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Domestic support measures in the context of adaptation and mitigation to climate change Background paper for The State of Agricultural Commodity Markets (SOCO) 2018

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Page 1: Domestic support measures in the context of adaptation and ... · Domestic support measures in the context of adaptation and mitigation to climate change Background paper for The

Domestic support measures in the context of adaptation and mitigation

to climate change

Background paper for The State of Agricultural Commodity

Markets (SOCO) 2018

Page 2: Domestic support measures in the context of adaptation and ... · Domestic support measures in the context of adaptation and mitigation to climate change Background paper for The

Domesticsupportmeasuresinthecontextofadaptationandmitigation

toclimatechange

Backgroundpaperfor

TheStateofAgriculturalCommodity

Markets(SOCO)2018

JosephW.Glauber

SeniorResearchFellowInternationalFoodPolicyResearchInstitute

FormerChiefEconomistUSDepartmentofAgriculture

FoodandAgricultureOrganizationoftheUnitedNationsRome,2018

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Required citation: Glauber, J. W. 2018. Domestic Support Measures in the Context of Adaptation / Mitigation to Climate Change. The State of Agricultural Commodity Markets (SOCO) 2018: Background Paper. Rome, FAO. 2018. 40 pp.Licence: CC BY-NC-SA 3.0 IGO. The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO. © FAO, 2018

Some rights reserved. This work is made available under the Creative Commons Attribution-NonCommercial-ShareAlike 3.0 IGO licence (CC BY-NC-SA 3.0 IGO; https://creativecommons.org/licenses/by-nc-sa/3.0/igo). Under the terms of this licence, this work may be copied, redistributed and adapted for non-commercial purposes, provided that the work is appropriately cited. In any use of this work, there should be no suggestion that FAO endorses any specific organization, products or services. The use of the FAO logo is not permitted. If the work is adapted, then it must be licensed under the same or equivalent Creative Commons license. If a translation of this work is created, it must include the following disclaimer along with the required citation: “This translation was not created by the Food and Agriculture Organization of the United Nations (FAO). FAO is not responsible for the content or accuracy of this translation. The original English edition shall be the authoritative edition. Any mediation relating to disputes arising under the licence shall be conducted in accordance with the Arbitration Rules of the United Nations Commission on International Trade Law (UNCITRAL) as at present in force. Third-party materials. Users wishing to reuse material from this work that is attributed to a third party, such as tables, figures or images, are responsible for determining whether permission is needed for that reuse and for obtaining permission from the copyright holder. The risk of claims resulting from infringement of any third-party-owned component in the work rests solely with the user. Sales, rights and licensing. FAO information products are available on the FAO website (www.fao.org/publications) and can be purchased through [email protected]. Requests for commercial use should be submitted via: www.fao.org/contact-us/licence-request. Queries regarding rights and licensing should be submitted to: [email protected]. Cover photograph: ©FAO/Soliman Ahmed

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Contents Acronyms........................................................................................................................................................................ivAbstract.............................................................................................................................................................................v1.Introduction................................................................................................................................................................12.Agriculture’scontributiontoglobalGHGemissions.............................................................................23.Theeffectsofclimatechangeonglobaltrade...........................................................................................34.WTOdisciplinesaffectingdomesticsupportpolicies...........................................................................74.1SupportmeasuresandtheAgreementonAgriculture.......................................................................74.2DefiningGreenBoxsubsidies..........................................................................................................................95.Thepotentialimpactofinternationaltradingrulesonclimatepolicies.......................................95.1TaxingGHGemissions.....................................................................................................................................105.2ProvidingsubsidiestoincreaseGHGefficiencyinproduction....................................................115.3ProvidingsubsidiestoreduceGHGemissionsorsequestercarbon.........................................135.4Measurestoincreaseresiliencetoproducerstotheeffectsofclimatechange...................145.4.1Agriculturalinsuranceanddisasterassistance...............................................................................155.4.2Publicstockholdingprograms.................................................................................................................185.4.3Structuraladjustmentpayments............................................................................................................195.5Regulatorypoliciestoaddressclimatechange....................................................................................206.DesigningWTO-compatibleCSApolicies..................................................................................................217.Conclusions..............................................................................................................................................................23

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Acronyms CSA ClimateSmartAgricultureWTO WorldTradeOrganizationCO2 CarbonDioxideAMS AggregateMeasurementofSupportAFOLU Agriculture,ForestryandOtherLandUseAoA AgreementonAgricultureGHG GreenhouseGasR&D Research&DevelopmentIBLI Index–BasedLivestockInsuranceUNCTAD UnitedNationsConferenceonTrade&SupportCRP ConservationReserveProgramACEP AgriculturalConservationEasementProgram

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AbstractClimateSmartAgriculture(CSA)hasbeenpromotedasakeyapproachinaddressingtheeffectsofclimatechange.Firstlaunchedin2009,CSAreferstoagriculturaltechnologiesthatarewellsuitedtoincreasefarmerlivelihoodsinthefaceofachangingclimateby1)raisingagriculturalproductivity;2)buildingresilienceoflivelihoodsandfarmingsystems;and3)reducingcarbonemissions.Whilegovernmentimplementationofmitigationandadaptationpoliciesmaybeaneffectivemeanstohelpaddressclimatechange,concernsarise,ifCSApoliciesruncountertointernationaltradedisciplines.Inparticular,CSApoliciescouldcomeintodirectconflictwithWTOtraderules,ifthesepoliciesservetoinsulatedomesticproducersfromcompetition.Thus,theycouldpotentiallydistortproductionandtrade.ThispaperexaminesCSApoliciesinthecontextoftheWTOagreements,includingdomesticsupportdisciplinesundertheWTOAgreementonAgriculture.

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1.IntroductionClimatechangewilllikelyhavesignificantimpactsonagriculturalproduction,particularlyindevelopingcountrieshighlydependentonrainfed-agriculture(McCarthy,LipperandZilberman,2018).FindingsofthefifthassessmentreportoftheIntergovernmentalPanelonClimateChangeconcludethat“allaspectsoffoodsecurityarepotentiallyaffectedbyclimatechangeincludingfoodaccess,utilization,andpricestability”(Porteretal.,2014,p.488).Thus,thepotentialimpactsofclimatechangewillfurthercomplicatethegoalofmeetingfoodandnutritiondemandsforagrowingglobalpopulationandgrowingconsumerincomes,aslaidoutintheUnitedNationsSustainableDevelopmentGoals(UN,2015).ClimateSmartAgriculture(CSA)isanapproachdevelopedbytheFoodandAgricultureOrganizationoftheUnitedNations(FAO)todevelopthetechnical,policyandinvestmentconditionstoachievesustainableagriculturaldevelopmentforfoodsecurityunderclimatechange(FAO,2013).TheCSAapproachhasthreemainpillars:1)sustainablyincreasingagriculturalproductivityandincomes;2)adaptingandbuildingresiliencetoclimatechange;and3)reducingand/orremovinggreenhousegasemissions,wherepossible.CSAaimstoimprovefoodsecurity,helpcommunitiesadapttoclimatechangeandcontributetoclimatechangemitigationbyadoptingappropriatepractices,developingenablingpoliciesandinstitutionsandmobilizingneededfinances(FAO,2013).Tradecanhelpmitigatetheeffectsofclimatechangeonfoodsecuritybyprovidingabufferagainstshorttermdisruptionsinsupplies,causedbydroughts,floodsorotherextremeweatherevents,eventswhichareprojectedtobemorelikelyasglobaltemperaturesrise(Lantz,BaldosandHertel,2015).Theimportanceoftradehasincreasedinrecentyears,aslargersharesofglobalconsumptionaresuppliedbyimports.Thesetrendsareprojectedtocontinueoverthenexttenyears(OECD-FAO,2017;O’DonoghueandHansen,2017).Overthelongerterm,tradewillbecomeevenmorecritical,aschangingclimatescausefoodproductiontoshiftgeographicallyandmorehighlyvariableweatherincreasespricevolatility.Whilegovernmentimplementationofmitigationandadaptationpoliciesmaybeaneffectivemeanstohelpaddressclimatechange,concernsariseifCSApoliciesruncountertointernationaltradedisciplines.Inparticular,CSApoliciescouldcomeintodirectconflictwithWTOtraderules,ifthosepoliciesdistortproductionandtrade.ThispaperconsidershowCSApoliciesmayaffectproductionandtrade;andassuch,comportwithexistingWTOrules.Section2discussesagriculture’scontributiontoglobalgreenhousegas(GHG)emissions.InSection3,recenttrendsininternationaltradearereviewedandtheimpactsofGHGemissionsoninternationaltradearediscussed,includinghowtradecanpotentiallyhelpachievesustainableagriculturaldevelopmentforfoodsecurityunderclimatechange.WTOdisciplinesaffectingdomesticsupportpoliciesareanalyzedinmoredetailinSection4.Section5focusesonhowCSApoliciesmaypotentially

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conflictwithWTOtraderules,includingtheAgreementonAgriculture,andtheAgreementonSubsidiesandCountervailingMeasures.Section6offersrecommendationsonhowCSApoliciescanbebestdesignedtoensurecompatibilitywithWTOrulesorhowWTOrulescouldbemodifiedtoaccommodateCSApolicies,withoutcreatinglargetradedistortions.ConcludingcommentsareofferedinSection7.

2.Agriculture’scontributiontoglobalGHGemissionsAgricultureisamajorcontributortoglobalgreenhousegasesthroughcropandlivestockproduction,aswellasthroughlandconversion.Agriculturecontributestoclimatechangedirectlybyemittingmethane(CH4)andnitrousoxide(N2O)incropandlivestockproduction,andindirectlybyaffectingnetCO2emissionsthroughitsimpactonsoil,forestsandotherlanduses.Agriculturecanalsoservetosequesteratmosphericcarbon,throughsoilmanagementpracticesandplantingofperennialcropsandtrees.Agricultureisanemissions-intensivesector,whichtypicallyemitsafargreatershareofGHGgasesthanitproducesineconomicactivity.TheWorldBank(2017)estimates,thatagricultureaccountsforabout3.8percentoftotalGDPin2015,comparedto24percentofglobalGHGemissions.IntheUnitedStates,agricultureaccountsforabout10percentoftotalGHGemissionswhiletheagriculturalsectoraccountsforonly1percentofGDP(USDAandERS,2017).EstimationbySmithetal.(2014)showed,thattotaldirectandindirectGHGcontributionsfromagriculture,forestryandotherlanduses(AFOLU)in2010,wasthesecondlargestsourceofGHGemissions(afterfossilfueluse),accountingfor24percentoftotalglobalanthropogenicemissions.BasedonFAOSTATdata,BlandfordandHassapoyannes(2017)estimated,thatdirectemissionsfromagricultureaccountforabout10–12percentofglobalGHGemissionsin2012–2014.Agricultureisthelargestcontributortonon-CO2GHGemissions,accountingfor56percentofemissions.Livestockareestimatedtoaccountfor80percentofthedirectemissions,largelyintheformofCH4.Ruminantsaccountformorethan80percentoftotallivestock-relatedGHGemissions(Havliketal.,2014).LandusegeneratesCO2emissionsbychangingthecarbonstockinforestland(soilandbiomass),andinthesoilofcropland,grassland,andwetlands(peatlandsandfloodedland).Gibbsetal.(2010)estimate,thatbetween1980and2000,83percentofagriculturallandexpansioninthetropicsoccurred,becauseofdeforestation,muchofwhichwasdonetoincreaselivestockproduction.BlandfordandHassapoyannes(2017)estimated,thatdeforestationaccountedfor59percentofgloballanduseemissionsin2012–2014.Agricultureisalsoanenergyintensivesector,usingfossilfuelsforanumberofproductionactivities,includingfuelfortrucksandmachinery,naturalgasandelectricitytopowerpumps,andprovideheatingandcoolingforlivestockoperations.Agricultureutilizesfertilizersandpesticidesthatareproducedinanenergy-intensivemanner.

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WhileemissionsfromenergyusearenotaccountedforundertheAFOLUsector,theyaccountforalmostonepercentofglobalGHGemissions(BlandfordandHassapoyannes,2017).Alsoomittedinthosecalculationsareemissionsfromfurtherdownstreamprocessing,forexamplefoodproductionanddistribution. Blancoetal.(2014)estimated,thatbetween1970and2010,GHGemissionsfromAFOLUincreasedby20percent,althoughthenetchangesince1990hasbeenminimal,dueinparttodecreaseinlanduseemissions.BlandfordandHassapoyannes(2017)estimated,thatduringtheperiod1990-2014emissionsfromdeforestationandotherlandusesdroppedbynearly25percent.Yet,whilelanduseemissionshavetrendeddownward,theirdeclinehasbeenoffsetbyincreasesinagriculturalemissions.Overtheperiod1990to2010,agriculture’sdirectemissionsincreasedby15percent,duetoanincreaseintheuseofsyntheticfertilizersandincreasedlivestocknumbers(BlandfordandHassapoyannes,2017).Withfooddemandprojectedtoincreasebyasmuchas60percentbetween2010and2050(FAO,2017),agriculturalGHGemissionsarelikelytoincreaseproportionately,unlesstherearesignificantoffsetseitherthroughdecreasedlanduseemissionsorincreasedemissionefficienciesinagriculturalproduction.

3.TheeffectsofclimatechangeonglobaltradeClimatechangewillpotentiallyhavesignificanteffectsoninternationaltradeinagriculturalproducts,astherelativecomparativeadvantageofcountrieschangeswithshiftsinproduction.Tradecanhelpmitigatetheimpactsofclimatechangebyhelpingtobalanceshiftsinsupplyanddemand.Butaswehaveseeninthepast,marketdistortionscausedbygovernmentpolicies,caninterferewithtradeandexacerbatepricevolatility.Figure1:Growthinworldagriculturalexports2000–2015

Source:WTOStatisticsDatabase2017

0200400600800

100012001400160018002000

20002001

20022003

20042005

20062007

20082009

20102011

20122013

20142015

2016

Billion USD

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Agriculturaltradehasincreasedmorethan200percentsince2000(Figure1).Higherincomegrowth,increasedpopulationandmoreopenmarketsbroughtoninpartbycompletionoftheUruguayRound,whichbroughtagricultureundermultilateraltraderulesanddisciplinesthathaveallcontributedtoitsgrowthinbothvolumeandvalue.Since2000,importsaccountforalargershareoftotalconsumptionformanycommodities.Forexample,soybeansimportsnowaccountforalmost43percentoftotalglobalconsumptioncomparedtoonly31percentin2000(Figure2a).Wheatimports–asashareoftotalconsumption–haveincreasedfrom17percentto24percentoverthesameperiod.Meatimportshaveincreasedaswell(Figure2b).Figures2a&2b:Importsaspercentofglobalconsumptionof(a)Cropsand(b)Livestockproducts

Source:USDAForeignAgriculturalService

0%5%

10%15%20%25%30%35%40%45%50%

2000/2001

2001/2002

2002/2003

2003/2004

2004/2005

2005/2006

2006/2007

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2010/2011

2011/2012

2012/2013

2013/2014

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2015/2016

2016/2017

2017/2018

2a. Crops

Wheat Maize Rice Soybeans

0%

2%

4%

6%

8%

10%

12%

14%

16%

2000/2001

2001/2002

2002/2003

2003/2004

2004/2005

2005/2006

2006/2007

2007/2008

2008/2009

2009/2010

2010/2011

2011/2012

2012/2013

2013/2014

2014/2015

2015/2016

2016/2017

2017/2018

2b. Livestock products

Swine Beef and veal Chicken Butter Cheese

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BaselineforecastsbytheUSDepartmentofAgriculture(O’DonoghueandHansen,2017)andOECD-FAO(2017)suggest,thatthesetrendsarelikelytocontinueoverthenexttenyears.Figures3aand3bshowprojectedimportsaspercentoftotalglobalconsumptionformajorgrainsandmeatproducts.Allyears,showmodestincreasesinimportpenetration(definedastheshareofimportsinconsumption).NeithertheUSDAbaselinenorOECD–FAObaselineexplicitlytakeintoaccounttheimpactsofclimatechangeonproduction.Figure3:Projectedimportsaspercentofconsumptionofcropsandmeats

Source:USDAERSInternationalBaselineDataSince2005therehavealsobeensignificantchangesinthecompositionoftrade.Inparticular,wehaveseenthegrowingimportanceofdevelopingcountries,bothintermsoftheirgrowingshareofglobalimportsandtheirgrowingshareofglobalexports(Figure4).Forexample,Brazilhasbecomethenumberonesoybeanexporter,surpassingtheUnitedStatessince2011.Expansionofmaizearea,particularlydoubledcroppedarea,hasboostedBrazil’sshareofmaizeexportsaswell.TheBlackSearegionoftheFormerSovietUnion

18.0%

18.5%

19.0%

19.5%

20.0%

20.5%

21.0%

0

100

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2014

/15

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/17

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/18

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/23

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/24

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2025

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2026

/27

3a.Crops

Wheat Maize Rice Soybeans Imports as percent of consumption

Import(milliontonnes)

as%ofconsumption

8.5%

9.0%

9.5%

10.0%

10.5%

11.0%

0.05.0

10.015.020.025.030.035.040.0

2014

/15

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/17

2017

/18

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2019

/20

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3b.Meats

Beef and veal Swine Poultry Imports as percent of consumption

as%of consumption

Import (milliontonnes)

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(Kazakhstan,RussiaandUkraine)nowaccountsforalmost30percentofworldwheatexportsandhasbecomeasignificantexporterofmaizeandothercoarsegrains,aswellassoybeans.Figure4:GrowthofSouth-Southtrade

Source:UNCTADStatOntheimportside,abouttwo-thirdsofsoybeanstradedgloballyareimportedbyChina,andthatsharecontinuestogrow.Chinahasbecomeagrowingmarketformaizeandothercoarsegrains,aswellasswineandpoultry(Gale,HansenandJewison,2016).AfricahasbecomealargeandgrowingmarketforriceexporterssuchasIndia,Pakistan,VietnamandThailand(Nigatuetal.,2017).South–Southtrade–asashareoftotalagriculturaltrade–hasgrownfrom13percentin2000toalmost25percentin2014(UNCTAD,2017).Thattranslatestoaboutonequarterofthegrowthoverthepast15years,duetoSouth-Southtrade.Howclimatechangewillaffectfuturetradepatternsislesscertain,althoughitwillalterthecomparativeadvantageofsomeregionsoverothers(Huangetal.,2011).Itisimportanttorecognize,thatacountry’scomparativeadvantageinproducingacropisnotstatic,butchangeswithrelativechangesinregionalyields,costs,andotherfactors(Leamer,1984).WorkbyNelsonetal(2010)suggests,thatwhiletrademaynotbeabletofullyoffsettheimpactsofclimatechange,itcanpartiallymitigateitsimpactbybalancingsupplyanddemandacrossregions.SimilarresultshavebeenconfirmedinmorerecentanalysisbyMartinezetal.(2017),whoconcluded,thatwhileregionalyieldswillbeadverselyaffected,consumptionismoremodestlyaffected,becauseoftrade.Inadditiontopotentiallyalteringregionalcropandlivestockproduction,climatechangewilllikelyresultinmorevariableweather,whichwillexacerbateyieldvolatilityandincreasevulnerabilitytoinsectsandotherpests,someofwhichmaybeexacerbatedbypropagationofinvasivespeciesthroughtrade(FAO2013;Westphaletal.,2008).

0%5%10%15%20%25%30%35%40%45%

1995

1996

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2002

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DevelopingcountryshareofglobalimportsDevelopingcountryshareofglobalexportsSouth-Southtradeaspercentofglobaltrade

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Tradehelpsmitigateregionalproductionshortfalls,thoughaswasseeninthefoodpricespikesof2007/08and2010/11,concernsarise,thattrademayexposeexportingcountriestoincreasedpricevolatilityindomesticmarkets.ResearchbyMinot(2014)andCeballoset al.(2017)foundlittleevidence,thatinternationalpricevolatilitywastransmittedtodomesticmarketsexceptinthosecases,whenexportswerelargerelativetodomesticconsumption.However,tradeintegrationinmanydevelopingcountriesislikelylimitedduetohightransportationandothertransactionscosts,whichlimittradeflows(Bouët,CosnardandLaborde,2017).Concernsoverheightenedinternationalpricevolatilityin2007/08and2010/11promptednumerouscountriestoimposeexportrestrictionsorotherinsularpolicies(Demeke,PangrazioandMaetz,2009).Manyofthosepolicies–whilepotentiallydampeningpriceincreasesindomesticmarkets–onlyservedtoincreasepricesandpricevolatilityininternationalmarkets.Moreover,suchbeggar-thy-neighborpoliciesresultedinothercountriesadoptingsimilarpolicies,furtherexacerbatingpricevolatilityandhurtingnetimportingcountries(Anderson,IvanicandMartin,2014).

4.WTOdisciplinesaffectingdomesticsupportpoliciesSincecompletionoftheUruguayRoundin1994andcreationoftheWorldTradeOrganizationthefollowingyear,agriculturehasbeenbroughtintoasystemofmultilateralrulesanddisciplines,includingmarketaccess,exportcompetitionanddisciplinesgoverningagriculturalsupport(Josling,TangermanandWharley,1996).Agriculturalpoliciesdesignedtoaddressclimatechangewouldbesubjecttothoseandmanyotherrules.AsthefocusofthepaperisprimarilyonCSApolicies,abriefdescriptionofthedomesticsupportprovisionsoftheUruguayRoundAgreementonAgriculturefollows.AmoredetailedlegalanalysiscanbefoundinHäberli(2018).14.1SupportmeasuresandtheAgreementonAgricultureDomesticsupportdisciplinesundertheWTOAgreementonAgriculture(AoA)distinguishbetweenprogramsthatareviewedasnon-orminimally-tradedistorting(so-calledGreenBoxsubsidies)andthosethatarenot(AmberBoxsubsidies).GreenBoxsubsidiesarejudgedtohaveno,oratmost,minimaltrade‐distortingeffectsandareexemptfromreductionundertheAoA.TobeincludedintheGreenBox,programsmustnotbetiedtocurrentproductionorcurrentmarketprices,andmustmeetspecificpolicycriteriaspelledoutinAnnex2oftheAoA.AmberBoxsubsidiesarejudgedtohavemorethanminimaltrade‐distortingeffects,andarecappedunderthetermsoftheAoA.AmberBoxsupportincludespaymentsto

1 Border measures are discussed in Blandford (2017).

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producersthataretiedtocurrentproductionlevels,marketpricesupportprograms,andotherpoliciesthatmakepaymentsbasedoncurrentoutputandcurrentmarketpricessuchascountercyclicalincomesupportprograms.Thesesubsidiesareconvertedintoanaggregatemeasurementofsupport(AMS)usingamethodologysetoutinAnnex3andAnnex4oftheAoA(Effland,2011).UndertheAoA,eachcountrywhichreportednon-exemptdomesticsupportduringthe1986-88baseperiodcommittedtobinditstotalAMSataveragelevelscalculatedoverthebaseperiodandthenreduceitbyaprescribedpercentage(fordevelopedcountries,by20percentover6years;fordevelopingcountries,by13percentover10years).AmberBoxsubsidiesarefurtherclassifiedintotwogroups—product-specificandnon-product-specificsupport—andbothcategoriesaresubjecttodeminimisteststhatexemptsupportbelowaspecificshareofthecurrentvalueofproductionfromthereportedAMS.Fordevelopedcountries,iftheestimatedlevelofsupportislessthan5percentofthevalueofcurrentproduction,supportisconsidereddeminimisandexcludedfromcalculationsofthetotalcurrentAMS.Thedeminimisthresholdfordevelopingcountriesis10percentofthevalueofcurrentproduction.2WTOmemberswhohadlargersubsidiesthanthedeminimislevelsatthebeginningofthepost–UruguayRoundreformperiodwerecommittedtoreducethesesubsidiesinaggregate(by20percentfordevelopedcountriesand10percentfordevelopingcountries).Countrieswithoutdomesticsupportreductioncommitmentsareeffectivelyboundbydeminimislevels.Athirdcategoryoftrade–distortingsupport,calledBlueBoxsupport,isaddressedinArticle6.5oftheAoA.AnysubsidiesandotherformsofincometransfersthatwouldnormallybeincludedintheAmberBoxareplacedintheBlueBoxiftheprogramunderwhichthoseincometransfersoccuralsorequiresfarmerstolimitproductionandbasepaymentsonfixedareaandyieldsormadeon85percentorlessofabaselevelofproduction,or,inthecaseoflivestock,suchpaymentsarebasedonafixednumberofhead.UndertheAoA,BlueBoxexpendituresarenotcappedand,therefore,notsubjecttoanylimitationorreductioncommitments.Therearealsoexemptionsfordevelopingcountries(sometimescalleda“SpecialandDifferential(S&D)Box”),coveredunderprovisionsinArticle6.2oftheAoA.Theseexemptionsincludegovernmentmeasuresofassistancetoencourageagricultureandruraldevelopment,generallyavailableinvestmentsubsidies,andagriculturalinputsubsidiesgenerallyavailabletolow-incomeorresource-poorfarmers.Lastly,asdemonstratedintheUS–UplandCottondispute,non–GreenBoxsupportmeasuresmaybechallengedundertheWTOAgreementonSubsidiesandCountervailingMeasures,ifthosemeasureswereshowntocauseseriousprejudicetoanothermember’sinterest,for

2 As a condition of its accession to the WTO, the de minimis threshold for China is set at 8.5 percent of the value of production.

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example,bydisplacingexportstothird–countrymarkets,significantpricesuppressioninworldmarketsorincreasedmarketsharebythesubsidizingcountry.4.2DefiningGreenBoxsubsidiesExemptpoliciesundertheGreenBoxmustmeetspecificcriterialaidoutinAnnex2oftheAoA.Toqualify,GreenBoxsubsidiesmustnotdistortproductionortrade,oratmostcauseminimaldistortion(Annex2,Paragraph1).Subsidiesmustbegovernment–funded(notthroughindirectsupportsuchashigherconsumerprices)andmustnotinvolvepricesupport.Inaddition,asreflectedinTable1,Paragraphs2through13ofAnnex2detailspecificcategoriesforgovernmentserviceprograms.Table1:GreenBoxCategories

Paragraph Description2 Provisionofgeneralservicesthatprovidebenefitstoagricultureortheruralcommunity

suchasresearchandextension,pestanddiseasecontrol,inspectionservices,marketingandpromotionservicesandinfrastructuralservices

3 Publicstockholdingprogramsforfoodsecuritypurposes4 Domesticfoodaidprograms6 Decoupledincomesupporttoproducers7 Governmentfinancialparticipationinincomeinsuranceandincomesafety–netprograms8 Payments(madeeitherdirectlyorbywayofgovernmentfinancialparticipationincrop

insuranceschemes)forrelieffromnaturaldisasters9 Structuraladjustmentassistanceprovidedthroughproducerretirementprograms10 Structuraladjustmentassistanceprovidedthroughresourceretirementprograms11 Structuraladjustmentassistanceprovidedthroughinvestmentaids12 Programsforenvironmentalprograms13 Paymentstoproducersindisadvantagedregionsunderregionalinvestmentprograms

In2013,MembersagreedaspartoftheBalipackagetoaddthefollowingactivitiestogeneralservicesprogramstopromoteruraldevelopment,foodsecurityandpovertyalleviation,particularlyindevelopingcountries.Includedwereprogramsrelatingtolandreformandrurallivelihoodsecurity,suchas:landrehabilitation;soilconservationandresourcemanagement;droughtmanagementandfloodcontrol;ruralemploymentprograms;issuanceofpropertytitles;andfarmersettlementprograms.

5.ThepotentialimpactofinternationaltradingrulesonclimatepoliciesUndertheUNClimateAgreementconcludedinParisinNovember2015,countriesagreedtotakeactionstokeeptheriseinglobalaveragetemperaturethiscenturyfrompre-industriallevelstobelow2°C(UNFrameworkConventiononClimateChange,2017).WithAFOLUemissionsaccountingfor24percentoftotalglobalGHGemissions,policymakerswillneedtoaddresstheprojectedgrowthinAFOLUemissions,ifthe

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objectivesoftheParisAgreementaretobemet.Moreover,reductionsmusttakeplace,whilemeetingSustainableDevelopmentGoalsofeliminatinghungerby2030.TherearebasicallythreepolicyapproachestoreducenetGHGemissions:1)taxingGHGemissionsdirectly;2)subsidizingpracticesthatwouldreduceGHGemissionsorsequesterCO2;and3)reducingGHGemissionsorsequesteringCO2throughregulation.Inaddition,therearepoliciesthataretargetedatmitigatingthefinancialimpactsofclimatechange,suchasagriculturalinsurance.ThissectionexaminessuchpoliciesinthecontextofhowtheymightimpactproductionandpotentiallybeviewedbyWTOagreements,includingtheAoA.5.1TaxingGHGemissionsIneconomics,anexternalityisthecostorbenefitthataffectsaparty,whodidnotchoosetoincurthatcostorbenefit.Unregulatedmarketswithsignificantnegativeexternalitiesareconsideredinefficientinthat,marketpricesdonotreflectthetrue(societal)costofthatgoodorservice.Becausethecostofthenegativeexternalityisnotincluded,producersproducemore(andconsumersconsumemore),thantheywouldhad,hadthecostoftheexternalitybeenreflectedintheprice.Taxingtheproducerforthecostoftheexternalitywould,intheory,“internalize”theexternality,sothatcostsandbenefitswillaffectmainlyparties,whochoosetoincurthem.CarbontaxeshavebeenproposedtoaddressthesocietalexternalitiescausedbyGHGemissionsthroughglobalwarming.Acarbontaxappliedtoagriculturalemissions,wouldhaveanumberofconsequences.Theimmediateeffectwouldbetoraisepricesofagriculturalproducts.Table2showstheeffectsofaUSD20/tonnesCO2epriceoneffectivecarbontaxesforgrains(wheat),rice,beefandchickenforselectedcountries.ThedataonGHGemissionsweredrawnfromrecentworkbyBlandfordandHassapoyannes(2017)thatderivesdirectGHGemissionspertonneofproductproducedforvariouscountries,usingFAOSTATdata.Thetaxeswerethencomparedtoaverageannualcommoditypricesfor2016(WorldBankGroup,2017)todemonstratetheirrelativemagnitudes.Table2—EffectsofaUSD20/tonnescarbontaxonselectedagriculturalpricesforselectedcountriesCountry Wheat Rice Beef Sheepmeat ChickenAustralia 3.0% 3.4% 11.0% 13.4% 0.2%Brazil 2.2% 2.5% 16.5% 16.7% 0.2%China 2.6% 4.0% 12.5% 5.9% 0.6%Ethiopia 1.2% 7.1% 71.5% 25.2% 2.8%EuropeanUnion 2.4% 13.1% 8.2% 10.1% 0.2%India 3.6% 3.5% 54.4% 22.4% 0.5%Indonesia 2.4% 5.6% 22.6% 22.3% 2.9%NewZealand 2.4% --- 8.9% 8.1% 0.2%UnitedStatesofAmerica 2.4% 5.6% 6.0% --- 0.2%

Source:BlandfordandHassapoyannes2017,WorldBankGroup2017

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BecauseoftherelativeGHG–inefficiencyofextensivelivestockproduction,beefpriceswouldriserelativetograinsandpoultry,likelyshiftingconsumptiontowardsbeefsubstitutes.Note,thatpriceimpactswouldbelesssevereforcountrieswhereagriculturalproductionismoreefficientvis-à-visGHGemissions.Intheexamplehere,theimpactofaUSD20/tonnesCO2ecarbontaxwouldhaveaproportionategreaterpriceimpactongrass-andrange-fedbeefproducers(India,Indonesia,Ethiopia),thanincountrieswhereconfinedfeedingwasmoreprevalent(EUandU.S.).WhileTable2isusefulforillustrativepurposes,inpractice,acarbontaxwouldbemuchmoredifficulttoimplement,sinceGHGemissionsdependonnumerousfactors,includingpractice,cropandregion(Eveetal.,2014).Anyestimatesderivedforacarbontaxwouldbefraughtwithuncertainty,sinceemissionsareoftenfromnon-pointsourcesandthisisthereasonwhytheyaredifficulttomeasure.Amorelikelyapproachwouldbeforcountriestoimposeamoretargetedtaxonaspecificsector,suchasfossilfuelproductionthatwouldthenhaveindirectimpactsinenergy–intensivesectorssuchasagriculture.Alternatively,capandtradeschemescouldbeintroducedthatlimitthetotalamountofemissionsandallowtradingofemissionpermits.Capandtradeschemeswouldpenalizehigheremittingproductsandservices,whileprovidingincentivesforadaptionofmoreefficienttechnologies.Butcapandtradeschemeswouldstillbechallengingforagriculture,duetothehighcostsofmonitoring,necessarytoensuretheintegrityofthetradingscheme.Domestictaxesaretypicallynotcoveredunderinternationalagreementssincetheyarelikelytodepress,ratherthanenhanceoutput.Nonetheless,asBlandford(2013)pointsout,exemptingsectorslikeagriculturefromemissionscaps,couldraisetheissueofimplicitsubsidizationbyallowingexemptsectorstosellemissionscredits.Likeacarbontax,thevalueofcarbonoffsetswouldbesubjecttosimilaruncertaintyinmeasurement,aswellasmonitoringandenforcementissues.Offsetscouldalsopresentfoodsecurityconcerns,forexample,ifcroplandweretakenoutofproductionforcarbonsequestrationpurposes.5.2ProvidingsubsidiestoincreaseGHGefficiencyinproduction UndertheCSAapproach,mitigationmeasuresforclimatechangearepromotedthatareinlinewiththe“foodsecurityfirst”objective.Oneapproachistoimproveefficiencybydecouplingproductiongrowthfromemissionsgrowth.Thisinvolvesreducingemissionsperkilogramoffoodoutput–includedinthiscalculationaretheeffectsofemissionsfromreduceddeforestationperkilogramoffood.Thesecondwayistoincreaseresourceefficiencybyincreasingproductivity.Publiclyfundedresearchisanotherwaygovernmentscanhelpmitigatetheimpactsofclimatechange,throughincreasingtheproductivityandGHG–efficiencyofplantandanimalproduction.Publicfinancingofagriculturalresearchanddevelopmenthasledtolargeandsustainedagriculturalproductivitygains(Alstonetal.,2010;AlstonandPardey,2014).Figure5showsUSagriculturalproductivitysince1948.Whileproductivityhasincreasedover150percentsince1948,inputusehasremainedmoreorlessconstant.

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Figure5:U.S.TotalFactorProductivity

Source:USDAandEconomicResearchServiceFuglie(2017)argues,thatthepublic–goodsnatureofknowledgecapital,namelythenon-excludabilityoffreeridersinenjoyingthebenefitsofResearchandDevelopment(R&D);andthesmall–holderstructureoffarming,haveimpliedamajorroleofgovernmentininvestinginagriculturalR&D.AndwhileprivateinvestmentinR&Dhasgrown,asrecentlyas2011,publicinstitutionsaccountedforaboutthree–quartersoftotalglobalspendingonagriculturalresearch(Fuglie,2017).ResearchbyBaldosandHertel(2014)pointstotheroleoftotalfactorproductivitygrowthinmitigatingGHGemissionsbyincreasingcarbonefficiency(amountofproductionperGHGemission).WorkbyWiseetal.(2009)shows,thatifproductiontechnologieswerefrozenat2005levels,land–usechangecarbonemissions(assumingnomitigationstrategies)wouldbemorethan70billiontonsCO2ehigheroverthe21stcentury,becausegreateramountsoflandwouldhavebeennecessarytoproducethesameamountoffood.However,duetotheso-calledreboundeffect,someoftheproductivitygainsmaybepartiallyoffsetbyincreasedproduction,atleastatthenationallevel,duetoimprovedprofitability.Atthegloballevel,reboundimpactsarelikelysmaller,sincedemandelasticitiesandmostproductivitygainswillbepassedthroughintermsoflowerprices.PublicexpendituresforCSAResearchandDevelopmentwouldlikelybeconsistentwithParagraph2ofAnnex2oftheAoA.Otherexamplesofgeneralservicespolicieswouldbetechnicalassistanceprogramsaimedathelpingcropandlivestockproducersdevelopandimplementnutrientmanagementplans;andresearchactivities,thatpromotesoilhealthandreduceGHGemissionsfromcroplandandlivestock.Thesepoliciesdonotinvolvedirectpaymentstoproducersorprocessors,noraretheseactivitiesfundedbytransfersfromconsumers.Butiftheydo,thesepolicieswouldbeconsideredamberandsubjecttodiscipline.

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InputsubsidiestoencourageadoptionofnewGHGtechnologieswouldgenerallybeconsideredAmberBoxprograms,sincetheyaretiedtoproductionortheinputitself.Theexceptionwouldbeforresourcepoororlowincomefarmersindevelopingcountries,whocouldclaimthesemeasuresunderArticle6.2oftheAoA.

5.3ProvidingsubsidiestoreduceGHGemissionsorsequestercarbonClimatesmartpoliciesthatprovideproducersfinancialincentivestoadoptpolicieswhichreduceGHGemissionsorincreasecarbonsequestration,mustmeetspecificcriteriatobeconsidered“GreenBox”undertheAoAandthisiswhytheyareexemptfromWTOdiscipline.Forexample,consideraclimatesmartpolicythatwouldpaylivestockproducerstoinstallanaerobicdigesterstocaptureGHGemissions.Toqualifyasanenvironmentalprogramconsistentwithparagraph12ofAnnex2oftheAoA,theamountofthepaymentmustbelimitedtothe“extracostsorlossofincomeinvolvedwithcomplyingwiththegovernmentprogramme”(Paragraph12(b)).Totheextentthatsuchpoliciesalsoprovideanincentivecomponenttoencourageadaptation,thismaymakethemineligibleforGreenBoxprotection.Cost-shareprogramsforestablishingconservationpracticesonagriculturallandhavesupportedimplementationoffarmingpracticesandstructuresthatreducelossoffertilitythroughsoilerosion;facilitateimproveddrainage,waterstorage,andmoreefficientirrigation;andprovidemanurestorageandassistancewithmeetingnutrientmanagementregulations(Claassen,DuquetteandHorowitz,2013).IntheUnitedStatesofAmerica,programsliketheEnvironmentalQualityIncentivesProgramandtheConservationStewardshipProgram–thathelpcoverinputcostsandincomeforegoneforenvironmentallyfriendlypractices–mayreduceproductivityortakesomeyearstoachievefullproductioncapacity.Theproductioneffectsofcost–shareprogramsaredifficulttocalculatefortworeasons.First,theadditionalityofsuchprogramsisoftenuncertain,whichmeansthatsomeproducerswouldhaveadoptedsuchpracticeswithoutincentivepaymentsorcost–share(McFarland,2011;Claassen,DuquetteandHorowitz,2013;Mezzatesta,NewburnandWoodward,2013).Shouldsubsidiesbeprovidedforallproducers,whouseapracticeorforjustthose,whonewlyadoptsuchapractice?Intheformercase,the“additionality”gainedbythesubsidymaybesmall,inwhichcase,themarginalcostofadoptionisquitehigh.Ifthesubsidyisrestrictedtojustthose,whonewlyadoptapractice,producerswhohadpreviouslyadoptedthepracticemayhaveincentivesnowtodiscontinuethepractice,iftheybelievetheywillbepaidforre–enrollingintheprogram.Second,althoughtheimpactofsomeofthesepracticesoncropyieldsmaybebeneficialoverthelongrunbyimprovingsoilfertility,plantingconditions,andwateravailability–thatcouldpotentiallyleadtoincreasedproductionandlowerprices–intheshortruntheimpactsarelikelyminorand,forsomepractices,productivitywillremainbelowconventionalpractices.

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CSApoliciestoencouragecarbonsequestrationincludeputtingcroplandintolongtermsetasides.Forexample,theUnitedStateshasoperatedtheConservationReserveProgram(CRP)since1986.UndertheCRP,producersarepaidayearlyrentalpaymentinexchangeforremovingenvironmentallysensitivelandfromagriculturalproductionandplantingspeciesthatwillimproveenvironmentalquality.CRPcontractsarecompetitivelyawardedonthebasisofenvironmentalbenefitsandtypicallyextendfor10to15years.Sinceitsfirstyearofoperationin1986,theCRPhasidledonaverage12.6millionhectares(ha)annually,butinrecenthigh–priceyears,contractsmaturedandmanyfarmersoptedtobringlandoutofretirement.The2014farmbillrestrictstheenrollmentoflandintheCRPto10.1millionhectares(ha)–equivalentto25millionacres–,andasofSeptember2017,only9.5millionhectares(ha)wereenrolledintheCRP,downfrom13millionhectares(ha)atitspeak.Thereductioninlanduseintensity,providedbytheCRP,canprovidemultipleenvironmentalbenefits,includingsubstantialGHGmitigation,=thatoccursascarbonissequesteredinsoilsorvegetation(USDA,2016).RecenteffortsbytheUSDepartmentofAgriculturetoaugmentbenefitsundertheCRP,haveincludedenrollinglandsintopermanentorlong-termeasementswithintheAgriculturalConservationEasementProgram(ACEP),withStateEasementProgramsundertheConservationReserveEnhancementProgram,andwithprivatepartners.Othereffortsincludetargetingeligiblelandstoenrolladditionalriparianbuffers,wetlands,andotherconservationpracticeswithlargeGHGmitigationbenefitsintoCRPandenrollingorganicsoils–ahighlyconcentratedsourceofGHGemissions–intoCRPorACEP.Twoconcernsarisewithlandsetasideprograms.First,idlingcroplandcouldpotentiallyexacerbatefoodsecurity.Bakeretal.(2010)considertheimpactofacarbonoffsetprogramthatpaysproducerstoconvertcroplandtoforestland.AssumingacarbonpriceofUSD50/tonnesCO2e,theyfoundthatproducerswouldafforestasmuchcroplandas15.8millionhectares(ha).Whilefarmincomeswouldrise,consumerswouldlose.Second,afforestingcroplandmayencourageindirectlanduseeffectselsewhere.Tothedegreethatretiringcroplandreducessupply,theresultingpriceincreasesmayencourageproduction(reboundeffect),particularlyincountrieswherecropproductionmaybelessGHG–efficientorwhereexpansionofproductionoccursthroughdeforestationorpastureconversion.Tothedegreepossible,carbonsequestrationeffortsviaafforestationofcroplandshouldbetargetedtowardscroplandwiththepoorestandleastefficientyieldsfromaGHGperspective.5.4Measurestoincreaseresiliencetoproducerstotheeffectsofclimatechange UndertheAoA,theGreenBoxaccommodatesanumberofmitigationmeasuresthatcanhelpproducersadjusttoincreasedweathervolatilitythatwilllikelyaccompanyclimate

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change.Agriculturalinsuranceisavailableinover100countries(MahulandStutley,2010).Annex2oftheAoAalsoaccommodatespublicreserveprogramsthatcanhelpbuffertheimpactsofproductionshortfallstomeetfoodsecurityneeds.Forproducers,whoselivelihoodsareadverselyaffectedbyclimatechange,Annex2allowsstructuraladjustmentprograms,suchasproducerretirementprogramstotransitionproducers,tomoreeconomicallyviablelivelihoods.And,throughtheBaliDecision,Annex2wasextendedtoincludeactivitiestopromoteruraldevelopmentandlandreform,suchaslandrehabilitation;soilconservationandresourcemanagement;droughtmanagementandfloodcontrol;ruralemploymentprogrammes;issuanceofpropertytitles;andfarmersettlementprogrammes.5.4.1Agriculturalinsuranceanddisasterassistance Agriculturalinsuranceanddisasterassistanceprogramscanpotentiallymitigatetheeffectsofincreasedclimatevariabilityduetoclimatechange(SkeesandEnkh-Amgala,2002;FAO,2013).Disasterprogramsaretypicallypaymentprogramsthatcompensateproducersforlossesincurredduetoanaturaldisaster.Suchprogramsoftenareinitiatedexpost,whichmeans,thataproducermayhavenoguaranteeofreceivingsuchapaymentattimeofplanting.Insurance,bycontrast,guarantees,exante(typicallypriortoplanting)apaymentcontingentonaqualifiedloss.Inreturn,theproducertypicallypaysapremiumforsuchprotection,thoughthepremiumisoftentimessubsidizedbythegovernment.3IndevelopedeconomiessuchastheUnitedStates,Japan,Canada,andEurope,agriculturalinsuranceisgenerallycharacterizedbyindemnity–basedprogramsthatprovidecropandlivestockcoverageagainstnamedperils,multipleperils,and,morerecently,priceandrevenuerisks.Individual–basedcoverageisexpensive,becauseofthehighcostofadministeringcontractsandadjustinglosses.Moreover,individual–basedpoliciesarepronetomoralhazardandadverseselectionproblems,whichaddtothemonitoringcosts4(Kalra,2013).Becausethesecostsaregenerallyhighrelativetootherriskmanagementstrategies–suchascropdiversification,futuresmarkets,oroff–farmincome–,demandforagriculturalinsuranceproducts,intheabsenceofsubsidies,tendstobelow.Thisexplainswhyprivateunsubsidizedmarketsformultipleperilinsurancehavegenerallyfailed(WrightandHewitt,1994;GoodwinandSmith,1995)andwhythelargerinsuranceprogramsintheUnitedStates,Canada,andJapanaregenerallyhighlysubsidized.Intheircomprehensivereviewofagriculturalinsuranceprograms,MahulandStutley(2010)found,thatalmosttwo-thirdsofthecountriessurveyed,reportedthattheysubsidizedpremiumcosts.Thesecountriesaccountedformorethan90percentoftotalpremiums,atanaveragesubsidyrateof47percent.Forexample,thepubliccostsoftheUSprogram,whichareestimatedataboutone-thirdof2014totalglobalpremiumvolume,areprojected

3 Not all disaster assistance programs are ex post. Some countries offer producers ex ante disaster protection. In such a case they operate effectively like a fully subsidized insurance program (Glauber, 2004). 4 Moral hazard problems arise when insured producers alter their behavior after purchasing insurance to affect their likelihood of collecting an indemnity. Adverse selection problems arise when risks vary across insurance buyers and buyers know more about the risks they face than does the insurer who sets the rates (Hirshleifer and Riley, 1992).

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toexceedUSD8billionannuallyoverthenext10years,anexpenditureofalmost90centsforeveryUSD1premiumwritten(CBO,2017).Withsuchhighprogramcosts,itislittlewonder,thatthelargeragriculturalinsuranceprogramsaregenerallyfoundindevelopedcountries,orincreasingly,inlargeemergingeconomies,likeIndiaandChina.Thehighcostsofcontractingwithlargenumbersofdispersedsmallholders–whentherearefixedcoststocontractingandpoorlydevelopedlegalinstitutionsforenforcingcontracts–haveledmanytoconclude,thatconventional,indemnity–basedinsurancedoesnotworkforsmallholderfarmersindevelopingcountries(Hazell,1992).Toaddresstheseconcerns,index–basedinsuranceproductsbasedonspecificperilsorevents(forexample,regionalyieldloss,drought,orflood)andrecordedataregionallevel(forexample,byregionalweatherstations)havebeenpromoted.Examplesofsuchproductsincludearea–yieldinsurance,wherepremiumsandindemnitiesarebasedontheaverageyieldinaregion,orweather–basedindices,suchasrainfallinsurance,whereproducersreceiveapaymentifrainfallintheregionfallsbelowadesignatedlevel(Skees,Hazell,andMiranda,1999;Carter,2012).Suchcontractstypicallyminimizemoralhazardandadverseselectionissues(Miranda,1991)andcanbeprovidedatlowercosts,becauselossadjustmentandmonitoringcostsaresomuchlower(Skees,BlackandBarnett,1997).Indexinsuranceschemeshavebeenpilotedinanumberofdevelopingcountries,withsomewhatlimitedsuccess(MirandaandFarrin,2012;Carteretal.,2014).Participationinpilotprogramshasbeengenerallylimited(Binswanger-Mkhize,2012).Smith(2016)pointsout,thatsmall–holderfarmersalreadyhavewaysofmitigatingrisk,includinginformalcommunity–basedinitiatives,enterprisediversification,andoff–farmemployment.Anotherdrawbackistheexistenceofbasisrisk;thatis,thedegreetowhichtheregionalyieldorweathervariableiscorrelatedwiththeindividualfarmyield.Producers,whoseyieldsarepoorlycorrelatedwiththeaggregateindexmayfindsuchinsuranceofferstobeinsufficientriskprotection;thus,basisriskcanacttolimitdemand.OneexceptionisIndia’sWeatherBasedCropInsuranceScheme,anindex–basedinsuranceprogramthathasgrownconsiderablysinceitsintroductionin2007toincludemorethan9millionIndianproducersin2010–11,withacombinedcommercialpremiumvolumeofaboutUSD260million(Clarkeetal.,2012;Mahul,Verma,andClarke,2012).However,theprogramisheavilysubsidized,andparticipationismandatory,ifproducersparticipateingovernmentcreditprograms.RecentworkbyBertram-HuemmerandKroehnert(2018)oflivestockindexinsuranceinMongoliaconcludes,thatinsurancemitigatedtheimpactsofdroughtforproducers,whoparticipatedinthepilot.Somebelieve,thatthepotentialmarketforweather–basedinsuranceproductsismorelikelylimitedtoinsuringrelativelylargegroupsoffarmers,eitherdirectlyorindirectlythroughaggregators,suchasinputproviders,creditproviders,orbuyersincontractfarmingsituations(Binswanger-Mkhize,2012;Smith,2016).Anotherpotentialuseofweather–basedcontractswouldbebynationalgovernmentstomitigatewide–spreademergencieslikedroughts(MirandaandFarrin,2012).

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AgriculturalinsurancehaswitnesseddramaticgrowthsincethelaunchoftheUruguayRound,largelytheresultofsubstantialgovernmentsupportmeasures.Thelevelsofsupportformanyprogramshaveraisedconcerns,thatinadditiontoprovidingriskmitigation,subsidiesmaybedistortingproductionandtrade.Whencropinsuranceisavailableandpriced,sothatthefarmcanacquirecoverage,riskaversefarmsproducemore.Butthepuresubsidyimpactalsomatters.RecentpapersbyBabcock(2015)andDu,FengandHennessy(2017)pointout,thatifproducersareparticipatinginthecropinsuranceprogramprimarilyto“harvest”subsidies,theyarenotactingoptimally.Thismeans,thattheyarenotchoosingoptimallevelsofcoveragetomaximizesubsidies.Theirstudiesconclude,thatfarmers’decisionsabouthowmuchcropinsurancetobuy,arenotgenerallyconsistentwitheitherexpectedprofitorsimplemodelstakingriskaversionintoaccount.Farmersdonotpickcoveragelevelsthatmaximizeexpectedsubsidynordotheydemandfullinsurancecoverage.However,overtime,producershavetendedtosignupforhighercoveragelevels,wheretheperunitsubsidiestendtobehigher.Glauber(2013)shows,thatintheUnitedStatesofAmericatheaveragecoveragelevelsformostrowcropshavegrownsignificantlyandcontinuouslysincethelate1990s,whensubsidieswereincreasedforhighercoveragelevels.MeasurementofimpactsoftheUScropinsuranceprogramhavefocusedonplantedareaandtheeffectsofinsuranceoninputuse.Goodwin,Vandeveer,andDeal(2004)examinedMidwesterncornandsoybeanproducersandwheatandbarleyproducersintheNorthernPlainsandfound,thata30percentdecreaseinpremiumcostswerelikelytoincreasebarleyacreagebyabout1.1percentandcornacreagebylessthan0.5percent.Soybeanandwheatacreageshowednostatisticallysignificantimpact.Ligon(2012)analyzedtheimpactofcropinsuranceonspecialtycropsandconcluded,thattheintroductionofcropinsurancehadalargeandpositiveimpactontreecrops,butanegligibleimpactonnon–treecrops.GoodwinandSmith(2012)havequestioned,whethertheresultsofearlierstudiescontinuetoberelevant,giventhatsubsidylevelsaremuchhighernowthanwhenearlierresearchwasconductedandrevenuepolicieshavelargelyreplacedyieldcoverages.Forexample,theGoodwin,Vandeveer,andDealstudyexaminedtheeffectsofinsurancesubsidiesovertheperiod1986–1993,priortoenactmentofmajorlegislationin1994and2000,thatdramaticallyincreasedsubsidylevels,andpriortotheintroductionofrevenueinsurance(Glauber,2004).Morerecently,Yu,SmithandSumner(2018)found,thatincreasedcropinsurancesubsidyrateshavehadsignificantlypositiveimpactsonproductionofmajorfieldcrops,butthemagnitudeoftheoverallproductionincreaseshavebeensmallasashareoftotalproduction.Theaforementionedstudieshavemostlyindicated,thatcropinsurancesubsidieshavehadsmallimpactsonproductionoverallinareas,whereinsuranceisbroadlyavailableacrosscrops.Cropinsurancelikelyhaslargerimpactsoncropchoicewheninsuredcropscompeteagainstuninsuredcrops,orwhencrops–whererevenueinsuranceisavailable–competeagainstcrops,whereonlyyieldinsuranceisavailable(WuandAdams,2001).Glauber(2017)pointedout,thatmeetingthestrictcriteriainparagraph7(incomeinsurance)orparagraph8(naturaldisasterandcropinsurance)ofAnnex2oftheAoAmay

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makeitdifficulttoreportinsuranceprogramsintheGreenBox.Forexample,bothParagraphs7and8,limitcoverageto70percentofexpectedincomeoryieldandestablishguaranteesbasedon5yearsorlessofhistoricaldata.Mostarea-basedyieldprogramsorweather-basedderivativeproductstendtoofferhighercoveragelevelsandcoveragelevelstendtobebasedonexpectedyieldorincomeoutcomes,whichmaydifferfromaveragesofpastoutcomes.Moreover,the70percentcoveragelimitisarguablyoverlystringentforindexproducts,sinceindexvolatilityistypicallysubstantiallylessthanvolatilityforindividualyieldorrevenue-basedcoverage.Glauber(2017)noted,thatbecauseofthevariancewithAnnex2criteria,mostcountries–thatnotifyinsuranceprogramstotheWTO–notifythemasAmberBoxprograms.Increasedyieldvariabilityduetoclimatechangewillincreasethecostsofinsuringtheserisks,aspremiumcostswillrise.Thismayreducetheattractivenessofagriculturalinsuranceasamitigationoption,unlessgovernmentscontinuetosubsidizealargeshareofthepremiumcosts.Andinsurancecompaniesmaybelesswillingtounderwriteriskswithoutlargepublicsupportintheformofreinsurance(Glauber,2004).5.4.2Publicstockholdingprograms Liketrade,stocksservetomitigatetheimpactofproductionshortfalls(WilliamsandWright,1991).Privatestockholderstypicallyholdinventorieswhenexpectedspeculativeprofitsarenon–negative.Thishappens,whenexpectedpricesequalorexceedthecostofpurchasingandstoringthecommodity.Whensuppliesareabundantandpricesarelow,stockholderstendtopurchaseandholdmorestocks.Duringperiodsofscarcity,whenpricesarehigh,stockholdersreleasestocksontothemarketandinventorylevelsfall.Stocks,muchliketrade,tendtobuffertheimpactsofsupply.Unliketrade,whichmaybenegative(imports)orpositive(exports),stocksarelimitedinthat,onecanstoreforfutureshortfalls,butcannotborrowfromthefuturetomitigatecurrentshortfalls.Publicstockholdingprogramsdatebackatleasttwothousandyears(Sumner,AlstonandGlauber,2010).Forexample,intheBiblicalstoryJosephtellsthePharaohtostoregrainduringtimesofabundancetoforestallshortagesduringtimesofdrought(Genesis41:53–57).Chen(1974)describedstockholdingschemesinChinainthefirstcenturyBCE.Morerecently,theUnitedStatesofAmericaintroducedgovernmentstockpilingprogramsinthe1930s(GlauberandEffland,2017)andtheEuropeanUnionintroducedpriceinterventionschemesunderitsCommonAgriculturalPolicyinthe1960s(Josling,1974).SubsequentreformsintheUnitedStatesofAmericaandtheEuropeanUnionhavegreatlydiminishedtheroleofthosepublicstockholdingprograms,butlargenationalreserveprogramsexistinmanydevelopingcountriessuchasChinaandIndia(G20,2011).Large-scalepublicstockholdingprogramshavebeencriticizedforanumberofreasons(WrightandPrakash,2011).First,theytendtobecostly,bothintermsofcostsofprocurementandthecostsofstorage.Second,stockholdingprogramsoftenoperateonpre–announcedprocurementpricesthatwhensethighrelativetocurrentmarketpricescanleadtolargestockacquisitionsanddistortproductiondecisions.Theexperienceofthe

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EuropeanUnion,UnitedStatesofAmericaandmorerecently,China,hasbeenthatsuchpoliciescanleadtoburdensomegovernmentstockpilelevels.Thosestockscanfurtherdistortmarketswhengovernmentsdecidetodrawdownpublicstocksbydumpingthemonworldmarkets.Lastly,publicstockholdingprogramsoftenoperateinamannerthatdiscouragesprivatestockpiling,whichreducestheeffectivenessinstabilizingmarketprices.Unlikelargescalebufferstockschemes,smallpublicreservesforpurposesofmeetingshort–termemergencyfoodneedscanhelpmitigateproductionshortfalls,particularlyincountries,wheretransportationcostsmaylimitordelayimportsofneededsupplies.Inaddition,theiroperationislesslikelytodisruptstockholdingbymerchants,andotherprivatesectormarketparticipants.OnesuchexampleistheWorldFoodProgramme’s(WFP)ForwardPurchasingprogramthataimstoachievemorerapidandcost-effectivefooddeliverytobeneficiariesacrosscountriesinvariousregions(WFP,2010).TheAoAallowsforcertainpublicly-fundedgovernmentprogramswithno(oratmostminimal)tradedistortingeffectsoreffectsonproduction,tobeexemptedfromdomesticsupportreductioncommitments,providedtheyalsomeetpolicyspecificcriteriathatarelaidoutinparagraph3ofAnnex2oftheAoA.Ofparticularconcernis,howcountriesprocuregrainorotherfoodstuffsforthereserve.Ifprocurementisbasedonpre-announcedstatutorypricesthatexceedbase-periodreferenceprices,thencountriesmustreportthesemeasuresasAmberBox(andifthesupportforthosecommoditiesexceeddeminimislevels).Theprovisionsinparagraph3havebeencontroversialintheWTOwithsomedevelopingcountriesseekingtorelaxcriteriaintheprovisionstoallowforpublicstockholdingprogramsindevelopingcountries.Thechangeshavebeenstronglyopposedbyanumberofdevelopedcountriesandexportingdevelopingcountries,whichexpressedconcern,thatifadministeredpricesaresethighenough,theywoulddistortproducerproductiondecisions,potentiallyleadingtosurplusesthatcoulddepressglobalmarketprices.5.4.3Structuraladjustmentpayments Climatechangecouldhavesevereadverseimplicationsforproducersinaffectedregions.Incaseswhereclimatechangehasdramaticallyaffectedcropsorlivestockproduction,structuraladjustmentprogramscouldhelpcountriesmitigatethoseimpactsbyprovidingaidtobuildregionalinfrastructuretosupportalternativecrops,orevenbytakinglandoutofcroporlivestockproduction,orinmoreextremecasesbyassistingproducerswholeaveagriculturealtogether.Structuralmeasuresthataredesignedtoassistpermanentlydisadvantagedproducersorregions,arecoveredinAnnex2oftheAoAunderParagraph9(producerretirementprograms),Paragraph10(resourceretirementprograms),Paragraph11(regionalinvestmentaids)andParagraph13(regionaladjustmentprograms).Duetothecostsofsuchprograms,themeasures–coveredunderParagraphs9,10,11and13–havebeen

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largelyusedbydevelopedmembers,suchastheEuropeanUnionandtheUnitedStatesofAmerica.Internationalfundingwilllikelybenecessarytoassistpoorercountriesinmakinglargestructuraladjustmentsofthiskind.5.5Regulatorypoliciestoaddressclimatechange Inadditiontosubsidiesandtaxes,climatechangemitigationcanalsobeimposedthroughregulation.RestrictionscouldbeplacedoncertainpracticestoreduceGHGemissions(forexample,regulatinghowmanureismanaged)orbyregulationsthatmandatetheproductionofproductsthataremoreGHGefficient.Biofuelmandateshavebeentoutedasclimatesmartpolicies,thoughtheyremaincontroversial,becauseoftheirpotentialimpactonGHGemissions,whenagriculturalproductionpracticesanddirectandindirectlanduseeffectsareconsidered(USDA,2016).UnitedStatesofAmericabiofuelpolicieshavestimulateddemandforbiofuelsandtheirfeedstocks.From2005to2011,USproductionofcorn-basedethanolincreasedfrom3.9billiongallonsto13.9billiongallons,atanannualgrowthrateofalmost24percentperyear.Cornuseforethanolgrewbyabout3.4billionbushels,accountingformorethan40percentoftotalcornusein2011/12.UnitedStatesofAmericabiodieselproductionrosefromjust90milliongallonsin2005tomorethan1.2billiongallonsby2014.About25percentofsoybeanoilusegoestobiodieselproduction;otherimportantfeedstocksincludeanimalfatsandothervegetableoils.

AsBabcockandFabiosa(2011)pointout,anumberofotherfactorswerecriticalforethanol’sgrowth.First,thephase-outofMethylTertiaryButylEster(MTBE)asagasolineadditivein2004and2005boosteddemandforethanolasitsreplacementinoxygenatedfuelmarkets.Thisgrowthinethanoldemandcombinedwithexistingdemandsubsidiesandalimitedsupplyofethanoltogreatlyincreaseethanolprices,ledtothewideprocessingmarginsin2006and2007.Largemarginsfurtherspurredinvestmentinethanolproductioncapacity.Second,therapidriseinoilpricesbeginningin2006encourageddiscretionaryblendingofethanolasasubstituteforgasoline.Therapidriseincornandothercommoditypricesin2007–2008promptedconcernsabouttheimpactofethanolonfoodpricesbothintheUnitedStatesofAmericaandabroad.Manycritics,likeWright(2014),blamedbiofuelproductionforincreasedpricesandvolatility.Condon,KlemickandWolverton(2015)reviewedawiderangeofstudiesthatconsideredtheimpactofethanolproductiononcornpricesduringtheperiod2007–2010.Theirmeta–analysisconcludesthataboutone-thirdofthepriceincreaseincornpricesovertheperiodwaslikelyduetoincreasedethanolproduction.Since2011,UnitesStatesofAmeriicacornethanolproductionhasremainedrelativelyflatatabout14to15billiongallons,reflectingautomobileperformanceconstraintsthatlimitethanolpenetrationinmotorfueluseat10percent(theso–calledblendwall).Today,theblendertaxcreditsforethanolhavebeeneliminatedashavethehighsupplementalduties

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onethanolimports.TheRenewableFuelStandard(RFS)mandatesestablishedundertheEnergyIndependenceSecurityActof2007havebeenrelaxedreflectingtheblendwallconstraint.Asaresult,cornuseforethanolremainsatabout5.1billionbushelsperyearandisnotprojectedtogrowmuchoverthenext10years(O’DonoghueandHansen,2017).TheRFS’simpactoncurrentcornpricesislikelysmall.Ethanoliscurrentlypricecompetitiveasanoctaneenhanceringasolineproduction(IrwinandGood,2015).Asaresult,evenwithloweroilprices,ethanolproductionmarginsremaincompetitiveandethanolproductionlevelshaveremainedabovemandatesundertheRFS.Thus,eliminationofthemandateswouldlikelyhavelittleimpactonethanolproductionandhencecornuseandprices,atleastintheshortrun.Overthelongrun,itscompetitivenesswouldlargelybedrivenbytherelativepricedifferencebetweencornandpetroleumabsentconsumptionmandates.Bycontrast,UnitedStatesofAmericabiodieselproductionisheavilydependentonthemandatesandthecurrentUSbiodieseltaxcredit,whichprovidesUSD1/galloncreditforblendersofbiodieselfuel.UndertherecentRFSfor2016,mandatesforbiodieselweresetat1.9billiongallons.Intheabsenceofthemandatesandtaxcreditsitisunlikelythatbiodieselproductionwouldbemorethanone-thirdofcurrentlevels,asanumberofstatesandmunicipalitiesmandatebiodieseluse.Lastly,concernshavebeenraisedabouttheimpactofbiofuelpoliciesonindirectlandusechange(Searchingeretal.,2017).ThemodestGHGemissionsreductionduetofirstgenerationbiofuel(suchasmaize)usemaybelargelyoffsetbytheimpactofhigherpricesonworldproduction,particularlyifproductionexpansionisaresultofdeforestationorpastureconversion.WTOdomesticsupportissuesarepotentiallyraised,whensubsidiesareusedtoencouragebiofuelproductionorconsumption,which,inturn,haspotentialimpactsonfeedstockproduction(forexample,cornforethanolproduction,soybeansforsoybeanoil-basedbiodieselproduction).Assuch,biofuelpoliciesdistortfeedstockproductionandthisisthereasonwhytheyareamberinnature.Forexample,underitsBiomassCropAssistanceProgram(BCAP)theUnitedStatesofAmericaprovidesfinancialassistancetoownersandoperatorsofagriculturalandnon-industrialprivateforestlandwhowishtoestablish,produce,anddeliverbiomassfeedstocks.TheUnitedStatesofAmericahasnotifiedBCAPexpendituresasAmberBox.

6.DesigningWTO-compatibleCSApolicies ClimateSmartAgricultureaimstoachievesustainableagriculturaldevelopmentforfoodsecurityunderclimatechange.Forthemostpart,thosegoalsarecompatiblewiththeWTOgoalsoffreeandopentrade.Indeed,aswasdiscussedinSection3,internationaltradeisitselfamitigatingstrategyinmeetingthefoodsecuritychallengesofclimatechange.An

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opentradingsystemwillbestservethepotentialneedsofbalancingfuturesupplyanddemandregardlessofhowthosefactorswillbeaffectedbyclimatechange.Tothisend,furtherprogressinloweringtariffsandotherbordermeasuresandeliminatingtrade-distortingdomesticsupportwillhelpfacilitatetimelyandappropriateexportstomeetfoodsecurityconcernsoverthelongrunandmoreimportantly,duringtimesofdistresscausedbyclimate–inducedcropfailures.Inaddition,progressshouldbemadetowardseliminatingtheuseofexportrestrictionsandotherdistortions.Ideally,theexternalitiescausedbyGHGemissionswouldbefullyincorporatedinmarketprices;inpractice,thiswilllikelyneverbethecase.Nonetheless,CSApoliciesaimedatreducingGHGemissions,orsequesteringCO2,ormitigatingtheeffectsofclimatechangeitself,shouldnotbebackdoorwaysofpromotingprotectionismordistortingdomesticproduction.Suchpolicies,whileattractivefromanarrowdomesticperspective,willlikelyhavemoreconsequentialadverseimpactsininternationalmarkets,particularlyfordevelopingcountrieswhowillbelesslikelytoaffordsuchsupportmeasures.Inthissense,CSApoliciesshouldbecompatiblewiththeoverarchingconditionsoftheGreenBoxofprovidingminimaltrade–orproduction–distortingsupport.ThatisnottosaythatreformstotheprovisionsinAnnex2shouldnotbeconsidered.AsGlauber(2017)pointsout,theAnnex2provisiongoverninginsurancearenotwelladaptedtocurrentinsuranceprograms,particularlyindexinsuranceandweatherderivatives,whichareincreasinglybeingusedindevelopingcountries(MirandaandFarrin,2012).Thatsaid,heavilysubsidizedinsuranceprograms,particularlythosethatprovidepriceandrevenueprotection,candistortproductionsincetheyaredirectlycoupledtoactualproduction.Increasingproductivity,particularlyindevelopingcountrieswhereyieldgapsareoftengreatest,shouldbeapriorityofanyCSApolicy.MorepublicR&DshouldbedirectedtowardsclimateresilientvarietiesandtowardsanaimofincreasingGHGefficiency.WhileArticle6.2oftheAoAallowsforsubsidizedinputusetoincreaseproductivityinresourcepoordevelopingcountries,inputsubsidiesfordevelopingcountriesthatpromotelessGHG–efficientproductiontechnologiesshouldbeviewedwithmorecaution.Resourceretirementprogramsmayoffersignificantopportunitiesforcarbonsequestrationthroughafforestation.However,theimpactofsequesteredcarbononGHGemissionsmustbeanalyzedinaglobalcontextintermsofindirectlanduseaswellasfoodsecurityconcerns.Likewise,biofuelmandatesshouldbelimitedtonon–foodandnon–feedfeedstocks,thoughlanduseeffectsofconvertingpotentialcroplandtobiofueluseremainanissueofconcern.

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7.Conclusions

AddressingclimatechangeinawaythatensuresmeetingtheUNSustainableDevelopmentGoalswillposesignificantchallengesintheyearsahead.Ofbroaderconsiderationiswhethertheexigenciesofclimatechangerequirerethinkingrulesunderlyingtheglobaltradingsystem,particularlythosegoverningdomesticsupport.ShouldmeasuresthatencouragetheadoptionofGHG–efficientpoliciesbeencouraged,eveniftheyincreaseproductionandtrade?Suchpoliciesmaybeefficientfromaglobalperspective,yetcouldleadtoadverseconsequencesforproducersattheregionalorcountrylevel—particularlypenalizingdevelopingcountrieswhoseresourcesmaybeinsufficienttomatchthatofmoredevelopedcountries.ClimateSmartAgricultureisanimportanttooltohelpmitigateagriculture’scontributiontoGHGemissionsaswellashelpproducersandcommunitiesbetteradapttotheconditionsbroughtonbyclimatechange.FreeandopentradeshouldbeseenasanintegralpartofanyCSAstrategy.Effortsatfurtherliberalizationthroughreductionsintariffandnon–tariffbarriers,trade–distortingdomesticsupport,andexportsubsidiesandrestrictionsshouldbevigorouslypursued.

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