CALIFORNIA AIR RESOURCES BOARD Re ......8150 Sunset Boulevard Mixed‐Use Project Los Angeles, CA 90046 January March 2014 Prepared for: AG‐SCH 8150 SUNSET BOULEVARD OWNER, L.P

80 South Lake, Suite 570, Pasadena, California 91101 INTERNET www.pcrnet.com TEL 626.204.6170 FAX 626.204.6171

January 29, 2014 CALIFORNIA AIR RESOURCES BOARD

Re: GREENHOUSE GAS EMISSIONS METHODOLOGY AND DOCUMENTATION PURSUANT TO THE “JOBS AND ECONOMIC IMPROVEMENT THROUGH ENVIRONMENTAL LEADERSHIP ACT” FOR THE 8150 SUNSET BOULEVARD MIXED-USE PROJECT

To California Air Resources Board:

On behalf of the Project Applicant, AG-SCH 8150 Sunset Boulevard Owner, L.P., PCR Services Corporation has prepared a Greenhouse Gas Emissions Methodology and Documentation assessment for the 8150 Sunset Boulevard Mixed Use Project (the “Project”), to demonstrate that the Project meets the greenhouse gas emissions requirements of the Jobs and Economic Improvement Through Environmental Leadership Act (“the Act”). We greatly appreciate the time and consideration that Air Resources Board (ARB) Staff has granted us regarding this important Project.

As is detailed in the assessment, the Project would incorporate a number of project characteristics and project design features to avoid, minimize, and reduce greenhouse gas (GHG) emissions. Our findings conclude that the Project would result in no net additional GHG emissions in accordance with the requirements of the Act.

We look forward to your review of this assessment. Please do not hesitate to call me at 626-204-6170, should any questions or comments arise regarding this assessment. We appreciate this opportunity and look forward to hearing from you.

Sincerely, PCR SERVICES CORPORATION Heidi Rous Vice President/Director

ApplicationforCEQAStreamliningUnderthe“JobsandEconomicImprovementthroughEnvironmentalLeadershipAct”(PublicResourcesCodeSection21178etseq.)

GREENHOUSEGASEMISSIONSMETHODOLOGYANDDOCUMENTATION

FortheProposed

8150SunsetBoulevardMixed‐UseProjectLosAngeles,CA90046

JanuaryMarch2014

Preparedfor:

AG‐SCH8150SUNSETBOULEVARDOWNER,L.P.P.O.Box10506

BeverlyHills,CA90213

Preparedby:

PCRSERVICESCORPORATION80SouthLakeAvenue,Suite570

Pasadena,CA91101TEL626.204.6170FAX626.204.6171

8150SunsetBoulevardMixedUseProject GreenhouseGasEmissionsMethodologyandDocumentationPCRServicesCorporation i

TABLE OF CONTENTS

Page

1.0EXECUTIVESUMMARY..................................................................................................................................................1 2.0INTRODUCTION...............................................................................................................................................................3

2.1 Purpose......................................................................................................................................................................................3 2.2 ProjectDescription...............................................................................................................................................................3 2.3 AssemblyBill900..................................................................................................................................................................4

3.0GREENHOUSEGASEMISSIONSMETHODOLOGY..................................................................................................7 3.1 GlobalClimateChangeandGreenhouseGases.........................................................................................................7 3.2 BaselineOperationalEmissions......................................................................................................................................8 3.3 ProjectOperationalEmissions......................................................................................................................................19

4.0COMPARISONOFPROJECTTOBASELINECONDITION....................................................................................37

APPENDICES

APPENDIXA:BASELINECONDITIONGREENHOUSEGASEMISSIONSAPPENDIXB:PROJECTGREENHOUSEGASEMISSIONS

LIST OF FIGURES

Figure Page1 AerialPhotographwithSurroundingLandUses....................................................................................................5 2 ProposedSitePlan...............................................................................................................................................................6 3 GreenhouseGasEmissions–BaselineandFutureProjectYearTrends...................................................40

LIST OF TABLES

Table Page1 BaselineConditionFloorArea........................................................................................................................................9 2 BaselineConditionElectricalDemandGreenhouseGasEmissions.............................................................11 3 BaselineConditionNaturalGasCombustionGreenhouseGasEmissions................................................13 4 BaselineConditionMobileSourceGreenhouseGasEmissions.....................................................................15 5 BaselineConditionSolidWasteDisposalGreenhouseGasEmissions.......................................................16 6 BaselineConditionWaterandWastewaterGreenhouseGasEmissions...................................................18 7 BaselineConditionAreaandStationarySourceGreenhouseGasEmissions..........................................19 8 SummaryofAnnualGHGEmissionsundertheBaselineConditions..........................................................20 9 ProjectFloorArea.............................................................................................................................................................20 10 EstimatedUnmitigatedProjectConstructionGreenhouseGasEmissions...............................................22

LIST OF TABLES (Continued)

Table Page

8150SunsetBoulevardMixedUseProject GreenhouseGasEmissionsMethodologyandDocumentationPCRServicesCorporation ii

11 ProjectElectricalDemandGreenhouseGasEmissions.....................................................................................25 12 ProjectNaturalGasCombustionGreenhouseGasEmissions........................................................................26 13 ProjectMobileSourceGreenhouseGasEmissions.............................................................................................30 14 ProjectSolidWasteDisposalGreenhouseGasEmissions...............................................................................31 15 ProjectWaterandWastewaterGreenhouseGasEmissions...........................................................................33 16 ProjectAreaandStationarySourceGreenhouseGasEmissions..................................................................34 17 SummaryofAnnualGHGEmissionsundertheProject....................................................................................35 18 EvaluationofNetGHGEmissionsfortheProject................................................................................................38

– PRELIMINARY WORKING DRAFT –

8150SunsetBoulevardMixedUseProject GreenhouseGasEmissionsMethodologyandDocumentationPCRServicesCorporation 1

1.0 EXECUTIVE SUMMARY

PCR Services Corporation (PCR) has been retained to conduct a comprehensive greenhouse gas (GHG)emissionsassessmentforthe8150SunsetBoulevardMixedUseProject(“theProject”)andtodemonstratethat the Projectmeets the requirements of the JobsandEconomic ImprovementThroughEnvironmentalLeadershipAct(“theAct”)(PublicResourcesCodeSection21178etseq.),alsoreferredtoasAssemblyBill(AB) 900. In September 2011, the Governor signed the Act, which required the Governor to establishproceduresforapplyingforstreamlinedenvironmentalreviewundertheCaliforniaEnvironmentalQualityAct (CEQA) forprojects thatmeetcertain requirements. TheOfficeofPlanningandResearch (OPR)hasprovidedapprovedguidelinesforsubmittingapplicationsforstreamlinedenvironmentalreviewpursuanttotheAct.WithrespecttoGHGemissions,aprojectmustdemonstratethatitwouldnotresultinanynetadditional GHGs including GHG emissions from employee transportation in accordance with PublicResourcesCodeSection21183(c).

TheProjectwouldredeveloptheexisting2.56‐acrecommercialpropertylocatedat8150SunsetBoulevardintheCityofLosAngeleswithamixofnewresidentialandcommercialuses.ConstructionoftheProjectisanticipatedtobeginin2014andbecompletedinmid‐2017.TheProjectsiteiscurrentlyoccupiedwithtwostructures built in 1960 and in 1988 and contain 80,000 square feet of retail tenancy inclusive of thefollowinguses:fast foodrestaurants,checkcashingfacility,dry‐cleaners(off‐sitedrycleaning), icecreamshop,walk‐inbankfacility,fitness,massageparlor,petgroomingservices,storagefacilityanddentaloffice.Operationof theseusescurrentlygeneratesGHGemissions fromenergydemand(electricityandnaturalgas), mobile sources traveling to and from the site, waste generation, water demand and wastewatergeneration,andotherareaandstationarysourcessuchaslandscapingequipment.TheemissionsofGHGsfromthecurrentsiteconstitutetheBaselineCondition.

TheProjectwoulddemolish theexistinguses anddevelopup to333,903square feetof commercial andresidentialspace.WhilethetotalsquarefootagewouldincreaseundertheProjectrelativetotheexistingsquare footage, the Project would be built to meet and exceed today’s energy and water efficiencystandardsandwould incorporateamixofresidential,commercial,retail,andrestaurantusesthatwouldreduce vehicle trips to and from the site, Project‐related vehicle miles traveled, and associated GHGemissions.

Under the Baseline Condition, the site generates approximately 7,407 metric tons of carbon dioxideequivalents (MTCO2e) per year. This excludes any one‐time construction GHG emissions that weregenerated when the existing uses and related infrastructure were originally built. Construction of theProjectwould generate one‐timeGHG emissions of approximately 1,589 1,631MTCO2e, during the firstyear and 2,608 2,346 MTCO2e during the second year. At Project buildout, the Site would generateapproximately 6,406 6,400 MTCO2e during the first full year of operation. Compared to the BaselineCondition, theProject’soperationalGHGemissionsrepresentanetreduction inGHGemissions fromthesiteofapproximately1,0011,007MTCO2eduringthefirstfullyearofoperation.

Future year emissions would decline as a greater percentage of motor vehicles meet more stringentemissions standards, including the Pavley Phase I and Phase II emissions standards and the 33 percentRenewables Portfolio Standard. The Project would reduce emissions through the use of grid‐source,renewable energy technologies and carbonmitigation projects for approximately seven years to ensurefutureyearcontemporaneousGHGemissionsdonotexceedtheBaselineConditionatanytime.Afterthis

1.0 Executive Summary – PRELIMINARY WORKING DRAFT – March 2014


sevenyearperiod,futureyearemissionswoulddeclinetobelowtheBaselineConditionwithouttheneedtopurchaseGHGreductioncredits.

Basedonthisassessment,theProjectwouldnotresultinanynetadditionalGHGsincludingGHGemissionsfromemployeetransportationinaccordancewithPublicResourcesCodeSection21183(c).Therefore,theProjectwouldmeettheGHGemissionsrequirementsforstreamlinedenvironmentalreviewunderCEQA.



2.0 INTRODUCTION

2.1 PURPOSE

PCRhasbeen retained to conducta comprehensivegreenhousegas (GHG)emissionsassessment for the8150SunsetBoulevardMixedUseProject (the “Project”) and todemonstrate that theProjectmeets therequirements of the Jobs and Economic Improvement Through Environmental LeadershipAct (“the Act”)(PublicResourcesCodeSection21178etseq.),alsoreferredtoasAssemblyBill(AB)900.Thisassessmentdescribes the methodology used to estimate the GHG emissions from baseline and Project conditions,providesanestimateofthenetchangeinGHGemissionsfortheproposedProjectascomparedtobaselineconditions,anddescribesthemethodologyusedtoquantifyGHGemissionreductionsfromprojectdesignfeaturesandmitigationmeasures.ThefollowingbaselineandProject‐relatedemissionsourceshavebeenevaluated:

Construction Activities – Fossil fueled on‐ and off‐road vehicles and equipment needed fordemolition,massandfinegrading,buildingconstruction,paving,andarchitecturalcoating;

DirectEmissionSources–Consumptionofnaturalgason‐siteforcooking,spaceheatingandwaterheating, combustion of fossil fuels for lawn care andmaintenance activities, andmotor vehiclesincludingemployeetransportation;and

Indirect Emission Sources – Off‐site electricity generation, wastewater treatment and waterconveyance,andsolidwastedisposal.

2.2 PROJECT DESCRIPTION

AG‐SCH8150SunsetBoulevardOwner,L.P.,(the“Applicant”)proposestoredevelopthe2.56‐acrepropertylocated at 8150 Sunset Boulevard (the “Project Site”) in the Hollywood community of the City of LosAngeles(the“City”).TheProjectSiteandsurroundingusesareshowninFigure1,AerialPhotographwithSurrounding Land Uses. The Project Site currently contains two commercial structures and otherimprovements,allofwhichwouldbedemolishedandremoved fromtheProjectSite. TheProjectwouldconsistoftwobuildingsoverasinglepodiumstructurewithvariouselementsranginginheightfromtwostories to 16 stories in height as measured from the intersection of Sunset and Crescent HeightsBoulevards.TheNorthBuildingwouldincludethreelevels(onesubterranean)ofentirelycommercialusesandwouldhaveamaximumheightofthreelevelsabovegradealongSunsetBoulevard.TheSouthBuildingwould include commercial uses on the first two levels, twelve levels of residential uses above thecommercialfloors,andarooftoprestaurant/loungelevelonLevel16.TheProjectwouldinclude111,339squarefeetofcommercialretailandrestaurantuseswithinthreelowerlevels(onesubterranean)andonerooftop level,249apartmentunits, including28affordablehousingunits,within the twelveupper levelsrepresenting222,564grosssquarefeetofresidentialspace.TheProjectwouldalsoprovideanew,9,134square‐footpublicspace(“CornerPlaza”)atthenortheastcornerofthesite(thisareais,andwillcontinueto be, owned by the City, although the Applicantwill be required to improve andmaintain the area), a34,050‐square‐foot central public plaza at the site interior (“Central Plaza”), public rooftopdeck/gardenareas (“SunsetTerrace”) along SunsetBoulevard, a private pool andpool deck area for residents (“PoolTerrace”), aswell as other resident‐only amenities totaling approximately 6,900 square feet thatwouldincludearesidentiallobby,residentrecreationroom,fitnesscenter,businesscenter,changingrooms,andlibrary, aswell as awrap‐around landscaped terrace on the fourth floor of the SouthBuilding (“Garden

2.0 Introduction – PRELIMINARY WORKING DRAFT – March 2014


Terrace”). Parkingforallproposeduseswouldbeprovidedon‐siteviaaseven‐level(threesubterraneanandsemi‐subterraneanlevels)parkingstructure(“ParkingStructure”)housedwithinthepodiumstructurethat includes 849 total parking spaces (295 for residential uses and 554 for commercial retail andrestaurantuses).Short‐andlong‐termbicycleparkingtotaling985spaceswouldalsobeprovidedon‐site,including 428 spaces for residential uses and 557 spaces for commercial uses. The total developmentwouldincludeupto333,903squarefeetofcommercialandresidentialspacewithamaximumfloor‐arearatio(FAR)of3:1.ThesiteplanisillustratedinFigure2,ProposedSitePlan.

2.3 ASSEMBLY BILL 900

InSeptember2011,theGovernorsignedtheAct,whichrequiredtheGovernortoestablishproceduresforapplyingforstreamlinedenvironmentalreviewundertheCaliforniaEnvironmentalQualityAct(CEQA)forprojects that meet certain requirements. The Office of Planning and Research (OPR) has providedapprovedguidelinesforsubmittingapplicationsforstreamlinedenvironmentalreviewpursuanttotheAct.WithrespecttoGHGemissions,aprojectmustdemonstratethat itwouldnotresult inanynetadditionalGHGs includingGHGemissions fromemployee transportation inaccordancewithPublicResourcesCodeSection21183(c).ForpurposesofCaliforniaPublicResourcesCodesection21183(c)thefollowingprocessapplies:

1. The applicant shall submit electronically to [email protected] a proposedmethodologyforquantifyingtheproject’snetadditionalGHGemissions.TheCARBwillreviewandcommentonthemethodology,atitsdiscretion,within30daysofsubmission.

2. At the same time, the applicant shall submit to [email protected] that the project does not result in any net additional GHG emissions. Thedocumentationmustatleastquantify:

a. Bothdirect and indirectGHGemissionsassociatedwith theproject’s constructionand operation, including emissions from the project’s projected energy use andtransportationrelatedemissions;and

b. Thenetemissionsoftheprojectafteraccountingforanymitigationmeasuresthatwill be monitored and enforced consistent with Public Resources Code section21183(d).

3. Within60daysofreceivingthedocumentation(in2.above),theCARBwilldeterminewhethertheconditionspecified inPublicResourcessection21183(c)hasbeenmetor, ifmore time isneeded,notifytheapplicantoftheexpectedcompletiondate.

4. TheCARBwilldetermineandreporttotheGovernorinwritingthataprojectdoesnotresultinany net additional emissions of greenhouse gases if the project demonstrates through acombinationofprojectdesignfeatures,compliancewith(orexceedingminimumrequirementsof)existing regulations,andmitigation that itwouldresult inzeroadditionalgreenhousegasemissions.

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FIGURE

Source: ESRI, 2010; PCR Services Corporation, 2013.

0 100 200 Feet

8150 Sunset Boulevard Mixed-Use ProjectGreenhouse Gas Emissions Methodology and Documentation

Aerial Photograph with Surrounding Land Useso 1

Project Boundary

FIGUREProposed Site Plan8150 Sunset Boulevard Mixed-Use Project

Greenhouse Gas Emissions Methodology and Documenta on2

Source: Hart | Howerton, 2013.P C R

0 40 Feet

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3.0 GREENHOUSE GAS EMISSIONS METHODOLOGY

3.1 GLOBAL CLIMATE CHANGE AND GREENHOUSE GASES

Thenaturalprocess throughwhichheat isretained in the troposphere1 iscalledthe“greenhouseeffect.”The greenhouse effect traps heat in the troposphere through a three‐fold process as follows:(1)short‐waveradiationintheformofvisiblelightemittedbytheSunisabsorbedbytheEarthasheat;(2)long‐waveradiationre‐emittedby theEarth; and (3)GHGs in theatmosphereabsorbingor trapping thelong‐wave radiation and re‐emitting it back towards the Earth and into space. This third process is thefocusofglobalclimatechangeactions.

ThemostcommonlyemittedGHGfromanthropogenic(i.e.,human)activitiesiscarbondioxide(CO2).NotallGHGspossessthesameabilityto induceclimatechange;asaresult,GHGcontributionsarecommonlyquantified in the units of equivalent mass of carbon dioxide (CO2e). Mass emissions are calculated byconvertingpollutant‐specificemissionstoCO2eemissionsbyapplyingtheproperglobalwarmingpotential(GWP)value.2ByapplyingtheGWPratios,project‐relatedCO2eemissionscanbetabulatedinmetrictonsofCO2e(MTCO2e)peryear.Typically,theGWPratiocorrespondingtothewarmingpotentialofCO2overa100‐year period is used as a baseline. The CO2e values are calculated for construction years aswell asexisting and project build‐out conditions in order to generate a net change in GHG emissions forconstructionandoperation.CompoundsthatareregulatedasGHGsarediscussedbelow.

Carbon Dioxide (CO2): CO2 is the most abundant GHG in the atmosphere and is primarilygeneratedfromfossilfuelcombustionfromstationaryandmobilesources.CO2isthereferencegas(GWPof1)fordeterminingtheGWPsofotherGHGs.

Methane (CH4): CH4 is emitted from biogenic sources (i.e., resulting from the activity of livingorganisms), incomplete combustion in forest fires, landfills, manure management, and leaks innaturalgaspipelines.TheGWPofCH4is21.

Nitrous Oxide (N2O): N2O produced by human‐related sources including agricultural soilmanagement,animalmanuremanagement,sewagetreatment,mobileandstationarycombustionoffossilfuel,adipicacidproduction,andnitricacidproduction.TheGWPofN2Ois310.

Hydrofluorocarbons (HFCs): HFCs are fluorinated compounds consisting of hydrogen, carbon,andfluorine.Theyaretypicallyusedasrefrigerantsinbothstationaryrefrigerationandmobileairconditioningsystems.TheGWPsofHFCsrangesfrom140forHFC‐152ato11,700forHFC‐23.

Perfluorocarbons (PFCs): PFCs are fluorinated compounds consisting of carbon and fluorine.They are primarily created as a byproduct of aluminum production and semiconductormanufacturing.TheGWPsofPFCsrangefrom5,700to11,900.

1 Thetroposphereisthebottomlayeroftheatmosphere,whichvariesinheightfromtheEarth’ssurfaceto10to12kilometers.2 GWPsandassociatedCO2evaluesweredevelopedbytheIntergovernmentalPanelonClimateChange(IPCC),andpublishedinits

SecondAssessmentReport,in1996. InaccordancewithinternationalandUnitedStatesconventiontomaintainthevalueofthecarbondioxide“currency,”GHGemissioninventoriesarecalculatedusingtheGWPsfromtheIPCCSecondAssessmentReport.

3.0 Greenhouse Gas Emissions Methodology – PRELIMINARY WORKING DRAFT – March 2014


SulfurHexafluoride(SF6):SF6isafluorinatedcompoundconsistingofsulfurandfluoride.Itisacolorless,odorless,nontoxic,nonflammablegas.Itismostcommonlyusedasanelectricalinsulatorinhighvoltageequipmentthattransmitsanddistributeselectricity.SF6hasaGWPof23,900.

TheClimateRegistry(TCR)haspreparedtheGeneralReportingProtocolforcalculatingandreportingGHGemissionsfromanumberofgeneralandindustry‐specificactivities.3Nospecificprotocolsareavailableforlandusedevelopmentprojects;however,theGeneralReportingProtocolhasbeenadaptedtoaddressthelandusedevelopmentGHGemissionsinthisassessment. Theinformationprovidedinthisassessmentisgenerally consistentwith theGeneralReportingProtocolminimumreporting requirements. TheGeneralReportingProtocolrecommendstheseparationofGHGemissionsintothreecategoriesthatreflectdifferentaspectsofownershiporcontroloveremissions.Theyinclude:

Scope 1: Direct GHG emissions from human activity (e.g., stationary combustion of fuels,mobilecombustionoffuelsintransportation).

Scope 2: Indirect GHG emissions associated with activities of the reporting entity but occur atsourcescontrolledbyanotherentity(e.g.,purchasedelectricityorpurchasedsteam).

Scope3: Indirectemissionsassociatedwithotheremissions sources, suchasemployeecommuteandbusinesstravelandwastedisposal.

AccordingtotheCaliforniaAirResourcesBoard(CARB),theconsiderationofso‐calledindirectemissionsprovides amore completepicture of theGHG footprint of a facility: “As facilities consider changes thatwouldaffecttheiremissions–additionofacogenerationunittoboostoverallefficiencyevenasitincreasesdirectemissions,forexample–therelativeimpactontotal(directplusindirect)emissionsbythefacilityshouldbemonitored.Annuallyreportedindirectenergyusagealsoaidstheconservationawarenessofthefacilityandprovidesinformation”toCARBtobeconsideredforfuturestrategiesbytheindustrialsector.4Additionally,theOfficeofPlanningandResearchdirectsleadagenciesto“makeagood‐faitheffort,basedon available information, to calculate, model, or estimate…GHG emissions from a project, including theemissionsassociatedwithvehiculartraffic,energyconsumption,waterusageandconstructionactivities.”5Therefore,directandindirectemissionsareconsideredinthisassessment.

3.2 BASELINE OPERATIONAL EMISSIONS

3.2.1 Description of Baseline Condition

The Project Site encompasses approximately 2.56 acres (111,339 square feet) of land area currentlyoccupiedbytwocommercialbuildingsandassociatedparking,asshowninFigure1.Thetwostructuresonthesitewerebuilt in1960and in1988andcontain80,000square feetof retail tenancy inclusiveof thefollowing uses: general retail, restaurants, ice creamparlor,walk‐in bank facility, fitness center, storagefacility,anddentaloffice.ThesquarefootageforeachoftheselandusesareprovidedinTable1,BaselineConditionFloorArea.

3 TheClimateRegistry,GeneralReportingProtocol,Version2.0,(2013).4 CaliforniaAirResourcesBoard, Initial Statement ofReasons forRulemaking,ProposedRegulation forMandatoryReporting of

GreenhouseGasEmissionsPursuanttotheCaliforniaGlobalWarmingSolutionsActof2006(AB32),(2007).5 OfficeofPlanningandResearch,TechnicalAdvisory,p.5.

March 2014 – PRELIMINARY WORKING DRAFT – 3.0 Greenhouse Gas Emissions Methodology


The main retail structure, completed in 1988, is a three‐level concrete and light‐gauge steel structureinclusive of a one‐level, partial below‐grade parking garage, three levels of above‐grade retail uses andsurface parking. The second structure is a two‐story building constructed in 1960 that fronts SunsetBoulevard. Inaddition, there is a standard‐sizedbillboardat the site thatuntil recentlywasdigital. Allexisting on‐site structures, parking, signage, and landscaping would be removed from the site prior toconstructionoftheProject.TheProjectSiteisgenerallyflat,withatopographythatslopesdownfromthenorthtothesouth.Landscapingonthesiteislimitedtoasmallnumberofornamentaltrees.

3.2.2 Baseline GHG Emission Sources and Calculation Methodology

(a) Construction

TheProjectSiteiscurrentlybuilt‐out.Asdiscussedpreviously,thetwostructuresontheProjectSitewerebuilt in 1960 and in 1988. Construction of the two structures and associated parking areas andinfrastructure resulted in one‐time GHG emissions of carbon dioxide (CO2) and smaller amounts ofmethane(CH4)andnitrousoxide(N2O)fromheavy‐dutyconstructionequipment,haultrucks,andworkervehicles. However,sufficientdetail isnotavailablewithrespecttotheconstructionschedule,equipmentusage,andnumberofhaultripstoprovideaquantitativeconstructionGHGemissionsassessmentforthebaseline condition. Therefore, construction‐related GHG emissions are not included for the baselinecondition. This is a conservative approach since, by excluding the baseline construction‐related GHGemissions, the Project would need to provide slightly greater GHG reductions in order to meet therequirementsofAB900ofnonetadditionalGHGemissions.

(b) Operational Energy – Electricity

The generation of electricity in California is achieved through the combustion of fossil fuels, primarilynaturalgas,usingsteamboilers, internalcombustionengines,andcombustionturbines. AportionoftheelectricitygeneratedinCaliforniaandimportedfromoutsidethestateisderivedfromthecombustionofcoalandothernon‐gaseousfossilfuels.ThecombustionoffossilfuelstoproduceelectricityresultsinGHG

Table 1

Baseline Condition Floor Area

Land Use Square Feet (sqft)

GeneralRetail 14,647StorageFacility 27,625

Walk‐inBankFacility 20,172Restaurant 2,056

IceCreamParlor 800FastFoodRestaurantwithoutDrive‐Thru 3,720FastFoodRestaurantwithDrive‐Thru 5,070

DentalOffice 2,360FitnessCenter 3,550

TotalFloorArea 80,000

Source: AG‐SCH 8150 Sunset Boulevard Owner LP, 2013



emissionsofCO2andsmalleramountsofCH4andN2O.TheseemissionsoccurduetotheelectricaldemandofthecommercialandretaillandusesthatcurrentoperateontheProjectSite.Theelectricitygenerationoccursoff‐site;therefore,electricityuseresultsinGHGemissionsthatareconsideredtobeindirect.

Emissions of GHGs associatedwith the Baseline Condition energy demand are based on the size of thecommercialandretaillanduses,theelectricaldemandfactorsforthelanduses,theGHGemissionfactorsfor the electricity utility provider, and the GWP values for the GHGs emitted. Annual electricity GHGemissionsinunitsofMTCO2earecalculatedasfollows:

Electricity:

AnnualEmissions[MTCO2e]=(∑i(Units×DE×EFE×GWP)i)÷2204.62 [Equation1]

Where: Units = Numberoflanduseunits(samelandusetype)[1000sqft] DE = Electricaldemandfactor[megawatt‐hour(MWh)/1000sqft/year] EFE = GHGemissionfactor[poundspermegawatt‐hour(MWh)] GWP = Globalwarmingpotential[CO2=1,CH4=21,N2O=310] 2204.62 = Conversionfactor[pounds/MT] i = Summationindex

Electrical demand is based ondata from theCaliforniaEnergyCommission (CEC)CaliforniaCommercialEndUseSurvey(CEUS),whichlistsenergydemandbybuildingtype.6ThedatafromtheCEUSisfrom2002.Since1978,theCEChasestablishedbuildingenergyefficiencystandards,whichareupdatedperiodically.Asdiscussedpreviously,theexistingbuildingsontheProjectSitewerebuiltin1960and1988.Thus,theuse of the CEUS 2002 survey data to represent the electrical demand for the Baseline Conditionwouldprovideaconservativeassessmentasfuturebuildingenergyefficiencystandardsaremorerestrictivethanprior standards. The CEUS provides data on a limited statewide basis or for each of the four largestpublicly owned utilities (Pacific Gas& Electric, Southern California Edison (SCE), SacramentoMunicipalUtilityDistrict,andSanDiegoGas&Electric).Forthepurposesofthisassessment,demandfactorsforSCEwereusedasmostrepresentativeoftheProjectSite.

TheLosAngelesDepartmentofWater andPower (LADWP)provideselectric service to theProject Site.Emission factors for GHGs due to electrical generation to serve the electrical demands of the BaselineConditionwere obtained from the LAWDP 2012 Power IntegratedResource Plan, which provides a CO2intensityof1,1561,094poundsofCO2perMWh.7Currently,LADWPprovides20percentofelectricityviarenewable sources.8 Emission factors for CH4 and N2O were obtained from the California EmissionsEstimatorModel(CalEEMod).9

6 California Energy Commission, California Commercial End‐Use Survey, http://capabilities.itron.com/CeusWeb/Chart.aspx.

AccessedNovember2013.7 LosAngelesDepartmentofWaterandPower,20122013PowerIntegratedResourcePlan,(2012)C‐11(2013)C‐12.8 LosAngelesDepartmentofWaterandPower,20122013PowerIntegratedResourcePlan,(2012)111(2013)ES‐31.9 CaliforniaAirPollutionControlOfficersAssociation,CaliforniaEmissionsEstimatorModel,http://www.caleemod.com/.Accessed

November2013March2014.



The estimated annual emissions from electrical demand from the Baseline Condition are provided inTable2,BaselineConditionElectricalDemandGreenhouseGasEmissions. DetailedemissionscalculationsareprovidedinAppendixA.

Table 2

Baseline Condition Electrical Demand Greenhouse Gas Emissions

Land Use

Units (1000 sqft)

Annual Electrical

Demand Factora (MWh/1000 sqft/year)

CO2 Factor b

(pounds/MWh)CH4 Factor

b (pounds/MWh)

N2O Factor c

(pounds/MWh)

Annual GHG Emissions d

(MTCO2e/year)

GeneralRetail 14.65 15.36 1,156 1,094 0.029 0.0062 118.21 111.89StorageFacility 27.63 4.29 1,156 1,094 0.029 0.0062 62.25 58.92

Walk‐inBankFacility 20.17 13.24 1,156 1,094 0.029 0.0062 140.39 132.88Restaurant 2.06 46.18 1,156 1,094 0.029 0.0062 49.90 47.23

IceCreamParlor 0.80 46.18 1,156 1,094 0.029 0.0062 19.42 18.38FastFoodRestaurantwithoutDrive‐Thru

3.72 46.18 1,156 1,094 0.029 0.0062 123.05 116.46

FastFoodRestaurantwithDrive‐Thru

5.07 46.18 1,156 1,094 0.029 0.0062 90.28 85.45

DentalOffice 2.36 20.30 1,156 1,094 0.029 0.0062 25.17 23.82FitnessCenter 3.55 20.30 1,156 1,094 0.029 0.0062 37.86 35.84TotalGHGEmissions

667 631

a California Energy Commission, California Commercial End Use Survey, http://capabilities.itron.com/CeusWeb/Chart.aspx. Accessed November 2013. Factors are based on the Southern California Edison (SCE) sector as representative of the Project Site location.

b Los Angeles Department of Water and Power, 2012 2013 Power Integrated Resource Plan, (2012) C‐11 (2013) C‐12.

c California Air Pollution Control Officers Association, California Emissions Estimator Model, http://www.caleemod.com/. Accessed January March 2014.

d Totals may not add up exactly due to rounding in the modeling calculations.

Source: PCR Services Corporation, 2014. Detailed emissions calculations are provided in Appendix A.

(c) Operational Energy – Natural Gas

TheexistinglandusesundertheBaselineConditionutilizenaturalgasprimarilyforheatingneeds.Naturalgas isalsousedforcooking. Thecombustionofnaturalgasresults inGHGemissionsofCO2andsmalleramountsofCH4andN2O.Thecombustionofnaturalgasoccurson‐site;therefore,theGHGemissionsareconsideredtobedirect.

TheemissionsofGHGsassociatedwithnaturalgascombustionundertheBaselineConditionarebasedonthesizeofthecommercialandretaillanduses,thenaturalgascombustionfactorsforthelandusesinunitsofmillionBritish thermal units (MMBtu), theGHG emission factors for natural gas combustion, and theGWPvaluesfortheGHGsemitted.AnnualnaturalgasGHGemissionsinunitsofMTCO2earecalculatedasfollows:



NaturalGas:

AnnualEmissions[MTCO2e]=(∑i(Units×DNG×EFNG×GWP)i)÷2204.62 [Equation2]

Where: Units = Numberoflanduseunits(samelandusetype)[1000sqft] DNG = Naturalgascombustionfactor[MMBtu/1000sqft/year] EFNG = GHGemissionfactor[pounds/MMBtu] GWP = Globalwarmingpotential[CO2=1,CH4=21,N2O=310] 2204.62 = Conversionfactor[pounds/MT] i = Summationindex

Natural gasdemand isbasedondata from theCECCaliforniaCommercialEndUseSurvey (CEUS),whichlistsenergydemandbybuilding type.10 Thedata from theCEUS is from2002. Since1978, theCEChasestablishedbuildingenergyefficiencystandards,whichareupdatedperiodically.Asdiscussedpreviously,theexistingbuildingson theProject Sitewerebuilt in1960and1988. Thus, theuseof theCEUS2002surveydata to represent the electrical demand for theBaselineConditionwouldprovide a conservativeassessmentas futurebuildingenergyefficiencystandardsaremorerestrictivethanpriorstandards. Forthepurposesofthisassessment,demandfactorsforSCEwereusedasmostrepresentativeoftheProjectSite.

The combustion of natural gas results in relatively equal amounts of GHG emissions per unit of gascombustedinthestate.EmissionfactorsforGHGsduetonaturalgascombustiontoservetheheatingandcooking demands of the Baseline Condition were obtained from the CalEEMod tool, which providesstatewideemissionfactors.11

TheestimatedannualemissionsfromnaturalgascombustionfromtheBaselineConditionareprovidedinTable 3, Baseline Condition Natural Gas Combustion Greenhouse Gas Emissions. Detailed emissionscalculationsareprovidedinAppendixA.

(d) Operational Mobile

Mobile source emission calculations associated with the Baseline Condition are calculated using theCalEEModtool,which incorporates theCARBemissions factormodel foron‐roadvehicles(EMFAC2011).EmissionsofGHGsassociatedwithmobilesourcesundertheBaselineConditionarebasedontheaveragedailytriprate,tripdistance,theGHGemissionfactorsforthemobilesources,andtheGWPvaluesfortheGHGsemitted.ThetypesofvehiclesthatvisittheSiteincludeallvehicletypesincludingautomobiles,light‐duty trucks,delivery trucks, andwastehaul trucks. Modeling for theBaselineConditionwas conductedusingthevehicle fleetmix fortheSouthCoastAirBasin forallvehicletypesasprovidedinEMFAC2011.AnnualmobilesourceGHGemissionsinunitsofMTCO2earegenerallycalculatedinCalEEModasfollows:


AccessedNovember2013.11 CaliforniaAirPollutionControlOfficersAssociation,CaliforniaEmissionsEstimatorModel,http://www.caleemod.com/.Accessed




Mobile:

AnnualEmissions[MTCO2e]=(∑i(Units×ADT×DTRIP×EF×GWP)i)÷2204.62 [Equation3]

Where: Units = Numberofvehicles(samevehiclemodelyearandclass) ADT = Averagedailytriprate[trips/day] DTRIP = Tripdistance[miles/trip] Days = Numberofdaysperyear[days/year] EF = GHGemissionfactor[poundspermile] GWP = Globalwarmingpotential[CO2=1,CH4=21,N2O=310] 2204.62 = Conversionfactor[pounds/MT]

i = Summationindex

TheCalEEModtoolallowstheinputofseveralvariablestoquantifymobilesourceemissions.ThenumberofmotorvehiclesthattraveltoandfromtheexistingProjectSiteisbasedontripgenerationratesforthe

Table 3

Baseline Condition Natural Gas Combustion Greenhouse Gas Emissions

Land Use

Units (1000 sqft)

Annual Natural Gas Demand

Factor a (MMBtu/1000 sqft/year)

CO2 Factor b

(pounds/MMBtu)CH4 Factor

b (pounds/MMBtu)

N2O Factor b

(pounds/MMBtu)

Annual GHG Emissionsc

(MTCO2e/year)

GeneralRetail 14.65 2.46 117.65 0.0023 0.0022 1.94StorageFacility 27.63 2.46 117.65 0.0023 0.0022 3.64Walk‐inBank

Facility 20.178.05 117.65 0.0023 0.0022 8.72

Restaurant 2.06 249.14 117.65 0.0023 0.0022 27.50IceCreamParlor 0.80 249.14 117.65 0.0023 0.0022 10.70

FastFoodRestaurant

withoutDrive‐Thru

3.72 249.14 117.65 0.0023 0.0022 67.82

FastFoodRestaurantwithDrive‐Thru

5.07 249.14 117.65 0.0023 0.0022 49.76

DentalOffice 2.36 68.32 117.65 0.0023 0.0022 8.66FitnessCenter 3.55 68.32 117.65 0.0023 0.0022 13.02TotalGHGEmissions

192

a California Energy Commission, California Commercial End Use Survey, http://capabilities.itron.com/CeusWeb/Chart.aspx. Accessed November 2013. Factors are based on the Southern California Edison (SCE) sector as representative of the Project Site location.

b California Air Pollution Control Officers Association, California Emissions Estimator Model, http://www.caleemod.com/. Accessed January March 2014.

c Totals may not add up exactly due to rounding in the modeling calculations.




BaselineCondition.TheProjecttrafficstudy12occasionallyreferencestripsonapassengercarequivalent(PCE)basisinordertoevaluatetrafficcongestiononroadways,whichisatypicalmethodologyforprojectsin the Los Angeles area. For the purposes of evaluating traffic congestion, PCE trips count passengervehicles as a singlevehicle andheavy‐duty trucksasusually twoor threepassengervehicle equivalentsdepending on the truck type (buses may also be counted as multiple passenger vehicle equivalents).However,airqualityandGHGassessmentstypicallydonotreferencePCEtripratesandusuallyestimateemissionsbasedonactual tripratesandemissionfactors forallvehicletypes. Thus, forthepurposesofestimatingemissions, thisassessmentuses theactual triprates(notadjusted forPCEtriprates)andtheassociated emissions factors for each vehicle type, as well as the vehicle fleet mix, as provided inEMFAC2011. Trip lengthvalues arebasedon the residential and commercial tripdistancesprovided inCalEEMod. The trip distances were applied to the maximum daily trip estimates, based on standardInstituteofTransportationEngineers(ITE)tripgenerationrates,foreachexistinglanduseprovidedbytheProjecttrafficstudy13toestimatethetotalvehiclemilestraveled(VMT).ThetripstakeintoaccountVMTreductions from characteristics including the existing site’s proximity to existing public transit and itsurbaninfilllocation.TheestimatedVMTreductionsarecalculatedusingtheequationsandmethodologiesprescribed in the California Air Pollution Control Officer’s Association (CAPCOA) guidance document,QuantifyingGreenhouseGasMitigationMeasures,whichprovidesVMTreductionvaluesfortransportationcharacteristicsandmeasures.14 BasedontheCAPCOAguidance,theexistingsiteresultsinapproximately16.5 percent less VMT compared to theVMT calculated using standard ITE trip rates and standard tripdistancevalues.

Emissionsfrompassengervehicles(i.e.,light‐dutyautomobilesandlight‐dutytrucks)idlingon‐siteduetoqueuingatthefastfoodrestaurantdrive‐thruwereestimatedoutsideoftheCalEEModsoftwarebasedonindustrydataregardingthepercentageofvisitorsatahamburgerfastfoodrestaurantusingthedrive‐thruandtheaveragewaittimes.Accordtotheindustrysurveydata,hamburgerfastfoodrestaurantshave57percentofvisitorsutilizingthedrive‐thru15withaveragewaittimesover130seconds(overtwominutes).16Inordernottooverestimateemissionsfromtheexistingfastfoodrestaurantandthusnotoverestimatetheamountofexistingemissionscredits,avalueof120second(or2minutes)wasusedinthisassessment.

EmissionsofGHGs frommotorvehiclesaredependentonmodelyearsand thespecific typesofvehiclesthat are used to travel to and from the existing Project Site. The emissions were calculated using arepresentative motor vehicle fleet mix for year 2013 as provided in CalEEMod. The estimated annualemissions frommobile sources from theBaselineCondition are provided inTable4,BaselineConditionMobileSourceGreenhouseGasEmissions.DetailedemissionscalculationsareprovidedinAppendixA.

12 Hirsch/Green Transportation Consulting, Inc., Traffic Impact Analysis Report, ProposedMixed‐Use Development, 8150 Sunset

Boulevard,Hollywood,California,November2013.13 Hirsch/Green Transportation Consulting, Inc., Traffic Impact Analysis Report, ProposedMixed‐Use Development, 8150 Sunset

Boulevard,Hollywood,California,November2013.14 CaliforniaAirPollutionControlOfficersAssociation,QuantifyingGreenhouseGasMitigationMeasures,(2010).15 The NPD Group, Drive‐Thru Windows Still Put the Fast in Fast Food Restaurants, Reports NPD, May 2012,

https://www.npd.com/wps/portal/npd/us/news/press‐releases/pr_120530a/.AccessedDecember2013.16 QSRMagazine,2012QSRDrive‐ThruStudy,http://www.qsrmagazine.com/print/50631.AccessedDecember2013.



(e) Operational Waste

Theexisting landusesunder theBaselineConditiongeneratemunicipalsolidwaste (MSW) fromday‐to‐day operational activities, which generally consists of product packaging, grass clippings, furniture,clothing,bottles, foodscraps,newspapers,plastic,andother itemsroutinelydisposedof in trashbins. AportionoftheMSWisdivertedtowasterecyclingandreclamationfacilities.Wastethatisnotdivertedisusuallysenttolocallandfillsfordisposal.MSWthatisdisposedinlandfillsresultsinGHGemissionsofCO2andCH4fromthedecompositionofthewastethatoccursoverthespanofmanyyears.

EmissionsofGHGsassociatedwithsolidwastedisposalundertheBaselineConditionarecalculatedusingtheCalEEModtool.Theemissionsarebasedonthesizeofthecommercialandretaillanduses,thewastedisposal rate for the land uses, the waste diversion rate, the GHG emission factors for solid wastedecomposition,andtheGWPvaluesfortheGHGsemitted.AnnualwastedisposalGHGemissionsinunitsofMTCO2earegenerallycalculatedinCalEEModasfollows:

Waste:

AnnualEmissions[MTCO2e]=(∑i(Units×DMSW×EFMSW×GWP)i)÷1.1023 [Equation4]

Where: Units = Numberoflanduseunits(samelandusetype)[1000sqft] DMSW = Wastedisposalrate[tons/1000sqft/year] EFMSW = GHGemissionfactor[tons/tonwaste] GWP = Globalwarmingpotential[CO2=1,CH4=21,N2O=310] 1.1023 = Conversionfactor[tons/MT] i = Summationindex

The CalEEMod tool allows the input of several variables to quantify solidwaste emissions. Themodelrequirestheamountofwastedisposed,whichistheproductofthewastedisposalratetimesthelanduseunits.AnnualwastedisposalratesusedinCalEEModarebasedondatafromtheCaliforniaDepartmentofResourcesRecyclingandRecovery(CalRecycle). Forcommercialandretaillanduses,theratesarebasedonstatewideaverages.ThetotalamountofwastedisposedwasreducedbythediversionratefortheCity

Table 4

Baseline Condition Mobile Source Greenhouse Gas Emissions

Land Use Fleet Mix Year

Estimated Annual VMT/ OR

Annual Idling Hours Annual GHG Emissions

(MTCO2e/year)

ExistingSite(Traveling) 2013(AllVehicleClasses)

13,291,777(VMT)a 6,358a

ExistingSite(IdlingatOn‐SiteDrive‐Thru)

2013(LDA,LDT1,LDT2)

17,442(IdlingHours) 98.28

TotalGHGEmissions 6,456

LDA = Light‐duty automobiles; LDT = Light‐duty trucks a Calculated using the California Emissions Estimator Model, http://www.caleemod.com/. Accessed January March 2014.




of Los Angeles of 60 percent, according to themost recent data available.17 The GHG emission factors,particularlyforCH4,dependoncharacteristicsofthelandfill,suchasthepresenceofalandfillgascapturesystemandsubsequentflaringorenergyrecovery.Thedefaultvalues,asprovidedinCalEEMod,forlandfillgas capture (e.g., no capture, flaring, energy recovery), which are statewide averages, are used in thisassessment.

The estimated annual emissions from solidwaste disposal from the Baseline Condition are provided inTable5,BaselineConditionSolidWasteDisposalGreenhouseGasEmissions.DetailedemissionscalculationsareprovidedinAppendixA.

Table 5

Baseline Condition Solid Waste Disposal Greenhouse Gas Emissions

Land Use Waste

Diversion a

Waste Disposal Rate after Diversion b

(tons/year) Landfill Gas (no capture) c

Landfill Gas (capture with

flaring) c

Annual GHG Emissions

(MTCO2e/year)

ExistingSite 60% 136.86 6% 94% 62.26TotalGHGEmissions 62

a County of Los Angeles, Countywide Integrated Waste Management Plan, 2012 Annual Report (2013).

b Waste generation factors for commercial and restaurant uses are from the Integrated Waste Management Board, Targeted Statewide Waste Characterization Study: Waste Disposal and Diversion Findings for Selected Industry Groups, June 2006.



(f) Operational Water and Wastewater

WaterandwastewatergeneratedfromtheexistinglandusesundertheBaselineConditionrequiresenergyto supply, distribute and treat. The combustion of fossil fuels to produce electricity results in GHGemissionsofCO2andsmalleramountsofCH4andN2O.Theelectricitygenerationoccursoff‐site;therefore,theelectricityusefromwaterandwastewaterresultsinGHGemissionsthatareconsideredtobeindirect.WastewateralsoresultsinemissionsofGHGsfromwastewatertreatmentsystems(e.g.,septic,aerobic,orlagoons)aswellasfromsolidsthataredigestedeitherthroughananaerobicdigesterorwithco‐generationfromcombustionofdigestergas.

The emissions of GHGs associated with water demand and wastewater generation under the BaselineConditionarecalculatedusingtheCalEEModtool.Theemissionsarebasedonthesizeofthecommercialandretaillanduses,thewaterdemandfactors,theelectricalintensityfactorsforwatersupply,treatment,anddistributionandforwastewatertreatment,theGHGemissionfactorsfortheelectricityutilityprovider,andtheGWPvaluesfortheGHGsemitted. AnnualwaterdemandandwastewaterGHGemissionsduetoelectricityaregenerallycalculatedinCalEEModasfollowsforindoorandoutdoorwaterdemand:

17 CountyofLosAngeles,CountywideIntegratedWasteManagementPlan,2012AnnualReport(2013).



WaterSupply,Treatment,andDistribution;WastewaterTreatment(electricity):

AnnualEmissions[MTCO2e]=(∑i(Units×DW×(EIW÷1000)×EFW×GWP)i)÷2204.62 [Equation5]

Where: Units = Numberoflanduseunits(samelandusetype)[1000sqft] DW = Waterdemandfactor[milliongallons(Mgal)/1000sqft/year] EIW = Electricityintensityfactor[kilowatt‐hours(kWh)/Mgal] 1000 = Conversionfactor[kWh/MWh] EFW = GHGemissionfactor[pounds/MWh] GWP = Globalwarmingpotential[CO2=1,CH4=21,N2O=310] 2204.62 = Conversionfactor[pounds/MT] i = Summationindex

TheCalEEModtoolcalculateswaterdemandbasedonannualratesinthePacificInstituteWasteNotWantNotreport.18 TheCalEEModtoolprovidesoptionstoaccountfortheuseofwatersavingfeaturessuchastheuseoflow‐flowwaterfixtures(e.g.,low‐flowfaucets,low‐flowtoilets).

TheCEC’sestimate forenergy intensityof thewateruse cycle inSouthernCalifornia, asprovided in the2006 CEC report Refining Estimates ofWater‐Related Energy Use in California, is used to calculate theenergyusagerelatedtowatersupply,treatment,anddistributionandwastewatertreatment.19 ThesameelectricityGHGemissionsfactorsdiscussedinSection3.2.2(b),OperationalEnergy–Electricity,areusedforwaterandwastewaterenergyusage.

TheemissionsofGHGsassociatedwithwastewatertreatmentprocessemissionsarealsocalculatedusingtheCalEEMod tool. The emissions arebasedon the typeof treatment (e.g., aerobic, facultative lagoons,septic systems). The emissions are calculating using the default settings in CalEEMod for the type ofwastewater treatment. Calculation formulasaredescribed indetail in theCaliforniaEmissionsEstimatorModel User’s Guide, Appendix A.20 As stated in the User’s Guide, the GHGs emitted from each type ofwastewatertreatmentarebasedontheCARB’sLocalGovernmentOperationsProtocol(LGOP),21whicharein turn based onUnited States Environmental ProtectionAgency (USEPA)methodologies.22 The defaultCalEEMod settings forwastewater treatment are: 10.33percent septic tank, 87.46percent aerobic, 2.21percentfacultativelagoonsand100percentanaerobiccombustionofgas.

TheestimatedannualemissionsfromwaterandwastewaterfromtheBaselineConditionareprovidedinTable 6, Baseline Condition Water and Wastewater Greenhouse Gas Emissions. Detailed emissionscalculationsareprovidedinAppendixA.

18 Gleick,P.H.;Haasz,D.;Henges‐Jeck,C.;Srinivasan,V.;Cushing,K.K.;Mann,A.2003.WasteNot,WantNot:ThePotentialforUrban

WaterConservation inCalifornia.Publishedby thePacific Institute forStudies inDevelopment,Environment,andSecurity.Fullreport available online at: http://www.pacinst.org/reports/urban_usage/waste_not_want_not_full_report.pdf. Appendicesavailableonlineat:http://www.pacinst.org/reports/urban_usage/appendices.htm.

19 CaliforniaEnergyCommission,RefiningEstimatesofWater‐RelatedEnergyUseinCalifornia,PIERFinalProjectReport,CEC‐500‐2006‐118,(2006).

20 CaliforniaAirPollutionControlOfficersAssociation,CaliforniaEmissionsEstimatorModelUser’sGuide,(2013).21 CaliforniaAirResourcesBoard,LocalGovernmentOperationsProtocol,Chapter10:WastewaterTreatmentFacilities,(2008).22 United States Environmental Protection Agency, Inventory ofUS Greenhouse Gas Emissions and Sinks: 1990‐2006, Chapter 8:

Waste,(2008).



(g) Operational Area and Stationary

Area sourcesofGHGemissions resulting from theoperationof the existing landuses at theProject Siteunder theBaselineCondition includeequipmentusedtomaintain landscaping,suchas lawnmowersandtrimmers.ThecombustionoffossilfuelstooperatetheseequipmentresultsinGHGemissionsofCO2andsmalleramountsofCH4andN2O. Theemissionsoccuron‐siteandareadirectresultofactivityfromtheexistinglanduses;therefore,theGHGemissionsareconsideredtobedirect.Therearenoothersubstantialstationarysourceson‐site,suchasgeneratorsorindustrialsizedboilers.

The emissions of GHGs associated with operational area sources under the Baseline Condition arecalculatedusingtheCalEEModtool.Theemissionsforlandscapingequipmentarebasedonthesizeofthecommercialandretaillanduses,theGHGemissionfactorsforfuelcombustion,andtheGWPvaluesfortheGHGs emitted. Annual GHG emissions from landscaping equipment in units of MTCO2e are generallycalculatedinCalEEModasfollows:

LandscapingEquipment:

AnnualEmissions[MTCO2e]=(∑i(Units×EFLE×ALE×GWP)i)÷106 [Equation6]

Where: Units = Numberoflanduseunits(samelandusetype)[1000sqft] EFLE = GHGemissionfactor[grams(g)/1000sqft/day] ALE = Landscapingequipmentoperatingdaysperyear[day/year]

Table 6

Baseline Condition Water and Wastewater Greenhouse Gas Emissions

Land Use

Indoor Water

Demand a (gal/year)

Outdoor Water

Demand a (gal/year)

Supply Water b

(kWh/Mgal)

Treat Water b

(kWh/Mgal)

Distribute Water b

(kWh/Mgal)

Wastewater Treatment b (kWh/Mgal)

Annual GHG Emissions c

(MTCO2e/year)

GeneralRetail 339,452 208,048 9,727 111 1,272 1,911 3.96StorageFacility 258,420 – 9,727 111 1,272 1,911 2.09Walk‐inBank

Facility467,535 286,555 9,727 111 1,272 1,911 5.45

Restaurant/IceCreamParlor/Fast

Food1,534,346 97,934 9,727 111 1,272 1,911 12.97

DentalOffice 231,483 44,092 9,727 111 1,272 1,911 2.13FitnessCenter 82,373 50,487 9,727 111 1,272 1,911 0.96ParkingLot – 542,755 9,727 111 1,272 1,911 3.17TotalGHGEmissions

31

a City of Los Angeles, Department of Public Works, Bureau of Sanitation. Indoor and outdoor water demand rated rates are derived based on the ratio of indoor to outdoor water demand in CalEEMod.






GWP = Globalwarmingpotential[CO2=1,CH4=21,N2O=310] 106 = Conversionfactor[g/MT] i = Summationindex

The CalEEMod tool uses landscaping equipment GHG emission factors from the CARB OFFROAD2011model and the CARB TechnicalMemo: Change in Population and Activity Factors for Lawn and GardenEquipment(6/13/2003).23TheCalEEModtoolestimatesthatlandscapingequipmentoperatefor250daysperyearintheSouthCoastAirBasin.

The estimated annual emissions from area and stationary sources under the Baseline Condition areprovided inTable7,BaselineConditionAreaand Stationary SourceGreenhouseGasEmissions. DetailedemissionscalculationsareprovidedinAppendixA.

Table 7

Baseline Condition Area and Stationary Source Greenhouse Gas Emissions

GHG Emissions Source Annual GHG Emissions

(MTCO2e/year)

LandscapingEquipment 0.004TotalGHGEmissions 0.004


(h) Summary of Baseline Condition GHG Emissions

AsummaryoftheGHGemissionsundertheBaselineConditionisprovidedinTable8,SummaryofAnnualGHGEmissionsundertheBaselineCondition.

3.3 PROJECT OPERATIONAL EMISSIONS

3.3.1 Description of Project Condition

TheProjectwoulddemolishandremovedthetwoexistingstructuresandassociated infrastructure fromtheProject Site. TheProjectwould construct twobuildings over a single podium structure. TheNorthBuildingwould include three levels (onesubterranean)ofentirelycommercialuses. TheSouthBuildingwould include commercial uses on the first two levels, twelve levels of residential uses above thecommercialfloors,andarooftoprestaurant/loungelevelonLevel16.TheProjectwouldinclude111,339squarefeetofcommercialretailandrestaurantuseswithinthreelowerlevels(onesubterranean)andonerooftop level,249apartmentunits, including28affordablehousingunits,within the twelveupper levelsrepresenting222,564grosssquarefeetofresidentialspace.TheProjectwouldalsoprovideanew,9,134square‐foot Corner Plaza at the northeast corner of the site, a 34,050‐square‐foot Central Plaza, publicrooftopdeck/gardenareasalongSunsetBoulevard,aprivatepoolandpooldeckareaforresidents,aswell23 CaliforniaAirResourcesBoard,OFFROADModelingChangeTechnicalMemo:ChangeinPopulationandActivityFactorsforLawn

andGardenEquipment,(6/13/2003),http://www.arb.ca.gov/msei/2001_residential_lawn_and_garden_changes_in_eqpt_pop_and_act.pdf.AccessedNovember2013.



asotherresident‐onlyamenitiestotalingapproximately6,900square feet. Parkingforallproposeduseswould be provided on‐site via a seven‐level Parking Structure housedwithin the podium structure thatincludes849totalparkingspaces.Short‐andlong‐termbicycleparkingtotaling985spaceswouldalsobeprovidedon‐site,including428spacesforresidentialusesand557spacesforcommercialuses.Thetotaldevelopmentwould includeup to333,903 square feetof commercial and residential space. The squarefootageforeachoftheselandusesareprovidedinTable9,ProjectFloorArea.

Table 9

Project Floor Area

Land Use Dwelling Units (DU) or Square Feet (sqft)

Residential 249DU(incl.28affordableunits)ResidentialAmenities(e.g.,pool,etc.) 49,840sqft

ParkingStructure 305,652 sqft

GeneralRetail 51,150 sqftSupermarket 24,811 sqftWalk‐inBank 5,094 sqft

QualityRestaurants 22,189 sqftDance/YogaStudios 8,095 sqft

TotalCommercialFloorArea(excludingParkingStructure) 111,339

Source: AG‐SCH 8150 Sunset Boulevard Owner LP, 2013

Table 8

Summary of Annual GHG Emissions under the Baseline Conditions

GHG Emissions Source Annual GHG Emissions a

(MTCO2e/year)

Electricity 667 631NaturalGas 192

Mobile(Traveling) 6,358Mobile(IdlingatOn‐SiteDrive‐Thru) 98

Waste 62WaterandWastewater 31AreaandStationary 0.0

Total 7,407 7,372

a Totals may not add up exactly due to rounding in the modeling calculations. Source: PCR Services Corporation, 2014.



Forthepurposesofthisassessment,inordertoprovideacomparisonoftheProject’sGHGemissionswiththeBaselineCondition, and toassess futureGHGemissions trendsof theProject, emissionsofGHGsareestimatedformilestoneyearstheinitialproposedconstructionyearof2015throughyear2025,whenGHGemissionsareprojectedtogenerallystabilize.Withinthe2015through2025period,thereareseveralkeymilestoneyears.Themilestoneyearsassessedcorrespondscorrespondtothefollowingcircumstances:

2015:InitialyearofProjectconstruction;

2016:SecondyearofProjectconstruction;

2017:Expectedinitialoperationalyear;

2020:Theyear inwhichelectricutilities, includingLADWP,areexpectedtosupply33percentofelectricityviarenewablesources;

2023:Theyear inwhich theProjectwouldmeet theminimumrequirements for thepurchaseofgreenpower,carbonoffsets,and/orrenewableenergycertificates(RECs)andwouldnolongerberequiredtopurchaseinaccordancewiththeUSGBCLEED®EnergyandAtmosphereCredit7[v4];and

2025:Theyear inwhichthe2017‐2025 light‐dutyvehicleGHGemissionsandCorporateAverageFuelEconomystandardsaretobefullyimplementedfornewvehicles.

3.3.2 Project GHG Emission Sources and Calculation Methodology

(a) Construction

ConstructionoftheProjectwouldresultinone‐timeGHGemissionsofCO2andsmalleramountsofCH4andN2O fromheavy‐duty constructionequipment,haul trucks, andworkervehicles. Constructionemissionsare forecasted by assuming a conservative estimate of construction activities (i.e., assuming allconstructionoccursattheearliestfeasibledate)andapplyingtheoff‐roadandon‐roademissionsfactors.Theemissionsare estimatedusing theCalEEMod tool,which incorporates theCARBOFFROAD2011andEMFAC2011models. TheoutputvaluesusedinthisanalysisareadjustedtobeProject‐specificbasedonequipment types and the construction schedule. These values are applied to the construction phasingassumptions togenerateGHGemissionsvalues foreachconstructionyear. TheCalEEMod toolprovidesoptionsforspecifyingequipment,horsepowerratings,loadfactors,andoperationalhoursperday.Sinceaconstructioncontractor(s)hasnotyetbeenretainedfortheProject,specificequipmentspecificationsarenot yet known. Therefore, recommended default equipment and vehicle horsepower ratings and loadfactorsprovidedinCalEEModareusedinthisassessment.Thisassessmentalsoassumesequipmentwouldoperatefor8hoursduringaworkday.

ConstructionoftheProjectwouldoccuroveranumberofphasesandincludeactivitiessuchasdemolition,debrisandsoilhauling,buildingconstruction,architecturalcoating,andpaving.Informationregardingtheactivitiesthatwouldoccurduringthesephasesisprovidedbelow:

Demolition: This phase is anticipated to begin in 2015 and last for approximately twomonths.Constructionequipmentwould includeanexcavator, loader, concretesaw,haul trucks,andotherconstructionequipment.Approximately6,500cubicyards(cy)ofdebriswouldbehauledoff‐site.



GradingandExcavation:Thisphaseisanticipatedtobeginafterthedemolitionphaseandlastforapproximately fourmonths. Construction equipmentwould include a drill rig, excavator, dozer,loaders,scraper,watertruck,andhaultrucks.Approximately58,500cyofsoilwouldbeexported.

BuildingConstruction: Thisphaseisanticipatedtobegininmid‐2015andlast forapproximately18 months. During this phase, the parking structure and residential and commercial buildingswould be constructed. Construction equipment would include a concrete pump, generator, off‐highwaytruck,cranes,lifts,welders,andotherconstructionequipment.

SiteWork/Closeout: This phase is anticipated to begin in 2016 and last for approximately ninemonths. During this phase, concretewould be poured during construction of the buildings andinfrastructure and surfaces would be paved. Construction equipment would include a concretepump,concretetrucks,andpavingequipment.

ArchitecturalCoating: Thisphase isanticipated tobegin inmid‐2016and last forapproximatelyfivemonths.Duringthisphase,theinteriorandexteriorcoatingwouldbeappliedtotheresidentialand commercial buildings. Coating equipment would include a mixer, mobile crane, and aircompressor.

The emissions of GHGs associated with construction of the Project were calculated for each year ofconstruction activity. Detailed emissions calculations are provided in Appendix B. Results of the GHGemissionscalculationsarepresentedinTable10,EstimatedUnmitigatedProjectConstructionGreenhouseGasEmissions.AlthoughGHGsaregeneratedduringconstructionandareaccordinglyconsideredone‐timeemissions, it is important to themwhen assessing all of the long‐termGHGemissions associatedwith aproject.

Table 10

Estimated Unmitigated Project Construction Greenhouse Gas Emissions

Emission Source Annual GHG Emissions a

(MTCO2e/year)

ConstructionYear1(2015) 1,631ConstructionYear2(2016) 2,346Total 3,977 a Totals may not add up exactly due to rounding in the modeling calculations Detailed emissions calculations

are provided in Appendix B.

Source: PCR Services Corporation, 2014

(b) Operational Energy – Electricity

The emissions of GHGs associated with electricity demand for the Project are calculated using theCalEEMod tool. EmissionsofGHGsassociatedwithoperationof theProjectarebasedon thesizeof thecommercial,retail,restaurant,andresidentiallanduses(includingresidentialamenitiessuchastheprivatepool and pool deck), the electrical demand factors for the land uses, the GHG emission factors for theelectricityutilityprovider,andtheGWPvaluesfortheGHGsemitted.AnnualelectricityGHGemissionsarecalculatedusingthegeneralformulashownpreviouslyasEquation1. Forresidentiallanduses,emission



factorsarespecified inunitsofdwellingunits (DU) insteadof1,000sqft. Thisassessmentalso includeselectricity‐related GHG emissions from the proposed enclosed parking structure, which would includeelevators,lighting,andaventilationsystem.

TheCalEEModtoolcalculateselectricaldemandbasedondatafromtheCEUS,whichlistsenergydemandbybuildingtype.24 However,sincethedatafromtheCEUSisfrom2002,theCalEEModtoolincorporatescorrectionfactorstoaccountforcompliancewiththe2008/2010Title24BuildingStandardsCode.While,therecentlyamended2013Title24BuildingStandardsCode isscheduledtogo intoeffecton January1,2014,theProjectwouldmeetorexceedtheamendedstandardsviameasuresimplementedtoachievetheUnited States Green Building Council (USGBC) Leadership in Energy and Environmental and Design®(“LEED®”)Silverrating.TheProjectwouldbedesignedtoincorporateProjectDesignFeatures(PDFs)thatwouldreduceitsenergydemandwiththegoalofachievingorexceedingtherequirementsoftheStateofCaliforniaGreenBuildingStandards(CALGreen)Code,theCityofLosAngelesGreenBuildingCode,andtheUSGBC LEED® Silver rating. Thus, the Project would reduce its electricity demand as compared to thedefault electricity factors in the CalEEMod tool. The PDFswere accounted for in the CalEEMod tool byselecting the appropriate options in the “mitigationmeasures” section of themodel. A summary of theenergy‐efficiencyPDFsisprovidedbelow:

GreenBuildingMeasures:TheProjectwouldbedesignedandoperatedtomeetorexceedtheapplicablerequirementsof theStateofCaliforniaGreenBuildingStandardsCodeandtheCityofLosAngelesGreenBuildingCodeandachievetheUSGBCLEED®SilverCertification.TheProjectwouldincorporatemeasuresandperformancestandardstosupportitsLEED®SilverCertification,whichincludebutarenotlimitedtothefollowing:

TheProjectwould implementaconstructionwastemanagementplantorecycleand/orsalvageaminimum of 75 percent of nonhazardous construction debris or minimize the generation ofconstructionwaste to 2.5 pounds per square foot of building floor area. (LEED®Materials andResourcesCredit5[v4]25);

TheProjectwouldbedesignedtooptimizeenergyperformanceandreducebuildingenergycostby10 percent for new construction compared to ASHRAE 90.1‐2010, Appendix G and the Title 24BuildingStandardsCode.(LEED®EnergyandAtmosphereCredit2[v4]);

TheProjectwouldreduceemissionsthroughtheuseofgrid‐source,renewableenergytechnologiesandcarbonmitigationprojects.TheProjectwouldengageinacontractforqualifiedresources,foraminimumoffiveyears,tobedeliveredatleastannually.Thecontractwouldspecifytheprovisionof 100percent of theProject’s energy fromgreenpower, carbonoffsets, and/orRECsduring thefirstfiveyearsofoperation.TheProjectwouldcommittoprovidingaminimumof1015percentofthe Project’s energy from green power, carbon offsets, and/or RECs for two years after theminimumfiveyearperiod.(LEED®EnergyandAtmosphereCredit7[v4]);and

TheProjectwouldreduceindoorwaterusebyaminimumof35percentbyinstallingwaterfixturesthatexceedapplicablestandards.(LEED®WaterEfficiencyCredit2[v4]).


AccessedNovember2013.25 Thebracketedtext“v4”denotesversion4oftheLEED®BuildingDesignandConstructioncredits.



The LADWP provides electric service to the Project Site. Emission factors for GHGs due to electricalgenerationtoservetheelectricaldemandsoftheProjectwereobtainedfromtheLADWP20122013PowerIntegrated Resource Plan, which provides a CO2 intensity of 1,156 1,094 pounds of CO2 per MWh.26Currently,LADWPprovides20percentofelectricityviarenewablesources.27By2020,LADWPisexpectingtoprovidemeettheState’sRenewablesPortfolioStandardofatleast33percentofelectricityviarenewablesourcespursuanttotheState’sRenewablesPortfolioStandard. BasedondataobtainedfromCARBstaff,“[i]fanapplicantwouldliketouseanEF[emissionfactor]thatrepresentsthestate’sRenewablePortfolioStandard (RPS) law and growth in electricity demand, the EF of 595 lbs CO2/MWh may be used.”28According to CARB staff, the “EF represents a ‘marginal’ supply profile for new generation that will beadded to the grid in the years 2020 and beyond, and is consistentwith themethodology used in stateemission rule impact assessments.”29 Therefore, consistentwith theCARB staff recommendation, aCO2intensityfactorof595poundsofCO2perMWhwasusedforelectricityemissionsforyears2020through2025. Thus, by 2020, the CO2 intensity should be reduced to 968 pounds of CO2 per MWh if LADWPreplaces its2011energyportfoliowith renewable sourcesonaproportionatebasis (e.g., calculatedasaproportionwhere1,156poundsofCO2perMWhrepresentsa20percentrenewablesportfolio).EmissionfactorsforCH4andN2OwereobtainedfromtheCaliforniaEmissionsEstimatorModel(CalEEMod).30 Themilestone year 2017 emissions Emissions for years 2017 through 2019 take into account the currentLADWPrenewablemixofapproximately20percent(1,1561,094poundsofCO2perMWh).Themilestoneyears2020,2023,and2025emissionstakeintoaccountarenewablemixof33percent(968poundsofCO2perMWh).

TheestimatedannualemissionsfromelectricaldemandfromtheProjectatmilestoneyearsareprovidedinTable 11, Project Electrical Demand Greenhouse Gas Emissions. Detailed emissions calculations areprovidedinAppendixB.

(c) Operational Energy – Natural Gas

The emissions of GHGs associated with natural gas demand for the Project are calculated using theCalEEMod tool. EmissionsofGHGsassociatedwithoperationof theProjectarebasedon thesizeof thecommercial,retail,restaurant,andresidentiallanduses(includingresidentialamenitiessuchastheprivatepool andpool deck), thenatural gas demand factors for the landuses, theGHGemission factors for thenaturalgascombustion,andtheGWPvaluesfortheGHGsemitted.AnnualnaturalgasGHGemissionsarecalculatedusingthegeneralformulashownpreviouslyasEquation2. Forresidentiallanduses,emissionfactorsarespecifiedinunitsofDUinsteadof1,000sqft.

26 LosAngelesDepartmentofWaterandPower,2012PowerIntegratedResourcePlan,(2012)C‐11.27 LosAngelesDepartmentofWaterandPower,2012PowerIntegratedResourcePlan,(2012)111.28 CaliforniaAirResourcesBoard,StatewideEmissionFactors(EF)ForUseWithAB900Projects,March2014.Theemissionfactorof

595 lbs CO2/MWh is from the California LEV III Initial Statement Of Reasons (ISOR, Dec. 7, 2011),http://www.arb.ca.gov/regact/2012/leviiighg2012/leviiighg2012.htm,basedonanalysiswithCA‐GREETmodel.ThisdocumentisprovidedinAppendixB.

29 CaliforniaAirResourcesBoard,StatewideEmissionFactors(EF)ForUseWithAB900Projects,March2014.30 CaliforniaAirPollutionControlOfficersAssociation,CaliforniaEmissionsEstimatorModel,http://www.caleemod.com/.Accessed

January2014.



TheCalEEModtoolcalculatesnaturalgasdemandbasedondatafromtheCEUS,whichlistsenergydemandbybuildingtype.31 However,sincethedatafromtheCEUSisfrom2002,theCalEEModtoolincorporatescorrectionfactorstoaccountforcompliancewiththe2008/2010Title24BuildingStandardsCode.While,therecentlyamended2013Title24BuildingStandardsCode isscheduledtogo intoeffecton January1,2014,theProjectwouldmeetorexceedtheamendedstandardsviameasuresimplementedtoachievetheUSGBC LEED® Silver rating. The Projectwould be designed to incorporate PDFs thatwould reduce itsenergydemandwiththegoalofachievingorexceedingtherequirementsoftheCALGreenCode,theCityofLosAngelesGreenBuildingCode,andtheUSGBCLEED®Silverrating. Thus,theProjectwouldreduceitsnatural gasdemandascompared to thedefault electricity factors in theCalEEMod tool. ThePDFswere


AccessedNovember2013.

Table 11

Project Electrical Demand Greenhouse Gas Emissions

Land Use

Units (DU or

1000 sqft)

Annual Electrical Demand Factor a (MWh/unit/year)

CO2 Factor b

(pounds/MWh)CH4 Factor

c (pounds/MWh)

N2O Factor c

(pounds/MWh)


(MTCO2e/year)

2017‐2019 Residential 249 3.46 1,156 1,094 0.029 0.0062 434.17 410.93

ResidentialAmenities 49.84 11.78 1,156 1,094 0.029 0.0062 305.30 288.96GeneralRetail 51.15 14.68 1,156 1,094 0.029 0.0062 390.62 369.72Supermarket 24.81 38.63 1,156 1,094 0.029 0.0062 455.47 431.09Walk‐inBank 5.09 13.97 1,156 1,094 0.029 0.0062 37.02 35.03

QualityRestaurants 22.19 45.92 1,156 1,094 0.029 0.0062 511.40 484.03Dance/YogaStudios 8.10 11.78 1,156 1,094 0.029 0.0062 49.59 46.93ParkingStructure 305.65 6.35 1,156 1,094 0.029 0.0062 1,009.37 955.35

TotalGHGEmissions 3,193 3,0222020‐2025/2023/2025

Residential 249 3.46 968 595 0.029 0.0062 363.71 223.92ResidentialAmenities 49.84 11.78 968 595 0.029 0.0062 255.75 157.45

GeneralRetail 51.15 14.68 968 595 0.029 0.0062 327.23 201.46Supermarket 24.81 38.63 968 595 0.029 0.0062 381.55 234.90Walk‐inBank 5.09 13.97 968 595 0.029 0.0062 31.01 19.09

QualityRestaurants 22.19 45.92 968 595 0.029 0.0062 428.41 263.75Dance/YogaStudios 8.10 11.78 968 595 0.029 0.0062 41.54 25.57ParkingStructure 305.65 6.35 968 595 0.029 0.0062 845.56 520.57

TotalGHGEmissions 2,675 1,647

a California Air Pollution Control Officers Association, California Emissions Estimator Model, http://www.caleemod.com/. Accessed November 2013 March 2014. Demand factor accounts for a 10 percent reduction in Title 24 energy demand.

b Los Angeles Department of Water and Power, 2012 Power Integrated Resource Plan, (2012) C‐11.



Source: PCR Services Corporation, 2014. Detailed emissions calculations are provided in Appendix B.



accounted for in the CalEEMod tool by selecting the appropriate options in the “mitigation measures”sectionofthemodel.Asummaryoftheenergy‐efficiencyPDFsisprovidedaboveinPDF‐GHG‐1.

The combustion of natural gas results in relatively equal amounts of GHG emissions per unit of gascombustedinthestate.EmissionfactorsforGHGsduetonaturalgascombustiontoservetheheatingandcookingdemandsoftheProjectwereobtainedfromtheCalEEModtool,whichprovidesstatewideemissionfactors.32 TheemissionsofGHGsduetonaturalgasdemandwouldberelativelysteadyforthemilestoneyearsassessed(2017,2020,2023,and2025).

The estimated annual emissions from natural gas combustion from the Project Baseline Condition areprovided in Table 12, Project Natural Gas Combustion Greenhouse Gas Emissions. Detailed emissionscalculationsareprovidedinAppendixB.

Table 12

Project Natural Gas Combustion Greenhouse Gas Emissions

Land Use

Units (DU or

1000 sqft)

Annual Natural Gas Demand

Factor a (MMBtu/unit

/year)

CO2 Factor b

(pounds/ MMBtu)

CH4 Factor b

(pounds/ MMBtu)

N2O Factor b

(pounds/ MMBtu)


(MTCO2e/year)

Residential 249 6.30 117.65 0.0023 0.0022 84.28ResidentialAmenities 49.84 17.37 117.65 0.0023 0.0022 46.49

GeneralRetail 51.15 1.58 117.65 0.0023 0.0022 4.34Supermarket 24.81 21.56 117.65 0.0023 0.0022 28.71Walk‐inBank 5.09 9.88 117.65 0.0023 0.0022 2.70

QualityRestaurants 22.19 228.49 117.65 0.0023 0.0022 272.20Dance/YogaStudios 8.10 17.37 117.65 0.0023 0.0022 7.55TotalGHGEmissions 446

a California Air Pollution Control Officers Association, California Emissions Estimator Model, http://www.caleemod.com/. Accessed November 2013 March 2014. Demand factor accounts for a 10 percent reduction in Title 24 energy demand.




(d) Operational Mobile

MobilesourceemissioncalculationsassociatedwiththeProjectBaselineConditionarecalculatedusingtheCalEEModtool.EmissionsofGHGsassociatedwithmobilesourcesfromoperationoftheProjectarebasedontheaveragedailytriprate,tripdistance,theGHGemissionfactorsforthemobilesources,andtheGWP

32 CaliforniaAirPollutionControlOfficersAssociation,CaliforniaEmissionsEstimatorModel,http://www.caleemod.com/.Accessed




values for the GHGs emitted. The types of vehicles that would visit the Site include all vehicle typesincludingautomobiles, light‐dutytrucks,deliverytrucks,andwastehaultrucks. ModelingfortheProjectwasconductedusingthevehiclefleetmixfortheSouthCoastAirBasinasprovidedinEMFAC2011.AnnualmobilesourceGHGemissions inunitsofMTCO2earegenerallycalculated inCalEEModusingthegeneralformulashownpreviouslyasEquation3. Forresidential landuses, tripgenerationratesarespecified inunitsoftripsperDUinsteadofper1,000sqft.

TheCalEEModtoolallowstheinputofseveralvariablestoquantifymobilesourceemissions.ThenumberofmotorvehiclesthattraveltoandfromtheProjectSiteisbasedontripgenerationratesasdocumentedinthe traffic study for the Project.33 As was discussed previously, the Project traffic study34 occasionallyreferences trips on a PCE basis in order to evaluate traffic congestion on roadways. However, for thepurposes of estimating emissions, this assessment uses the actual trip rates (not adjusted for PCE triprates) and the associated emissions factors for each vehicle type, as well as the vehicle fleet mix, asprovided inEMFAC2011. Trip lengthvalues arebasedon the residential andcommercial tripdistancesprovidedinCalEEMod.CalEEModprovidestripdistancesforhome‐work,home‐shopping,andhome‐otherforresidentialtripsandcommercial‐customer,commercial‐work,andcommercial‐nonwork(e.g.,deliverytrips)fornon‐residentialtrips.Sincetheprojectwouldincludebothresidentialandcommerciallanduses,allofthesetriplengthswereincludedinthemodel.ThetripdistancesaremultipliedbytheaveragedailytripestimatestoestimatetheaveragedailyVMT.TheProjectwouldincorporatecharacteristicsandPDFsthat would reduce trips and VMT as compared to standard ITE trip generation rates. The Projectcharacteristics listedbeloware consistentwith theCAPCOAguidancedocument,QuantifyingGreenhouseGas Mitigation Measures,35 which provides emission reduction values for recommended mitigationmeasures, and would reduce VMT and vehicle trips to the Project site by approximately 35.5 percentcomparedtoadevelopmentwithoutthesecharacteristics.TheywouldthereforeresultinacorrespondingreductioninVMTandassociatedairpollutantemissions

ProjectCharacteristics:TheProjectcharacteristicslistedbelowareconsistentwiththeCAPCOAguidancedocument, andwould reduce vehicle trips to and from theProject site compared to a business‐as‐usualprojectwithouttheseProjectcharacteristics.TheywouldthereforeresultinacorrespondingreductioninVMTandassociatedGHGemissions.

IncreasedDensity: Increaseddensity,measuredintermsofpersons, jobs,ordwellingunitsperunitarea,reducesemissionsassociatedwithtransportationasitreducesthedistancepeopletravelforworkorservicesandprovidesafoundationfortheimplementationofotherstrategiessuchasenhanced transit services. The Project would increase the site density to approximately 97dwelling units per acre and 118 jobs per acre (refer to Section 4.H, Population, Housing, andEmployment,ofthisDraftEIR).

LocationEfficiency:LocationefficiencydescribesthelocationoftheProjectrelativetothetypeofurbanlandscapesuchasanurbanarea,compactinfill,orsuburbancenter.Ingeneral,comparedto

33 Hirsch/Green Transportation Consulting, Inc., Traffic Impact Analysis Report, ProposedMixed‐Use Development, 8150 Sunset

Boulevard,Hollywood,California,November2013.34 Hirsch/Green Transportation Consulting, Inc., Traffic Impact Analysis Report, ProposedMixed‐Use Development, 8150 Sunset

Boulevard,Hollywood,California,November2013.35 CaliforniaAirPollutionControlOfficersAssociation,QuantifyingGreenhouseGasMitigationMeasures,(2010).



thestatewideaverage,aprojectcouldrealizeVMTreductionsupto65percentinanurbanarea,upto 30 percent in a compact infill area, or up to 10 percent in a suburban center from landuse/location strategies. The Project Site represents an urban/compact infill locationwithin theHollywood community of the City of Los Angeles. The Project Site is served by existing publictransportationlocatedwithinaquarter‐mile.TheProjectSiteiswithinanactiveurbancenterwithmanyexistingoff‐sitecommercialandresidentialbuildingsandservesasaneasterngatewaytotheSunset Strip. The location efficiency of the Project Sitewould result in synergistic benefits thatwould reduce vehicle trips and VMT compared to the statewide average and would result incorrespondingreductionsintransportation‐relatedemissions.

Increased LandUseDiversity andMixed‐Uses: The Project would co‐locate complementarycommercial and residential land uses in close to proximity to existing off‐site commercial andresidentialuses. TheProjectwould includeon‐siteretailandresidential landusesandwouldbelocatedwithinaquarter‐mileofoff‐sitecommercialandresidentialuses. TheProjectSite isalsolocatedwithinaquarter‐mileofopenspace/parkusesatHavenhurstPark. Theincreasesinlanduse diversity and mix of uses on the Project Site would reduce vehicle trips and VMT byencouraging walking and non‐automotive forms of transportation, which would result incorrespondingreductionsintransportation‐relatedemissions.

IncreasedDestinationAccessibility:TheProjectwouldbelocatedinanareathatoffersaccesstomultipleothernearbydestinationsincludingthe8000Sunsetcommercialcenter,whichincludesamovie theater, fitnesscenter,restaurants,andgrocerystore, theLaughFactorycomedyclub,andmany other commercial and recreational destinations along the Sunset Strip. The access tomultiple destinations in close proximity to the Project Sitewould reduce vehicle trips and VMTcompared to the statewide average and encourage walking and non‐automotive forms oftransportationandwouldresultincorrespondingreductionsintransportation‐relatedemissions.

IncreasedTransitAccessibility: The Project would be locatedwithin a quarter‐mile of publictransportation,includingexistingMetrobusroutes(e.g.,2/302,218,and780Rapid).TheProjectwouldprovideaccess toon‐siteuses fromexistingpedestrianpathways. TheProjectwouldalsoprovideapproximately985totalbicycleparkingspaces(428bicycleparkingspacesforresidentialuses and 557 spaces for commercial uses to encourage utilization of alternative modes oftransportation.TheincreasedtransitaccessibilitywouldreducevehicletripsandVMTversusthestatewideaverageandencouragewalkingandnon‐automotiveformsoftransportationandwouldresultincorrespondingreductionsintransportation‐relatedemissions.

IntegratedAffordableandBelowMarketRateHousing: Belowmarket ratehousingprovidesgreater opportunity for people to live closer to job centers and to accommodatemorepeople inurbaninfillareas.TheProjectwouldinclude28belowmarketratedwellingunits(approximately11percentofthetotalnumberofdwellingunits),whichwouldresultinanincreaseinalternativetransitusageandacorrespondingreductionintransportation‐relatedemissions.

Provide Pedestrian Network Improvements: Providing pedestrian access that minimizesbarriersand links theProjectSitewithexistingorplannedexternalstreetsencouragespeople towalkinsteadofdrive. TheProjectwouldprovideaninternalpedestriannetworkthatlinkstotheexisting off‐site pedestrian network including existing off‐site sidewalks,would result in a smallreductioninVMTandassociatedtransportation‐relatedemissions.



EmissionsofGHGs frommotorvehiclesaredependentonmodelyearsand thespecific typesofvehiclesthat are used to travel to and from the existing Project Site. The emissions were calculated using arepresentativemotorvehicle fleetmix foryears2017 through2025and2020asprovided inCalEEMod.ThemobilesourceGHGemissionsforyear2017wereestimatedbasedonthedirectresultoutputfromtheCalEEMod tool. However, the CalEEMod tool may not adequately reflect future year GHG emissionsbecauseitmilestoneyears2023and2025wereestimatedbyusingtheresultsofthe2017modelrunandapplyingareductionfactorbasedontheaverageGHGemissionsfactorforthe2016and2023/2025vehicleemissionsstandards.ThiswasdonebecausetheCalEEModtooldoesnotincorporatetheemissionfactorsfor the 2017‐2025 vehicle emissions standards. The national policy for fuel efficiency and emissionsstandards for the United States auto industry requires that new passenger cars and light‐duty trucksachieveanaveragefueleconomystandardof35.5milespergallon(mpg)and250gramsofCO2permilebymodel year 2016 (Phase I standards), based on USEPA calculation methods. In August 2012, morestringentphased‐instandardswereadopted fornewmodelyear2017through2025passengercarsandlight‐dutytrucks.By2020,newvehiclesareprojectedtoachieve41.7mpg(ifGHGreductionsareachievedexclusivelythroughfueleconomyimprovements)and213gramsofCO2permile(PhaseIIstandards).By2023,newvehiclesareprojectedtoachieve49.4mpg(ifGHGreductionsareachievedexclusivelythroughfueleconomyimprovements)and180gramsofCO2permile(PhaseIIstandards).By2025,newvehiclesare required to achieve 54.5 mpg (if GHG reductions are achieved exclusively through fuel economyimprovements)and163gramsofCO2permile(PhaseIIstandards). CARBstaffhasprovidedfutureyearCO2 emission factors for statewide on‐roadmobile sources thatmay be used for AB 900 projects if theproject’smobilesourcesinclude“allvehicleclassifications.”36 Asdiscussedabove,itwasassumedthatallvehicle typeswouldvisit thesite. Therefore, thisassessmentuses theCO2emission factorsprovidedbyCARBstafftoestimatefutureyear(2018through2025)GHGemissionsfrommobilesources.EmissionsofCH4andN2Owereestimatedbasedon thedirectresultoutputs fromtheCalEEModtool foryears2018through 2025. From a GHG emissions standpoint, the 2020, 2023, and 2025 Phase II standards areapproximately14.8percent,28.0percentand34.8percentlowerthanthePhaseIstandards,respectively.Thus,a14.8percent,28.0percent,and34.8percentreductionfactorwasappliedtothe2017modelresulttoestimatethe2020,2023,and2025mobilesourceGHGemissions,respectively.Thereasonthatthe2017modelrunwasusedwasbecausethe2017modelrungenerallycoincideswiththeendingmodelyearforthePhase Istandards(i.e.,2016); therefore, the fleetmixwouldgenerallyreflect theappropriatevehicleturnover rates for older vehicles that are replaced with newer vehicles meeting the adopted neweremissionsstandards.

Theestimatedannualemissions frommobilesources fromtheProjectareprovided inTable13,ProjectMobileSourceGreenhouseGasEmissions.DetailedemissionscalculationsareprovidedinAppendixB.

(e) Operational Waste

The Project would generate MSW from day‐to‐day operational activities, which generally consists ofproductpackaging,grassclippings,furniture,clothing,bottles,foodscraps,newspapers,plastic,andotheritems routinely disposed of in trash bins. A portion of the MSW is diverted to waste recycling andreclamationfacilities.Wastethatisnotdivertedisusuallysenttolocallandfillsfordisposal.MSWthatisdisposed in landfills results inGHG emissionsof CO2 andCH4 from thedecompositionof thewaste thatoccursoverthespanofmanyyears.

36 CaliforniaAirResourcesBoard,StatewideEmissionFactors(EF)ForUseWithAB900Projects,March2014.



Emissions of GHGs associated with solid waste disposal under the Project are calculated using theCalEEModtool. Theemissionsarebasedonthesizeofthecommercial,retail,restaurant,andresidentiallanduses,thewastedisposalrateforthelanduses,thewastediversionrate,theGHGemissionfactorsforsolid waste decomposition, and the GWP values for the GHGs emitted. Annual waste disposal GHGemissions in units of MTCO2e are generally calculated in CalEEMod using the general formula shownpreviouslyasEquation4.

The CalEEMod tool allows the input of several variables to quantify solidwaste emissions. Themodelrequirestheamountofwastedisposed,whichistheproductofthewastedisposalratetimesthelanduseunits.AnnualwastedisposalratesusedinCalEEModarebasedondatafromCalRecycle.ThetotalamountofwastedisposedwasreducedbythediversionratefortheCityofLosAngelesof60percent,accordingto

Table 13

Project Mobile Source Greenhouse Gas Emissions

Land Use Fleet Mix Year

(All Vehicle Classes) Estimated Annual

VMT CO2 Emission Factor

(grams/mile) Annual GHG Emissions

(MTCO2e/year)

ProjectSite 2017 12,427,524 CalEEMod 1 5,414ProjectSite 2018 12,427,524 430 5,344ProjectSite 2019 12,427,524 423 5,257ProjectSite 2020 12,427,524 415 5,158ProjectSite 2021 12,427,524 408 5,071ProjectSite 2022 12,427,524 400 4,971ProjectSite 2023 12,427,524 391 4,859ProjectSite 2024 12,427,524 384 4,772ProjectSite 2025 12,427,524 375 4,660

2017(FullImplementationofPavleyPhaseI)

ProjectSite2017

(AllVehicleClasses)12,427,524 5,414.21

TotalGHGEmissions 5,4142020(PartialImplementationofPavleyPhaseII)

ProjectSite 2020(AllVehicleClasses)

12,427,524 4,612.73

TotalGHGEmissions 4,6132023(PartialImplementationofPavleyPhaseII)

ProjectSite2023

(AllVehicleClasses)12,427,524 3,898.08

TotalGHGEmissions 3,8982025(FullImplementationofPavleyPhaseII)

ProjectSite 2025(AllVehicleClasses)

12,427,524 3,529.93

TotalGHGEmissions 3,530

Source: PCR Services Corporation, 2014. Detailed emissions calculations are provided in Appendix B. 1 Mobile source GHG emissions for 2017 are based on the direct model result output from CalEEMod.



themostrecentdataavailable.37TheGHGemissionfactors,particularlyforCH4,dependoncharacteristicsof the landfill, such as the presence of a landfill gas capture system and subsequent flaring or energyrecovery. Thedefault values, asprovided inCalEEMod, for landfill gas capture (e.g., no capture, flaring,energyrecovery),whicharestatewideaverages,areusedinthisassessment.

The estimated annual emissions from solid waste disposal from the Project are provided inTable 14,ProjectSolidWasteDisposalGreenhouseGasEmissions. The emissions of GHGsdue towaste generationwould be relatively steady for the milestone years assessed (2017, 2020, 2023, and 2025). DetailedemissionscalculationsareprovidedinAppendixB.

Table 14

Project Solid Waste Disposal Greenhouse Gas Emissions

Land Use Waste

Diversion a

Waste Disposal Rate after Diversion b

(tons/year) Landfill Gas (no capture) c

Landfill Gas (capture with

flaring) c


(MTCO2e/year)

Residential 60% 222.30 6% 94% 101.13GeneralRetail 60% 75.95 6% 94% 34.55Supermarket 60% 165.78 6% 94% 75.42Walk‐inBank 60% 7.56 6% 94% 3.44

QualityRestaurants 60% 434.76 6% 94% 197.78Dance/YogaStudios 60% 12.02 6% 94% 5.47TotalGHGEmissions 418

a County of Los Angeles, Countywide Integrated Waste Management Plan, 2012 Annual Report (2013). b Waste generation factors for residential units are based on factors provided in the L.A. CEQA Threshold Guide. Generation factors

for others uses are from the Integrated Waste Management Board, Targeted Statewide Waste Characterization Study: Waste Disposal and Diversion Findings for Selected Industry Groups, June 2006.

c California Air Pollution Control Officers Association, California Emissions Estimator Model, http://www.caleemod.com/. Accessed

January March 2014. Waste disposal rate is based on the rates provided in CalEEMod minus the amount of waste diverted based on data from the City of Los Angeles. Landfill gas no capture and capture with flaring percentages are based on CalEEMod default statewide average values.



(f) Operational Water and Wastewater

Waterandwastewatergenerated fromtheexisting landusesunder theProjectwouldrequireenergy tosupply,distributeandtreat.ThecombustionoffossilfuelstoproduceelectricityaswellasthewastewatertreatmentprocessresultsinGHGemissionsofCO2andsmalleramountsofCH4andN2O.

TheemissionsofGHGsassociatedwithwaterdemandandwastewatergenerationunder theProjectarecalculated using the CalEEMod tool. The emissions are based on the size of the commercial, retail,

37 CountyofLosAngeles,CountywideIntegratedWasteManagementPlan,2012AnnualReport(2013).



restaurant, andresidential landuses, thewaterdemand factors, theelectrical intensity factors forwatersupply, treatment, and distribution and for wastewater treatment, the GHG emission factors for theelectricity utility provider, and the GWP values for the GHGs emitted. Annual water demand andwastewater GHG emissions due to electricity are generally calculated in CalEEMod using the generalformulashownpreviouslyasEquation5.

TheCalEEModtoolcalculateswaterdemandbasedonannualratesinthePacificInstituteWasteNotWantNotreport.38 TheCalEEModtoolprovidesoptionstoaccountfortheuseofwatersavingfeaturessuchastheuseoflow‐flowwaterfixtures(e.g.,low‐flowfaucets,low‐flowtoilets).TheProjectwouldincorporatePDFstoreduceindoorandoutdoorwaterusage,assummarizedpreviousinPDF‐GHG‐1.Implementationof thesePDFswouldreduce indoorwaterusagebyapproximately35percentcompared to typicalusagevalues fordevelopmentsmeeting theminimumrequirements. Thesewater reduction factorshavebeenaccountedforintheCalEEModtool.

TheCEC’sestimate forenergy intensityof thewateruse cycle inSouthernCalifornia, asprovided in the2006 CEC report Refining Estimates ofWater‐Related Energy Use in California, is used to calculate theenergyusagerelatedtowatersupply,treatment,anddistributionandwastewatertreatment.39 ThesameelectricityGHGemissionsfactorsdiscussedinSection3.3.2(b),OperationalEnergy–Electricity,areusedforwaterandwastewaterenergyusage.

TheemissionsofGHGsassociatedwithwastewatertreatmentprocessemissionsarealsocalculatedusingtheCalEEMod tool. The emissions arebasedon the typeof treatment (e.g., aerobic, facultative lagoons,septic systems). The emissions are calculating using the default settings in CalEEMod for the type ofwastewater treatment. Calculation formulasaredescribed indetail in theCaliforniaEmissionsEstimatorModel User’s Guide, Appendix A.40 As stated in the User’s Guide, the GHGs emitted from each type ofwastewatertreatmentarebasedontheCARB’sLocalGovernmentOperationsProtocol(LGOP),41whicharein turn based onUnited States Environmental ProtectionAgency (USEPA)methodologies.42 The defaultCalEEMod settings forwastewater treatment are: 10.33percent septic tank, 87.46percent aerobic, 2.21percentfacultativelagoonsand100percentanaerobiccombustionofgas.

Theestimatedannualemissions fromwaterandwastewater fromtheProjectareprovided inTable15,ProjectWaterandWastewaterGreenhouseGasEmissions. DetailedemissionscalculationsareprovidedinAppendixB.

38 Gleick,P.H.;Haasz,D.;Henges‐Jeck,C.;Srinivasan,V.;Cushing,K.K.;Mann,A.2003.WasteNot,WantNot:ThePotentialforUrban

WaterConservation inCalifornia.Publishedby thePacific Institute forStudies inDevelopment,Environment,andSecurity.Fullreport available online at: http://www.pacinst.org/reports/urban_usage/waste_not_want_not_full_report.pdf. Appendicesavailableonlineat:http://www.pacinst.org/reports/urban_usage/appendices.htm.

39 CaliforniaEnergyCommission,RefiningEstimatesofWater‐RelatedEnergyUseinCalifornia,PIERFinalProjectReport,CEC‐500‐2006‐118,(2006).

40 CaliforniaAirPollutionControlOfficersAssociation,CaliforniaEmissionsEstimatorModelUser’sGuide,(2013).41 CaliforniaAirResourcesBoard,LocalGovernmentOperationsProtocol,Chapter10:WastewaterTreatmentFacilities,(2008).42 United States Environmental Protection Agency, Inventory ofUS Greenhouse Gas Emissions and Sinks: 1990‐2006, Chapter 8:

Waste,(2008).



(g) Operational Area and Stationary

AreasourcesofGHGemissionsresultingfromoperationoftheProjectincludeequipmentusedtomaintainlandscaping,suchaslawnmowersandtrimmers.Thecombustionoffossilfuelstooperatetheseequipmentresults in GHG emissions of CO2 and smaller amounts of CH4 and N2O. There are no other substantialstationarysourceson‐site,suchasgeneratorsorindustrialsizedboilers.ResidentialhearthswouldnotbeinstalledintheProject’sresidentialuses.

TheemissionsofGHGsassociatedwithoperationalareasourcesundertheProjectarecalculatedusingtheCalEEModtool. Theemissionsforlandscapingequipmentarebasedonthesizeofthecommercial,retail,

Table 15

Project Water and Wastewater Greenhouse Gas Emissions

Land Use

Indoor Water

Demand a (gal/year)

Outdoor Water

Demand a (gal/year)

Supply Water b

(kWh/Mgal)

Treat Water b

(kWh/Mgal)

Distribute Water b

(kWh/Mgal)

Wastewater Treatment b (kWh/Mgal)


(MTCO2e/year)

2017‐2019(CO2IntensityFactor:1,1561,094 poundsperMWh)Residential 5,423,736 5,260,435 9,727 111 1,272 1,911 73.26 69.70GeneralRetail 770,487 726,505 9,727 111 1,272 1,911 10.29 9.79Supermarket 584,769 27,821 9,727 111 1,272 1,911 4.75 4.53Walk‐inBank 76,784 72,402 9,727 111 1,272 1,911 1.03 0.98

QualityRestaurants

1,900,314 186,605 9,727 111 1,272 1,911 16.01 15.27

Dance/YogaStudios

121,942 114,982 9,727 111 1,272 1,911 1.63 1.55

ParkingStructure – 2,856,125 9,727 111 1,272 1,911 16.67 15.78TotalGHGEmissions

124 118

2020‐2025/2023/2025(CO2IntensityFactor:968 595 poundsperMWh)Residential 5,423,736 5,260,435 9,727 111 1,272 1,911 62.46 41.04GeneralRetail 770,487 726,505 9,727 111 1,272 1,911 8.77 5.77Supermarket 584,769 27,821 9,727 111 1,272 1,911 4.10 2.80Walk‐inBank 76,784 72,402 9,727 111 1,272 1,911 0.87 0.57

QualityRestaurants

1,900,314 186,605 9,727 111 1,272 1,911 13.78 9.39

Dance/YogaStudios

121,942 114,982 9,727 111 1,272 1,911 1.39 0.91

ParkingStructure – 2,856,125 9,727 111 1,272 1,911 13.97 8.60TotalGHGEmissions

105 69

a City of Los Angeles, Department of Public Works, Bureau of Sanitation. Indoor and outdoor water demand rated are derived based on the ratio of indoor to outdoor water demand in CalEEMod.

b California Air Pollution Control Officers Association, California Emissions Estimator Model, http://www.caleemod.com/. Accessed

November 2013 March 2014. c Totals may not add up exactly due to rounding in the modeling calculations.




restaurant,andresidentiallanduses,theGHGemissionfactorsforfuelcombustion,andtheGWPvaluesfortheGHGsemitted. AnnualGHGemissions from landscapingequipment inunitsofMTCO2earegenerallycalculated in CalEEMod using the general formula shownpreviously as Equation 6. The CalEEMod tooluses landscaping equipment GHG emission factors from the CARB OFFROAD2011model and the CARBTechnicalMemo:ChangeinPopulationandActivityFactorsforLawnandGardenEquipment(6/13/2003).43TheCalEEModtoolestimatesthatlandscapingequipmentoperatefor250daysperyearintheSouthCoastAirBasin.

The estimated annual emissions from area and stationary sources under the Project are provided inTable16,ProjectAreaandStationarySourceGreenhouseGasEmissions.DetailedemissionscalculationsareprovidedinAppendixB.

Table 16

Project Area and Stationary Source Greenhouse Gas Emissions

GHG Emissions Source Annual GHG Emissions

(MTCO2e/year)

LandscapingEquipment 4.29TotalGHGEmissions 4


(h) Summary of Project GHG Emissions

A summary of the GHG emissions under the Project is provided inTable 17, Summary of Annual GHGEmissionsundertheProject.

43 CaliforniaAirResourcesBoard,OFFROADModelingChangeTechnicalMemo:ChangeinPopulationandActivityFactorsforLawn

andGardenEquipment,(6/13/2003),http://www.arb.ca.gov/msei/2001_residential_lawn_and_garden_changes_in_eqpt_pop_and_act.pdf.AccessedNovember2013.



Table 17

Summary of Annual GHG Emissions under the Project

GHG Emissions Source

Annual GHG Emissions a

(MTCO2e/year)

2015 2016 b 2017 2018 2019 2020 2021 2022 c 2023 c 2024 2025

Construction 1,631 2,346 – – – – – – – – –Electricity 252 3,022 3,022 3,022 1,647 1,647 1,647 1,647 1,647 1,647Electricity

(GreenPower/RECs) (252) (3,022) (3,022) (3,022) (1,647) (1,647) (247) (247) – –NaturalGas 37 446 446 446 446 446 446 446 446 446Mobile 451 5,414 5,344 5,257 5,158 5,071 4,971 4,859 4,772 4,660Waste 35 418 418 418 418 418 418 418 418 418

WaterandWastewater 10 118 118 118 69 69 69 69 69 69AreaandStationary 0.3 4 4 4 4 4 4 4 4 4

Total(withGreenpower/RECs) 1,631 2,879 6,400 6,330 6,243 6,095 6,008 7,308 7,196 7,356 7,244

Construction 1,631 2,346 – – – –Electricity – 266 3,193 2,675 2,675 2,675

Electricity(100%GreenPower/RECs)

– (266) (3,193) (2,675) – –

NaturalGas – 37 446 446 446 446Mobile – 451 5,414 4,613 3,898 3,530Waste – 35 418 418 418 418

WaterandWastewater – 10 124 105 105 105AreaandStationary – <1 4 4 4 4

Total(withGreenpower/RECs) 1,631 2,880 6,406 5,586 7,546 7,178

a Totals may not add up exactly due to rounding in the modeling calculations. b Based on the expected construction schedule, the Project could be operational during the last month of year 2016. Therefore, estimated

operational emissions associated with approximately one month of operational activity are included for year 2016. c The purchase of a minimum of 15 percent of the Project’s annual electricity use in 2022 and 2023 would result in a GHG emissions reduction

of approximately 247 MTCO2e. Source: PCR Services Corporation, 2014.



4.0 COMPARISON OF PROJECT TO BASELINE CONDITION

Table18,EvaluationofNetGHGEmissionsfortheProject,providesasummaryofthedeterminationofnetadditional GHG emissions comparing the existing site GHG emissions and the Project GHG emissionsincluding construction‐related emissions. The GHG emissions trends are also presented graphically inFigure3,GreenhouseGasEmissions–BaselineandFutureProjectYearTrends.

BasedontheseGHGemissionsestimates,theProjectwouldnotresultinnetadditionalcontemporaneousGHGemissionscomparedtothebaselineannualoperationalemissionsatanytimewiththeexceptionofaslightincreaseinGHGemissionsinyear2023iftheProjectdoesnotcontinueitspurchaseofgreenpower,carbonoffsets,and/orRECsbeyondtheminimumof fiveyearsasrequiredunder theLEED®EnergyandAtmosphereCredit.

TheProjectshallcommittoextendingitscontracttopurchaseatleast1015percentofitselectricityfromgreenpower, carbonoffsets, and/orRECs for at least an additional twoyearsbeyond theminimum fiveyearrequirement.Basedontheanticipatedoperationalyearof2017(firstfullcalendaryear),theProjectwouldnotresultinnetcontemporaneousGHGemissionscomparedtotheBaselineCondition,takingintoaccounttheadditionaltwoyearsofgreenpower,carbonoffsets,and/orRECsofatleast1015percentoftheProject’selectricity. Therefore, thisanalysisdemonstrates that theProjectmeets theGHGemissionsrequirements of the “Jobs and Economic Improvement through Environmental Leadership Act” (PublicResourcesCodeSection21178etseq.)andwouldresultinnonetGHGemissions.

4.0 Comparison of Project to Baseline Condition – PRELIMINARY WORKING DRAFT – March 2014


Table 18

Evaluation of Net GHG Emissions for the Project

GHG Emissions Source Annual GHG Emissions a

(MTCO2e/year)

2015 2016 c 2017 d 2018 2019 2020 2021 2022 2023 2024 2025

BaselineAnnualOperationsb 7,372 7,372 7,372 7,372 7,372 7,372 7,372 7,372 7,372 7,372 7,372Project Construction 1,631 2,346 – – – – – – – – –Electricity 252 3,022 3,022 3,022 1,647 1,647 1,647 1,647 1,647 1,647Electricity(GreenPower/RECs) (252) (3,022) (3,022) (3,022) (1,647) (1,647) (247) (247) – –NaturalGas 37 446 446 446 446 446 446 446 446 446Mobile 451 5,414 5,344 5,257 5,158 5,071 4,971 4,859 4,772 4,660Waste 35 418 418 418 418 418 418 418 418 418Water&Wastewater 10 118 118 118 69 69 69 69 69 69AreaandStationary 0.3 4 4 4 4 4 4 4 4 4

Total(withGreenpower/RECs) 1,631 2,879 6,400 6,330 6,243 6,095 6,008 7,308 7,196 7,356 7,244NetChange (5,741) (4,492) (972) (1,042) (1.129) (1,277) (1,364) (64) (176) (16) (128)ExceedsBaseline? No No No No No No No No No No No BaselineAnnualOperationsb 7,407 7,407

7,407 7,407 7,407 7,407

Project Construction 1,631 2,346 – – – –Electricity – 266 3,193 2,675 2,675 2,675Electricity(100%GreenPower/RECs)

– (266) (3,193) (2,675) – –

NaturalGas – 37 446 446 446 446Mobile – 451 5,414 4,613 3,898 3,530Waste – 35 418 418 418 418WaterandWastewater

– 10124 105 105 105

AreaandStationary – <1 4 4 4 4Total(withGreenpower/RECs) 1,631 2,880 6,406 5,586 7,546 7,178NetChange (5,776) (4,528) (1,001) (1,821) 139 (229)NetChangewithGreenpower/RECsExtensionforTwoYears(10%minimum)

(129)e

ExceedsBaseline? No No No No No No

a Totals may not add up exactly due to rounding in the modeling calculations. b As of December 30, 2013, 5,761 square feet of the existing 80,000 square feet is unoccupied due to expired lease agreements or because the

Applicant bought out the lease in order to facilitate the proposed development. The Applicant may sign new lease agreements or extend existing lease agreements at any time for the full 80,000 square feet retail space without the need for discretionary approvals.

c Based on the expected construction schedule, the Project would be operational during the last month of year 2016. Therefore, estimated operational

March 2014 – PRELIMINARY WORKING DRAFT – 4.0 Comparison of Project to Baseline Condition


emissions associated with approximately one month of operational activity are included for year 2016. d Year 2017 is expected to be the first full year of Project operations. e The purchase of a minimum of 10 15 percent of the Project’s annual electricity use in 2022 and 2023 would result in a GHG emissions reduction of

approximately 268 247 MTCO2e.

Source: PCR Services Corporation, 2014.

FIGUREGreenhouse Gas Emissions –

Baseline and Future Project Year Trends3

Source: PCR Services Corpora on, 2014.P C R8150 Sunset Boulevard Mixed-Use Project

Greenhouse Gas Emissions Methodology and Documenta on

0

1,000

2,000

3,000

4,000

5,000

6,000

7,000

8,000

2015 2016 2017 2020 2023 2025

GHG

Emis

sion

s (M

TCO

2e)

Year

Project

Baseline AnnualOpera ons

2015-2016: Project Construc on

2017: Project Opera ons (First full calendar year, 100% greenpower/offsets/RECs)2020: Project Opera ons (100% greenpower/offsets/RECs, 33% RPS, Pavley Phase II -

par al implementa on)2023: Project Opera ons (At least 10% greenpower/offsets/RECs, 33% RPS, Pavley

Phase II - par al implementa on)

2025: Project Opera ons (33% RPS, Pavley Phase II - full implementa on)


8150SunsetBoulevardMixedUseProject GreenhouseGasEmissionsMethodologyandDocumentationPCRServicesCorporation

APPENDIX A BASELINE CONDITION GREENHOUSE GAS EMISSIONS

8150 Sunset Boulevard Mixed Use ProjectDraft EIRAppendix A, Baseline Condition Greenhouse Gas Emissions

Appendix A.1Baseline Condition GHG Emissions – Electricity

8150SU

NSETBOULEVARDMIXED

USE

PROJECT

Greenhouse

Gas

EmissionsMethodology

andDocumentation

Baselin

eConditionElectricalD

eman

dFactors

EndUse

EndUse

FloorStock

AnnualEn

ergyUsage

1PerUnitAnnualEn

ergyUsage

(1000sqft)

(GWh/year)

(MWh/1000sqft/year)

Health

106,471

2,161

20.30

Restaurant

61,623

2,846

46.18

Retail

309,601

4,755

15.36

SmallO

ffice

157,884

2,091

13.24

Wareh

ouse

353,765

1,517

4.29

Notes:

1.

Source:PCRServices

Corporation,2013.

Baselin

eConditionElectricalD

eman

dGreenhouse

Gas

Emissions

LandUse

Units

PerUnitAnnualEn

ergyUsage

CO2Factor1

CH4Factor2

N2OFactor2

AnnualGHGEm

issions

(1000sqft)

(MWh/1000sqft/year)

(pounds/MWh)

(pounds/MWh)

(pounds/MWh)

(MTC

O2e/year)

Gen

eralRetail

14.65

15.36

1,156

0.029

0.0062

118.21

Storage

Facility

27.63

4.29

1,156

0.029

0.0062

62.25

WalkinBankFacility

20.17

13.24

1,156

0.029

0.0062

140.39

Restaurant

2.06

46.18

1,156

0.029

0.0062

49.90

IceCream

Parlor

0.80

46.18

1,156

0.029

0.0062

19.42

FastFoodRestaurantwithDrive

Thru

5.07

46.18

1,156

0.029

0.0062

123.05

FastFoodRestaurantwithoutDrive

Thru

3.72

46.18

1,156

0.029

0.0062

90.28

Den

talO

ffice

2.36

20.30

1,156

0.029

0.0062

25.17

FitnessCen

ter

3.55

20.30

1,156

0.029

0.0062

37.86

TotalG

HGEm

issions

80.00

666.53

Notes:

1.

LosAngelesDep

artm

entofWater

andPower,2012Power

IntegratedResourcePlan,(2012).

2.

CaliforniaAirPollutionControlO

fficersAssociation,CaliforniaEm

issionsEstimatorModel,http://w

ww.caleemod.com/.

AccessedNovember

2013.

Source:PCRServices

Corporation,2014.

CaliforniaEnergy

Commission,CaliforniaCommercialEndUse

Survey

,http://capabilities.itron.com/Ceu

sWeb

/Chart.aspx.

AccessedNovember

2013.Factorsarebased

ontheSouthernCaliforniaEdison(SCE)

sectoras

representative

oftheProject

Site

location.

Appendix A.2Baseline Condition GHG Emissions – Natural Gas

8150SU

NSETBOULEVARDMIXED

USE

PROJECT

Greenhouse

Gas


andDocumentation

Baselin

eConditionNaturalG

asCombustionFactors

EndUse

EndUse

FloorStock

AnnualEn

ergyUsage

1MillionBritish

therm

alPerUnitAnnualEn

ergyUsage

(1000sqft)

(10,000therm

s/year)

units[M

MBtu]perYear

(MMBtu/1000sqft/year)

Health

106,471

7,274

7,274,000

68.32

Restaurant

61,623

15,353

15,353,000

249.14

Retail

309,601

762

762,000

2.46

SmallO

ffice

157,884

1,271

1,271,000

8.05

Wareh

ouse

353,765

869

869,000

2.46

Notes:

1.

Source:PCRServices

Corporation,2013.

Baselin

eConditionNaturalG

asDeman

dGreenhouse

Gas

Emissions

LandUse

Units

PerUnitAnnualEn

ergyUsage

CO2Factor1

CH4Factor1

N2OFactor1

AnnualGHGEm

issions

(1000sqft)

(MMBtu/1000sqft/year)

(pounds/MMBtu)

(pounds/MMBtu)

(pounds/MMBtu)

(MTC

O2e/year)

Gen

eralRetail

14.65

2.46

117.65

0.0023

0.0022

1.94

Storage

Facility

27.63

2.46

117.65

0.0023

0.0022

3.64

WalkinBankFacility

20.17

8.05

117.65

0.0023

0.0022

8.72

Restaurant

2.06

249.14

117.65

0.0023

0.0022

27.50

IceCream

Parlor

0.80

249.14

117.65

0.0023

0.0022

10.70


Thru

5.07

249.14

117.65

0.0023

0.0022

67.82


Thru

3.72

249.14

117.65

0.0023

0.0022

49.76

Den

talO

ffice

2.36

68.32

117.65

0.0023

0.0022

8.66

FitnessCen

ter

3.55

68.32

117.65

0.0023

0.0022

13.02

TotalG

HGEm

issions

80.00

191.75

Notes:

1.

CaliforniaAirPollutionControlO

fficersAssociation,C

aliforniaEm

issionsEstimatorModel,http://w

ww.caleemod.com/.

AccessedNovember

2013.

Source:PCRServices

Corporation,2014.

CaliforniaEnergy

Commission,C

aliforniaCommercialEndUse

Survey

,http://capabilities.itron.com/Ceu

sWeb

/Chart.aspx.

AccessedNovember

2013.Factorsarebased

ontheSouthernCaliforniaEdison(SCE)

sectoras

representative

oftheProjectSite

location.

Appendix A.3Baseline Condition GHG Emissions – On Site Mobile SourceQueuing at existing Fast Food Drive Thru

8150 SUNSET BOULEVARD MIXED USE PROJECT

Draft Environmental Impact Report

Air Quality Operational Emissions

Baseline Condition Estimated Fast Food with Drive Thru On Site Idling Emissions

Existing Land Use

Size

(sf) Daily Trips1

Percent Using

Drive Thru2

Drive Thru

Daily Trips

Idling Minutes

per Drive Thru

Trip3Total Idling

Hours per Day

Total Idling

Hours per

Year

Fast Food with Drive Thru 5,070 2,515 57% 1,434 2 48 17,442

Notes:

1. Hirsch/Green Transportation Consulting, Inc., Traffic Impact Analysis Report, Proposed Mixed Use Development, 8150 Sunset Boulevard,

Hollywood, California, November 2013.

2. The NPD Group, Drive Thru Windows Still Put the Fast in Fast Food Restaurants, Reports NPD, May 2012,

https://www.npd.com/wps/portal/npd/us/news/press releases/pr_120530a/. Accessed December 2013. A value of 57 percent

was used corresponding to the drive thru percentage for hamburger fast food restaurants.

3. QSR Magazine, 2012 QSR Drive Thru Study, http://www.qsrmagazine.com/print/50631. Accessed December 2013. Based on the study,

an average wait time of 129.75 seconds was recorded for Wendy's, which was faster than other hamburger fast food restaurants.

In order not to overestimate emissions from the existing fast food restaurant and thus not overestimate the amount of existing

emissions credits, a value of 120 second (or 2 minutes) was used in this assessment.

Air Basin VMT Emission Rates (grams per mile)

(miles per day) CO2 CH4 N2O CO2e

2013 LDA Gas 474,344.67 1,013.04 – 0.0092 –

2013 LDA Diesel 1,518.49 399.09 – 0.0110 –

2013 LDT1 Gas 54,821.31 1,185.50 – 0.0273 –

2013 LDT1 Diesel 71.68 385.81 – 0.0115 –

2013 LDT2 Gas 165,153.32 1,420.34 – 0.0187 –

2013 LDT2 Diesel 73.55 391.63 – 0.0113 –

Weighted Average 1,121.81 0.0570 0.0129 1,127.00

Emission Rates (grams per hour)

Weighted Average 5,609.03 0.2850 0.0644 5,634.99

Emission Rates (metric tons per hour)

Weighted Average 5.61E 03 2.85E 07 6.44E 08 5.63E 03

Note:

1. California Air Resources Board, EMFAC2011, http://www.arb.ca.gov/msei/modeling.htm. Accessed December 2013. Emission factors

are based on running exhaust emissions from EMFAC2011 for Years 2013, LDA, LDT1, and LDT2 at 5 miles per hour per CARB guidance.

Existing Land Use Emissions (metric tons per year)

CO2 CH4 N2O CO2e

Fast Food with Drive Thru 97.83 0.0050 0.0011 98.28


Emission Factors

(grams/mile @ 5 MPH)1

EMFAC2011 Emission RatesRegion Type: Air BasinRegion: South CoastCalendar Year: 2013Season: AnnualVehicle Classification: EMFAC2011 CategoriesRegion CalYr Season Veh_Class Fuel MdlYr Speed VMT ROG_RUNEX TOG_RUNEX CO_RUNEX NOX_RUNEX CO2_RUNEX CO2_RUNEX(Pavley I+LCFS) PM10_RUNEX PM2_5_RUNEX SOX_RUNEX

(miles/hr) (miles/day) (gms/mile) (gms/mile) (gms/mile) (gms/mile) (gms/mile) (gms/mile) (gms/mile) (gms/mile) (gms/mile)South Coast 2013 Annual LDA GAS Aggregated 5 474344.67 0.237076095 0.333857713 3.137562711 0.220739842 1101.868558 1013.041646 0.012494462 0.011427214 0.0036094South Coast 2013 Annual LDA DSL Aggregated 5 1518.493 0.169760222 0.193260717 1.091999023 0.880313341 452.3122042 399.0904211 0.128349403 0.118081457 0.0031967South Coast 2013 Annual LDT1 GAS Aggregated 5 54821.314 0.595923234 0.777769465 8.343011389 0.657325778 1268.639344 1185.498091 0.028630856 0.026224635 0.0041729South Coast 2013 Annual LDT1 DSL Aggregated 5 71.676197 0.297942256 0.339187445 1.772520941 1.223692682 431.7922214 385.8110745 0.251489648 0.231370475 0.0033402South Coast 2013 Annual LDT2 GAS Aggregated 5 165153.32 0.293968262 0.426849124 4.132392612 0.45042172 1503.999815 1420.341119 0.013225691 0.012137507 0.0049172South Coast 2013 Annual LDT2 DSL Aggregated 5 73.549358 0.225335426 0.256529401 1.425179668 1.196024554 432.8498527 391.6300667 0.18435689 0.169608344 0.00328

Title : LDA; LDT CH4

Version : Emfac2011 LDV V2.50.58.094 Sp: Trip Assign Santa Clara County

Run Date : 2013/12/06 12:22:08

Scen Year: 2013 All model years in the range 1969 to 2013 selected

Season : Annual

Area : South Coast

*****************************************************************************************

Year: 2013 Model Years 1969 to 2013 Inclusive Annual

Emfac2011 LDV Emission Factors: V2.50.58.094 Sp: Trip Assign Santa Clara County

South Coast Basin Average Basin Average

Table 1: Running Exhaust Emissions (grams/mile; grams/idle hour)

Pollutant Name: Methane Temperature: 60F Relative Humidity: 30%

Speed LDA LDA LDA LDA LDT1 LDT1 LDT1 LDT1 LDT2 LDT2 LDT2 LDT2 ALL ALL ALL ALL

MPH NCAT CAT DSL ALL NCAT CAT DSL ALL NCAT CAT DSL ALL NCAT CAT DSL ALL

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

5 0.776 0.049 0.008 0.052 0.805 0.073 0.014 0.08 0.795 0.062 0.01 0.065 0.784 0.054 0.008 0.057

EMFAC2011 Emissions InventoryRegion Type: Air BasinRegion: South CoastCalendar Year: 2013Season: AnnualVehicle Classification: EMFAC2011 CategoriesRegion CalYr Season Veh_Class Fuel MdlYr Speed Population VMT Trips Fuel_GAS Fuel_DSL Fuel_DSL Fuel_DSL Fuel_DSL

(miles/hr) (vehicles) (miles/day) (trips/day) (1000 gallon(1000 gallons/day) (gallons/day(gallons/mile(gallons/veh hour)South Coast 2013 Annual LDA DSL Aggregated Aggregated 19553.64 604666.77 112931.86 0 20.087031 20087.031 0.03322 0.0428033South Coast 2013 Annual LDT1 DSL Aggregated Aggregated 968.62073 29350.192 5088.5683 0 1.0187834 1018.7834 0.0347113 0.0438245South Coast 2013 Annual LDT2 DSL Aggregated Aggregated 886.19568 30108.384 4994.3971 0 1.0262687 1026.2687 0.0340858 0.0482525

Appendix A.4Baseline Condition GHG Emissions – CalEEMod Outputs forMobile, Area, Waste, andWater

Cal

EE

Mod

Ver

sion

: Cal

EE

Mod

.201

3.2.

2P

age

1 of

1D

ate:

11/

25/2

013

5:55

PM

8150

Su

nse

t B

lvd

Mix

ed U

se P

roje

ct -

BA

SE

LIN

E (

Mo

bile

, Are

a, W

aste

, Wat

er)

So

uth

Co

ast

Air

Bas

in, A

nn

ual

1.0

Pro

ject

Ch

arac

teri

stic

s

1.1

Lan

d U

sag

e

Land

Use

sS

ize

Met

ricLo

t Acr

eage

Flo

or S

urfa

ce A

rea

Pop

ulat

ion

Str

ip M

all

14.6

510

00sq

ft0.

3414

,647

.00

0

Unr

efrig

erat

ed W

areh

ouse

-No

Rai

l27

.63

1000

sqft

0.63

27,6

25.0

00

Gen

eral

Offi

ce B

uild

ing

20.1

710

00sq

ft0.

4620

,172

.00

0

Fas

t Foo

d R

esta

uran

t w/o

Driv

e T

hru

6.58

1000

sqft

0.15

6,57

6.00

0

Fas

t Foo

d R

esta

uran

t with

Driv

e T

hru

5.07

1000

sqft

0.12

5,07

0.00

0

Hea

lth C

lub

3.55

1000

sqft

0.08

3,55

0.00

0

Med

ical

Offi

ce B

uild

ing

2.36

1000

sqft

0.05

2,36

0.00

0

Par

king

Lot

58.1

110

00sq

ft0.

7358

,109

.00

0

1.2

Oth

er P

roje

ct C

har

acte

rist

ics

Urb

aniz

atio

nU

rban

Win

d S

pee

d (

m/s

)2.

2P

reci

pit

atio

n F

req

(D

ays)

31

Clim

ate

Zo

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CO

2 In

ten

sity

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ty

(lb

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ten

sity

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1.3

Use

r E

nte

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Co

mm

ents

& N

on

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Dat

a

Pro

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tics

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nsity

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tor:

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Dep

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f Wat

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ower

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2 P

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Use

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tora

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acili

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ear T

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Appendix A.5Baseline Condition GHG Emissions – CalEEMod Inputs for WasteandWater

8150SU

NSETBOULEVARDMIXED

USE

PROJECT

Greenhouse

Gas


andDocumentation

Baselin

eConditionSolid

Waste

DisposalR

ates

LandUse

Units

Waste

DisposalR

ate1

Waste

DiversionRate1

Waste

DisposalR

ateafterDiversion

(1000sqft)

(tons/1000sqft/year)

(%)

(tons/year)

ExistingLandUses

80.000

4.28

60%

136.86

Notes:

1.

Refer

toSection4.K.3,Solid

Waste,ofthe8150SunsetBoulevard

Mixed

Use

ProjectDraftEIR.Based

onannualwaste

generationof342.14tonsper

year.

Source:PCRServices

Corporation,2014.

Baselin

eConditionSolid

Waste

Greenhouse

Gas

Emissions

Refer

toCalEEM

odoutputfiles.

8150SU

NSETBOULEVARDMIXED

USE

PROJECT

Greenhouse

Gas


andDocumentation

Baselin

eConditionWaterDeman

dRates

LandUse

Units

BasedonCalEEMod

IndoorWaterDeman

dRate1

OutdoorWaterDeman

dRate1

IndoorWaterDeman

dOutdoorWaterDeman

d

(1000sqft)

LandUse

Type

(gal/1000sqft/year)

(gal/1000sqft/year)

(%)

(%)

Gen

eralRetail

14.647

Stripmall

74,073

45,399

62%

38%

Storage

Facility

27.625

Unrefrigerated

wareh

ouse

231,250

100%

0%

WalkinBankFacility

20.172

Bank/Gen

eralofficebuilding

177,734

108,934

62%

38%

Restaurant

2.056

Fastfoodrestaurantw/o

drive

through

303,534

19,374

94%

6%

IceCream

Parlor

0.800


drive

through

303,534

19,374

94%

6%


Thru

5.070

Fastfoodrestaurantw/drive

through

303,534

19,374

94%

6%


Thru

3.720


drive

through

303,534

19,374

94%

6%

Den

talO

ffice

2.360

Med

icalofficebuilding

125,481

23,901

84%

16%

FitnessCen

ter

3.550

Healthclub

59,143

36,249

62%

38%

Parking

58.109

ParkingLot

0%

100%

LandUse

Units

TotalW

aterDeman

dRate2

IndoorWaterDeman

d3

OutdoorWaterDeman

d3

TotalW

aterDeman

d

(1000sqft)

(gal/1000sqft/year)

(gal/year)

(gal/year)

(gal/year)

Gen

eralRetail

14.647

37,380

339,452

208,048

547,500

Storage

Facility

27.625

9,355

258,420

258,420

WalkinBankFacility

20.172

37,383

467,535

286,555

754,090

Restaurant

2.056

IceCream

Parlor

0.800


Thru

5.070


Thru

3.720

Den

talO

ffice

2.360

116,769

231,483

44,092

275,575

FitnessCen

ter

3.550

37,425

82,373

50,487

132,860

Parking

58.109

9,340

542,755

542,755

TotalW

aterDeman

d2,913,609

1,229,871

4,143,480

Notes:

1.

2.

Refer

toSection4.K.1,W

ater

Supply,ofthe8150SunsetBoulevard

Mixed

Use

ProjectDraftEIR.Based

ondailywater

dem

andratesmultipledby365daysper

year.

3.

Indoorandoutdoorwater

dem

andratesarederived

based

ontheratioofindoorto

outdoorwater

dem

andinCalEEMod.

Source:PCRServices

Corporation,2014.

Baselin

eConditionWateran

dWastewaterGreenhouse

Gas

Emissions

Refer

toCalEEM

odoutputfiles.

Gleick,P.H.;Haasz,D

.;Hen

gesJeck,C.;Srinivasan,V

.;Cushing,K.K.;Mann,A

.2003.W

aste

Not,WantNot:ThePotentialforUrban

Water

ConservationinCalifornia.Published

bythePacificInstitute

forStudiesinDevelopmen

t,Environmen

t,andSecurity.Fullreportavailableonlineat:

http://w

ww.pacinst.org/rep

orts/urban_u

sage/w

aste_n

ot_want_not_full_report.pdf.Appen

dices

availableonlineat:h

ttp://w

ww.pacinst.org/rep

orts/urban_u

sage/appen

dices.htm

.http://w

ww.caleemod.com/.

AccessedNovember

2013.

DefaultRates

Site

SpecificRates

PercentofTo

tal

140,158

1,534,346

97,934

1,632,280


8150SunsetBoulevardMixedUseProject GreenhouseGasEmissionsMethodologyandDocumentationPCRServicesCorporation

APPENDIX B PROJECT GREENHOUSE GAS EMISSIONS

8150 Sunset Boulevard Mixed Use ProjectDraft EIRAppendix B, Project Greenhouse Gas Emissions

Appendix B.1GHG Emissions Summary

8150 SUNSET BOULEVARD MIXED USE PROJECTDraft EIRGreenhouse Gases - Operational EmissionsGreenhouse Gas Emissions Methodology and Documentation

Summary of Estimated Unmitigated Annual GHG EmissionsSource Baseline Project GHG Emissions a

GHG Emissions a, b 2015 2016 c 2017 d 2020 2023 2025

Baseline ConditionArea 0.0 Energy - Natural Gas 192 Energy - Electricity 667 Water 31 Waste 62 Mobile - Traveling 6,358 Mobile - On-site Drive-Thru Idling 98

Subtotal 7,407 7,407 7,407 7,407 7,407 7,407 7,407

ProjectConstruction 1,631 2,346 - - - - Area 0.3 4 4 4 4 Energy - Natural Gas 37 446 446 446 446 Energy - Electricity 266 3,193 2,675 2,675 2,675 Energy - 100% Green Power/RECs (266) (3,193) (2,675) - - Water 10 124 105 105 105 Waste 35 418 418 418 418 Mobile 451 5,414 4,613 3,898 3,530

Subtotal (without 100 % Green Power/RECs) 1,631 3,146 9,599 8,261 7,546 7,178 Subtotal (with 100% Green Power/RECs) 1,631 2,880 6,406 5,586 7,546 7,178

Net Change from Baseline Condition (5,776) (4,528) (1,001) (1,822) 139 (229) (268)

Net Change with Green Power/Offsets/RECs Extension (5,776) (4,528) (1,001) (1,822) (129) (229) Exceeds Baseline? No No No No No No

Notes:

a Totals may not add up exactly due to rounding in the modeling calculations.

b As of December 30, 2013, 5,761 square feet of the existing 80,000 square feet is unoccupied due to expired lease agreements or because the Applicant

bought out the lease in order to facilitate the proposed development. The Applicant may sign new lease agreements or extend existing lease agreements

at any time for the full 80,000 square feet retail space without the need for discretionary approvals.

c Based on the expected construction schedule, the Project would be operational during the last month of year 2016. Therefore, estimated operational

emissions associated with approximately one month of operational activity are included for year 2016.

d Year 2017 is expected to be the first full year of Project operations.

e The purchase of a minimum of 10 percent of the Project’s annual electricity use in 2023 would result in a GHG emissions reduction of approximately

268 MTCO2e.


Green Power/Offset/RECs Extention for 2 Years (10% minimum) e

Appendix B.2Project GHG Emissions – CalEEMod Inputs and Outputs forConstruction

8150SunsetBoulevard

Mixed

Use

Project

ConstructionEm

issions

ConstructionSched

uleandCaliforniaEm

issionsEstimatorModel(CalEEM

od)Inputs

ModelRunPhase

StartDate

EndDate

No.W

ork

Days

Dem

oTo

ns

Dem

oTruck

TotalO

ne

Way

Trips

ExportCY

ImportCY

HaulTruck

TotalO

ne

Way

Trips

Ven

dorOne

Way

Trips/Day

Worker

One

Way

Trips/Day

Demolition

Demolition

1/5/2015

3/10/2015

47

3,250

321

013

Grading/Excavation

Grading

3/11/2015

7/15/2015

91

58,500

11,700

015

BuildingConstruction


5/21/2015

12/2/2016

402

95

346

Sitework/Closeout


3/11/2016

12/2/2016

191

95

346

ArchitecturalCoating

ArchitecturalCoating

4/29/2016

10/19/2016

124

069

ConstructionActivityPhase

Source:PCRServiceCorporation,(2013).Constructionschedule,equipment,andmodelinputsareadaptedforuse

intheCaliforniaEm

issionsEstm

atorModel(CalEEMod)basedondataprovidedbytheProjectManagementConsultant(AMAManagement[An

AnthonyMasonAssociates,Inc.Company]).

8150 Sunset Boulevard Mixed Use Project

Construction Emissions

Construction Equipment and California Emissions Estimator Model (CalEEMod) Inputs

Heavy Duty Equipment No. of HD Equip

Hours of

Operation/Day

Hours of

Operation/Week

Demolition Concrete/Industrial Saws 1 8 40

Excavators 1 8 40

Other Construction Equipment 2 8 40

Tractors/Loaders/Backhoes 1 8 40

Grading/Excavation Bore/Drill Rigs 1 8 40

Excavators 1 8 40

Rubber Tired Dozers 1 8 40

Scrapers 1 8 40

Tractors/Loaders/Backhoes 2 8 40

Building Construction Aerial Lifts 2 8 40

Cranes 2 8 40

Generator Sets 1 8 40

Off Highway Trucks 1 8 40

Other Construction Equipment 4 8 40

Pumps 1 8 40

Welders 1 8 40

Sitework/Closeout Off Highway Trucks 2 8 40

Paving Equipment 1 8 40

Pumps 1 8 40

Architectural Coating Air Compressors 2 8 40

Construction Activity Phase

Source: PCR Service Corporation, (2013). Construction schedule, equipment, and model inputs are adapted for use in the California Emissions Estmator Model (CalEEMod) based on data

provided by the Project Management Consultant (AMA Management [An Anthony Mason Associates, Inc. Company]).

1.3

Use

r E

nte

red

Co

mm

ents

& N

on

-Def

ault

Dat

a

Pro

ject

Cha

ract

eris

tics

- C

O2

Inte

nsity

Fac

tor:

Los

Ang

eles

Dep

artm

ent o

f Wat

er a

nd P

ower

, 201

2 P

ower

Inte

grat

ed R

esou

rce

Pla

n, (

2012

).

Land

Use

- U

nit S

izes

as

liste

d in

Sec

tion

2, P

roje

ct D

escr

iptio

n, o

f the

815

0 S

unse

t Bou

leva

rd M

ixed

Use

Pro

ject

Dra

ft E

IR; P

opu

latio

n 52

8 as

list

ed in

S

ectio

n 4.

H, P

opul

atio

n an

d H

ousi

ng, o

f the

Dra

ft E

IR.

Con

stru

ctio

n P

hase

- E

stim

ated

Con

stru

ctio

n S

tart

/End

: Jan

201

5/D

ec 2

016.

Off-

road

Equ

ipm

ent -

Air

com

pres

sors

.

CO

2 In

ten

sity

(l

b/M

Wh

r)11

56C

H4

Inte

nsi

ty

(lb

/MW

hr)

0.02

9N

2O In

ten

sity

(l

b/M

Wh

r)0.

00631

Clim

ate

Zo

ne

11O

per

atio

nal

Yea

r20

14

Uti

lity

Co

mp

any

Los

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eles

Dep

artm

ent o

f Wat

er &

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er

1.2

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er P

roje

ct C

har

acte

rist

ics

Urb

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nU

rban

Win

d S

pee

d (

m/s

)2.

2P

reci

pit

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n F

req

(D

ays)

Sup

erm

arke

t24

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1000

sqft

0.50

24,8

11.0

00

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ip M

all

51.1

510

00sq

ft0.

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.00

0

Apa

rtm

ents

Hig

h R

ise

249.

00D

wel

ling

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t1.

0022

2,56

4.00

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lity

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taur

ant

22.1

910

00sq

ft0.

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0

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lth C

lub

8.10

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sqft

0.19

8,09

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0

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lose

d P

arki

ng w

ith E

leva

tor

305.

6510

00sq

ft0.

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5,65

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ulat

ion

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ce B

uild

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5.09

1000

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t Acr

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rea

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sion

: Cal

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3.2.

2P

age

1 of

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ate:

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0:00

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8150

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t B

lvd

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on

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ctio

n

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uth

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ast

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ject

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quar

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ater

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8.81

5217

8.81

521.

3000

e-00

30.

0000

178.

8424

0.05

580.

0130

0.06

880.

0159

0.01

190.

0279

Ven

dor

0.08

050.

8191

1.05

591.

9700

e-00

3

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Hau

ling

0.00

000.

0000

0.00

000.

0000

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Un

mit

igat

ed C

on

stru

ctio

n O

ff-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0032

6.91

3532

6.91

350.

0876

0.00

0032

8.75

210.

1291

0.12

910.

1215

0.12

15T

ota

l0.

2731

2.88

221.

5770

3.52

00e-

003

0.00

0032

6.91

3532

6.91

350.

0876

0.00

0032

8.75

210.

1291

0.12

910.

1215

0.12

15O

ff-R

oad

0.27

312.

8822

1.57

703.

5200

e-00

3

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

3.5

Sit

ewo

rk/C

lose

ou

t -

2016

Un

mit

igat

ed C

on

stru

ctio

n O

n-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0065

4.17

7165

4.17

710.

0247

0.00

0065

4.69

620.

5279

0.02

020.

5481

0.14

160.

0186

0.16

02T

ota

l0.

2691

1.27

973.

8906

8.10

00e-

003

0.00

0042

8.55

1742

8.55

170.

0231

0.00

0042

9.03

640.

4574

3.89

00e-

003

0.46

130.

1215

3.58

00e-

003

0.12

51W

orke

r0.

1676

0.24

622.

5583

5.62

00e-

003

0.00

0022

5.62

5422

5.62

541.

6400

e-00

30.

0000

225.

6598

0.07

040.

0164

0.08

680.

0201

0.01

500.

0351

Ven

dor

0.10

161.

0336

1.33

232.

4800

e-00

3

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Hau

ling

0.00

000.

0000

0.00

000.

0000

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Mit

igat

ed C

on

stru

ctio

n O

ff-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0042

.213

842

.213

84.

9800

e-00

30.

0000

42.3

183

0.03

250.

0325

0.03

250.

0325

To

tal

2.32

740.

3922

0.31

154.

9000

e-00

4

0.00

0042

.213

842

.213

84.

9800

e-00

30.

0000

42.3

183

0.03

250.

0325

0.03

250.

0325

Off-

Roa

d0.

0609

0.39

220.

3115

4.90

00e-

004

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Arc

hit.

Coa

ting

2.26

64

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

3.6

Arc

hit

ectu

ral C

oat

ing

- 2

016

Un

mit

igat

ed C

on

stru

ctio

n O

n-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0051

8.45

5751

8.45

570.

0196

0.00

0051

8.86

710.

4184

0.01

610.

4344

0.11

220.

0148

0.12

70T

ota

l0.

2133

1.01

423.

0834

6.43

00e-

003

0.00

0033

9.64

0633

9.64

060.

0183

0.00

0034

0.02

470.

3625

3.09

00e-

003

0.36

560.

0963

2.84

00e-

003

0.09

91W

orke

r0.

1328

0.19

512.

0275

4.46

00e-

003

0.00

0017

8.81

5217

8.81

521.

3000

e-00

30.

0000

178.

8424

0.05

580.

0130

0.06

880.

0159

0.01

190.

0279

Ven

dor

0.08

050.

8191

1.05

591.

9700

e-00

3

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Hau

ling

0.00

000.

0000

0.00

000.

0000

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Mit

igat

ed C

on

stru

ctio

n O

ff-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0032

6.91

3132

6.91

310.

0876

0.00

0032

8.75

170.

1291

0.12

910.

1215

0.12

15T

ota

l0.

2731

2.88

221.

5770

3.52

00e-

003

0.00

0032

6.91

3132

6.91

310.

0876

0.00

0032

8.75

170.

1291

0.12

910.

1215

0.12

15O

ff-R

oad

0.27

312.

8822

1.57

703.

5200

e-00

3

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Mit

igat

ed C

on

stru

ctio

n O

n-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0043

.972

543

.972

52.

3700

e-00

30.

0000

44.0

222

0.04

694.

0000

e-00

40.

0473

0.01

253.

7000

e-00

40.

0128

To

tal

0.01

720.

0253

0.26

255.

8000

e-00

4

0.00

0043

.972

543

.972

52.

3700

e-00

30.

0000

44.0

222

0.04

694.

0000

e-00

40.

0473

0.01

253.

7000

e-00

40.

0128

Wor

ker

0.01

720.

0253

0.26

255.

8000

e-00

4

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Ven

dor

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Hau

ling

0.00

000.

0000

0.00

000.

0000

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Mit

igat

ed C

on

stru

ctio

n O

ff-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0042

.213

842

.213

84.

9800

e-00

30.

0000

42.3

183

0.03

250.

0325

0.03

250.

0325

To

tal

2.32

740.

3922

0.31

154.

9000

e-00

4

0.00

0042

.213

842

.213

84.

9800

e-00

30.

0000

42.3

183

0.03

250.

0325

0.03

250.

0325

Off-

Roa

d0.

0609

0.39

220.

3115

4.90

00e-

004

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Arc

hit.

Coa

ting

2.26

64

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Mit

igat

ed C

on

stru

ctio

n O

n-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

0.00

0043

.972

543

.972

52.

3700

e-00

30.

0000

44.0

222

0.04

694.

0000

e-00

40.

0473

0.01

253.

7000

e-00

40.

0128

To

tal

0.01

720.

0253

0.26

255.

8000

e-00

4

0.00

0043

.972

543

.972

52.

3700

e-00

30.

0000

44.0

222

0.04

694.

0000

e-00

40.

0473

0.01

253.

7000

e-00

40.

0128

Wor

ker

0.01

720.

0253

0.26

255.

8000

e-00

4

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Ven

dor

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

0.00

000.

0000

Hau

ling

0.00

000.

0000

0.00

000.

0000

Tot

al C

O2

CH

4N

2OC

O2e

Cat

egor

yto

ns/y

rM

T/y

r

PM

10T

otal

Fug

itive

PM

2.5

Exh

aust

PM

2.5

PM

2.5

Tot

alB

io-

CO

2N

Bio

- C

O2

Un

mit

igat

ed C

on

stru

ctio

n O

ff-S

ite

RO

GN

Ox

CO

SO

2F

ugiti

ve

PM

10E

xhau

stP

M10

Appendix B.3Project GHG Emissions – CalEEMod Outputs for Electricity,Natural Gas, Mobile, Area, Waste, andWater (First Full InitialOperational Year)

Cal

EE

Mod

Ver

sion

: Cal

EE

Mod

.201

3.2.

2P

age

1 of

1D

ate:

1/8

/201

4 11

:33

AM

8150

Su

nse

t B

lvd

Mix

ed U

se P

roje

ct -

PR

OJE

CT

So

uth

Co

ast

Air

Bas

in, A

nn

ual

1.0

Pro

ject

Ch

arac

teri

stic

s

1.1

Lan

d U

sag

e

Land

Use

sS

ize

Met

ricLo

t Acr

eage

Flo

or S

urfa

ce A

rea

Pop

ulat

ion

Gen

eral

Offi

ce B

uild

ing

5.09

1000

sqft

0.12

5,09

4.00

0

Enc

lose

d P

arki

ng w

ith E

leva

tor

305.

6510

00sq

ft0.

0030

5,65

2.00

0

Hea

lth C

lub

8.10

1000

sqft

0.19

8,09

5.00

0

Qua

lity

Res

taur

ant

22.1

910

00sq

ft0.

2522

,189

.00

0

Apa

rtm

ents

Hig

h R

ise

249.

00D

wel

ling

Uni

t1.

0019

1,32

4.00

528

Str

ip M

all

51.1

510

00sq

ft0.

5051

,150

.00

0

Sup

erm

arke

t24

.81

1000

sqft

0.50

24,8

11.0

00

Use

r D

efin

ed R

ecre

atio

nal

49.8

4U

ser

Def

ined

Uni

t0.

0049

,840

.00

0

1.2

Oth

er P

roje

ct C

har

acte

rist

ics

Urb

aniz

atio

nU

rban

Win

d S

pee

d (

m/s

)2.

2P

reci

pit

atio

n F

req

(D

ays)

31

Clim

ate

Zo

ne

11O

per

atio

nal

Yea

r20

17

Uti

lity

Co

mp

any

Los

Ang

eles

Dep

artm

ent o

f Wat

er &

Pow

er

CO

2 In

ten

sity

(l

b/M

Wh

r)11

56C

H4

Inte

nsi

ty

(lb

/MW

hr)

0.02

9N

2O In

ten

sity

(l

b/M

Wh

r)0.

006

1.3

Use

r E

nte

red

Co

mm

ents

& N

on

-Def

ault

Dat

a

Pro

ject

Cha

ract

eris

tics

- C

O2

Inte

nsity

Fac

tor:

Los

Ang

eles

Dep

artm

ent o

f Wat

er a

nd P

ower

, 201

2 P

ower

Inte

grat

ed R

esou

rce

Pla

n, (

2012

).

Land

Use

- U

nit S

izes

(re

fer

to S

ectio

n 2,

Pro

ject

Des

crip

tion,

of t

he 8

150

Sun

set B

lvd

Mix

ed-U

se P

roje

ct D

EIR

); P

opul

atio

n: 5

28

(ref

er to

Sec

tion

4.H

, P

opul

atio

n/H

ousi

ng, o

f the

Dra

ft E

IR);

Use

r D

efin

ed R

esid

entia

l=R

esid

entia

l Am

eniti

es/R

oof D

ecks

.V

ehic

le T

rips

- R

efer

to "

Trip

Gen

erat

ion

Rat

e" w

orks

heet

pro

vide

d in

this

App

endi

x.

Woo

dsto

ves

- N

o re

side

ntia

l woo

d-st

oves

; No

resi

dent

ial h

eart

hs.

Ene

rgy

Use

- C

alE

EM

od d

efau

lt en

ergy

dem

and

rate

s. U

ser

Def

ined

Rec

reat

iona

l=R

esid

entia

l Am

eniti

es/R

oof D

eck

(fac

tors

are

from

Hea

lth C

lub/

Rac

quet

C

lub)

.W

ater

And

Was

tew

ater

- R

efer

to "

Pro

ject

Wat

er D

eman

d R

ates

" w

orks

heet

pro

vide

d in

this

App

endi

x.

Sol

id W

aste

- R

efer

to "

Pro

ject

Sol

id W

aste

Dis

posa

l Rat

es"

wor

kshe

et p

rovi

ded

in th

is A

ppen

dix.

Sol

id w

aste

rat

e is

incl

usiv

e o

f 60%

div

ersi

on.

Ene

rgy

Miti

gatio

n -

LEE

D v

4 C

redi

ts: E

Ac2

(ex

ceed

Titl

e 24

by

10%

); E

Ac5

(1%

ren

ewab

le e

nerg

y ge

nera

tion)

(re

fer

to "

Pre

limin

ary

LEE

D S

core

card

" pr

ovid

ed in

this

App

endi

x); E

nerg

y E

ffici

ent A

pplia

nces

.W

ater

Miti

gatio

n -

LEE

D v

4 C

redi

ts: W

Ec2

(re

duce

indo

or w

ater

dem

and

by 3

5%)

(ref

er to

"P

relim

inar

y LE

ED

Sco

reca

rd"

prov

ided

in th

is A

ppen

dix)

.

Tab

le N

ame

Col

umn

Nam

eD

efau

lt V

alue

New

Val

ue

tblE

nerg

yUse

Ligh

tingE

lect

0.00

3.55

tblE

nerg

yUse

NT

24E

0.00

5.75

tblE

nerg

yUse

NT

24N

G0.

004.

45

tblE

nerg

yUse

T24

E0.

002.

75

tblE

nerg

yUse

T24

NG

0.00

14.3

6

tblF

irepl

aces

Fire

plac

eDay

Yea

r25

.00

0.00

tblF

irepl

aces

Fire

plac

eHou

rDay

3.00

0.00

tblF

irepl

aces

Fire

plac

eWoo

dMas

s1,

019.

200.

00

tblF

irepl

aces

Num

berG

as21

1.65

0.00

tblF

irepl

aces

Num

berN

oFire

plac

e24

.90

0.00

tblF

irepl

aces

Num

berW

ood

12.4

50.

00

tblL

andU

seLa

ndU

seS

quar

eFee

t5,

090.

005,

094.

00

tblL

andU

seLa

ndU

seS

quar

eFee

t30

5,65

0.00

305,

652.

00

tblL

andU

seLa

ndU

seS

quar

eFee

t8,

100.

008,

095.

00

tblL

andU

seLa

ndU

seS

quar

eFee

t22

,190

.00

22,1

89.0

0

tblL

andU

seLa

ndU

seS

quar

eFee

t24

9,00

0.00

191,

324.

00

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Documents

CALIFORNIA AIR RESOURCES BOARD Re ......8150 Sunset Boulevard Mixed‐Use Project Los Angeles, CA 90046 January March 2014 Prepared for: AG‐SCH 8150 SUNSET BOULEVARD OWNER, L.P