Section 2.6 Noise - San Diego County, California · 2019-10-22 · Draft Final Environmental Impact...

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  Draft Final Environmental Impact Report Agriculture Promotion Project 2.61 February 2017 ICF 54.15  Section 2.6 Noise This section describes the general noise conditions in the County and pertinent regulations that govern noise, and discusses the potential for impacts on noise as a result of project implementation. 2.6.1 Existing Conditions This section discusses the characteristics of noise and vibration and how they are evaluated, and describes the existing ambient noise environment, including the sources of noise, in the County in relation to noise‐sensitive land uses. Ambient noise data and baseline information reviewed for this section include the Noise Technical Report for the County of San Diego General Plan Update (County of San Diego 2009c), General Plan Update (County of San Diego 2011a), County of San Diego General Plan, Noise Element Background Report (County of San Diego 2011a), and Guidelines for Determining Significance: Noise (County of San Diego 2009d). 2.6.1.1 Ambient Noise Setting The County is characterized as a primarily rural environment with low‐density development that contributes to its perceived quality of life and its peace and tranquility. However, several higher‐ density communities, including the Valle de Oro Community Planning Area (CPA), Spring Valley CPA, and Sweetwater CPA, also exist, which have a louder ambient noise environment. Major sources of noise include transportation and non‐transportation related activities. Non‐transportation‐related noise generators are commonly called stationary, fixed, area, or point sources of noise. Industrial processing; mechanical equipment; pump stations; and heating, ventilating, and air conditioning (HVAC) equipment are examples of fixed‐location, non‐transportation noise sources within the County. Some non‐transportation sources are not stationary but are typically assessed as point or area sources due to the limited area in which they operate, such as truck deliveries, agricultural field machinery, and mining equipment. 2.6.1.2 Characteristics of Noise and Vibration Noise is typically defined as unwanted sound. Sounds are perceived based on their loudness (i.e., volume or sound pressure level) or pitch (i.e., tonal or frequency content). The standard unit of measure for sound pressure levels is the decibel (dB). The standard unit used to describe the tonal or frequency content is hertz (Hz). Typical frequency ranges are 20–20,000 Hz for audible noise, 100–3,000 Hz for normal speech, 20–200 Hz for low frequency sound, and less than 20 Hz for infrasound. Table 2.6‐1 shows the sound pressure level, in decibels, of the corresponding frequency of infrasound and low frequency sound necessary for the sound to be heard by the average person. Customarily, the young, non‐pathological ear can perceive sounds ranging from 20–20,000 Hz. Infrasound, at certain frequencies and at high levels, can be audible to some people. To account for the pitch of sounds and the corresponding sensitivity of human hearing, the raw sound pressure level is adjusted with an A‐weighting scheme based on frequency that is stated in units of decibels (dBA). Table 2.6‐2 depicts typical A‐weighted sound levels for various noise sources. A‐weighting is acceptable if there is largely middle and high frequency noise present, but if the noise is unusually high at low frequencies, or contains prominent low frequency tones, the A‐

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Section 2.6 Noise 

ThissectiondescribesthegeneralnoiseconditionsintheCountyandpertinentregulationsthatgovernnoise,anddiscussesthepotentialforimpactsonnoiseasaresultofprojectimplementation.

2.6.1 Existing Conditions 

Thissectiondiscussesthecharacteristicsofnoiseandvibrationandhowtheyareevaluated,anddescribestheexistingambientnoiseenvironment,includingthesourcesofnoise,intheCountyinrelationtonoise‐sensitivelanduses.AmbientnoisedataandbaselineinformationreviewedforthissectionincludetheNoiseTechnicalReportfortheCountyofSanDiegoGeneralPlanUpdate(CountyofSanDiego2009c),GeneralPlanUpdate(CountyofSanDiego2011a),CountyofSanDiegoGeneralPlan,NoiseElementBackgroundReport(CountyofSanDiego2011a),andGuidelinesforDeterminingSignificance:Noise(CountyofSanDiego2009d).

2.6.1.1 Ambient Noise Setting 

TheCountyischaracterizedasaprimarilyruralenvironmentwithlow‐densitydevelopmentthatcontributestoitsperceivedqualityoflifeanditspeaceandtranquility.However,severalhigher‐densitycommunities,includingtheValledeOroCommunityPlanningArea(CPA),SpringValleyCPA,andSweetwaterCPA,alsoexist,whichhavealouderambientnoiseenvironment.Majorsourcesofnoiseincludetransportationandnon‐transportationrelatedactivities.Non‐transportation‐relatednoisegeneratorsarecommonlycalledstationary,fixed,area,orpointsourcesofnoise.Industrialprocessing;mechanicalequipment;pumpstations;andheating,ventilating,andairconditioning(HVAC)equipmentareexamplesoffixed‐location,non‐transportationnoisesourceswithintheCounty.Somenon‐transportationsourcesarenotstationarybutaretypicallyassessedaspointorareasourcesduetothelimitedareainwhichtheyoperate,suchastruckdeliveries,agriculturalfieldmachinery,andminingequipment.

2.6.1.2 Characteristics of Noise and Vibration 

Noiseistypicallydefinedasunwantedsound.Soundsareperceivedbasedontheirloudness(i.e.,volumeorsoundpressurelevel)orpitch(i.e.,tonalorfrequencycontent).Thestandardunitofmeasureforsoundpressurelevelsisthedecibel(dB).Thestandardunitusedtodescribethetonalorfrequencycontentishertz(Hz).Typicalfrequencyrangesare20–20,000Hzforaudiblenoise,100–3,000Hzfornormalspeech,20–200Hzforlowfrequencysound,andlessthan20Hzforinfrasound.Table2.6‐1showsthesoundpressurelevel,indecibels,ofthecorrespondingfrequencyofinfrasoundandlowfrequencysoundnecessaryforthesoundtobeheardbytheaverageperson.Customarily,theyoung,non‐pathologicalearcanperceivesoundsrangingfrom20–20,000Hz.Infrasound,atcertainfrequenciesandathighlevels,canbeaudibletosomepeople.

Toaccountforthepitchofsoundsandthecorrespondingsensitivityofhumanhearing,therawsoundpressurelevelisadjustedwithanA‐weightingschemebasedonfrequencythatisstatedinunitsofdecibels(dBA).Table2.6‐2depictstypicalA‐weightedsoundlevelsforvariousnoisesources.A‐weightingisacceptableifthereislargelymiddleandhighfrequencynoisepresent,butifthenoiseisunusuallyhighatlowfrequencies,orcontainsprominentlowfrequencytones,theA‐

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weightingmaynotgiveavalidmeasure.Humanhearingcausessoundsdominatedbylow‐frequencycomponentstoseemlouderthanbroadbandsoundsthathavethesameA‐weightedlevel.Therefore,otherweightingschemesareused.

Agivenlevelofnoisewouldbemoreorlesstolerabledependingonthesoundlevel,durationofexposure,characterofthenoisesources,timeofdayduringwhichthenoiseisexperienced,andactivityaffectedbythenoise.Forexample,noisethatoccursatnighttendstobemoredisturbingthanthatwhichoccursduringthedaybecausesleephasthepotentialtobedisturbed.Additionally,restatnightisacriticalrequirementintherecoveryfromexposuretohighnoiselevelsduringtheday.Inconsiderationofthesefactors,differentmeasuresofnoiseexposurehavebeendevelopedtoquantifytheextentoftheeffectsanticipatedfromtheseactivities.Forexample,someindicesconsiderthe24‐hournoiseenvironmentofalocationbyusingaweightedaveragetoestimateitshabitabilityonalong‐termbasis.Othermeasuresconsiderportionsofthedayandevaluatethenearbyactivitiesaffectedbyitaswellasthenoisesources.ThemostcommonlyusedindicesformeasuringcommunitynoiselevelsaretheEquivalentEnergyLevel(Leq),andtheCommunityNoiseEquivalentLevel(CNEL).

Thedecibellevelofasounddecreases(orattenuates)exponentiallyasthedistancefromthesourceofthatsoundincreases.Forasinglepointsourcesuchasapieceofmechanicalequipment,thesoundlevelnormallydecreasesbyabout6dBAforeachdoublingofdistancefromthesource.Soundthatoriginatesfromalinear(orline)source,suchasaheavilytraveledtrafficcorridor,attenuatesbyapproximately3dBAperdoublingofdistance,providedthatthesurroundingsiteconditionslackgroundeffectsorobstaclesthateitherscatterorreflectnoise.

Noise Effects 

Noisehasanimportanteffectonthequalityoflife.Anindividual’sreactiontoaparticularnoisedependsonmanyfactors,suchasthesourceofthenoise,itsloudnessrelativetothebackgroundnoiselevel,andthetimeofday.Thereactiontonoisecanalsobehighlysubjective;theperceivedeffectofaparticularnoisecanvarywidelyamongindividualsinacommunity.Becauseofthenatureofthehumanear,asoundmustbeabout10dBAgreaterthanthereferencesoundtobejudgedastwiceasloud.Ingeneral,a3dBAchangeincommunitynoiselevelsisperceivable,while1–2dBAchangesgenerallyarenotperceived.Althoughthereactiontonoisewouldvary,itisclearthatnoiseisanimportantcomponentoftheenvironment,andexcessivelynoisyconditionscanaffectanindividual’shealthandwell‐being.Theeffectsofnoiseareoftenonlytransitory,butadverseeffectscanbecumulativewithprolongedorrepeatedexposure.Theeffectsofnoiseonacommunitycanbeorganizedintosixbroadcategories:sleepdisturbance,permanenthearingloss,humanperformanceandbehavior,socialinteractionofcommunication,extra‐auditoryhealtheffects,andgeneralannoyance.

Noise‐Sensitive Land Uses 

Noise‐sensitivelandusesincludeareaswhereanexcessiveamountofnoisewouldinterferewithnormalactivities.Primarynoise‐sensitivelandusesincluderesidentialuses,publicandprivateeducationalfacilities,hospitals,convalescenthomes,hotels/motels,daycarefacilities,andpassiverecreationalparks.Sleepdisturbanceisthemostcriticalconcernforanoise‐sensitivelanduseona24‐hourbasisorlongercomparedtoactivitiesthatareoccupiedonlyaportionofaday.

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Groundborne Vibration 

Groundbornevibrationpropagatesfromthesourcethroughthegroundtoadjacentbuildingsbysurfacewaves.Vibrationmaybecomposedofasinglepulse,aseriesofpulses,oracontinuousoscillatorymotion.Thefrequencyofavibratingobjectdescribeshowrapidlyitisoscillating,measuredinHz.Thenormalfrequencyrangeofmostgroundbornevibrationthatcanbefeltgenerallystartsfromalowfrequencyoflessthan1Hztoahighfrequencyofabout200Hz.Vibrationenergyspreadsoutasittravelsthroughtheground,causingthevibrationamplitudetodecreasewithdistanceawayfromthesource.Ambientandsourcevibrationareoftenexpressedintermsofthepeakparticlevelocity(PPV)orrootmeansquare(RMS)velocityininchespersecondthatcorrelatesbestwithhumanperception.TheFederalTransitAdministration(FTA)estimatesthatthethresholdofperceptionisapproximately0.0001inch/secondRMS,andthelevelatwhichcontinuousvibrationsbegintoannoypeopleisapproximately0.001inch/secondRMS(FTA2006).

Vibration Sensitive Land Uses 

Groundbornevibrationcandisruptvibration‐sensitivelandusesbycausingmovementofbuildings,rattlingofwindowsanditemsinsidebuildings,rumblingsounds,andevenpropertydamage.Vibration‐sensitivelandusesincludebuildingswherevibrationwouldinterferewithoperationswithinthebuilding,suchasvibration‐sensitiveresearchandmanufacturing,hospitalswithvibration‐sensitiveequipment,anduniversityresearchoperations.Thedegreeofsensitivitytovibrationdependsonthespecificequipmentthatwouldbeaffectedbythevibration.Residentialusesarealsosensitivetoexcessivelevelsofvibrationofeitheraregularoranintermittentnature.AccordingtotheTransitNoiseandVibrationImpactAssessment(FTA2006),thebackgroundvibrationlevelinresidentialareasistypically0.00003inch/secondRMS,whichislowerthanthe0.0001inch/secondRMSthresholdofperceptionforhumans.ThereareseveralsourcesofgroundbornevibrationintheunincorporatedCounty,includingconstruction,railroadoperations,andextractiveminingoperations(seeTable2.6‐3).

Noisesassociatedwithagriculturaloperationsincludevarioustypesofheavymachineryusedforlandmanagementandoperations,suchastractorsandtrucks,aircraftusedforcropdusting,woodworkingmachinery,processingequipment,bird‐scaringdevices,grainandhaydryersandfans,andmechanicalventilationfans.MostoftheagriculturalareasintheCountyareinruralandremoteareas,andtheexistingambientnoiselevelsinagriculturalareasarerelativelylow.Duetothesizeoftheprojectarea,baselinenoisemeasurementswerenotrecorded;however,themostrecentCountywidenoisemeasurementsavailableincludea2008communitynoisesurveythatidentifiedagriculturaloperationsashavinganoiselevelrangeof44.4–68.3dBA(CountyofSanDiego2009c).Nomajorcircumstancessincethetimeofthe2008noisesurveyhaveoccurredinagriculturalareasthatwouldsubstantiallyaffectthesurveyresults.

Temporary and/or Nuisance Noise 

Temporaryconstructionactivitiesaredisturbingtoresidentsbutaredifficulttoattenuateandcontrol.NoisecomplaintsoccurmorefrequentlyindenselydevelopedareasoftheunincorporatedCounty,suchastheSpringValleyCPAandValledeOroCPA,aswellasareasthatareheavilyagricultural,suchastheFallbrookCPAandValleyCenterCPA.

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Community Noise Survey 

DuringFebruaryandMarch2008,PBS&Jconductednoisemeasurementswiththepurposeofestablishingbaselinesfortransportationandnon‐transportationnoisegeneratorsthroughouttheCounty.LocationsweremonitoredusingaLarson–DavisAmericanNationalStandardsInstituteTypeIIintegratingsoundlevelmetertoestablishexistingambientnoiselevels.Noisemeterlocationsvariedforeachmeasurementaccordingtositeaccessibility.Atotalof44short‐term(15‐minute)measurementswereconductedtoprovideabasisforunderstandingtheoverallexistingnoiseenvironmentoftheCounty.A15‐minutesampleisconsidereda“snapshot”ofthebaselinenoiseenvironmentatagiventime;however,thesoundlevelwouldvarydependingontime,day,orseason.

Theresultsofthecommunitynoisesurveyshowthatthelocationswiththehighestnoiselevels(between70and74dBALeq)wereroadways(includingInterstate[I]8),boulevards,aprimearterial,aSprinterpass‐byareainNorthCountyMetroSubregion,ashootingrangeinValledeOroCPA,theRamonaLandfill,andconstructioninSpringValleyCPA.Thelocationswiththelowestnoiselevels(between43and50dBA)werearesortinBorregoSprings,residentialdevelopmentsinSanDieguitoCPAandLakesideCPA,andnoise‐sensitivebiologicalresourcesinLakesideCPA,allofwhichweresubjecttolimitedtrafficnoise.OtherlandusedesignationsinthisrangewerearecreationalparkinJulianCPA,aschoolinPala/PaumaValleySubregionwithschoolbellsandchildrenatrecess,andagriculturaluseinPala/PaumaValleySubregionusingtractorsandforklifts.

Noise Contours 

Noiselevelcontoursareusedasaguideforminimizingtheexposureofcommunityresidentstonoise.Noisecontoursrepresentlinesofequalnoiseexposure.Contoursareusedtoprovideageneralvisualizationofsoundlevelsandshouldnotbeconsideredasabsolutelinesofdemarcation.NoisecontoursforroadwaynoisesourcesattheCounty‐widelevelweremostrecentlydevelopedaspartoftheCounty’sGeneralPlanUpdate,whichwasapprovedin2011.Assuch,existingconditionsforthisprojectrelyuponinformationgatheredandpresentedintheCounty’sGeneralPlan,whichuses2008noisemeasurementscollectedbyPBS&J.TheexistingnoisecontoursareshownintheCounty’sGeneralPlanUpdateEIRasFigure2.11‐2,andnoisecontoursforfuturebuild‐outconditionsin2030areshownintheCounty’sGeneralPlanUpdateEIRasFigure2.11‐3.NoisecontoursareexpressedasCNELvalues.

2.6.2 Regulatory Setting 

Noiseissubjecttoregulatoryoversightatthreelevels:federal,state,andlocal.

2.6.2.1 Federal Regulations 

Federal Aviation Administration Standards 

EnforcedbytheFederalAviationAdministration(FAA),14CodeofFederalRegulations(CFR)150prescribestheprocedures,standards,andmethodologygoverningthedevelopment,submission,andreviewofairportnoiseexposuremapsandairportnoisecompatibilityprograms,includingtheprocessforevaluatingandapprovingordisapprovingthoseprograms.Title14alsoidentifieslandusesthatarenormallycompatiblewithvariouslevelsofexposuretonoisebyindividuals.Itprovidestechnicalassistancetoairportoperators,inconjunctionwithotherlocal,state,andfederal

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authorities,toprepareandexecuteappropriatenoisecompatibilityplanningandimplementationprograms.FAAestablishesaCNELof65dBAasthenoisestandardassociatedwithaircraftnoise.

U.S. Environmental Protection Agency 

TheU.S.EnvironmentalProtectionAgency(EPA)hasindicatedthatresidentialnoiseexposureof55–65dBAisacceptablewhenanalyzinglandusecompatibility(EPA1981);however,theseguidelinesarenotregulatory.Withregardtonoiseexposureandworkers,thefederalOccupationalSafetyandHealthAdministration(OSHA)establishesregulationstosafeguardthehearingofworkersexposedtooccupationalnoise(29CFR1910.95).OSHAspecifiesthatsustainednoiseover85dBA(8‐hourtime‐weightedaverage)canbeathreattoworkers’hearing,andifworkerexposureexceedsthisamount,theemployermustdevelopandimplementamonitoringplan(29CFR1910.95(d)(1)).

U.S. Office of Surface and Mining Reclamation and Enforcement 

TheU.S.OfficeofSurfaceMiningReclamationandEnforcement(OSM)hasestablishedguidelinesrelatedtoblastingforsurfaceminingactivities.OSMguidelinesrequiretheoperatortodistributeablastingschedule,postblastingsigns,andcontrolaccesswithintheblastingarea.OSMhasestablishedairblastandgroundvibrationlimitsatthelocationofanydwelling,publicbuilding,school,church,orcommunitybuildingoutsidethepermitarea.ThestandardPPVdamagethresholdforresidentialstructuresis2.0inchespersecond.ThisrequirementisbasedonthefindingsandrecommendationsofseveralreportsmadebytheformerU.S.BureauofMines.

2.6.2.2 State Regulations 

California Noise Control Act of 1973 

Sections46000through46080oftheCaliforniaHealthandSafetyCode,knownastheCaliforniaNoiseControlActof1973,findsthatexcessivenoiseisaserioushazardtothepublichealthandwelfareandthatexposuretocertainlevelsofnoisecanresultinphysiological,psychological,andeconomicdamage.Italsofindsthatthereisacontinuousandincreasingbombardmentofnoiseintheurban,suburban,andruralareas.TheCaliforniaNoiseControlActdeclaresthattheStateofCaliforniahasaresponsibilitytoprotectthehealthandwelfareofitscitizensbythecontrol,prevention,andabatementofnoise.ItisthepolicyofthestatetoprovideanenvironmentforallCaliforniansfreefromnoisethatjeopardizestheirhealthorwelfare.

California Airport Noise Standards  

The1990CaliforniaAirportNoiseStandardsaredesignedtocausetheairportproprietor,aircraftoperator,localgovernments,pilots,andtheCaliforniaDepartmentofTransportation’sDivisionofAeronauticstoworkcooperativelytodiminishnoise.Theregulationsaccomplishtheseendsbycontrollingandreducingnoiseinthecommunitiesinthevicinityofairports.ThelevelofnoiseacceptabletoareasonablepersonresidinginthevicinityofanairportisestablishedasaCNELvalueof65dBA.Thelimitationsonairportnoiseinresidentialcommunitiesareestablishedasfollows.

a. ThecriterionCNELis65dBAforproposednewairportsandforactivemilitaryairportsbeingconvertedtocivilianuse.

b. ThecriterionCNELforexistingcivilianairportsis65dBA.

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California Airport Land Use Planning Handbook 

TheCaliforniaAirportLandUsePlanningHandbookprovidesguidancefortheassessmentofnoisecompatibilityoflandusesnearairports.Guidanceisbasedonexistingfederalandstateregulationsandpolicies.Thehandbookstatesthat65dBAisthebasiclimitofacceptablenoiseexposureforresidentialandothernoise‐sensitivelandusesandrecommendsanannualCNELstandardof60dBAtobeusedfornewresidentialdevelopment;however,thisstandardhasbeensetwithrespecttorelativelynoisyurbanareasandmaybetoohighofanoiseleveltobeappropriateasastandardforlandusecompatibilityplanning.Thelevelofnoisedeemedacceptableinonecommunityisnotnecessarilythesameinanother.Anoiselevelabove60dBACNELmaybeconsideredincompatiblewithsomeresidentialuses.Accordingtothehandbook,noisecompatibilitystandardstypicallyplaceprimaryemphasisonresidentialareasbecauseresidentialdevelopmentisoneofthemostnoise‐sensitivelandusesandusuallycoversthegreatestproportionofurbanland.ThreeCNELsarecommonlyusedasthelimitforacceptableresidentialnoiseexposure:CNEL65,60,or55dBA.Thehandbookalsoincludesnormalizationfactorsasamethodforadjustingaircraftnoiselevelsusedfordeterminingandpredictingcommunityreactions.Becausetheacceptableresidentialnoiselevelstandardmayvarybetweencommunities,noisecompatibilityissuesareaddressedintheAirportLandUseCompatibilityPlans(ALUCPs)preparedforindividualairports.

AlllandusejurisdictionsintheCountyhaveordinancesthatregulateactivitiesinordertoreducenoiseimpacts.Asstatedpreviously,anynoisegeneratedbytheconstruction,operation,andmaintenanceofprojectsundertheproposedZoningOrdinanceAmendmentwouldberequiredtocomplywiththestandardsandregulationsgoverningnoiselimitswithintheapplicablejurisdiction.

2.6.2.3 Local Regulations 

Airport Land Use Compatibility Plans 

ALUCPsareplansthatguidepropertyownersandlocaljurisdictionsindeterminingwhattypesofproposednewlandusesareappropriatearoundairports.Theyareintendedtoprotectthesafetyofpeople,property,andaircraftonthegroundandintheairinthevicinityofanairport.ALUCPsarebasedonadefinedareaaroundanairportknownastheAirportInfluenceArea.ALUCPsincludepoliciesthataddressnoisecompatibilityissuesassociatedwithairportsandtheirrespectiveAirportInfluenceAreas(AIAs).

County of San Diego General Plan Update, Noise Element 

TheGeneralPlanUpdateNoiseElementestablishesnoiseandlandusecompatibilitystandardsandoutlinesgoalsandpoliciestoachievethesestandards.TheCounty’sGeneralPlanNoiseElementcharacterizesthenoiseenvironmentintheCountyandprovidesthecontextfortheCounty’snoise/landusecompatibilityguidelinesandstandards.TheNoiseElementalsodescribestheCounty’sgoalsforachievingthestandardsandintroducespoliciesdesignedtoimplementthegoals.UnderimplementationoftheGeneralPlanUpdate,theCountywouldusetheNoiseCompatibilityGuidelinesandNoiseStandards(TablesN‐1andN‐2)todeterminethecompatibilityoflanduseswhenevaluatingproposeddevelopmentprojects.TheNoiseCompatibilityGuidelinesindicaterangesofcompatibilityandareintendedtobeflexibleenoughtoapplytoarangeofprojectsandenvironments.

Alanduselocatedinanareaidentifiedasacceptableindicatesthatstandardconstructionmethodswouldattenuateexteriornoisetoanacceptableindoornoiselevelandthatpeoplecancarryout

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outdooractivitieswithminimalnoiseinterference.Landusesthatfallintotheconditionallyacceptablenoiseenvironmentshouldhaveanacousticalstudythatconsidersthetypeofnoisesource,thesensitivityofthenoisereceptor,andthedegreetowhichthenoisesourcehasthepotentialtointerferewithsleep,speech,orotheractivitiescharacteristicofthelanduse.Forlandusesindicatedasconditionallyacceptable,structuresmustbeabletoattenuatetheexteriornoisetotheindoornoiselevelasindicatedintheNoiseStandards.Forlanduseswheretheexteriornoiselevelsfallwithintheunacceptablerange,newconstructiongenerallyshouldnotbeundertaken.

San Diego County Code of Regulatory Ordinances Title 3, Division 6, Chapter 4, Sections 36.401–36.435, Noise Ordinance 

TheNoiseOrdinanceestablishesprohibitionsfordisturbing,excessive,oroffensivenoiseaswellasprovisionssuchassoundlevellimitsforthepurposeofsecuringandpromotingthepublichealth,comfort,safety,peace,andquietforitscitizens.Plannedcompliancewithsoundlevellimitsandotherspecificpartsoftheordinanceallowspresumptionthatthenoiseisnotdisturbing,excessive,oroffensive.Limitsarespecifieddependingonthezoningplacedonaproperty(e.g.,varyingdensitiesandintensitiesofresidential,industrial,andcommercialzones).Wheretwoadjacentpropertieshavedifferentzones,thesoundlevellimitatalocationonaboundarybetweentwopropertiesisthearithmeticmeanoftherespectivelimitsforthetwozones,exceptforextractiveindustries.The1‐houraveragesoundlevellimitapplicabletoextractiveindustries,includingbutnotlimitedtoborrowpitsandmines,wouldbe75dBAatthepropertylineregardlessofthezoneinwhichtheextractiveindustryislocated.ItisunlawfulforanypersontocauseorallowthecreationofanynoisethatexceedstheapplicablelimitsoftheNoiseOrdinanceatanypointonorbeyondtheboundariesofthepropertyonwhichthesoundisproduced.

Section36.404oftheCountyNoiseOrdinancecontainssoundlevellimitsspecifictoreceivinglanduses.Soundlevellimitsareintermsofa1‐houraveragesoundlevel.TheallowablenoiselimitsdependupontheCounty’szoningdistrictandtimeofday.TheproposedprojectwouldbelocatedinanyzonewithintheCounty.Table2.6‐4liststhesoundlevellimitsfortheCounty.Sections36.408through36.410oftheCountyNoiseOrdinancesetslimitsonthetimeofdayanddaysoftheweekthatconstructioncanoccur,aswellassettingnoiselimitsforconstructionactivities.Insummary,theordinanceprohibitsoperatingconstructionequipmentonthefollowingdaysandtimes.

MondaysthroughSaturdaysexceptbetweenthehoursof7a.m.and7p.m.

Sundaysanddaysappointedbythepresident,governor,orboardofsupervisorsforapublicfast,Thanksgiving,orotherholiday.

Inaddition,Section36.409requiresthatbetweenthehoursof7a.m.and7p.m.,noequipmentcanbeoperatedsoastocausean8‐houraverageconstructionnoiselevelinexcessof75dBAwhenmeasuredattheboundarylineofthepropertywherethenoisesourceislocated,oronanyoccupiedpropertywherethenoiseisbeingreceived.

San Diego County Zoning Ordinance Section 5250‐5260, Airport Land Use Compatibility Plan Use Regulations  

ALUCPsestablishanAIAthatdenotesareaswherelandusesshouldbereviewedforcompatibilitywiththeairportsoperations.TheCountyofSanDiegoZoningOrdinanceincludesaSpecialAreaDesignator“C”—AirportLandUseCompatibilityPlan—thatisassignedtopropertiesintheAIAs.ThroughtheapplicationoftheSpecialAreaDesignator,newdevelopment,redevelopment,

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expansions,conversionsandotherusesoflandlocatedthatrequireCountyapprovalarerequiredtobereviewedagainsttheestablishedcriteriaandpoliciesoftheapplicableALUCP.UnlessthepropertyisalreadydevotedtotheproposedincompatibleuseortheALUCPisoverriddenbytheCountyinamannerwhichrenderstheusecompatiblewiththeALUCP,theproposal,mustcomplywiththeestablishedpoliciesandcriteriaoftheapplicableALUCP.

2.6.3 Analysis of Project Effects and Determination of Significance  

TheproposedprojectconsistsofanamendmenttotheZoningOrdinancethatwouldpromoteaccessoryagriculturaloperationsthroughouttheunincorporatedCountyofSanDiego,asdescribedinChapter1,ProjectDescription,Location,andEnvironmentalSetting.ThefollowingimpactanalysisgenerallysummarizesanticipatedconstructionandoperationalnoisesthatwouldresultwithfutureimplementationoftheproposedchangestotheZoningOrdinanceandconcludeswhetherthoseincreaseswouldresultinsignificantenvironmentalimpacts.Onecommentletterthatisrelevanttonoisewasreceivedduringthe30‐daypubliccommentperiod.TheClevelandNationalForestindicatedthatnoiseisofparticularconcernfortheagencyandrequestedthattheEIRconsidereffectsofintensifiedlandusesontheforest.

2.6.3.1 Excessive Noise Levels 

Guidelines for the Determination of Significance 

ThefollowingsignificanceguidelinefromAppendixGoftheStateCEQAGuidelinesappliestoboththedirectandcumulativeimpactanalyses.Asignificantimpactwouldresultiftheproposedprojectwould:

ResultintheexposureofpersonstoorgenerationofnoiselevelsinexcessofstandardsestablishedbytheCounty’sGeneralPlan,County’sNoiseOrdinance,County’sNoiseCompatibilityGuidelines,orCounty’sZoningOrdinance.

Analysis 

NoiselevelsintheunincorporatedCountyareregulatedbytheCounty’sNoiseOrdinanceandtheCountyGeneralPlanNoiseElement.TheNoiseOrdinanceregulatesnoiselevelsassociatedwithongoingoperationsandtemporaryconstruction,andincludespermissiblenoiselevels(onsitenoiseimpacts).TheNoiseElementdesignatespermissiblenoiselevels(dBA)forvariouslandusezonesandregulates24‐hourtimevaryingnoisesourcessuchasvehiclenoiselevelsassociatedwithdevelopment(onsiteandoffsitenoiseimpacts).

AtrafficreportwaspreparedfortheproposedprojecttodeterminepotentialtrafficimpactsonarearoadwaysduetooperationofanincreasednumberofaccessoryagriculturaloperationsintheCounty.Oftheindividualaccessoryusesincludedaspartoftheproject,fivetypesofuseswereincludedasanticipatedtrafficgenerators,includingagriculturalhomestays,agriculturalstores,creamery/dairy,microbreweries,cideries,andmicro‐distilleries,andwineries.Thetripsassociatedwitheachwerethenaveragedacrossallparcelswithsimilarzoning,andanoveralltripgenerationratebycommunityplanningareawasdetermined(refertoSection2.7.3.1formoreinformationonmethodologyforcalculatingtripgeneration).ThemosttripsassociatedwiththeprojectwouldoccurinValleyCenter(about4,900newtrips),representinganincreaseofabout2.2percentinthat

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community.ThelargestincreaseinpercentagewouldoccurinRainbow,wherea5.6percentincreasewouldoccurwithanadditional904trips.

General Construction Related Impacts 

FutureconstructionactivitiesthatarelikelytobeassociatedwiththeaccessoryagriculturalusesthatarepromotedbytheproposedZoningOrdinanceupdateswouldgenerallyinvolveatemporaryincreaseinnoiserelatedtoconstructionequipmentandactivitiesassociatedwithlandclearing,miscellaneouslandimprovements,andtheconstructionofstructuresupto5,000squarefeet.

Noiselevelgenerationwouldchangeday‐to‐day,dependingonthelevelofactivity,duration,andthespecifictypeofconstruction.Assuch,thefollowingnoiseanalysisdoesnotincludeprecisenoiselevels,ratheraqualitativeanalysisisprovidedthatgenerallydiscussesprimarynoisegeneratorsassociatedwithbothconstructionandoperation.Relatedconstructionactivitiesthatwouldproducetemporaryincreasesinnoisewouldincludetypicalconstructionequipmentsuchastractors,loaders,backhoes,excavators,graders,forklifts,andwelders.Asummaryoftypicalconstructionequipmentnoiselevelsat50feetisprovidedinTable2.6‐5.Itisnotanticipatedthatdrillingorblastingwouldberequiredtosupporttheconstructionofanyoftheusesthatwouldbepromotedbytheproposedproject.Constructionactivitiesaretemporaryinnatureandwouldnotgenerateexcessivenoiseoveralongdurationoftime.Manyoftheaccessoryagriculturalusespromotedbytheprojectareanticipatedtoresultoflimitedconstructionequipmentoperationsastheywilllikelybelocatedonexistingdevelopedsitesorwillnotrequiresubstantialnewdevelopment,resultinginminimalornograding.

AllfutureconstructionrelatedtotheproposedprojectwouldberequiredtocomplywiththeCounty’sNoiseOrdinanceSection36.408,whichestablisheslimitsonhourofoperationforconstructionequipment,aswellasSections36.409and36.410,whichsetssoundlevellimitsonconstructionequipment(includingimpulsivetypenoisesources).Insummary,theordinanceprohibitsoperatingconstructionequipmentonthefollowingdaysandtimes.

MondaysthroughSaturdays,exceptbetweenthehoursof7a.m.and7p.m.

Sundaysoraholiday(January1,thelastMondayinMay,July4,thefirstMondayinSeptember,December25,andanydayappointedbythepresidentasaspecialnationalholidayorthegovernorofthestateasaspecialstateholiday).Apersonmay,however,operateconstructionequipmentonaSundayorholidaybetweenthehoursof10a.m.and5p.m.attheperson’sresidenceprovidedcompliancewithSections36.409and36.410oftheCounty’sNoiseOrdinance.

Thecodealsorequiresthatbetween7a.m.and7p.m.noconstructionequipmentbeoperatedsoastocausean8‐houraverageconstructionnoiselevelinexcessof75dBAwhenmeasuredattheboundarylineofthepropertywherethenoisesourceislocated,oronanyoccupiedpropertywherethenoiseisbeingreceived.Primarynoise‐generatingactivitiestypicallyoccurduringthesitepreparationandgradingphaseofaproject,whichisatemporaryactivity.Additionally,theaccessoryagriculturalusesareanticipatedtobelocatedonexistingdevelopedsites,resultinginminimalornograding.ItisexpectedthatanyfutureconstructionoftheaccessoryagricultureusesthatwouldbepromotedundertheproposedprojectwouldnotexceedtheCounty’sstandardofan8‐houraverageof75dBAatthepropertyline.Therefore,itisnotexpectedthatconstructionactivitieswouldviolatetheCounty’snoiseregulations.Constructionimpactsassociatedwiththe

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proposedprojectareconsideredtobelessthansignificant,andnomitigationmeasuresareincludedforconstruction.

Operational Impacts  

Generally,onsiteoperationalnoisesassociatedwiththeprojectwouldconsistoftypicalagriculturalnoisesrelatedtomachinery,animals,andvehicles,allofwhichwouldbeincreasedsomewhatwithadoptionoftheproposedamendmentstotheZoningOrdinance.Projectimpactsforbothoff‐andonsitenoisesarediscussedinthissection.Operationalnoisesassociatedwithagriculturalhomestays,agriculturalstands,animalraising,andaquaponics/fishmarketsareanticipatedtobeminimalastheydonottypicallyinvolvealargeamountofnoisymachineryanddonotinvolveasubstantialamountofnewvisitororsupportingvehicletrips.Operationalcharacteristicsassociatedwithagriculturalstores,agriculturalmicrobreweries,cideries,andmicro‐distilleries,andwineriesareanticipatedtogeneratethemostvisitors(oftheusesassociatedwiththeproposedproject)andalsoinvolvemachineryandequipmentthatcanbeassociatedwithhigherlevelsofnoisegeneration.Thesevarioususesarediscussedfurtherbelow.

Agricultural Homestay 

Agriculturalhomestayswouldinvolvesomeincrementaladditionofemployees,andwhilesomedailytripswouldincrease,theywouldnotbeexpectedtohaveaconsiderableincreaseintrafficvolumeorassociatedtrafficnoise.Operationsonanagriculturalhomestaywouldincreasesomewhatwiththeadditionofmoretemporaryworkersonagivenagriculturalproperty.Assuch,thegeneraluseoftypicalagriculturalequipment,suchastractorsandothermotorizedequipmentandvehicles,wouldincreaserelativetoexistingconditions;however,becauseagriculturalhomestayswouldincludelodginginanexistingresidenceoraseparate500‐square‐footcabin,theuseofadditionalnoise‐generatingequipmentwouldnotbeanticipatedtobenoticeablefromsurroundingpropertiesorexceedanyestablishednoisestandards,norareonsitenoisesanticipatedtobenoticeablylouderwiththepromotionofagriculturalhomestayswithinA70,A72,RR,S90,orS92zones.

Agricultural Roadside Stands 

Itisnotanticipatedthatatripwouldbecreatedspecificallytovisitaroadsidestand.Instead,itismorelikelythatpatronsofaroadsidestandwouldstopalongthewaytoanotherdestination,andassuch,thepromotionofroadsidestandswouldnotresultinasignificantimpactrelatedtoeitheron‐oroffsitenoise.Also,anagriculturalstandmayrequiretheadditionofanotheremployeetooperatethestand;however,theonsitenoisesassociatedwithanadditionalemployeearenotanticipatedtoresultinaviolationofanyCountynoiserequirements,andimpactswouldremainlessthansignificant.

Agricultural Stores, Microbreweries, Cideries, and Micro‐Distilleries, and Wineries 

Operationalcharacteristicsassociatedwithagriculturalstores,agriculturalmicrobreweries,cideries,andmicro‐distilleries,andwineriesareanticipatedtogeneratethemostvisitors(oftheusesassociatedwiththeproposedproject)duetothefactthattheywouldhavetastingroomsand/orretailareasthatwouldservevisitorsthatwouldtypicallyarrivebyapersonalvehicle.Thesetopicswerealsothefocusofthetrafficstudypreparedfortheproject(AppendixE).Furthermore,becausemostagriculturalareasareinmoreremoteorruralareas,publictransportationorothernon‐motorizedmeansoftransportation(e.g.,walkingorbicycling)arenotanticipated.Agricultural

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stores,bothsmallandlarge,aswellasagriculturalmicrobreweries,cideries,andmicro‐distilleries,andwinerieswouldattractretailcustomersandcouldresultinanincreaseinoffsitetrafficnoisethatcouldexceedtheCounty’sCNELlimitsintheGeneralPlanNoiseElement;however,onsitenoiseincreasesarenotexpectedtoresultinasignificantimpact.Operationsonsitewouldincreaserelativetotheamountofvisitors/customersonthesite,andtypicalnoisessuchasdriving/parkingandcongregatingwouldsomewhatincreaseoneachindividualparcelwithasmallorlargeagriculturalstore,agriculturalmicrobrewery,cidery,ormicro‐distillery,orwinery.Theseonsiteincreasesinactivitiesarenotexpectedtoviolateanynoiseregulations.Furthermore,theproposedlanguagetotheZoningOrdinancespecificallyprohibitseventssuchasweddingsandconcertsfromoccurringinconjunctionwithasmallagriculturalstoreandprohibitsamplifiedsoundforagriculturalmicrobreweries,cideries,andmicro‐distilleries,andwineries.

Largeagriculturalstoresandlargemicrobreweries,cideries,andmicro‐distillerieswouldberequiredtoobtainanAdministrativePermitandwouldhavetospecifyanyspecialeventsthatwouldoccuronthesite.Althoughsmallagriculturalstoresandsmallagriculturalmicrobreweries,cideries,andmicro‐distillerieswouldbeallowedpursuanttoapprovalofaministerialaction(e.g.,aZoningVerificationPermit),largeagriculturalstoresandlargeagriculturalmicrobreweries,cideries,andmicro‐distilleries,andwinerieswouldrequireadiscretionarypermit(e.g.,AdministrativePermit).Agradingpermitisanticipatedforeithertypeofagriculturalstoreoragriculturalmicrobrewery,cidery,andmicro‐distillery(e.g.,smallandlarge).AspartoftheCounty’spermitreviewprocess,alldiscretionaryprojectsareevaluatedunderCEQAandwouldberequiredtoimplementmeasurestominimizeimpactsrelativetoexcessivenoiselevels.

Potentialoffsitenoisesources,includingvehiculartrafficanddeliverytrucks,couldpotentiallyresultinsignificantnoiseimpacts.Agriculturalstores,bothlargeandsmall,aswellasagriculturalmicrobreweries,cideries,andmicro‐distilleries,andwinerieswouldalsogenerateadditionaltripstoagriculturalareasandresultinoperationalnoiseincreaseswhichcouldexceedtheCounty’sNoiseElementCNELdependingonhowmanyaredevelopedandwheretheyarelocated.Duringharvestperiods,operationsonsiteswithagriculturalmicrobreweries,cideries,andmicro‐distilleriesandwinerieswouldinvolveadditionalnoisesassociatedwithharvestingequipment,withanincreaseinoverallactivitiesontheproperty,includingadditionalemployeesandadditionalvehicletripsthatcouldresultinsignificanton‐andoffsitenoises.

Agricultural Tourism 

Agriculturaltourismwouldinvolveonsitetours,educationalactivities,andu‐pickoperations,allofwhichwouldsomewhatincreasenoiselevelsonsite.Pursuanttotheproposedregulations,noamplifiedsoundwouldbepermittedassociatedwiththeseevents,anditisanticipatedthatanyincreaseinnoisefromadditionalvisitorsandoperationoftypicalfarmequipmentwouldnotexceedanyestablishednoisestandardsintheCounty.Someadditionaltripswouldincreaserelativetoexistingconditions;however,itisnotanticipatedthatagriculturaltourismwouldresultinenoughadditionaltripstopotentiallyexceedanyCNELnoisecontoursorothernoisepoliciesincludedintheNoiseElementoftheCounty’sGeneralPlan.Impactswouldremainlessthansignificant.

Animal Raising 

Foranimalraising,theincreaseinanimalswouldsomewhatincreaseanimalnoisesonagivensite;however,theadditionofanimalsisnotexpectedtoresultinanincreasethatwouldresultinaviolationorexceedanceofanyCounty‐establishednoiseregulationsintheZoningCodeorGeneralPlan.Also,becauseanimalraisingregulationsarenotrelatedtoanyretailorothercommercial

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activitiesthatwouldpromoteorincreasetrafficonaregularbasis,itisnotexpectedthattheproposedchangestoanimalraisingwouldresultinoffsitenoiseimpactsassociatedwithtraffic.

Aquaponics 

TheoperationofaquaponicsonanagriculturalpropertywouldberequiredtocomplywithSection36.401oftheSanDiegoCountyCodeofRegulatoryOrdinancesrelatingtonoiseabatementandcontrol.Ifnecessary,applicantswouldberequiredtoinstallnoisebarriersaroundnoise‐generatingequipmenttocomplywiththeCounty’sOrdinance.Regardingoffsitenoisesassociatedwithtraffic,aquaponicsonagriculturalpropertieswouldnothavearetailcomponentasfishmarketswouldbeheldatfarmer’smarketsoncommercialorschoolproperties.Assuch,aquaponicswouldnothaveanyretailorothercommercialcomponentsthatwouldincreasetraffictoalevelthatwouldviolateanycommunitynoiselevelstandardsestablishedintheCounty’sGeneralPlan.Impactswouldremainlessthansignificant.

Creameries/Dairies 

Implementationoftheproposedcreamery/dairyusescouldresultinindividualdevelopmentprojectsinvolvinguptoa4,000‐square‐footbuilding;constructionofancillaryparkingareas,driveways,fences,andoutdoorseating;andanincreaseinsiteactivityrelatedtoadditionalvisitorsandnewemployees.Creamery/dairyuseswouldrequirethedevelopmentofnon‐residentialstructurestosupporttheproductionofbutter,cream,milk,orcheesewithinanenclosedbuilding,andwouldalsorequireindoorspaceforproductstorageintendedforwholesalesalesaswellasretailsales.TheproposedamendmentstotheCounty’sZoningOrdinanceforcreameries/dairiesincludespecificlanguagethatalloperationsmustcomplywiththeprovisionsofSection36.401oftheCounty’sZoningCodeasitrelatestonoiseabatement.However,similartoagriculturalstoresandmicrobreweries,whicharediscussedabove,increasedvehicletripscouldresultinpotentiallysignificantimpacts.

Fishermen’s Markets 

Fishermen’smarketsinvolvetheretailsaleoffishtothegeneralpubliconatemporarybasisandincommercialorschoolareas,likelyinconjunctionwithafarmers’market.Whilesomenoiseswouldbetemporarilygeneratedrelatedtoattractingcustomersinanoutdoorsetting,thesenoiseswouldconsistofsomeadditionalvehicles,peopletalking,andemployeessettingupandbreakingdownanoutdoortentorboothstructure.Thesenoiseswouldalsooccurfromothervendorsifinconjunctionwithafarmers’market.Becausetheseincreasesinnoisewouldbetypicalofafarmers’marketandwouldconsistofpeopletalkingandemployeessettingupanoutdoorbooth,itisnotexpectedthatthepromotionoffishermen’smarketswouldexceedanylocalregulationspertainingtonoise.

Mobile Butchering 

Mobilebutcheringoperationalnoiseswouldintroducenewnoisestoagriculturalareaswheninoperationassociatedwithanimalprocessingequipmentinsideamobileunit;however,theincreaseswouldbetemporaryandarenotanticipatedtoresultinnoiselevelsthatwouldexceedanyCountystandards.AsdescribedintheZoningOrdinanceupdatelanguage,severalrequirementsformobilebutcheringoperationswouldbeenforcedthatwouldreduceassociatednoises.Specifically,asstatedinproposedSection6126,setbacksrequirementswouldrequireatleast25feetfromapropertylineandhoursofoperationwouldbeduringdaytimehours,generally7a.m.–8p.m.,Mondaythrough

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Saturday,and9a.m.–6:00p.m.onSundays.Nooffsiteortraffic‐relatednoiseincreasesareassumedwithoperationofamobilebutcheringbusiness,exceptfortheindividualtripofthebutcheringvehicleitself.Assuch,on‐andoffsitenoiseimpactsduringtheoperationofmobilebutcheringactivitiesonagriculturalpropertiesareanticipatedtoremainlessthansignificantandnomitigationmeasuresarenecessary.

Summary 

Insummary,theproposedamendmentstotheCounty’sZoningOrdinanceforagriculturalmicrobreweries,cideries,andmicro‐distilleries,wineries,andcreameries/dairiesincludespecificlanguagethatalloperationsmustcomplywiththeprovisionsofSection36.401oftheCounty’sZoningCodeasitrelatestonoiseabatement.However,theserequirementsintheproposedZoningOrdinanceupdatedlanguageandtheexistingNoiseOrdinancerequirementsdonotaddressvehiclenoise.Therefore,newvehiculartrafficanddeliverytrucksassociatedwiththeaccessoryusescouldcontributetoincreasesinoffsitenoise,andinsomeselectareascouldcontributetonoiselevelsthatexceedCountystandards.Becausethereisnoguaranteethatoffsitenoisesourcesrelatedtoincreasesintrafficthatwouldbegeneratedfromfuturemicrobreweries/cideries/micro‐distilleries,stores,andwineriesintheunincorporatedCountywouldnotresultinsignificantimpacts,potentialfutureoffsitenoiseimpactsduringoperationsareconsideredtobepotentiallysignificant(ImpactN‐1).

2.6.3.2 Excessive Groundborne Vibration 

Guidelines for the Determination of Significance 

ThefollowingsignificanceguidelinefromAppendixGoftheStateCEQAGuidelinesappliestoboththedirectandcumulativeimpactanalyses.Asignificantimpactwouldresultiftheprojectwould:

Resultintheexposureofpersonstoorgenerationofexcessivegroundbornevibrationorgroundbornenoiselevels.

Analysis 

Groundbornevibrationistypicallyassociatedwithhighimpactconstructionequipment,suchasapiledriver,orwithvibrationsfromnon‐impactconstructionactivity,suchasautomobileortrucktraffic.Vibrationfromtrucktrafficistypicallybelowthethresholdofperceptionwhentheactivityismorethanabout50feetfromanoisereceptor.

Anyfuturesite‐specificprojectsthatwouldimplementtheproposedchangestotheCounty’sZoningOrdinancearenotanticipatedtorequiretheuseofhigh‐impactconstructionequipmenttoerectaccessoryagriculturalstructures,suchasanagriculturalstoreormicrobrewery.Likewiseitisnotanticipatedthatanyoftheproposedaccessoryagriculturaloperationswouldresultinadditionaltrucktrafficwithin50feetofanoisereceptor.Forprojectsthatwouldrequireadiscretionarypermit,includinglargeagriculturalmicrobreweries,cideries,andmicro‐distilleries,wineries,andsomeanimalraisingprojects,additionalCEQAreviewwouldberequired,whichwouldincludeconsiderationofpotentialimpactsrelatedtoexcessivegroundbornevibration.However,noneofthecomponentsoftheproposedprojectareanticipatedtoresultinsignificantimpactsrelatedtogroundbornevibrationandimpactswouldbelessthansignificant.

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2.6.3.3 Permanent Increase in Ambient Noise Levels 

Guidelines for the Determination of Significance 

ThefollowingsignificanceguidelinefromAppendixGoftheStateCEQAGuidelinesappliestoboththedirectandcumulativeimpactanalyses.Asignificantimpactwouldresultiftheprojectwould:

Causeasubstantialpermanentincreaseinambientnoiselevelsintheprojectvicinityabovelevelsexistingwithouttheproposedproject.

Analysis 

Vehicle Traffic Noise 

Operationalvehicletrafficwouldvarydependingontheuse,andthevariousaveragedailytripratesforeachaccessoryagriculturaluseisprovidedasAppendixEandalsopresentedinSection2.7,TransportationandTraffic.Thesetripswouldconsistofemployeeandvisitortripsandalsosomedeliverytrips.Thenumberoftripswouldbegreatestfortheagriculturalmicrobreweries,cideries,andmicro‐distilleriesandwineries,asthesefacilitiesareanticipatedtohavethelargestcommercialspacesandattractthemostvisitors.Employeesatthesefacilitieswouldalsolikelyoutnumberemployeesrelatedtootheraccessoryagriculturalusesincludedaspartoftheproposedproject.AsshownintheTrafficStudy,increasesinvehiclescouldrepresentasmuchasa5.6percentincrease(Rainbowcommunity)andasmuchas4,894newtrips(ValleyCentercommunity).Bothofthesecommunitiesareconsideredrural,andwiththeadditionofalargeincreaseintheRainbowcommunityandalargenumberofoveralltripsintheValleyCentercommunity,itispossiblethatasubstantialpermanentincreaseinambientnoiselevelscouldresultinsignificantenvironmentalimpacts(ImpactN‐2).

Onsite Generated Noise 

Accessoryagriculturaloperationsthatwouldbeimplementedwithadoptionoftheproposedprojectwouldresultinpermanentincreasesinlanduseactivities,therebyresultinginadditionalemployees/farmworkersandadditionalvisitorsforcommercialoperations.Permanentincreasesinnoisesrelatedtoagriculturalhomestays,agriculturaltourism,andanimalraisingwouldmostlybelimitedtosomeadditionalemployeesonaparticularproperty,andassuch,noisesassociatedwithoperatingmachineryanddrivingtractorsandtruckswouldsomewhatincrease;however,itisnotexpectedthattheseonsiteincreaseswouldexceedlimitsintheCounty’sNoiseOrdinance.Therefore,theywouldnotresultinasubstantialpermanentincreaseinambientnoiselevelsintheprojectvicinity.

Mobilebutcheringwouldinvolvetheuseofprocessingequipment(e.g.,animalprocessingequipment),refrigerationunits,dieselgenerators,andhotwaterheaters.TheproposedamendmentlanguagetotheZoningOrdinanceasitrelatestomobilebutcheringonsiteoperationswouldrestrictoperationsfromoccurringmorethansixtimesperyearandnotmorethan3consecutivedaysonthesamepropertyorwithin1mileofanotherpropertyusedformobilebutcheringbythesameowner.Hoursofoperationwouldalsoberestrictedtodaytimehoursandoperationswouldobeyasetbackrequirementof25feetfromanypropertyline,aswellasthenoiselimitsintheNoiseOrdinance.Assuch,mobilebutcheringoperationswouldnotbepermittedtooccuronaregularorpermanentbasis,andanyincreasesinnoisewouldbetemporaryandperiodic.

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Althoughthegrowingseasonwouldnotbeyearround,agriculturalmicrobreweries,cideries,andmicro‐distilleries,andwineriescouldoperateandsellproductsonaregularbasisandresultinpermanentincreasesinonsitenoise.Agriculturalmicrobreweries,cideries,andmicro‐distilleries,andwinerieswouldinvolvetheuseofprocessingequipment(e.g.,hopsseparators,grapecrushers),refrigerationunits,andpestcontroldevices,suchasbirdalarms,allofwhichareregulatedbytheNoiseOrdinanceanddiscussedabove.Largeagriculturalmicrobreweries,cideries,andmicro‐distilleries,agriculturalstores,andwinerieswouldresultinadditionalcustomersonsite,andsomeincreasesinnoisewouldresultfromgeneralconversationandvehiclesparking,forexample.Smallagriculturalmicrobreweries,cideries,andmicro‐distillerieswouldnotpermitretailsales,tastingrooms,oronsitesalesofanykind.

Theproposedprojectincludessomerequirementsforspecificusesthatwouldreducepotentialnoiseincreases.Forinstance,tastingroomswouldnotbeallowedtooperatebefore10a.m.orafterlegalsunsetandwouldnotallowevents,includingbutnotlimitedtoweddingsandparties.ApprovaloftheproposedZoningOrdinanceamendmentswouldadoptnewregulationsthatwouldpromotetheseusestobeimplementedonactiveagriculturalpropertieseitherbyright(wineries),ministerialpermitapproval(aZoningVerificationPermitforsmallmicrobreweries,cideries,andmicro‐distilleries),oradiscretionarypermit(anAdministrativePermitforlargemicrobreweries,cideries,andmicro‐distilleries).Itisalsopossiblethatadiscretionarygradingpermitwouldberequiredforthedevelopmentofanyoftheseuses.Underthosecircumstanceswherefuturediscretionaryreviewisrequired,moredetailedCEQAreviewwouldalsooccuratthattime.Aspartofthisreview,eachindividualprojectwouldberequiredtodemonstratecompliancewiththeCounty’sNoiseOrdinance.Duetotheruralnatureofmostactiveagriculturalpropertiesandthepromotionofaccessoryusesontheseproperties,theincreasedonsiteoperationsthatcouldoccurmayconsiderablyincreasenoiselevelsinthevicinitytoalevelthatwouldbeconsideredsubstantial.Itisthereforeexpectedthattheincreasedonsiteactivitieswouldresultinasignificantenvironmentalimpactrelatedtoapermanentincreaseinambientnoiselevels(ImpactN‐3).

2.6.3.4 Temporary or Periodic Increase in Ambient Noise Levels 

Guidelines for the Determination of Significance 

ThefollowingsignificanceguidelinefromAppendixGoftheStateCEQAGuidelinesappliestoboththedirectandcumulativeimpactanalyses.Asignificantimpactwouldresultiftheprojectwould:

Causeasubstantialtemporaryorperiodicincreaseinambientnoiselevelsintheprojectvicinityabovelevelsexistingwithouttheproposedproject.

Analysis 

Adoptionoftheproposedprojectisnotexpectedtoresultinasubstantialtemporaryorperiodicincreaseinambientnoiselevelsintheprojectvicinity.Constructionrelatedtotheproposedprojectwouldconsistprimarilyofbuildingstructuresupto5,000squarefeet,noneofwhichareanticipatedtoresultinsubstantialtemporaryorperiodincreasesinambientnoiselevelscomparedtoexistingnoiseconditions.Constructionactivitiesincluding,butnotlimitedto,sitegrading,truck/constructionequipmentmovement,enginenoise,androckexcavationwouldhavethepotentialtoresultintheexposureofon‐oroffsiteareastonoiseinexcessofthestandardslistedintheCountyCodeSections36.408and36.409.TypicalconstructionequipmentnoiselevelsareprovidedinTable2.6‐5.Constructionactivitieswouldgeneratesomeadditionaltemporarytrafficon

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projectarearoadwaysrelatedtoequipmentandmaterialsdeliveriesandifcontractorsorotherconstructionworkersareretainedtoconstructanystructures.Itisexpectedthatmostofthestructuresthatwouldbedevelopedassociatedwithimplementingtheproposedprojectwouldnotrequireextensiveconstructiontimeframes,andanytemporaryincreasesinnoiserelatedtoconstructionwouldremainlessthansignificant.Asstatedpreviously,mostoftheproposedaccessoryagriculturaluseswouldrequireagradingpermitandwouldprepareadditionalCEQAanalysisonaproject‐by‐projectbasisinthefuture.However,itisnotanticipatedthatanyaccessoryuseswouldresultinsignificanttemporarynoiseimpacts.Accessoryusesthatwouldnotnecessarilyinvolvestructuresincludeagriculturalhomestays(ifusingexistingstructuresforhousing),agriculturaltourism,animalraising,fishmarkets,andmobilebutcheringuses.Noperiodicincreasesinconstructionareanticipatedfortheseuses.Overall,impactsrelatedtoperiodicortemporaryincreasesinnoiseduringconstructionwouldremainlessthansignificant.

2.6.3.5 Airport‐Related Noise Exposure  

Guidelines for the Determination of Significance 

PursuanttoarecentCaliforniaSupremeCourtrulingonCaliforniaBuildingIndustryAssociation(CBIA)v.BayAreaAirQualityManagementDistrict(BAAQMD)(CaseNo.S213478,December17,2015),CEQAdoesnotrequireanalysisofhowexistingenvironmentalconditionswillimpactaproject’sfutureusersorresidents.Therefore,significancethresholdsarenotestablishedforthistopic.However,PublicResourcesCodeSection21096(a)requiresthatanEIRdiscussairport‐relatednoiseproblemsiftheprojectislocatedwithin2milesofapublicuseairport.Therefore,anassessmentofairport‐relatednoiseissuesisprovidedbelow.

Analysis 

SixpublicairportsarelocatedintheunincorporatedCounty:AguaCalienteAirstrip(DesertSubregion),BorregoValleyAirport(DesertSubregion),FallbrookCommunityAirpark(FallbrookCPA),JacumbaAirport(MountainEmpireSubregion),OcotilloAirstrip(DesertSubregion),andRamonaAirport(RamonaCPA).Mostoftheseincludesomeagriculturaluseswithin2milesoftheairports;thus,theproposedprojectcouldresultinnewaccessoryagriculturalusesinproximitytoexistingairports.AirportLandUseCompatibilityPlanshavebeenpreparedbytheSanDiegoRegionalAirportAuthorityforalloftheseairports.TheseALUCPsincludenoisecompatibilitypoliciesforreviewingnewdevelopmentaswellascurrentandfuturenoiselevelsthataregeneratedbytheairport.TheCountyofSanDiegohasestablishedazoningoverlaycongruentwitheachairport’sAIA,whichestablishestheCounty’sALUCPAreaRegulations.Theseregulationsrequirethat“[n]ewdevelopment,redevelopment,expansions,conversionsandotherusesoflandlocatedwithintheAIAofanadoptedALUCPforwhichCountyapprovalorpermitarerequiredshallbereviewedagainsttheestablishedcriteriaandpoliciesoftheALUCP.”Furthermore,“[u]nlessthepropertyisalreadydevotedtotheproposedincompatibleuseortheALUCPisoverriddenbytheCountyinamannerwhichrenderstheusecompatiblewiththeALUCP,theproposal,mustcomplywiththeestablishedpoliciesandcriteriaoftheapplicableALUCP.”Asaresult,potentialnoiseissueswouldbeaddressedthroughtheCounty’sreviewandapplicationoftheALUCPnoisecompatibilitypolicies,andimpactsfromairport‐relatednoiseexposurewouldbelessthansignificant.

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2.6.4 Cumulative Impacts Analysis 

Thegeographicscopeofcumulativeimpactanalysisfornoiseislimitedtoareassurroundingnoise‐generatingsources,suchasroadways,agricultural,orindustrialuses,becausenoiseimpactsarelocalizedinnature.Geographicscopecanbetheentireareawithinwhichtheresourcehasthepotentialtooccur.ForthepurposeofthisEIR,thegeographicscopeforthecumulativeanalysisofnoiseimpactsincludestheSanDiegoregion.

2.6.4.1 Noise Exposure 

Acumulativenoiseimpactresultingfrompastprojectswouldoccurifconstructionandoperationassociatedwithcumulativeregionallanduseprojects,suchasthoseidentifiedinadjacentcityandcountygeneralplansandregionaltransportationplans,wouldexceedthenoisecompatibilityguidelinesandstandardsoftheNoiseElement.However,developmentandconstructionproposedundermostcumulativeprojectswouldbesubjecttoregulationsthatrequirecompliancewithnoisestandards,suchasthosecontainedintheStateofCaliforniaCodeofRegulationsandthoserequiredbytheOfficeofSurfaceandMining.AlthoughtheCountyhasadoptedmeasuresandplansdesignedtoregulateandaddressnoiselevelsintheCounty,pastprojectshaveresultedinacumulativeimpact.

Asdiscussedpreviously,implementationoftheproposedprojectwouldberequiredtocomplywiththeCounty’sNoiseCompatibilityGuidelines,GeneralPlanNoiseElementNoiseStandards,andNoiseOrdinancepriortoapproval.Additionally,aspartoftheCounty’sdiscretionaryreviewprocess,futurediscretionaryprojectswouldbeevaluatedunderCEQAandwouldberequiredtoimplementmeasurestominimizeimpactsonambientnoise.However,past,present,andfutureprojectsinSanDiegoCountycouldcontinuetoresultinimmitigablenoiseimpacts.Whenthesignificantproject‐levelimpactonnoise(ImpactN‐1)isconsideredatthecumulativelevel,theproject’scontributiontoacumulativeimpactisconsideredtobesignificant(ImpactN‐4).

2.6.4.2 Excessive Groundborne Vibration 

Acumulativegroundbornevibrationimpactwouldoccurifoneormorecumulativeprojectswouldresultintheexposureofpersonstoorgenerationofexcessivegroundbornevibrationorgroundbornenoiselevels.Asgroundbornevibrationistypicallyassociatedwithconstruction,severalconstructionprojectswithinproximityofoneanotherwouldhavetosimultaneouslyoccurinordertocombineandcreateasignificantcumulativeimpactasaresultofgroundbornevibration.Assuch,acumulativeimpactrelatedtoexcessivegroundbornevibrationisnotpresentinthecumulativestudyarea.Attheprojectlevel,therearenospecificplansortimescalesforindividualconstructionprojects,anditisnotpossibletodetermineexactvibrationlevels,locations,ortimeperiodsforconstruction.Regardless,individualprojectswouldmostlyinvolveconstructionofstructuresnottypicallyassociatedwithgroundbornevibration.Therefore,cumulativeprojectsarenotexpectedtoresultinacumulativelyconsiderableimpact.

AllfuturedevelopmentassociatedwiththeproposedprojectwouldberequiredtocomplywiththeCounty’sNoiseCompatibilityGuidelines,GeneralPlanNoiseElementNoiseStandards,andNoiseOrdinancepriortoapprovalandareanticipatedtomeetthevibrationlimitsshowninTables2.6‐3and2.6‐6.Therefore,implementationoftheproposedprojectwouldnotcontributetoacumulativelyconsiderableimpactregardinggroundbornevibration.Impactswouldremainlessthansignificant.

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2.6.4.3 Permanent Increase in Ambient Noise Levels 

Acumulativenoiseimpactwouldoccurifconstructionanddevelopmentassociatedwithcumulativeregionallanduseprojects,suchasthoseidentifiedinadjacentcityandcountygeneralplansandregionaltransportationplans,whencombinedwouldresultinasubstantialpermanentincreaseinambientnoiseintheprojectvicinityabovelevelsexistingwithouttheproposedprojects.Forexample,theextensionofStateRoute(SR)905fromI‐805totheU.S.–MexicointernationalborderandwideningofSR‐94fromSR‐125toJamachaRoadwouldresultinapermanentincreaseinambientnoiseduetoanincreaseinroadwaynoise.Pastprojectshaveresultedinapermanentincreaseinambientnoiselevelsandacumulativelysignificantimpacthasoccurred.

FutureimplementationoftheproposedprojectwouldberequiredtocomplywiththeCounty’sNoiseCompatibilityGuidelines,GeneralPlanNoiseElementNoiseStandards,andNoiseOrdinancepriortoapproval.Additionally,aspartoftheCounty’sdiscretionaryreviewprocess,futurediscretionaryprojectswouldbeevaluatedunderCEQAandwouldberequiredtoimplementmeasurestominimizeimpactsonambientnoise.However,largerprojects,suchastheagriculturalmicrobreweriesandwineries,couldpotentiallycontributetoanincreaseinambientnoiselevels.Becausethereisnoguaranteeonaproject‐specificlevelthatmitigationmeasureswillreduceimpactstoalevelbelowsignificant,theproposedprojectwouldpotentiallycontributetoacumulativelyconsiderableimpact(N‐5).

2.6.4.4 Temporary or Periodic Increase in Ambient Noise Levels  

Acumulativenoiseimpactwouldoccurifconstructionassociatedwithoneormoreprojectsinproximitytooneanotherwouldresultinasubstantialtemporaryorperiodicincreaseinambientnoiselevelsintheprojectvicinityabovelevelsexistingwithouttheproposedprojects.However,astherearenospecificplansortimescalesforindividualprojects,itisnotpossibletodetermineexactnoiselevels,locations,ortimeperiodsforconstruction.Additionally,projectswouldhavetobeconstructedclosetogethertoresultinacumulativeimpact.Constructionprojectsinincorporatedjurisdictionswouldbesubjecttonoisestandardsandlimitsforthejurisdictioninwhichtheyareproposed.ProjectsproposedontriballandswouldnotbesubjecttoCountyofSanDiegonoiseregulationsandstandards;however,potentialconstructionnoise‐relatedimpactsintheseareaswouldbetemporaryandlimitedtotheareaimmediatelysurroundingtheproject.Similarly,acumulativenuisancenoiseimpactwouldoccurifnoiseassociatedwithoneormorelandusesinanareawouldresultincombinednoiselevelsthatwouldtemporarilyincreaseambientnoiselevelsbeyondthestandardsintheCountyNoiseOrdinance.However,theseeventswouldbeshort‐termandevent‐specificinnature.Therefore,apotentiallycumulativelyconsiderableimpactassociatedwithtemporaryincreasesinambientnoiselevelsisnotanticipatedtooccur.

2.6.5 Significance of Impacts Prior to Mitigation 

TheproposedprojectwouldresultinpotentiallysignificantimpactsrelatedtonoiselevelsinexcessofCountystandards(ImpactsN‐1,direct/indirectandN‐4,cumulative),andpermanentincreaseinambientnoiselevels(ImpactsN‐2andN‐3,direct/indirect,andN‐5,cumulative)asaresultofaccessoryagriculturaldevelopment.Theproposedprojectwouldnotresultinpotentiallysignificantimpactsassociatedwithexcessivegroundbornevibrationorexcessivenoiseexposurefromairports.

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2.6.6 Mitigation Measures 

2.6.6.1 Excessive Noise Levels 

TheproposedprojectwouldamendcurrentregulationsrelatedtoaccessoryagriculturalprojectsthatmaydirectlyorindirectlyresultinnoiselevelsinexcessofCountystandards(ImpactsN‐1,direct/indirectandN‐4,cumulative).Thesenoiseimpactswouldremainsignificantandunavoidable.Chapter4,ProjectAlternatives,providesadiscussionofalternativestotheproposedproject.Althoughthiswouldresultinareducedprojectareawithfewernewagriculturalusesreducingtheoverallnoiselevels,thereisnoguaranteethatmitigationmeasureswouldreduceimpactstoalevelbelowsignificant.Therefore,theReducedProjectAreaAlternativewouldresultinsignificantandimmitigableimpacts.

2.6.6.2 Excessive Groundborne Vibration 

Theprojectwouldnotresultinanysignificantimpactsduetoexcessivegroundbornevibration,andnomitigationmeasuresarerequired.

2.6.6.3 Permanent Increase in Ambient Noise Levels 

Theproposedprojectwouldamendcurrentregulationsrelatedtoaccessoryagriculturalprojectsthatmaydirectlyorindirectlyresultinasubstantialpermanentincreaseinambientnoiselevels(ImpactsN‐2andN‐3,direct/indirectandN‐5,cumulative).Theseimpactswouldremainsignificantandunavoidable.Chapter4,ProjectAlternatives,providesadiscussionofalternativestotheproposedproject.Althoughthiswouldresultinareducedprojectareawithfewernewagriculturalusesreducingtheoverallnoiselevels,thereisnoguaranteethatmitigationmeasureswouldreduceimpactstoalevelbelowsignificant.Therefore,theReducedProjectAreaAlternativewouldresultinsignificantandimmitigableimpacts.

2.6.6.4 Temporary or Period Increase in Ambient Noise Levels  

Theprojectwouldnotresultinanysignificantimpactsduetotemporaryorperiodincreasesinambientnoiselevels,andnomitigationmeasuresarerequired.

2.6.6.5 Airport‐Related Noise Exposure 

Theprojectwouldnotresultinanysignificantimpactsrelatedtoairport‐relatednoiseexposure,andnomitigationmeasuresarerequired.

2.6.7 Conclusion 

2.6.7.1 Excessive Noise Levels 

Implementationoftheproposedaccessoryagriculturalusesundertheproposedprojectwouldresultinsignificantimpactsrelativetonoisereceptors(ImpactsN‐1andN‐4).Thesenoiseimpactswouldremainsignificantandunavoidable.

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2.6.7.2 Excessive Groundborne Vibration 

Theproposedprojectwouldnotresultinasignificantadverseeffectduetoexposingpeopletoorgeneratingexcessivegroundbornevibrationorgroundbornenoiselevels.

2.6.7.3 Permanent Increase in Ambient Noise Levels 

Implementationoftheproposedaccessoryagriculturalusesundertheproposedprojectwouldresultinsignificantimpactsrelativetoapermanentincreaseinambientnoise(ImpactsN‐2,N‐3,andN‐5).

2.6.7.4 Temporary or Periodic Increase in Ambient Noise Levels  

Theproposedprojectwouldnotresultinasignificantadverseeffectduetotemporaryorperiodicincreaseinambientnoiselevels.

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Table 2.6‐1. Hearing Thresholds in the Infrasonic and Low Frequency Range 

Frequency(Hz) 4 8 10 16 20 25 40 50 80 100 125 160 200

Soundpressurelevel(dB)

107 100 97 88 79 69 51 44 32 27 22 18 14

Table 2.6‐2. Typical A‐Weighted Sound Levels Measured in the Environment and Industry 

CommonOutdoorActivitiesSoundLevel(dBA)a CommonIndoorActivities

110 Rockband

Jetflyoverat1,000feet

100

Gaslawnmowerat3feet

90

Dieseltruckat50mphat50feet Foodblenderat3feet

80 Garbagedisposalat3feet

Noisyurbanarea,daytime

Gaslawnmowerat100feet 70 Vacuumcleanerat3feet

Commercialarea Normalspeechat3feet

Heavytrafficat300feet 60

Largebusinessoffice

Quieturbanarea,daytime 50 Dishwasherinnextroom

Quieturbanarea,nighttime 40 Theater,largeconferenceroom(background)

Quietsuburbanarea,nighttime

30 Library

Quietruralarea,nighttime Bedroomatnight,concerthall(background)

Rustlingofleaves 20

Broadcast/recordingstudio

10

0

Source:Caltrans(2009).adBA=A‐WeightedDecibel

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Table 2.6‐3. Guidelines for Determining the Significance of Groundborne Vibration and Noise Impacts for Special Buildings 

TypeofBuildingorRoom

GroundborneVibrationImpactLevels(inches/secondRMS)

GroundborneVibrationImpactLevels(dBre20microPascals)

FrequentEventsa

OccasionalorInfrequentEventsb

FrequentEventsa

OccasionalorInfrequentEventsb

ConcertHalls,TVStudios,andRecordingStudios

0.0018 0.0018 25dBA 25dBA

Auditoriums 0.0040 0.010 30dBA 38dBA

Theatres 0.0040 0.014 35dBA 43dBASource:FTA2006aFrequentEventsisdefinedasmorethan70vibrationeventsperday.Mostrapidtransitprojectsfallintothiscategory.bOccasionalorInfrequentEventsaredefinedasfewerthan70vibrationeventsperday.Thiscombinedcategoryincludesmostcommuterrailsystems.

Table 2.6‐4. San Diego County Noise Ordinance Sound Level Limits (Table 36.404) 

Zone

ApplicableLimit1‐HourAverageSoundLevel(dB)

7a.m.to7p.m. 7p.m.to10p.m. 10p.m.to7a.m.

(1) RS,RD,RR,RHM,A70,A72,S80,S81,S87,S90,S92,RV,andRUwithadensityoflessthan11dwellingunitsperacre

50 50 45

(2) RRO,RC,RM,C30,S86,V5andRVandRUwithadensityof11ormoredwellingunitsperacre

55 55 50

(3) S94,V4,andallothercommercialzones

60 60 55

(4) V1,V2 60 55 Seebelow

V1 60 55 55

V2 60 55 50

V3 70 70 65

(5) M50,M52,andM54 70 70 70

(6) S82,M56,andM58 75 75 75

(7) S88 Source:Caltrans(2009).Note:S88zonesareSpecificPlanningAreaswhichallowdifferentuses.ThesoundlevellimitsabovethatapplyinanS88zonedependontheusebeingmadeoftheproperty.Thelimitsinsubsection(1)applytopropertywitharesidential,agriculturalorcivicuse.Thelimitsinsubsection(3)applytopropertywithacommercialuse.Thelimitsinsubsection(5)applytopropertywithanindustrialusethatwouldonlybeallowedinanM50,M52,orM54zone.Thelimitsinsubsection(6)applytoallpropertywithanextractiveuseorausethatwouldonlybeallowedinanM56orM58zone.

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Table 2.6‐5. Typical Construction Equipment Noise Levels 

Equipment TypicalNoiseLevel(dBA)at50feetfromsource

AirCompressor 81

Backhoe 80

Compactor 82

ConcreteMixer 85

Crane,Derrick 88

Dozer 85

Grader 85

JackHammer 88

Loader 85

Paver 89

Pile‐Drive(Impact) 101

Pump 76

Roller 74

Scraper 89

Truck 88Source:CountyofSanDiego2011a:,2.11‐59.

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Table 2.6‐6. Guideline for Determining the Significance of Groundborne Vibration and Noise Impacts 

LandUseCategory

GroundborneVibrationImpactLevels

(inches/secondRMS)

GroundborneVibrationImpactLevels

(dBre20microPascals)

FrequentEventsa

OccasionalorInfrequentEventsb

FrequentEventsa

OccasionalorInfrequentEventsb

Category1:Buildingswherelowambientvariationisessentialforinterioroperations()researchandmanufacturingfacilitieswithspecialvibrationconstraints)

0.0018c 0.0018c N/A N/A

Category2:Residencesandbuildingswherepeoplenormallysleep(hotels,hospitals,residences,andothersleepingfacilities)

0.0040 0.010 35dBA 43dBA

Category3:Institutionallanduseswithprimarydaytimeuse(schools,churches,libraries,otherinstitutions,andquietuses)

0.0056 0.014 40dBA 48dBA

Source:FTA2006aFrequentEventsisdefinedasmorethan70vibrationeventsperday.Mostrapidtransitprojectsfallintothiscategory.bOccasionalorInfrequentEventsaredefinedasfewerthan70vibrationeventsperday.Thiscombinedcategoryincludesmostcommuterrailsystems.cThiscriterionlimitisbasedonalevelthatisacceptableformostmoderatelysensitiveequipmentsuchasopticalmicroscopes.Vibration‐sensitivemanufacturingorresearchwillrequiredetailedevaluationtodefineacceptablevibrationlevels.EnsuringlowervibrationlevelsinabuildingoftenrequiresspecialdesignonHVACsystemsandstiffenedfloors.