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Category-Level Product Environmental Footprints of Foods Recommendations for Further Evaluation Report No. CSS16-03 February 25, 2016 Martin Heller, Tara Narayanan, Robert Meyer, and Gregory Keoleian
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Page 1: Category-Level Product Environmental Footprints of Foods · Category-Level Product Environmental Footprints of Foods Recommendations for Further Evaluation Report No. CSS16-03 February

Category-Level Product Environmental Footprints of FoodsRecommendations for Further Evaluation

Report No. CSS16-03February 25, 2016

Martin Heller, Tara Narayanan, Robert Meyer, and Gregory Keoleian

Page 2: Category-Level Product Environmental Footprints of Foods · Category-Level Product Environmental Footprints of Foods Recommendations for Further Evaluation Report No. CSS16-03 February

1FoodCommodityRecommendations

1. IntroductionClimate,soilsandtopographymakefoodproductioninthestatesofOregonandWashingtonavaluableanddiverseeconomicsector.Tables1&3,below,indicatethetoprankingagriculturalcommoditiesinOregonandWashington,respectively.Inaddition,OregonandWashingtonrankasdominantU.S.producersofanumberofuniquecrops,asseeninTables2&4,makingtheirproductionpracticesrelevantnotonlylocallybuttonationalandinternationalconsumersaswell.Foodproductioncontributessignificantlytoenvironmentalconcerns,andbyextension,offerspotentialforsignificantimprovement.ProductionofthefoodconsumedintheU.S.accountsforontheorderof10%ofthecountry’stotalin-boundarygreenhousegasemissions1.Foodandbeveragescontributecloseto15%ofOregon’sconsumption-basedgreenhousegasemissions.Figure1demonstratesthecontributionbyvariousfoodsectorstothe7.9millionmetrictonsofCO2-eqattributabletofoodandbeverageconsumption(excludingrestaurants)inOregonin2014.Theseimpactsincludenotonlytheagriculturalproductionoffood,butalsocontributionsfromprocessing,distribution,andstorage.ItisimportanttonotethattheseemissionsareduetofoodandbeveragesconsumedbyOregonians,andonlyanestimated20%ofthemoccurduetoin-stateactivities.Figure2Figure3servetobetterdescribethespecificfoodsthatmakeupthehighlyaggregatedsectorsof“fruits&vegetables”and“meats”intheOregonConsumption-BasedEmissionInventory.Thesefiguresarebasedonpercapitanationalfoodavailability,combinedwithemissionfactorsforindividualfoodtypes1.Makingreductionsintheenvironmentalfootprintofsupplyingfoodrequiresanunderstandingofthesourcesofcurrentimpacts,alongwithguidanceastowhere

1Heller,M.C.andG.A.Keoleian(2014)."GreenhouseGasEmissionEstimatesofU.S.DietaryChoicesandFoodLoss."JournalofIndustrialEcology19(3):391-401.

STATEMENTOFWORK:

Reviewandrecommendationsoffoodtypesforfurtherresearch:Contractorwillprepareaseparatedocumentcontainingitsrecommendationsforwhichfoodtypes(commodities)to

studyinfurtherdetail.Forthepurposeofthiscontract,“commodity”isdefinednotonlyasa

farm-leveloutputbutratherasadistincttypeoffoodproduct.Forexample,“fluidmilk”(foruse

inmakingfoodproductsorfinalconsumptioninfluidform)isacommodity,while“yogurt”,“ice

cream”and“cheese”areseparatecommodities.Contractormayproposemorefoodtypesthan

budgetallows,andcontractormayrankorgroupcommodities(forexample“highpriority”,

“mediumpriority”,and“notrecommended”).Ataminimum,tencommoditieswillbe

recommendedas“highpriority”withatleastfouradditionalcommoditiesidentifiedas

contingencies.Recommendationswillbebasedonthequalityofenvironmentalinformation

available(basedontheresultsofliteraturescan),givingpreferencetohighvolumeproducts

producedorpurchasedinthestatesofOregonandWashington,whilealsotakingintoaccount

theorganizationalstructureoftheagriculturalandfoodindustryaswellasinterestby

institutionalbuyers.

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2FoodCommodityRecommendations

improvementeffortsshouldfocusformaximumeffectiveness.Theseanswersaren’talwaysintuitive.Forexample,aUSDAanalysisofenergyuseintheU.S.foodsystemfoundthattransportationrepresentedonlyabout3.5%theenergyusedintheU.S.foodsystemin2002,whereashouseholdactivities(refrigeration,cooking)contributed28%2.Similarly,researchersatCarnegieMellonfoundthattransportationasawholerepresentsonly11%oflife-cyclegreenhousegasemissionsassociatedwiththeU.S.foodsystem,withfinaldeliveryfromproducertoretailcontributingonly4%3.Bothofthesestudiesariseoutoflifecycleassessmentprinciples.Theobjectiveofthecurrentprojectistohighlightthosestagesofthelifecycleofindividualfoodcommoditiesthatcontributesignificantlytooverallenvironmentalimpacts(“hotspots”),toevaluateopportunitiestoreduceenvironmentalimpacts,andtoidentifyattributesandcharacteristicsofindividualfoodcommoditiesthataremeaningfulpredictorsofreducedenvironmentalimpact.Thiswillbedonethroughaseriesofsummaryreportscapturingwhatisknownabouttheenvironmentalimpactsofspecificfoodsorfoodcommodities,basedlargelyonreviewoftheLCAliterature,butdrawingfromotherscientificfieldsaswell.Thepurposeofthecurrentdocumentistorecommendthespecificcommoditiestofocusonforfurtherevaluation,aswellastoengagestakeholderstoofferfeedbackontheserecommendations.

2Canning,P.;Charles,A.;Huang,S.;Polenske,K.R.;Waters,A.EnergyuseintheUSfoodsystem;ERR-94;U.S.Dept.ofAgri.,Econ.Res.Serv.:2010.http://www.ers.usda.gov/media/136418/err94_1_.pdf3Weber,C.L.andH.S.Matthews(2008)."Food-milesandtherelativeclimateimpactsoffoodchoicesintheunitedstates."EnvironmentalScience&Technology42(10):3508-3513.

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3FoodCommodityRecommendations

4

4OregonDepartmentofAgriculture,“OregonAgricultureFactsandFigures”,July,2015.http://www.oregon.gov/ODA/shared/Documents/Publications/Administration/ORAgFactsFigures.pdf.

Table1.Oregon’stop20AgriculturalCommodities:20144(grayshadedcommodities

willnotbeconsideredinthisphaseoftheproject)

Table2.NationalRankingofOregonAgriculturalProduction:20144(grayshadedcommoditieswillnotbe

consideredinthisphaseoftheproject)

Commodity Ranking

amongstates

PercentofUS

production

Blackberries 1 100%

Boysenberries 1 100%

Hazelnuts 1 100%

Raspberries,black 1 100%

Ryegrassseed 1 92%

Orchardgrassseed 1 94%

Crimsonclover 1 85%

Fescueseed 1 61%

Sugarbeetsforseed 1 47%

Redcloverseed 1 75%

Pottedfloristazeleas 1 59%

Onions,storage 1 22%

Christmastrees 1 17%

Peppermint 2 32%

Sweetcherries 2 16%

Hops 2 12%

Dungenesscrab 3 27%

Pears 3 26%

Kentuckybluegrassseed 3 20%

Austrianwinterpeas 3 16%

Nurserystock 3 11%

Snapbeans,processing 3 5%

Raspberries,red 3 2%

Strawberries 3 1%

Garlic 3 <1%

Blueberries 4 15%

Greenpeas 4 11%

Mink 4 8%

Cranberries 4 6%

Winegrapes 4 1%

Rank Commodity Value-Dollar

1 Cattle&calves 922,031,000

2 Greenhouse&nursery 829,909,000

3 Hay 703,080,000

4 Milk 656,635,000

5 Grassseed 449,018,000

6 Wheat 302,056,000

7 Potatoes 164,703,000

8 Hazelnuts 129,600,000

9 Pears 127,392,000

10 Grapesforwine 118,320,000

11 Onions 106,334,000

12 ChristmasTrees 103,777,000

13 Blueberries 102,325,000

14 Cherries 82,709,000

15 Eggs 65,781,000

16 Mint,foroil 51,433,000

17 Blackberries 50,133,000

18 Crab 47,980,000

19 SweetCorn 45,121,000

20 Apples 42,240,000

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4FoodCommodityRecommendations

5

5USDANASS,“ValueofWashington’s2013AgriculturalProductionSurpassesTenBillionDollars,”January26,2015.http://www.nass.usda.gov/Statistics_by_State/Washington/Publications/Current_News_Release/2015/VOP_2014.pdf

CommodityRanking

amongstates

percentofUS

production

Redraspberries 1 93

Hops 1 79

Spearmintoil 1 73

Wrinkledseedpeas 1 60

Apples 1 57

Sweetcherries 1 51

Pears 1 50

Grapes,concord 1 37

Carrots,processing 1 37

Greenpeas,processing 1 34

Peppermintoil 1 31

Sweetcorn,Processing 2 25

Potatoes 2 24

Onions 2 21

Apricots 2 11

Nectarines 2 8

Grapes,all 2 5

Asparagus 3 25

Lentils 3 19

Grapes,Niagra 3 19

Prunesandplums 3 18

Blueberries 3 15

Dryediblepeas 3 12

Tartcherries 3 6

Barley 4 7

Wheat 4 7

Cranberries 5 2

Strawberries 5 0

Dryediblebeans 6 9

Peaches,freestone 7 2

Milk 10 3

Table3.Washington’stop10AgriculturalCommodities:20135(grayshadedcommodities

willnotbeconsideredinthisphaseoftheproject)

Table4.NationalRankingofWashingtonAgriculturalProduction:20135(grayshadedcommodities

willnotbeconsideredinthisphaseoftheproject)Rank Commodity Value-Dollars

1 Apples 2,189,095,000

2 Milk 1,298,880,000

3 Wheat 1,014,032,000

4 Potatoes 792,000,000

5 Cattleandcalves 706,447,000

6 Hay 675,050,000

7 Cherries 385,198,000

8 Grapes 278,640,000

9 Pears 225,392,000

10 Hops 202,101,000

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5FoodCommodityRecommendations

Fluidmilkandbutter49%

Cheese29%

Dry,condensed,

andevaporateddairyproduct18%

Icecreamandfrozendessert4%

Wetcornmilling7%

Fatsandoilsrekiningandblending18%

Sugarcanemillsandrekining

18%

Beetsugarmanufacturing

15%

Seasoninganddressing

manufacturing42%

Grainfarming6%

Treenutfarming4%

Flourmillingandmalt

manufacturing8%

Breakfastcereal

manufacturing6%

Confectionerymanufacturing

frompurchasedchocolate

7%Nonchocolateconfectionerymanufacturing

6%

Breadandbakeryproductmanufacturing

26%

Cookie,cracker,and

pastamanufacturing

13%

Tortillamanufacturing

2%

Snackfoodmanufacturing

22%

Coffeeandteamanufacturing

7%

Softdrinkandice

manufacturing56%

Breweries24%

Wineries10%

Distilleries3%

Meat&otheranimalproducts,exceptdairy,poultry&

eggs29%

Grains,BakedGoods,Cereals,Nuts

17%

Dairy13%

Beverages11%

FruitandVegetables

10%

PoultryandEggs8%

Condiments,OilsandSweeteners

4%

FrozenFood4%

OtherFoodandAgriculture

3% Seafood1%

Figure1.Foodconsumptioncontributestogreenhousegasemissionsthroughacombinationofthequantityof

foodsconsumedandtheemissionintensityofproducingagivenfood.Thisfigureshowsthepercentcontributions

ofdifferentfoodcategoriestothe“FoodandBeverages”portionofthe2014OregonConsumption-based

EmissionsInventory.

SeeFigure2

SeeFigure3

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6FoodCommodityRecommendations

Figure2.ContributionsofvariousfruitsandvegetablestothegreenhousegasemissionsassociatedwithtotalU.S.

fruitandvegetablefoodsupply.Basedon2010retail-levelfoodavailabilityfromUSDA,andmethodspresentedin

HellerandKeoleian,20141.

Figure3.ContributionsofdifferentmeattypestothegreenhousegasemissionsassociatedwithtotalU.S.red

meat(i.e.,excludingpoultry)supply.Basedon2010retail-levelfoodavailabilityfromUSDA,andmethods

presentedinHellerandKeoleian,20141.

fruitjuices19%

freshbananas9%

cannedfruit3%

freshcitrus3%

freshapples1%

frozenfruit1%

freshavocados1%

watermelon1%

driedfruit1%

allotherfruit4%

cannedvegetables14%

frozenvegetables14%

headlettuce4%

tomatoes3%

romaine&leaflettuce3%

bellpeppers2%

onions2%

potatoes2%

processedanddehydratedveg

2%sweetcorn2%

allothervegetables

7%

beef82%

veal0%

pork17%

lamb1%

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7FoodCommodityRecommendations

2. Selectioncriteria

WehaveattemptedtocombineourreviewofexistingLCAliteraturewithanappreciationoffoodproductionaswellasconsumptioninOregonandWashingtontorecommendacollectionofcommoditiesforfurtherresearchandsummaryreportdevelopment.Criteriaaccountedforintherecommendationsinclude:

• Productionconsiderations:o FoodcommoditiesproducedinlargevolumeinORand/orWA.o CommoditiesforwhichproductioninORand/orWArepresentalarge

fractionoftotalU.S.production.o CommoditiesforwhichtheenvironmentalimpactoftheirproductioninOR

andWAissignificant,basedonestimatedgreenhousegasemissionsassociatedwithon-farmproduction.

• Consumptionconsiderations:Foodsthatplayanimportantroleintheconsumption-basedemissionsofOR,and,byextension,WA.

• Dataavailabilityconsiderations:Foodcommoditiesand/orproductsforwhichtheavailableLCAliteratureisofsufficientquantityandqualitytooffersoundguidance.

• Diversityconsiderations:Foodsthatrepresentadiversityoffoodtypes,inordertodenotearangeofproductlifecyclesinthefinalsummarydocuments.Forexample,includingbothapples(ahardfruit)andraspberries(asoftfruit)maybewarrantedastheyrepresentverydifferenthandling,storageanddistributionproductchainsandmaythereforeprovidelessonstransferrabletootherfoodsoftheirtype.

Asthescopeofthisprojectislimitedtofoods,agriculturalcropsthatarenottypicallyfoodforhumans,suchasgrassandcloverseed(shadedgrayinTables1-4),werenotconsidered.Beefisnotrecommendedforfurtherevaluationinthecurrentphaseofthisprojectbasedinpartonhighvariabilityinproductionmethodsandassociatedenvironmentalimpacts.Inaddition,forcattlethatgrazeonrangelands(acommonproductionpracticeinOregon),theimpactsofgrazingonsoilcarboncanvarysignificantlyandsoilcarbonimpactslackclearstandardsforaccounting.Table5summarizesthescoringrubricusedtoarriveatrecommendedfoods.Foodsidentifiedasapotentialinterestforthisprojectweregivena0-5scoreineachoffourcategories,andarrangedbasedonthesumofthefourcategoricalscores.SubjectiverearrangementswerethenmadetoaccommodatethediversitycriteriaandtoaccountforLCAqualityscoresdeemedtoolowtowarrantfurtherresearch.Table6providesmoredetailedinformationonthefoodsproducedinlargequantitiesinORandWA,includingproductionquantityandvalueandacursoryestimateofthegreenhousegasemissionsattributabletothatproduction.ThisinformationledtothefirsttwocolumnsinthescoringrubricinTable5.Table7summarizesinformationonthequantityandqualityoftheLCAliteratureforconsideredfoodsasgatheredfromtheliteraturereview,andformsthebasisofthescoresinthethirdcolumnofTable5.Scoresinthefourthcolumn,consumptionimpact,arederivedfromthedistributionsinFigures1-3.BriefjustificationsforrecommendedfoodsfollowinSection3.

Page 9: Category-Level Product Environmental Footprints of Foods · Category-Level Product Environmental Footprints of Foods Recommendations for Further Evaluation Report No. CSS16-03 February

8FoodCommodityRecommendations

Table5.Summaryofscoringrubricandfoodsrecommendedforfurtherresearch.Higher

scoresarebetter.Thefirst15foodsarerecommendedasviableoptionsforproductfootprint

summaries.

Production

value

Production

impact*LCAdata

quality

Consumption

impact*Diversity

(foodtype)

1 Dairyanddairy

products

5 5 5 5 dairy

2 Wheatand

bread†5 5 5 4 Grain

3 Apples 5 4 5 2 Pomefruit

4 Potatoesand

products

4 5 4 2 Vegetable

5 Eggs 3 4 4 3 Egg

6 Wine 4 3 3 3 Beverage

7 Pork 1 2 5 4 Meat

8 Citrusfruits&

juices

0 0 5 3 Citrusfruit

9 Freshwater

Aquaculture

2 N/A 3 1 Fish

10 Raspberries 2 1 2 1 Softfruit

11 Pears 4 3 3 1 Pomefruit

12 Chicken N/A N/A 3 5 Meat

13 Hazelnuts 2 2 2 1 Nut

14 Bananas 0 0 4 3 Tropical

fruit

15 Tomatoes N/A N/A 5 2 Vegetable

16 Onions 3 4 1 2 Vegetable

17 Cherries,sweet 4 3 2 1 Stonefruit

18 Blueberries 3 2 2 1 Softfruit

19 Greenpeas(for

processing)

1 2 2 1 Processing

vegetable

20 Snapbeans,

processing

1 2 2 1 Processing

vegetable

21 Strawberries 1 1 3 1 Softfruit

22 Garlic 1 1 1 1 Vegetable

23 Carrots(for

processing)

N/A N/A 2 1 Processing

vegetable*“impact”isestimatedhereintermsoftherelativecontributiontostate-levelgreenhousegas

emissions.†mayincludeotherwheatproductsbeyondbreadN/A=datanecessaryforevaluationunavailablethroughUSDAQuickStats

Page 10: Category-Level Product Environmental Footprints of Foods · Category-Level Product Environmental Footprints of Foods Recommendations for Further Evaluation Report No. CSS16-03 February

Table6.SummaryofproductionquantityandvalueinO

regonandWashington,asw

ellasestimatedfarm

-levelgreenhousegasem

issions,forfoodsunderconsideration.

OregonProduction

WashingtonProduction

food2014production(lbs) a

$value(2014) a

rankingin$value

estimatedannualG

HGE

(atfarmgate) bkgCO

2 eq2014production(lbs) c

$value(2014) c

rankingin$value

estimatedannualG

HGE

(atfarmgate) bkgCO

2 eqdairy(farm

milk)

2,555,000,000656,635,000

41,263,232,000

6,584,000,0001,626,248,000

23,255,233,000

wheat

2,666,640,000302,056,000

6374,966,000

6,507,600,000719,270,000

3915,057,000

apples155,000,000

43,269,00020

17,577,0007,300,000,000

1,895,887,0001

827,806,000

potatoes2,256,200,000

178,240,0007

368,422,00010,147,500,000

771,210,0004

1,657,018,000

eggs94,914,000

65,781,00015

146,808,000254,583,000

176,805,00015

393,777,000

winegrapes

116,000,000118,320,000

1024,204,000

454,000,000251,970,000

894,728,000

pears432,000,000

127,392,0009

48,204,000832,000,000

233,824,0009

92,838,000

hazelnuts72,000,000

129,600,0008

16,982,000N/A

N/A

-

raspberries8,650,000

17,159,00037

800,00072,990,000

57,921,00024

6,754,000

aquaculture(foodfish)

N/A

1,536,587

-N/A

83,570,34917

-

strawberries

15,500,00013,125,000

403,797,000

9,900,00011,093,000

332,425,000

onions1,423,800,000

106,334,00011

251,872,0001,300,000,000

106,444,00011

147,418,000

blueberries87,300,000

102,325,00013

18,611,00094,600,000

112,638,00019

20,168,000

cherries,sweet

115,800,00082,709,000

1428,364,000

474,000,000502,370,000

7116,102,000

greenpeas(forprocessing)

82,860,00010,466,000

3920,296,000

236,880,00029,433,000

2558,021,000

Carrots(forprocessing)

N/A

N/A

-

(D)(D)

-

snapbeans(forprocessing)

6970000013,940,000

47,423,000

N/A

N/A

-

garlic1,200,000

1,080,000

354,000N/A

N/A

-

Pork(hogs)2,420,000

2,017,000

15,125,000(D)

(D)

-ahttp://w

ww.nass.usda.gov/Q

uick_Stats/Ag_Overview

/stateOverview

.php?state=OREG

ONandN

ASSQuickStatsdatabase:http://quickstats.nass.usda.gov/

bAnnualfarmgateG

HGem

issionsestimatedbasedonaverageem

issionfactorsfromFoodLCALiteratureReview

databaseand2014stateproductionvalues.chttp://w

ww.nass.usda.gov/Q

uick_Stats/Ag_Overview

/stateOverview

.php?state=WASHIN

GTO

NandN

ASSQuickStatsdatabase:http://quickstats.nass.usda.gov/

N/A=datanotavailablethroughU

SDAQuickStats

(D)=withheldbyU

SDAtoavoiddisclosingdataforindividualoperators

Marty Heller
Food Commodity Recommendations 9
Page 11: Category-Level Product Environmental Footprints of Foods · Category-Level Product Environmental Footprints of Foods Recommendations for Further Evaluation Report No. CSS16-03 February

Table7.Summaryofinform

ationgleanedfromtheFoodLCAliteraturereview

forfoodsunderconsideration.

LCAdataqualityandquantity

foodratingofLCAdata

#entriesinDB#studies

U.S.Studies?

NOTES

dairy(milkand

dairyproducts)high

8716

Yessom

ecomparisonsofconventional&

organic.Num

erousalternativeproductionmethods

represented;includesentrieson:butter(5),cheese(18),yogurt(11),wheat

high19

7Yes

Organicvs.conventionalcom

parisons,croprotationcomparisons;9additionalentriesforbread

appleshigh

2512

Yesnum

erouscomparisonsbetw

eenconventional&organic.O

nestudyexploreslocalcoldstoragevs.im

portsfromsouthernhem

isphere(inUKcontext)

Potatoesandpotatoproducts

high16

7No

conventional&organiccom

parisons;includespeeled,mashed,potatoflour,&

potatochips

eggshigh

309

Yescom

parisonsofproductionstyles

winegrapes

medium

11

4yes

comparisonsbetw

eenconventional&organic.;allfocusedongrapeproduction(donotinclude

impactsofw

inemaking)

pearslow

8

5no

comparisonsofconventional&

organicproductioninChina;studiesconsiderimpactsuptopointof

retailhazelnuts

low

92

no

raspberrieslow

5

3no

UKstudyexploresseasonality&

localvs.import

aquaculture(foodfish)

medium

27

8no

comparisonsofproductionsystem

s(recirculation,flow-through,etc)

strawberries

medium

11

7Yes

comparisonsofconventional&

organic,greenhouse&openfield,local&

import

onionsverylow

1

1no

nodetailedinfoonproductionimpacts

blueberrieslow

4

2Yes

comparesconventional&

organic

cherries,sweet

low

31

noconsiderslocalvs.im

ported

greenpeas(forprocessing)

low

31

noconsiderslocalvs.im

ported

Carrots(forprocessing)

low

52

no

snapbeans(forprocessing)

low

41

noconsiderslocalvs.im

ported

garliclow

3

1no

considerslocalvs.imported

Citrusfruitsandjuices

high17

12yes

Conventionalvs.organic.Concentratedandnot-from-concentratejuices.

Bananashigh

97

noStudylookingatU

Simporterandretailchain

Tomatoes

high47

11yes

Fieldvs.greenhouse,conventionalvs.organic,localvs.national;includesprocessedforms:paste,

chopped,puree,juice.chicken

medium

18

7yes

Variousproductionmethods

porkhigh

3915

yesVariousproductionm

ethods

Marty Heller
Food Commodity Recommendations 10
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11FoodCommodityRecommendations

3. RecommendedfoodsforfurtherevaluationanddevelopmentofCategoricalFootprintSummaries

Thefollowingparagraphsprovideabriefjustificationforthetoprecommendedcommodities.Notethatbudgetrestrictionswillpermitfurtherevaluationofonlytenfoods.Additionalfoodsareincludedheretoallowsomeflexibilityinthefinalselectionprocess.1.DairyanddairyproductsDairyisanimportanteconomiccommodityinbothOregonandWashington,andbecauseoftherelativelylargecarbonfootprintofdairyproduction,italsorepresentsasignificantfractionofthetotalgreenhousegasemissionsinthesestates(2%inOR6,3.5%inWA7).Dairyalsocontributessignificantlytoconsumptionbasedgreenhousegasemissions,contributing13%ofthefoodandbeveragesector,or1.7%ofthetotalconsumption-basedemissions.DairyproductionhasbeenextensivelystudiedwithLCA,includingacomprehensive,geo-spatiallyexplicitU.S.studysponsoredbyDairyManagementInc.TheCenterforSustainableSystems(CSS)waspartoftheresearchteamforthisnationalstudyandtheyhaveintimatefamiliaritywiththestudyanditsresults.CombinedwithothermilkLCAliterature,thiswillofferarobustsummarystatementabouttheenvironmentalimpactofdairyproductioninORandWA.Inaddition,CSShaspreviouslystudiedtheenvironmentaltrade-offbetweenenergyandwateruseinsourcingfeedcrops8andcanapplyinsightsfromthatworktodairyinthePacificNorthwest.Notethatwearecurrentlyrecommendingthatthefocusbeonfarm-gatemilk,asthebulkoftheenvironmentalimpactsforprocesseddairyproducts(cheese,yogurt,etc.)originateon-farm(aninsightthatwouldbecommunicatedthroughLCAevidenceinthefinalproductfootprintsummary).However,iftheinterestarises,specificconsumer-leveldairyproductscouldbeconsideredindependently.AccordingtoUSDAQuickStats,thereare20dairyprocessingplantsinOR,and10inWA,providingsomeindicationofthestructureofdairyprocessingintheregion.2.Wheatandwheatproducts(bread)WheatisalsoaveryimportantcropeconomicallyinbothOregonandWashington.Theregionproducesprimarilysoftwhitewheat,usedinpastries,cakes,pretzels,cookiesandAsiannoodles,butalsoincludeshardredwinterandspringwheats.Withmorethan85%ofOregon-grownwheatbeingexported,wheatisthe#1productexportedthroughthePortofPortland.AlargenumberofLCAstudiesonwheatexistintheliterature.Inaddition,wheatisoneofsevencommoditiescurrentlyrepresentedintheUSDA’sLCADigitalCommons9,withinventoriesderivedfromUSDAAgcensusandotherdataavailablespecificallyforORandWAproductionovermultipleyears.BreadproductionhasalsobeenextensivelystudiedviaLCA,offeringinsightintotherelativecontributionsofon-farm6BasedonOregon2014totalin-boundaryemissionsof60.1millionMTCO2eq.(http://www.oregon.gov/deq/AQ/Pages/Greenhouse-Gas-Inventory-Report.aspx#inventory)7BasedonWashington2012TotalGrossEmissionsof92.0millionMTCO2eq.(http://www.ecy.wa.gov/climatechange/docs/2012GHGtable.pdf)8Heller,M.C.andG.A.Keoleian(2011)."ExploringaWater/EnergyTrade-offinRegionalSourcingof

LivestockFeedCrops."EnvironmentalScience&Technology45(24):10619-10626.9https://www.lcacommons.gov/discovery/search

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activitiestotheremainderoftheproductchain.Whilestudiesthatexplicitlyexaminetheconsumerproductstypicallymadefromsoftwhitewheatwerenotuncoveredintheliteraturescan,furtherresearchwillfocusinthisdirection.3.ApplesWashingtonistheleadingproducerofapplesintheU.S.,withapplesbeingthestate’shighestvalueagriculturalcommodity.AppleproductionisalsoimportantinOregon.Long-termstorageincontrolledtemperatureandatmospherefacilitiesiscommonwithapples,andofteninmarketcompetitionwithfruitimportedout-of-seasonfromsouthernhemispheregrowingregions.Thisisaparticularlyinterestingtrade-offtoexaminewithLCA,andtwoidentifiedstudiesexaminetheseasonalityoflocalvs.importedapplesinaEuropeancontext.Appleprocessing(intojuices,sauce,etc.)isalsoimportanttotheappleindustryinthePacificNorthwest,andwhileLCAstudiesonthesefinalproductsspecificallywerenotidentified,weareinvestigatingothermeansofestimatingprocessingimpactsinordertoofferperspectiveontheirrelativeimportance.4.PotatoesandpotatoproductsPotatoesareOregon’s7thhighestvaluecrop;potatoesrank#4inWashington.Becauseofthelargevolumeofproduction,thepotatoindustryalsorepresentsanoticeableportionofeachstate’sgreenhousegasemissions:anestimated0.6%oftotalstateemissionsinOR,and1.8%inWA.Potatoesareannualvegetables,sotheirproductiontypologydiffersfromtheperennialfruitsincludedamongrecommendedcommodities.SomeoftheLCAsofpotatoesconsiderprocessedendformsandfindsignificantincreases(abovefarm-gateimpacts)incarbonfootprint:peeledpotatoes50-60%greater,mashedpotatoes2-2.8timesgreater,potatochips3-4timesgreater.Refinementofthistypeofinformationmayprovideinsightstohotspotsinpotatoprocessing,inadditiontoconsiderationsoftheproductionphase.5.EggsWhileperhapsnotconsideredaniconicPacificNorthwestfood,eggproductionisnonethelessastrongagriculturalcommodity,ranking15thindollarvalueinbothORandWA.Itisestimatedthateggscontributeabout1.5%ofthegreenhousegasemissionsassociatedwithOregonfoodandbeverageconsumption.Eggproductionpracticesvarywidely,withanumberofchoicesavailableinthemarketplace(organic,conventional,cagefree,freerange,etc).ManyoftheseoptionshavebeencomparedinLCAstudies(albeitinaEuropeancontext),offeringinsightsintodifferencesinenvironmentalimpact.Ingeneral,feedproductionaccountsforthelargestshareofimpactsineggproduction,sofeedconversionefficienciesleadtoreducedoverallemissions.Buttheseefficienciesneedtobeconsideredinlightoftheenvironmentalcostsoffeedsourcingasimpactsoffeedproductioncanvarysignificantly.Likewise,feedsourcinginthearidwestisofparticularinterestduetoirrigationneedsforfeedcropproduction;energy/watertrade-offsinfeedsourcing,mentionedpreviously,alsoapplyhere.6.WineWinegrapesareadistinctiveproductofthePacificNorthwestthatcontributessignificantlytotheagriculturaleconomyoftheregion.Viticulturepresentsauniquesetofperennial

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cultivationpracticeswithdistinctdifferencesfromorchardcrops.GrapeproductioninCalifornia’swinegrowingregionshasbeenanalyzedwithLCA,andinsightsgainedinthosestudiesmaybetranslatabletoORandWAwinegraperegions.StillotherLCAstudiesconsiderthefullwineproductionmethod,sheddinglightonstageswheremitigationstrategiesshouldbefocused.7.PorkWhilenotnecessarilyanemblematicfoodofPacificNorthwestagriculture,porkrepresentsanestimated4.5%ofthefoodandbeveragecomponentoftheOregonconsumption-basedgreenhousegasemissionsinventory.Italsooffersatellingexampleoftheimpactsofmeatproduction.Athorough‘cradle-to-grave’LCAofU.S.porkfoundthat62%ofthecarbonfootprintoccursonfarm,yet23.5%occursattheconsumerlevel(refrigeration,cooking,foodwastedisposal).AnumberofporkproductionstrategiesarecomparedintheLCAliterature.8.CitrusfruitsandjuicesClearly,citrusfruitsarenotproducedinthePacificNorthwest.Yet,citrusfruitandjuicesareacommonpartofthedietsofmostAmericans.Citrusjuicesare62%(bymass)ofthejuiceconsumedintheU.S.ThequalityofLCAresearchoncitrusproductionisquitehigh,andincludesatleastoneU.S.basedstudy.Aproductfootprintsummaryofcitrusfruitsandjuiceswilldemonstratetheimpact,relativetoon-farmproduction,ofcitrustransportfromFlorida(forexample)tothePacificNorthwest.Itmayalsodemonstratetheimpactsofconcentratedvs.not-from-concentratejuice.9.FreshwaterAquacultureBothOregonandWashingtonhaveaquacultureindustrieswithsignificantgrowthpotential.TheOregonDepartmentofAgriculturehasacknowledgedthisgrowthpotentialandhaspledgedtocontinuetosupportdevelopmentandexpansionofanaquacultureindustryinOregon10.Whiledemandforseafoodproductscontinuestogrow,aquaculturefacesnumeroushurdles,includingmisinformationandpublicmisperceptionsregardingtheaquacultureindustry11.LCAstudiesofaquaculturepracticeshavebeenconductedinregionsacrosstheglobe,withmanystudiesmakingdirectcomparisonsbetweenalternativeproductionpractices12.AcategoricalfootprintsummaryofaquaculturemaybevaluabletothedevelopingindustryinthePacificNorthwestinovercomingpopularmisconceptions.NotethatwhilecommercialwildcatchfisherieshavealsobeenanalyzedviaLCA,theyareregionallydependent(e.g.,howfarshipsmusttravelfromport)andwehavebeenunabletoidentifyLCAstudiesofPacificNorthwestfisheries.Wildcatchfisheries

10IndustryReportfromtheStateBoardofAgriculture,January,2015.http://www.oregon.gov/ODA/shared/Documents/Publications/Administration/BoardReport.pdf.11DevelopingAdditionalInvestmentinAquaFarminginOregon:aroadmapforsustainabledevelopment.OregonDepartmentofAgricultureRFP#2014-05.March,2015.http://www.oregon.gov/ODA/shared/Documents/Publications/MarketAccess/AquacultureInvestment.pdf12Cao,L.,J.S.Diana,G.A.Keoleian(2013)."Roleoflifecycleassessmentinsustainableaquaculture."ReviewsinAquaculture5(2):61-71.

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alsovarygreatlyyear-to-yeardependingonoceanandfishstockconditions,makingitmorechallengingtogeneralizeconclusionsfromLCAstudies.ItisourimpressionthattheenvironmentalperformanceofaquaculturepracticesislesslocationdependentandthereforelessonsgleanedfromLCAstudiescanbeappliedtocurrentorfutureproductioninthePacificNorthwest.10.Raspberries(caneberries)Caneberryproduction,includingredandblackraspberries,blackberries,andboysenberries,isveryimportantinthePacificNorthwest.OregonistheleadU.S.producerofblackberries,boysenberriesandblackraspberries,growingnearlyallofthecountry’scommercialcrop.Washingtonisthetopproducerofredraspberries,withORranking3rdamongstates.Thesesmall,softfruitshaveshortshelflivesasfreshberries,thusrequiringexpeditiousdistributionchannelsthatmaketheirlifecyclesconsiderablydifferentthanpomefruitssuchasapplesandpears.Becauseoftheirhighperishability,processingmethods(freezing,canning,preserves)areimportanttotheoverallproductchain.WehavefoundonlyafewLCAstudiesfocusedonraspberries;however,weanticipate(andwillconfirm)thatproductionmethodsamongcaneberriesmaybesimilarenoughthatcombiningcaneberriesintoasingleenvironmentalfootprintsummarywillbeappropriate.Ifwediscoverthisnottobetrue,wewouldlimitthisanalysistoraspberriesonly.InformationfromraspberryLCAswillbecombinedwithdataonenergyuseoffreezingandprocessingsoftfruitsandstudiesthatexaminetherelativeenvironmentalimpactoftransporttoofferenvironmentalimpactinformationofvaluetotheberryindustry.11.PearsPearproductionranks9thintermsofvalueofagriculturalcommoditiesinbothORandWA,withWAbeingthetopU.S.producerat50%oftheU.S.pearcrop,andORwith26%ofU.S.production.In2005,theOregonlegislaturenamedthepearthestatefruit.LCAstudiesofpearproductioninSwitzerlandPortugal,Italy,andChinahavebeenidentified.Fromanenvironmentalimpactperspective,pearcultivation,storage,processing,anddistributionislikelysimilartoapples;thisshouldbeconsideredinmakingthefinalcommodityselection.12.ChickenChickenmeatrepresentsanestimated6%ofthefoodandbeverageportionofOregonconsumption-basedgreenhousegasemissions.Perhapsbecauseoflowvolume,broilerproductioninOregonandWashingtondoesnotappearintheUSDAQuickStatsdatabase.ChickenthereforerepresentsanotherfoodthatislikelyconsumedinlargerquantitiesinthePacificNorthwestthatitisproduced.Similartoeggproduction,broilerproductionpracticesvarywidely,andmuchoftheimpactisconnectedwithfeedproduction.13.BananasAsidefromfeedgrains,bananasarethelargestfoodimportbymassintotheU.S.BasedontheestimatesshowninFigure2,bananasconstitute9%ofthecarbonfootprintoffruitandvegetableconsumption.Isthisduetolongtransportdistancesfromtropicalregions,orsimplybecausebananasareconsumedinlargequantities?Ifwe’regoingtoeatbananas,whatcanbedonetoreducetheimpactofthatconsumption?Aproductfootprintsummarywouldshedlightonthesetypesofquestions.

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14.HazelnutsOregonproducesvirtuallytheentireU.S.hazelnutcrop,andtheU.S.ranksthirdinglobalproduction.ThelargesthazelnutprocessorinNorthAmericaislocatedinOR.Todate,wehaveidentifiedonlytwoLCAstudiesthatconsiderhazelnuts:oneinanItaliancontextandtheotherinIran.TheItalianstudyconsidersdifferentfinalforms(hazelnutpaste,spreadablecream,chocolatecovered)andincludesestimatesofenergydemandforvariousprocessingsteps.Inaddition,wehaveidentifiedahazelnutenterprisebudgetfortheWillametteValleydevelopedbyOregonStateUniversity13whichshouldallowascan-levelestimateoftheenvironmentalimpactsofORhazelnutproduction.15.TomatoesTomatoesareaniconicvegetablethatisenjoyedbothfreshandprocessed.Becauseofthis,tomatoeshavebeenstudiedextensivelyviaLCA.Tomatoesalsoareagoodexampleofthecommonmisconceptionsassociatedwithenvironmentalimpactoffoodlifecycles.Intemperateclimates,out-of-seasonlocaltomatoesareoftenproducedinheatedgreenhouses,whichdrasticallyincreasestheenergyuseandcarbonfootprintassociatedwiththeirproduction.AnumberofLCAstudiescomparelocalout-of-seasonproductionwithimportedtomatoes.AU.S.basedLCAofprocessedtomatoesexploresthetrade-offsbetweenregionalproductiondifferences(inthiscase,CAvs.MI)andlong-distancetransport,withresultsbeingsomewhatcounter-intuitivetopopularbeliefs.OtherfoodsinTable5Table5listsanadditionaleightfoodsthatarerelevantandimportanttoagricultureinORandWA,butinmostcasestheavailableLCAliteratureisquitelimited.Onionsareaninterestingexample:Oregonisthenation’stoponionproducer,whileWashingtonranksnumber2.Whilethevalueoftheseonioncropsfallsfartherdownthe“topcommodities”listineachstate,becauseofthehighproductionvolume,weestimatethatthegreenhousegasemissionsassociatedwiththisproductionisrathersignificant.However,thereisverylittlepublicdomainLCAresearchthatanalyzesonionproduction.Similarly,thereisanotablevegetableprocessingindustryinORandWA:greenpeas,carrots,snapbeansandsweetcornallrankashighvolumeprocessedcrops.Whentakenindividually,thereislimitedLCAdataonproductionofthesecrops.Whiledifferencesincultivationandharvestingpracticesbetweenthesecropsmakefarm-gateimpactsvary,processingsteps–freezingorcanning–willbesimilar.Acombinedcategoricalfootprintsummarywithgeneralizedinformationontherelativeimportanceofprocessinganddistributiontotheoveralllifecyclemaybeavaluableaddition.4. ConclusionsandNextStepsRecommendationsoffoodcommoditiesforfurtherevaluationanddevelopmentofcategoricalfootprintsummariesweremadebasedonfivecriteria.Thefirstfiveoftherecommendedfoodsscorehighinregionalproductionvalue,estimatedenvironmental13Julian,JamesW.,ClarkF.Seavert,andJeffL.Olsen.Orchardeconomics:ThecostsandreturnsofestablishingandproducinghazelnutsintheWillametteValley.Corvallis,Or.:ExtensionService,OregonStateUniversity,2008.http://hdl.handle.net/1957/17438.

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impactofregionalproduction,quantityandqualityofLCAdata,andtheyscorereasonably

highinconsumption-basedimpactsaswell.Theremainingrecommendedfoods

demonstratetrade-offsincriteria.TheywereselectedbasedontheirscoringinTable5,as

wellastorepresentadiversityoffoodtypesinthefinalcollectionoffootprintsummaries.

Theserecommendationsserveasabasisforstakeholderinputanddeterminationofafinal

listfornextsteps.

Thesuccessofthisprojectisdependentonprovidinginformationtobusinessesand

organizationsthatmayfinditusefulindirectingchange.Oftentheeasebywhichchange

canbemadeisdependentontheorganizationalstructureofanindustry.Therefore,wewelcomeinputfromstakeholdersontheorganizationalstructurewithinthePacificNorthwestoftherecommendedfoodindustries,aswellassuggestionsofcommoditiesnotincludedherethatmaybeofparticularinteresttoinstitutionalbuyersand/orfoodprocessors.

Whiletheexactformandcontentoftheproductfootprintsummariesresultingfromthis

projectwillcontinuetoevolvethroughfurtherresearchanddiscussionwithstakeholders,

itwillbeimportanttomaintainreasonableexpectationsofwhatexistingliteraturecantell

us.Theproductfootprintsummarieswillnotbeabletoprovidedefinitivebenchmarkingoftheenvironmentalimpactofproducing(orconsuming)specificfoodsinthePacific

Northwest,norwilltheybeabletoprovidecomparativeinformationonspecificgrowing

practicesorgrowingregionswithinPacificNorthwest(sinceregion-specificLCAdatais

currentlyunavailable).Whattheywillbeabletodoisdemonstratetherelativeimpactsofon-farmproductioncomparedtoprocessing,distributionandtransportfortypicalproduct

chains,ortheaspectsofon-farmproductionthatareparticular“hotspots”intermsof

environmentalimpact(suchas,forexample,fertilizeruse.)Incaseswheretheliterature

demonstratesasignificantdifferenceintheenvironmentalimpactcategoriesbeing

investigated,wemaybeabletomakestatementsondifferencesingenericproduction

practices(e.g.,cagedvs.freerangeeggs).Totheextentpossible,LCAresultsfromthe

literaturewillbemodifiedtobetterrepresentthePacificNorthwestby,forexample,

adjustingforyieldorirrigationrates,ortypicaltransportdistances.

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