissions:HumanActivitiesDrivetheIncrease
Whilenaturalsourcessuchassoil,oceans,andtheatmospherecontributetoglobalN₂Oemissions,thesedonotresultinsignificantatmosphericaccumulation,asnaturalsystemscangraduallybalancethemovertime.7ThecurrentriseinN₂Oemissionsisprimarilydrivenbyhumanactivities.
In2019,agriculturewasthelargestcontributor,responsiblefor76%ofanthropogenicN₂Oemissions,followedbyenergy-relatedactivities(10%),industrialprocesses(8%),andwastemanagement(5%).8
7Alcamo,J.,&Bouwman,L.(2013).DrawingdownN₂Otoprotectclimateandtheozonelayer.UnitedNationsEnvironmentProgramme.
8ClimateWatch.(2019).
/
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Agriculture
N₂Oemissionsprimarilyarisefromagriculturallandandmanuremanagement.Whenfarmersusenitrogen-basedfertilizers,N₂Oisreleasedintothesoil.Additionally,manurefromlivestockandpoultrystoredortreatedcanalsoproduceN₂Othroughnaturalchemicalprocesses.
Energyactivities
Emissionsaremainlyfromthecombustionoffossilfuelsandbiomass.
Industrialprocess
Majorsourcesincludetheproductionofadipicandnitricacid.Adipicacidisprimarilyusedinnylonandpolyurethane.Nitricacidisessentialforthemanufactureofsyntheticfertilizers,pesticides,andrubber.
Wastemanagement
N₂Oemissionsmainlycomefromdomesticsewageandindustrialwastewatertreatment.
2.2.China’sN₂OEmissions:AgricultureandIndustryAreKeyContributors
AccordingtotheThirdBiennialUpdateReportonClimateChangeofthePeople'sRepublicofChina(Figure2),China'sN₂Oemissionsin2018reached1.915milliontons,accountingfor5%ofthenation'stotalGHGemissions(excludingLULUCF).Thelargestsourcewasagriculture(943,000tonsor49.2%),followedbyindustrialprocesses(441,000tonsor23%),energyactivities(411,000tonsor21.5%),andwastemanagement(119,000tonsor6.2%).
HistoricaldatafromChina’snationalgreenhousegasinventoryrevealsthatN₂Oemissionsrosesharplyby36%from2005to2014butstabilizedbetween2014and2018(Figure1).However,projectionsindicatethatwithoutstrongerpolicyintervention,emissionscouldcontinuetorise,potentiallyreachingbetween620and790milliontonsofCO2eby2050(Figure3).
waste
wastewater
treatment
Energy
Energy
Industry
Chemica
Industry
Industry
Agricutura
Land
Manure
Management
Figure1:China'sN₂Oemissions(10,000tons)Figure2:China'sN₂OemissionsbySector(2018)
Agricuture
Agricuture
Source:NationalCommunicationonClimateChangeandtheSecondandThirdBiennialUpdatesofthePeople'sRepublicofChinaonClimateChange
Industry
Energy
waste
Figure1:ProjectedN₂OemissiontrendsinChinaacrossdifferentstudies(MMTCO2e,GWP=298)
Source:Tengetal,(2019),9WRIdatafromSong,R.(2019),10EPAdatafromUSEPA.(2019),11iGDPdataisbasedon
EPSmodelanalysis.
9Teng,F.,Su,X.,&Wang,X.(2019).CanChinapeakitsnon-CO2GHGemissionsbefore2030byimplementingitsnationallydeterminedcontribution?EnvironmentalScience&Technology,53(21),12168–12176
10Song,R.(2019).OpportunitiestoAdvanceMitigationAmbitioninChina:Non-CO2GreenhouseGasEmissions.WorldResourcesInstitute.
11USEPA.(2019).GlobalNon-CO2GreenhouseGasEmissionProjections&MitigationPotential2015–2050.USEnvironmentalProtectionAgency.
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3.ProgressonN₂OEmissionReductionPolicies
3.1.ProgressinGlobalN₂OEmissionsReduction
CountriesandregionsareincreasinglytakingproactivestepstoreduceN₂Oemissions.IntheEuropeanUnion(EU),theFarmtoForkStrategyaimstoenhancesoilhealthandcutnitrogenfertilizeruseby20%by2030,aspartoftheGreenNewDeal.12AustraliaisprovidingfinancialincentivesthroughtheEmissionsReductionFundtoencouragebusinessesandindividualstodecreaseN₂Oemissionsinagriculture.13Since2013,theEUhasincludedtheregulationofN₂Oemissionsfromnitricacidandadipicacidproductioninitscarbonmarket.14Additionally,theUnitedStatesrecentlyannouncedthatmajorchemicalcompanieswillaimtoreduceN₂Oemissionsfromtheindustrialsectorbyabout50%by2025,relativeto2020levels.15
InternationalcollaborationonN₂Oreductionisalsogainingmomentum.DuringCOP21in2015,GermanylaunchedtheNitricAcidClimateActionGroup(NACAG)topromotetheinstallationofN₂Oemissionreductiontechnologiesatnitricacidandureaplantsglobally,providingtechnicalandfinancialsupporttoparticipatingcountries.Sixteencountries,includingArgentina,Indonesia,Mexico,andThailand,havejoinedthisinitiative.16In2023,ArgentinabeganinstallingN₂OemissionreductiondevicesandmonitoringequipmentinnitricacidproductionfacilitieswithNACAG'ssupport.17
TheUnitedStatesandBrazilalsolaunchedaresearchcollaborationcalled"Fertilize4Life"in2023,focusingonimprovingfertilizerapplicationefficiencyandreducingGHGemissionsfromfertilizers.ThisinitiativeispartoftheGlobalFertilizerChallengeinitiatedbytheU.S.18Furthermore,inthe2023SunnylandsStatement
12EuropeanCommision.(2020).FarmtoForkStrategy:
https://food.ec.europa.eu/system/files/2020-05/f2f_action-
plan_2020_strategy-info_en.pdf
13AustraliaGovernment:EmissionsReductionFund.
.au/agriculture-land/farm-food-
drought/climatechange/mitigation/cfi
14Oeko-Institut.(2021).N₂Omitigationpotentialsandcostsinthenitricacidsector:A2020assessmentfortheNitricAcidClimateActionGroup(NACAG).Oeko-Institut.
15TheWhiteHouse.(July23,2024)
./briefing-room/statements-releases/2024/07/23/fact-sheet-
biden-harris-administration-announces-new-actions-to-detect-and-reduce-climate-super-
pollutants/#:~:text=New%20Industry%20Leadership%20to%20Reduce,by%20over%2050%25%20since%202020.
16NACAG.IntroducingNitricAcidClimateActionGroup:
/
17NACAG.(2023).ArgentinatakesfurtherstepstowardsmitigatingN₂OemissionsintheNitricAcidSector.
/argentina-takes-further-steps-towards-mitigating-N₂O-emissions-in-the-nitric-acid-sector/
18Ibid.
onEnhancingCooperationtoAddresstheClimateCrisis,ChinaandtheU.S.expressedplanstocollaborateonmanagingN₂Oemissions.19
3.2.China'sN₂OEmissionReductionActions
WhileChinahasnotyetintroducedadedicatedplanforN₂Oemissioncontrol,ithasprioritizedthemitigationofnon-CO₂GHGs,includingN₂O,withinitsdualcarbonpolicies.Inits2021report,China’sAchievements,NewGoalsandNewMeasuresforNationallyDeterminedContributions,ChinahighlightedtheimportanceofdevelopingtargetedN₂Oreductionstrategiesforkeyindustries.
Inaddition,sector-specificpoliciesunderthedualcarbonpolicyframeworkareadvancingeffortstoreduceN₂Oemissions.Forexample,the14thFive-YearPlanforGreenAgriculturalDevelopment(2021)promotesreducedchemicalfertilizeruse,increasedefficiency,andbetterutilizationoflivestockmanure.The2022ActionPlanforCarbonSequestrationinAgricultureandRuralAreasaimstoenhancenitrogenfertilizerefficiencyandcutN₂Oemissions.Table1outlineskeypolicymeasuresdrivingN₂OmitigationeffortsinChina.
19Xinhua.(2023).ChinaandtheUnitedStatesreleaseasunnylandstatementonstrengtheningcooperationtoaddresstheclimatecrisis.
/2023-11/15/c_1129976165.htm
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Table1:China'skeypolicyactionsforN₂Oemissionreduction
ExistingEmissionReductionActions
PolicySources
TargetingGHGs,includingN₂O
•StrengthenthecontrolofotherGHGssuchasmethane,hydrofluorocarbons,and
perfluorocarbons
•Studyandimplementactionplansforcontrollingnon-carbondioxidegreenhousegas(non-CO₂
GHGs)emissions,continuetoimprovethe
technicalsystemformonitoring,reportingand
evaluatingnon-CO2GHGs,andgraduallyestablishandimprovethestatisticalaccountingsystem,
policysystemandmanagementsystemfornon-CO₂GHGsemissions
•IncorporateGHGscontrolintoEnvironmentalImpactAssessment(EIA)management
•Strengthenthecontrolofnon-CO₂GHGs,and
studyandformulateGHGsemissionstandardsforkeyindustries
•Outlineofthe14thFive-YearPlanfor
NationalEconomicandSocial
DevelopmentofthePeople'sRepublicofChinaandtheLong-RangeObjectivesThroughtheYear2035
•WorkingGuidanceforCarbonDioxidePeakingandCarbonNeutralityinFullandFaithfulImplementationoftheNewDevelopmentPhilosophy
•China'sLong-termDevelopment
StrategyforLowGreenhouseGas
EmissionsintheMiddleofthisCentury
•OpinionsoftheCPCCentralCommitteeandtheStateCouncilonDeepeningtheBattleofPollutionPreventionand
Control
•ImplementationPlanforSynergyinPollutionReductionandCarbon
Reduction
Mainemissionsources
ExistingEmissionReductionActions
PolicySources
Agriculturalactivities
Nitrogenfertilizeruse
•ReduceN₂OemissionsfromfarmlandandpeakN₂Oemissionsfromfarmlandby2020
•Improvenitrogenfertilizeruseefficiencyandreducenitrousoxideemissions
•Promotesoiltestingandformulatedfertilization,promotenitrogenfertilizerreductionandefficiencyimprovement,andorganicfertilizersubstitution
•Subsidiesforthepurchaseanduseoforganicfertilizers
•Constructalong-termmechanismforreplacing
chemicalfertilizerswithorganicfertilizersforfruits,vegetables,andtea
•Demonstrateandpromotenewfertilizerssuchasslow-releasefertilizersandwater-solublefertilizersandcreateagreencrop-livestockintegrated
system.
•13thFive-YearPlanforControllingGreenhouseGasEmissions,
•NationalAgriculturalSustainableDevelopmentPlan(2015-2030),
•14thFive-YearNationalAgriculturalGreenDevelopmentPlan,
•ImplementationPlanforAgriculturalandRuralCarbonEmissionReductionand
Sequestration,
•ImplementationPlanforBuildinga
NationalAgriculturalGreen
DevelopmentPilotZoneandPromotingComprehensiveGreenTransformationofAgriculturalModernization
DemonstrationZone,
•The14thFive-YearPlanforPromotingAgriculturalandRuralModernization
Livestockandpoultrymanure
•Resourceutilizationtargetsoflivestockandpoultrymanure
•Providefinancialsubsidiesfortheresourceutilizationoflivestockandpoultrymanure
Industrialsector
Nitricacidandadipicacid
•Improvetheproductionprocessofchemical
fertilizers,adipicacid,nitricacid,andcaprolactam,etc.
•Controlnon-CO₂GHGssuchasN₂Oinanorderly
manner
•Strengthenthemonitoring,research&
developmentofreductionalternative
technologies,andstandardsettingfornon-CO₂GHGs,includingN₂O
•IndustrialGreenDevelopmentPlan(2016-2020),
•14thFive-YearPlanforIndustrialGreenDevelopment,
•ImplementationPlanforScienceand
TechnologytoSupportCarbonPeakandCarbonNeutrality(2022-2030)
Waste
Sewagetreatment
•Strengthentheapplicationoflow-carbon
technologiessuchashigh-efficiencynitrogenandphosphorusremovaltoreducetheescapeofN₂Ointhedenitrificationprocess
•ImplementationOpinionsonPromotingtheSynergyofSewageTreatment,
PollutionReduction,andCarbonReduction
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Energyactivities
Fossilfuelandbiomassfuelcombustion
processes
•Duringthe14thFive-YearPlanperiod,thegrowthofcoalconsumptionhasbeenstrictlyand
reasonablycontrolled,andwillgraduallydecreaseduringthe15thFive-YearPlanperiod
•Promotethesubstitutionofcoalwithnaturalgasinindustrialandagriculturalapplications
•Promotetheorderlyreplacementofoldvehicleswithnewenergyvehiclesandtheuseofcleanenergyfornon-roadmobilemachinery
•ImplementationPlanforSynergyinPollutionReductionandCarbon
Reduction
4.OpportunitiesandChallengesforN₂OEmissionReductioninChina
InthecontextofChina’sN₂Oemissionreductionpolicy,thissectionwillidentifykeymeasuresandtechnologiesthatcanenhanceN₂Omitigationefforts,alongwithanoverviewoftheircurrentimplementationstatus.SincepoliciespromotingenergytransitionandairqualityimprovementscanhavesynergisticeffectsonreducingN₂Oemissionswithintheenergysector,thissectionwillprimarilyfocusonthetwolargestsourcesofN₂OemissionsinChina:agricultureandindustry.
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4.1.N₂OEmissionReductioninAgriculture
4.1.1.TechnologiesandPracticesforMitigatingAgriculturalEmissions
Improvingfertilizertypestoenhancenitrogenuseefficiency:
•Organicfertilizers:RegulatingmicrobialactivityinsoilthroughorganicfertilizerscanhelpreduceN₂Oemissions.However,challengessuchashighcosts,lowefficiency,andinsufficientinfrastructurehinderwidespreadadoption.20
•Biocharapplication:Theporousstructureofbiocharisconducivetomicrobialgrowthandaidsinnitrogenfixation,therebyreducingsoilN₂Oemissions.21
•Slow-releasefertilizerandnitrificationinhibitors:Slow-releasefertilizersallowforthegradualreleaseofnitrogen,reducingnitrogenfertilizerloss,loweringusage,andcuttingN₂Oemissions.Nitrificationinhibitorsfurtherdecreaseemissionsbyslowingthenitrificationprocessinthesoil.22
Optimizenitrogenfertilizerapplication:
•Soiltestingandformulation:Fertilizationtailoredtosoilnutrientneedshelpspreventover-fertilizationandimprovesfertilizerefficiency.Since2005,Chinahaspromotedsoiltestingandformulatedfertilizationtechnologies,butthereremainsagapbetweenpromotedareasandactualimplementation.23
•Integratedwaterandfertilizermanagement:Dripirrigationdeliversnutrientsstraighttotherootsofcrops,reducingsoilconditionsthatfavornitrificationanddenitrificationprocessesandtherebyreducingN₂Oemissions.Chinaisgraduallyexpandingtheuseofwater-fertilizerintegrateddripirrigation,especiallyinnorthernandnorthwesternregions.
•Precisionagriculture:Byusingsensorstogatherdataonsoilconditions,crophealth,weather,andtemperature,bigdataanalysiscanprovidefarmerswithtailoredrecommendationsforplanting,irrigation,andfertilization,improvingefficiencyandreducingemissions.
20Xinhua.(2020).Investigationofthedilemmaoforganicfertilizerpromotion
/cysc/sp/info/202010/13/t20201013_35881440.shtml
21Yan,S.,Shang,Z.,Deng,A.,&Zhang,W.(2022).SpatiotemporalcharacteristicsofnitrousoxideemissionsfromfarmlandinChinaandemissionreductionpathways.JournalofCrops,38(3),1–8.
22Zou,X.,Li,Y.,Gao,G.Z.,Wan,Y.,&Shi,S.(2011).ResearchandanalysisofmajorgreenhousegasemissionreductionmeasuresinChina'sagriculturalsector.EcologyandEnvironmentalSciences,20(8/9),1348–1358.
23Zheng,L.,Zhang,X.,&Wang,B.(2018).Preliminarystudyontheevolutionprocessoffertilizerandorganicfertilizersubsidypolicyandsupportingtechnologies.WorldEnvironment,4.
Optimizelivestockandpoultrymanuremanagement
•GHGsemissionsintheprocessoflivestockandpoultrymanurestoragecanbeeffectivelyreducedthroughreasonablemanagement,includingtheuseofsolid-liquidseparationinmanuremanagement,wheretheliquidundergoesanaerobicdigestionforbiogasproduction,whilethesolidiscompostedaerobically,andshorteningthestoragetimeofliquidmanure.
•AddingexcipientssuchasbiocharandbentonitetomanurestoragecanreduceN₂Oemissions.24Intheprocessoffertilizinglivestockandpoultrymanure,N₂Oemissionscanalsobereducedbyturningthepilesandforcedventilationinaerobiccomposting.25
Box2:N₂OemissionreductionpracticeinChina'sagriculture
Sinofert,withthesupportoftheMinistryofAgriculture,haslaunchedanintelligentfertilizerdistributionservicestationbasedonintelligentfertilizerblendingmachinesacrossthecountrysince2014.Theseintelligentfertilizerblendingmachinesenableprecisesoiltestingandfertilizerformulation.Largegrowersandretailfarmerscanbothusecorrespondingapplicationslinkedtotheinternet-enabledfertilizerterminals.Byenteringplantinginformationandprovidingsoiltestingsamples,thefertilizerblendercanquicklytestthesoilandsendtheresultstothecloud.
Accordingtothesoiltestingresults,thecloudservercalculatestheplantingplan,therequiredfertilizerformulaandprice,andultimatelygeneratesafertilizerorderthatissenttothefarmer'ssmartphone.Thefertilizersprovidedthroughthissmartblendingsystemgodirectlyfromthefactorytothefarmers,eliminatingmarkupcostsfromthedistributionchain.Calculationsshowthattheintelligentfertilizerdistributionsystemcanreducefertilizerusageandcostsby10%to30%,whilealsoincreasingcropyieldsbyover5%,resultinginamorethan10%increaseinfarmers'income.
24Lei,M.,Cheng,Y.,Miao,N.,Zhou,J.,&Chen,Z.(2019).Effectsofloessandotheradditivesonammoniaandgreenhousegasemissionsduringpigmanurestorage.JournalofEnvironmentalScience,39(12),4132–4139.
25Zhu,Z.,Dong,H.,Wei,S.,Ma,J.,&Xue,P.(2020).ImpactsofchangesinlivestockandpoultrymanuremanagementongreenhousegasemissionsinChina.JournalofAgro-EnvironmentScience,39(4),743–748.
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4.1.2.ChallengesinReducingN₂OEmissioninAgriculture
NitrogenfertilizerapplicationinagriculturallandistheprimarysourceofN₂OemissionsinChina'sagriculture.Achievingreductionsintheseemissionswhileensuringfoodsecurityandincreasingagriculturalproductionandincomepresentssignificantchallenges.ThemainplanadoptedbyChinaistoreducethequantityofchemicalfertilizersandwhileincreasingtheirefficiency,suchasthezero-growthactionofchemicalfertilizerandpesticideusewaslaunchedin2015.Specificactionsincludesupportingandencouragingtheuseofsoiltestingandformulatedfertilizationtechnology,utilizingorganicfertilizerresources,anddemonstratingnewfertilizers,suchasslow-releasefertilizersandwater-solublefertilizers,toreducetheuseofchemicalfertilizers.
Asintensivepoliciesaimedatreducingandimprovingfertilizerefficiencyhavebeenimplemented,theapplicationofchemicalfertilizersinChinahasslowlydeclinedsince2016,markingthefirstnegativegrowthinfertilizerusesince1974.26Thetargetforzerogrowthinchemicalfertilizerusewasalsoachievedthreeyearsearlyin2017.27Asshowninthefigurebelow,China'sfertilizerapplicationwas59.84milliontonsin2016,adecreaseof380,000tonsfrom2015,anditdecreasedto54.03milliontonsin2019.Atthesametime,N₂Oemissionsfromfertilizerusearedeclining.Despitethedownwardtrendinfertilizeruse,in2021,theintensityoffertilizerapplicationinChinaremainedabout307kg/ha,stillmorethantheinternationallyrecognizedsafetyupperlimitof225kg/ha.28Inthefuture,achievingdeepreductionsinN₂Oemissionstomeetthecarbonneutralitygoalwillrequirefurtherexplorationofdiversetechnologies.
26ChineseGovernmentNetwork.(2017).China'sagriculturalfertilizerconsumptionhasachievednegativegrowthforthefirsttimein43years.
/xinwen/2017-12/28/content_5251080.htm
27Xinhua.(2018).MinistryofAgricultureandRuralAffairs:Thetargetofzerogrowthintheuseofchemicalfertilizersand
pesticideshasbeenachieved3yearsaheadofschedule.
/politics/2018-04/25/c_1122739925.htm
28InstituteforGlobalDecarbonizationProgress.(2024).Chemicalfertilizerreductionandefficiencyimprovementandnitrousoxideemissionreduction:Observationsandprospects.iGDP.
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Figure2:China’sfertilizerapplication(10,000tons)&fertilizer-relatedN₂Oemissions(10,000tonsCO2e,2000-2019)
Source:AgriculturalfertilizerapplicationdatafromtheNationalStatisticalYearbook,fertilizerN₂OemissiondatafromFAO
Figure3:FertilizerapplicationintensityinChina(kg/ha,2000–2021)
Source:NationalStatisticalYearbook
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4.2.N₂OEmissionReductioninIndustry
ThemainemissionsofN₂Ointheindustrialsectorcomefromtheproductionprocessofnitricacidandadipicacidproduction.About90%oftheN₂OemissionsinChina'schemicalindustrycomefromtheproductionofadipicacid,followedbytheemissionofnitricacidproduction.29Atpresent,theprimarymethodforreducingN₂Oemissionsduringtheproductionofnitricacidandadipicacidiscatalyticdecompositiontechnology.
4.2.1.PracticesandTechnologiesforMitigatingIndustrialN2OEmissions
•MeasurestoreduceN₂Oemissionsintheproductionofadipicacidcanbecategorizedintotwomaintypes.Thefirstoneinvolvesdecomposition,whichbreaksdownN₂Ointonitrogenandoxygen.Thisincludesthermaldecompositionwithoutcatalyst,achievingaround88%decomposition,andcatalyticdecompositionusingcatalyst,achieving95%.Thesecondtypeofemissionreductionmeasureistopurifytheexhaustgasintohigh-purityN₂Oproducts.30Atpresent,somedomesticcompanieshavebuiltN₂Odecompositiondevicesintheiradipicacidproductionunits,usingcatalyststotreatN₂Oemissions,butmostcompaniesrelyonimportedcatalysts.Inaddition,afewcompanieshaveadoptedtechnologiestoextractN₂Ofromthetailgas.31
•MeasurestoreduceN₂Oemissionsinnitricacidproductioncanbedividedintoprimary,secondary,andtertiarycontrolmeasures.32TheprimarycontrolmeasuresinvolvereducingN₂Oformationbyimprovingtheammoniaoxidationcatalyst,whichcanreduceN₂Oemissionsby30%-85%,butonlyfornewplants.33ThesecondarycontrolmeasuresinvolveplacingtheN₂OpyrolysiscatalystaftertheammoniaoxidationcatalysttodecomposeN₂Ointhefurnace,withareductionefficiencyofabout80-90%.Thisapproachismorecommonlyappliedduetolower
29Liang,M.,Zhou,Z.,Ren,P.,Xiao,H.,Hu,Z.,Piao,S.,...&Yuan,W.(2024).Fourdecadesoffull-scalenitrousoxideemissioninventoryinChina.NationalScienceReview,11(3),nwad285.
30Jiang,Y.,Xu,Y.,&Ai,X.(2018).ReviewofN₂Oabatementtechnologiesinadipicacidproduction.ChemicalDesignLetters,
(9),56–57.
31Zhang,C.,&Yao,X.(2022).Analysisanddevelopmenttrendofgreenhousegastreatmentinthetailtemperatureofadipicacidindustrialproduction.HenanChemicalIndustry,(9),12–14.
32Jia,L.,Xing,F.,Li,C.,&Jian,L.(2023).ResearchprogressoncombinedremovaltechnologyofNOxandN₂Ofromnitricacidproductiontailgas.ChemicalIndustryandEngineeringProgress,42(7),3770–3779.
33Ibid.
investmentcosts
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