版權(quán)說(shuō)明:本文檔由用戶提供并上傳,收益歸屬內(nèi)容提供方,若內(nèi)容存在侵權(quán),請(qǐng)進(jìn)行舉報(bào)或認(rèn)領(lǐng)
文檔簡(jiǎn)介
CountingCarbonMoleculesinProducts:DisentanglingtheGrowingWebofCarbonIntensityMethods
MilanElkerbout,KatarinaNehrkorn,andBrandonHolmes
WorkingPaper25-27November2025
AbouttheAuthors
MilanElkerboutisafellowanddirectoroftheInternationalClimatePolicyInitiative
atResourcesfortheFuture(RFF),workingoninternationalclimatepolicyandonthe
interactionsbetweenclimateandtradepolicy.
KatarinaNehrkornisaresearchassociateatRFFwhoseresearchspansacross
internationalclimatepolicyandindustrialdecarbonization.NehrkornearnedherBA
ineconomicsfromtheUniversityofMichigan,afterwardsworkingatDeloitte’sRisk
andFinancialAdvisorydivisionfortwoyears.In2023,shecompletedherMScin
EnvironmentalEconomicsandClimateChangeattheLondonSchoolofEconomics.
BrandonHolmesisaresearchanalystatRFF.HolmesearnedhisMScinEnvironmental
andNaturalResourceEconomicsatDurhamUniversityintheUnitedKingdom.
AboutRFF
ResourcesfortheFuture(RFF)isanindependent,nonprofitresearchinstitutionin
Washington,DC.Itsmissionistoimproveenvironmental,energy,andnaturalresource
decisionsthroughimpartialeconomicresearchandpolicyengagement.RFFis
committedtobeingthemostwidelytrustedsourceofresearchinsightsandpolicy
solutionsleadingtoahealthyenvironmentandathrivingeconomy.
Workingpapersareresearchmaterialscirculatedbytheirauthorsforpurposesof
informationanddiscussion.Theyhavenotnecessarilyundergoneformalpeerreview.
Theviewsexpressedherearethoseoftheindividualauthorsandmaydifferfromthose
ofotherRFFexperts,itsofficers,oritsdirectors.
SharingOurWork
OurworkisavailableforsharingandadaptationunderanAttribution-
NonCommercial-NoDerivatives4.0International(CCBY-NC-ND4.0)license.You
cancopyandredistributeourmaterialinanymediumorformat;youmustgive
appropriatecredit,providealinktothelicense,andindicateifchangesweremade,
andyoumaynotapplyadditionalrestrictions.Youmaydosoinanyreasonable
manner,butnotinanywaythatsuggeststhelicensorendorsesyouoryouruse.
Youmaynotusethematerialforcommercialpurposes.Ifyouremix,transform,or
builduponthematerial,youmaynotdistributethemodifiedmaterial.Formore
information,visit
/licenses/by-nc-nd/4.0/
.
ResourcesfortheFuturei
ResourcesfortheFutureii
Abstract
ThisisthesecondResourcesfortheFuture(RFF)workingpaperoninteroperability
ofcarbonintensityquantificationmethods1Thispaperconnectstheongoingdebateoncarbonaccountingmethodswithexistingpracticesinlifecycleaccounting
andenvironmentalproductdeclarations.Acasestudycomparescarbonintensity
quantificationmethodsacrosstheEUcarbonborderadjustmentmechanisms,the
USEnvironmentalProtectionAgency’slabelingprogram,andanInternationalTrade
Commissionstudyonsteelandaluminumcarbonintensities.Thispaperfindsthat
theremaybelegitimateareaswhereproduct-levelcarbonintensityaccountingchoicesmaydiffer.Nevertheless,improvedinteroperabilitycouldstillbepossiblebydiscussingandrecognizingtrade-offsbetweenphysicalpropertiesandpolicyincentives.
1ToreadourfirstRFFpaperoninteroperability,see
/publications/
working-papers/trade-friendly-climate-policies-the-promise-of-interoperability/
.
CountingCarbonMoleculesinProducts:DisentanglingtheGrowingWebofCarbonIntensityMethodsiii
Contents
1.IntroductionandPolicyContext1
2.FromCountingtoAccounting2
2.1.InternationalvsCorporateAccounting3
3.RelevantPoliciesWeConsider5
4.WhatIsProduct-LevelAccounting?7
4.1.WhatIsaProduct?8
4.2.WhenAreProductsSubstitutes?9
5.AllocatingEmissionsfromFacilitiestoProducts10
5.1.IsAllocationAlwaysNecessary?10
5.2.Definitions11
5.3.FourFormsofAllocation11
5.4.OtherAllocationChallenges12
Box1.Recycling:HowtoTreatIt–ModuleDImplications13
Box2.AlternativeFuels15
6.CaseStudy:ComparingtheEUCBAM,EPALabelingProgram,
andUSITCStudy15
6.1.ProgramGoals17
6.2.EmissionTypes18
6.3.SystemBoundaries18
6.4.Facility-LevelQuantificationMethodologies19
6.5.Allocation19
6.6.LocationversusMarket-BasedAccountingforScope219
6.7.InteroperabilitywithDifferentStandards20
7.KeyTakeawaysandDiscussion20
References24
Appendix1.Life-CycleStagesinEPDs28
ResourcesfortheFutureiv
Appendix2.ISOStandards29
A2.1.ISO14067:Greenhousegases—Carbonfootprintofproducts—
Requirementsandguidelinesforquantification29
A2.2.ISO14025:EnvironmentalLabelsandDeclarations—TypeIII
EnvironmentalDeclarations—PrinciplesandProcedures29
A2.3.ISO14027:Environmentallabelsanddeclarations–development
ofproductcategoryrulesISO1402730
A2.4.ISO14044:Environmentalmanagement–lifecycleassessment–
Requirementsandguidelines30
A2.5.ISO14040:EnvironmentalManagement—LifeCycleAssessment
—PrinciplesandFramework31
A2.6.ISO21930:SustainabilityinBuildingsandCivilEngineeringWorks
—CoreRulesforEnvironmentalProductDeclarationsofConstruction
ProductsandServices32
A2.7.ISO/TR14069:GreenhouseGases—QuantificationandReporting
ofGreenhouseGasEmissionsforOrganizations—Guidanceforthe
ApplicationofISO14064-132
A2.8.ISO14064-1:ISO14064-1:2018,GreenhouseGases—Part1:Specification
withGuidanceattheOrganizationLevelforQuantificationandReportingof
GreenhouseGasEmissionsandRemovals33
A2.9.ISO14064-2:GreenhouseGases—Part2:SpecificationwithGuidanceat
theProjectLevelforQuantification,MonitoringandReportingofGreenhouse
GasEmissionReductionsorRemovalEnhancements33
A2.10.ISO14064-3:GreenhouseGases—Part3:SpecificationwithGuidance
fortheVerificationandValidationofGreenhouseGasStatements34
CountingCarbonMoleculesinProducts:DisentanglingtheGrowingWebofCarbonIntensityMethods1
1.IntroductionandPolicyContext
Countingcarbon—includinghowandwhytodoit—isgarneringmoreattentionin
climatepolicy.Newpoliciesthatintersectclimate,trade,sustainablefinance,and
domesticmanufacturingrequirecarbonintensitymetrics.Evenassomecountries
reappraisethepaceatwhichclimatepolicyshouldevolve,knowinghowmany
metrictonsofgreenhousegasesareassociatedwithaproduct,service,company,
orcountryremainscriticaltomanydecarbonizationpolicies.Whenmanycountries
aroundtheworldstartadoptingsuchpolicies,thepotentialforfrictionincreasesifthemethodologiesforcountingcarbondiffer.
Inaworkingpaperlastyear,wediscussedthisconceptofinteroperability(Elkerbout
andNehrkorn2024).TheOrganisationforEconomicCo-operationandDevelopment’sInclusiveForumonCarbonMitigationApproacheshasalsodonesignificantwork
toidentifychallengesandpotentialsolutionstocalculatingproduct-levelcarbon
intensitymetrics,includingrecentworkcomparingavailabledatasetsoncarbon
intensity(OECD2024,2025).Inthissecondpaper,weextendtheanalysistotheswiftlychangingdebateonwhatconstitutesappropriatecarbonaccounting,howitdiffers
fromgreenhousegasreporting,andhowcarbonintensityquantificationeffortsfor
climate-and-tradepoliciesrelatetolong-standingpracticesinenvironmentalproductdeclarationsandlife-cycleaccounting.
Forpoliciesatthenexusofclimateandtrade,measuringproduct-levelcarbonintensityasawaytodifferentiateamongproducerscanhaveimportantenvironmentaland
economicmotivationsandimplications,withloweraveragecarbonintensitiesusedtojustifysafeguardingmeasuresvis-à-vismorecarbon-intensiveproducers.Consider,
forexample,suchcarbonborderpoliciesastheEUandUKCarbonBorderAdjustmentMechanisms(CBAM)andtheproposedUSForeignPollutionFeeAct(FPFA)andCleanCompetitionAct(EuropeanCommission2023a;UKHMRCandHMTreasury2024;USCongress2025).Especiallybecausecountriesarestillfiguringouthowtoimplementthesenascentpolicies—andwithcompetitivenesshighonpolicymakers’minds—theinterestinunderstandingcarbonfootprintsatdifferentlevelsofgranularityisonly
increasing.
Procurementpoliciesareanotherexamplewherecarbonfootprintsmatter.Theycan
beaneffectivewaytosteerdemandtowarddomesticproducers,therebycontributingtodemandformoreprotectionoflocalindustries.Ifdomesticindustriesarelower-
carbon,orifacertaincarbonperformanceismandatedforenvironmentalreasons,thencountingcarbonbecomesimportantonceagain.
Forsustainablefinancepolicies,countingcarboncanincreasetransparencyandaccountabilityaroundagivenentity’sexposureorcontributiontoclimatechange.
Butaccountabilityisonlyoneofmanyreasonscountingcarbonisbecomingmore
important.Withanincreasingmixofvoluntaryandmandatorypoliciesacrossdifferent(sub)-nationaljurisdictions,howdifferentwaysofcountingcarbonmeasureupagainst
ResourcesfortheFuture2
eachotherbecomesmoresalient.Companiesmaybesubjecttomultiplepolicies
simultaneously,makinginteroperabilityofmethodologies,reporting,andverificationcritical.Withoutinteroperability,firms—especiallysmallerones—facehightransactioncosts.
Thesenewpoliciesareemergingagainstthebackgroundofarapidlychangingglobaltradesystemthatincreasinglyemphasizesprotectionofdomesticmanufacturing
industries—thesameindustriesforwhichcarbonaccountingisbothcriticaland
challenging.TheexampleoftheFPFAshowshowevenpoliciesthataimtosupport
domesticindustrycanrequirecarbonintensitynumbersforimplementation.When
manycountriesaroundtheworldstartadoptingsuchpolicies,thepotentialforfrictionincreasesifthemethodologiesforcarbonintensityquantificationdiffer.
Thisraisesseveralquestionsthatlieattheheartofthispaper:atwhatpointdoes
countingcarbonbecomeaccountingforcarbon,andisthereapolicyrelevant
difference?Isanew(global)approachtocarbonreportingandaccountingnecessarytoenablefurtherclimatepolicyimplementation,andtowhatextentissuchasystemcompatiblewithexistingcarbonreportingpractices?Anddospecificclimatepolicygoalsrequirespecificcarboncounting/accountingapproaches,oraretheypotentiallycompatiblewithamoreextensive,generallyappliedcarbonaccountingsystem?
Beforeturningtothesequestions,wediscussthedifferencebetweengreenhouse
gasreporting,focusedonemissionssourcesandproduction,andcarbonaccounting,focusedonproductsandtransactions.Bothareimportant,butwhiletheformerhasbeenputintopracticefordecades,thelatterissettobecomemoreimportantin
comingdecadesasclimatepoliciesthattargetcarbon-intensiveandtradedgoodsgrowinnumber.
Wethencontrastdifferenttypesofpoliciesthatrequireknowledgeaboutthecarbonmoleculesassociatedwithaproduct,whichinturnmeritsdiscussiononwhatismeantbya“product.”Wediscussrelatedpracticesandstandardsinlife-cycleaccounting,
environmentalproductdeclarations,andassociatedinternationalstandards.We
thenpresentthreepolicycases—theEUCBAM,aUSEnvironmentalProtection
Agency(EPA)carbon-intensitylabelingprogram,anda2025USInternationalTradeCommission(ITC)studytobenchmarkUSsteelandaluminumproduct-levelcarbonintensities—tohighlightwhereexistingpracticesandmethodsrelatedtocarbon
intensityquantificationmaygiverisetodifferencesofopinionorinterpretationandhowthiscouldaffectinteroperability.
2.FromCountingtoAccounting
Intheworldoffinance,“accounting”hasaspecificmeaningandextensivehistory.Oneofitscriticalfeaturesisdouble-entrybookkeeping,goingbackatleasttofifteenth-
century
Medici-eraFlorence
,whereanytransactionisrecordedonbothacreditanddebitsideoftheledger—hencethedoubleentry(Devlin2019).Notablehereistheemphasisontransactionsasthekeyeventtokeeptrackof,incontrasttoproductionitself.
CountingCarbonMoleculesinProducts:DisentanglingtheGrowingWebofCarbonIntensityMethods3
InstitutionalizedglobalclimatepolicycooperationgoesbacktotheestablishmentoftheIntergovernmentalPanelonClimateChange(IPCC)in1988andtheUnitedNationsFrameworkConventiononClimateChange(UNFCCC)in1992.Countinggreenhousegasemissionshasbeenacriticalmetricunderpinningmultilateralnegotiations.
Knowinghowmanymetrictonshavebeenandcontinuetobeemittedbydifferent
countriesisvaluablenotjusttoestimateandforecastevenmorefoundationalclimatesciencemetrics(suchascarbondioxide,orCO2,concentrationsintheatmosphere)butalsobecausedifferentiatedresponsibilitiesandequitybetweencountriesaresomeofthemostcontestedelementsofclimatediplomacy.
Countriestodaycontinuetomaintainso-calledgreenhousegasinventoriesandreporttheirannualemissionsaccordingtoIPCCstandardstotheUNFCCC(UNFCCC2014;UNFCCCn.d.a;Goodwinetal.2006).Themethodologyforthisreportingisbased
onIPCCguidelinesfrom2006(Egglestonetal.2006).Thisreportingfocuseson
sourcesandsinksandisnottheclimatepolicyversionoffinancialaccounting—i.e.,
carbonaccounting—butratherlikesimplecounting.Insteadoftransactions,reportingemissionssourcesandsinksfocusesonman-made(production)processesand/
ornaturalprocessesaddingorremovinggreenhousegasestotheatmosphere.
InteractionsamongcountriesusingcarbonunitsarealsoafeatureofArticle6ofthe
ParisAgreement,whichsetsupinternationalcarbontrading(UNFCCC2025).AlthoughArticle6introducesconceptssuchasindirectemissionsandprecursors,byand
largetheseguidelinesdealwithemissionssources.Thusclimatepolicy,globallyanddomestic,hasevolvedwithoutafully-fledgedmandatorycarbonaccountingsystem,evenascarbon-differentiatedtransactionsaregrowing.
Anaccountingframeworkmightsupportdifferentpolicygoalsdependingonhow
theinformationisused.Inconsistencyinunderlyingaccountingmethodscanreducecredibilityandcreateperverseincentives—particularlyifemissionsareunderreportedordouble-counted.Furthermore,alackofclearguidancemayencourage“method
shopping”inwhichapproachesarecombinedtoreporttheleastemissionspossible.
Inaninteroperablesystem,acarbonaccountingframeworkshouldstillbeabletoaccommodatedifferentpolicies,withdifferentincentives.Oncethepoliciesand
incentivesarealigned,it’sarguablymoreaccuratetospeakofharmonization,whichgoesbeyondinteroperability.
2.1.InternationalvsCorporateAccounting
Meanwhile,oneofthemostwidelyusedsystemstoquantifycarbonfootprintsinthebusinessworldistheGreenhouseGas(GHG)Protocol’sEmissionsScopes1,2,and3.(Bhatiaetal.2011).Scope1coversdirectemissionsandcorrespondsmorecloselytowhatisreportedasemissionsfromsourcesingreenhousegasinventories.Scope2emissionsareemissionsassociatedwithconsumedpowerorheatand,outside
oftheGHGProtocol,arereferredtoasindirectemissions.Scope3emissionsaretheemissionsinasupplychain(upstream)orassociatedwiththeuseofaproduct(downstream).Inprinciple,Scope2emissionscouldbeseenasanexampleof
upstreamScope3emissions,inthattheyareemissionsrelatedtoaninput—itjusthappenstobeahighlycommontypeofindirect,inducedemissions.
ResourcesfortheFuture4
TheGHGProtocolisanongovernmentalinitiativeandismostlyusedforcorporate
andvoluntaryclimateaction(Sotos2015).Theprotocolisnotubiquitouslyusedfor
compliancepolicies.Nevertheless,ithasbecomesowidelyusedthatlegislatorshavebegunreferringtoitinlegislationoftheirown.Forexample,California’sdisclosurelawsSB253andSB261repeatedlyrefertoemissionsscopesandstate,“TheGreenhouse
GasProtocolisthegloballyrecognizedGHGemissionsaccountingandreportingstandard”(CaliforniaStateLegislature2023a,2023b).
Itisneverthelessachoicemadebythelegislatortoadoptanexistingnon-
governmentalaccounting/reportingframework,ratherthantodraftanewsetof
rules.TheIPCC2006guidelinesfornationalGHGreportingdonotrefertoemissionsscopes,althoughconceptssuchasindirectemissionsandprecursors(aninputinto
anotherproductionprocess–anexampleofScope3emissions)areused.Byandlarge,however,theseguidelinesdealwithsourcesofemissions;whatintheGHGProtocol
wouldbeScope1emissions.
Inrecentyears,theE-ledgersInstitute,theEFIFoundation,andothershaveled
discussionsaboutnewcarbonaccountingframeworksthatcontrastwiththeGHG
Protocol(E-ledgersInstituten.d.;Monizetal.2025).AcommoncritiqueisthatundertheGHGProtocol,emissionscanbecountedmorethanonce.Indeed,allemissions
haveasourceandwillbecountedassomeentity’sdirect,Scope1emissions,eveniftheyalsocountasindirectemissionsoremissionsinotherentities’supplychains.ForproponentsoftheGHGProtocol,countingemissionsmorethanonceisfeature,notabug,asithighlightsdispersedresponsibilitiesforbothproducersandconsumers.
Ifemissionscanonlybecountedonce,eitheronlydirectemissionssourcesshouldbecounted,oramoreextensivesystemaccountingforcertaintransactionsisneeded.
Thisstatementshouldnotbeseenasendorsing(ordenying)theneedforanew
carbonaccountingsystem.TheexampleofnationalGHGinventoriesshowsthatsomeformsofreportingonlyemissionssourcescanbeanimportantunderpinningofclimatepolicy.Indeed,internationalclimatepolicyhasevolvedfornearlyfourdecadeswithoutasystemofcarbonaccountingofequivalentdepthtomodernfinancialaccounting
practices.
Thiscaneitherbeseenasevidencethatnosuchsystemisnecessarytomake
progressondecarbonization,orasproofthatfurtherdecarbonizationdependsonnewcarbonaccountingsystems.
Perhapsthemostcriticalchallengeinthecontextofvariousindustrialdecarbonizationpoliciesistheneedtoquantifythecarbonfootprintofvariousindustrialproducts,
whichrequiresgoingfromthefacilitylevel(whicharesourcesofdirectemissions)totheproductlevel.Dependingontheproduct,itmayalsoinvolveaccountingfortheemissionsfromseveralinputs,andthereforepossiblyfromseveralfacilities.
CountingCarbonMoleculesinProducts:DisentanglingtheGrowingWebofCarbonIntensityMethods5
3.RelevantPoliciesWeConsider
Publicprocurement,bordermeasures,andreportingdependonreliablecarbon
accountingmethodologiesbutmayentaildifferentpoliticalchoicesandrequirements.ThreecaseswediscussinmoredepthinSection6exemplifythesedifferences:
theEPAbegana
labelingprogram
toaidthe(nowdefunct)US
BuyClean
publicprocurementprogramforcleanerconstructionmaterials,whiletheEUCBAM
willrequireimporterstopayapricebasedonthecarbonintensityofarangeof
products(USEPA2025b;CEQn.d.).Andinthecaseofthe
USInternationalTrade
Commission’s(ITC’s)SteelandAluminum
study,policymakersaresimplytryingto
betterunderstandproduct-levelcarbonemissionsthroughreportingmandates(Petersetal.2025).
Currently,publicprocurementpoliciesandclimate-and-tradepoliciesusedifferent
frameworksforemissionsreporting.Publicprocurementpoliciestypicallydepend
ontheuseofEnvironmentalProductDeclarations(EPDs),whichreporttheresults
ofalife-cycleanalysis(LCA)tocalculatetheglobalwarmingpotential(GWP)1LCAs
areinformedbyproductcategoryrules(PCRs)whichsettherulesforconducting
anLCAandaregenerallynotstandardizedandcanvaryinquality.TheInternational
OrganizationforStandardization(ISO)2hasdoneworktostandardizetherulesand
processesforthedevelopmentofEPDs,LCAs,andPCRs;however,guidelinesare
relativelygeneric,andthereforeareasforpotentialdisagreementremain.ThesegapshavespurredtheIndustrialDeepDecarbonisationInitiative(IDDI),aspecializedUnitedNationsagencyfocusedonacceleratingindustrialdevelopment,tobeginworkonPCRharmonizationandpromotecomparabilityofEPDsacrossproductsandjurisdictions,thereforepromotinginteroperability(UNIDO2024).
Meanwhile,theEUCBAMisapolicydesignedtomirrortheEU’semissionstrading
system.Therefore,theEUisdesigningitsownmethodologiestotranslatefacility-
levelemissionstotheproductlevel.Thiscreatesanumberofrestraintsandpoliticalchoices,whichmaybedifferentthantheexistingrequirementsfromEPDs3,suchassystemboundaries,allocationmethods,anddataqualityrequirement.WewilldiscussthesechoicesandcompareapproachesinSection6.
1Inthiscontext,GWPrepresentsthecarbondioxideequivalent(CO2e)perunitofprod-uct/material(USEPA2024b).WediscussthisfurtherinSection6.
2SeeAppendix2foradescriptionofrelevantISOstandards.
3SeealsoE-ledgersInstitute(2024)foradiscussionofhowEPDscanbeastartingpointformoregranularproduct-levelcarbonaccountingbutarenotsufficientthemselves.
ResourcesfortheFuture6
Figure1.EnvironmentalProductDeclarationProcessand
RelationtoCarbon-IntensityQuantification
EPDCreationProcess
Rules:ProductCategoryRule(PCR)
ISO14027:providesprinciples,requirementsandguidelinesfordeveloping,reviewing,registeringandupdatingthePCR.
Ozonedepletion
Eutrophication
Wateruse
3
Calculation:LifeCycleAssessment(LCA)
ISO14067:specifiesprinciples,requirementsandguidelinesforthequantificationandreportingofthecarbonfootprintofaproduct.
A
ISO14040:describestheprinciplesandframeworkforanLCA
+
ISO14044:coversLCAstudiesandlifecycleinventorystudies
Reporting:EnvironmentProductDeclaration(EPD)
ISO21930:providestheprinciples,specificationsandrequirementstodevelopanenvironmentalproductdeclaration.
ISO14025:establishestheprinciplesandspecifiestheproceduresfordevelopingTypeIIIenvironmentaldeclarationprogrammesandTypeIIIenvironmental
declarations.
GlobalWarming
Potential(GWP)
Chemicalregulation
Water
conservationregulation
Public
Border
Waterqualityregulation
measures
procurement
Note:ISO21930andISO14025arelistedseparatelyintheEPDreportingprocess,asISO21930givesconstructionsectorspecificruleswhereasISO14025givesgeneralframeworkforEPDs.ForacompleteexpansionoftheISOs,pleaserefertoAppendix2.
Theabovefigureshowstherelationshipbetweeninternationalstandards,product
categoryrules,life-cycleassessments,environmentalproductdeclarations,andpolicy.PCRssettherulesfor
溫馨提示
- 1. 本站所有資源如無(wú)特殊說(shuō)明,都需要本地電腦安裝OFFICE2007和PDF閱讀器。圖紙軟件為CAD,CAXA,PROE,UG,SolidWorks等.壓縮文件請(qǐng)下載最新的WinRAR軟件解壓。
- 2. 本站的文檔不包含任何第三方提供的附件圖紙等,如果需要附件,請(qǐng)聯(lián)系上傳者。文件的所有權(quán)益歸上傳用戶所有。
- 3. 本站RAR壓縮包中若帶圖紙,網(wǎng)頁(yè)內(nèi)容里面會(huì)有圖紙預(yù)覽,若沒(méi)有圖紙預(yù)覽就沒(méi)有圖紙。
- 4. 未經(jīng)權(quán)益所有人同意不得將文件中的內(nèi)容挪作商業(yè)或盈利用途。
- 5. 人人文庫(kù)網(wǎng)僅提供信息存儲(chǔ)空間,僅對(duì)用戶上傳內(nèi)容的表現(xiàn)方式做保護(hù)處理,對(duì)用戶上傳分享的文檔內(nèi)容本身不做任何修改或編輯,并不能對(duì)任何下載內(nèi)容負(fù)責(zé)。
- 6. 下載文件中如有侵權(quán)或不適當(dāng)內(nèi)容,請(qǐng)與我們聯(lián)系,我們立即糾正。
- 7. 本站不保證下載資源的準(zhǔn)確性、安全性和完整性, 同時(shí)也不承擔(dān)用戶因使用這些下載資源對(duì)自己和他人造成任何形式的傷害或損失。
最新文檔
- 2026年廣西建設(shè)職業(yè)技術(shù)學(xué)院?jiǎn)握新殬I(yè)技能測(cè)試題庫(kù)參考答案詳解
- 2026年山東城市建設(shè)職業(yè)學(xué)院?jiǎn)握新殬I(yè)技能測(cè)試題庫(kù)及參考答案詳解
- 2026年安徽職業(yè)技術(shù)學(xué)院?jiǎn)握新殬I(yè)傾向性考試題庫(kù)帶答案詳解
- 2026年河南工業(yè)職業(yè)技術(shù)學(xué)院?jiǎn)握新殬I(yè)傾向性測(cè)試題庫(kù)及答案詳解1套
- 2026年浙江師范大學(xué)行知學(xué)院?jiǎn)握新殬I(yè)傾向性考試題庫(kù)及參考答案詳解1套
- 2026年鄭州衛(wèi)生健康職業(yè)學(xué)院?jiǎn)握新殬I(yè)適應(yīng)性測(cè)試題庫(kù)及答案詳解1套
- 2026年鄭州電子信息職業(yè)技術(shù)學(xué)院?jiǎn)握新殬I(yè)適應(yīng)性考試題庫(kù)附答案詳解
- 2026年皖西衛(wèi)生職業(yè)學(xué)院?jiǎn)握新殬I(yè)技能測(cè)試題庫(kù)及參考答案詳解一套
- 2026年成都航空職業(yè)技術(shù)學(xué)院?jiǎn)握新殬I(yè)技能考試題庫(kù)及答案詳解一套
- 2026年陜西國(guó)防工業(yè)職業(yè)技術(shù)學(xué)院?jiǎn)握新殬I(yè)傾向性考試題庫(kù)及參考答案詳解一套
- DB33∕T 2320-2021 工業(yè)集聚區(qū)社區(qū)化管理和服務(wù)規(guī)范
- 英文科技論文寫(xiě)作與學(xué)術(shù)報(bào)告慕課答案云堂在線
- 學(xué)堂在線 雨課堂 學(xué)堂云 人工智能原理 章節(jié)測(cè)試答案
- GB/T 3089-2020不銹鋼極薄壁無(wú)縫鋼管
- GB/T 2878.2-2011液壓傳動(dòng)連接帶米制螺紋和O形圈密封的油口和螺柱端第2部分:重型螺柱端(S系列)
- GB/T 23331-2020能源管理體系要求及使用指南
- GB/T 21238-2016玻璃纖維增強(qiáng)塑料夾砂管
- 化學(xué)品安全技術(shù)說(shuō)明書(shū)氬氣MSDS
- 斯坦福手術(shù)室應(yīng)急手冊(cè)中文版
- 質(zhì)量檢測(cè)計(jì)量器具配備一覽表
- 杜氏潰瘍專(zhuān)業(yè)知識(shí)
評(píng)論
0/150
提交評(píng)論