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� � 3 <br /> �!„ q �E"i � t <br /> . . � t �a t '4"� $•v,. <br /> :�i dt F i .. _. ''�� �# 7 <br /> r`' � .��si� ,. R . _ _. ���E�a «��1�< e.. ��.—� ?��Wx� ,.a.� � �,5 a ,.1�a.1'��. <br /> y <br /> 5.2 Air Quality and Health Risk <br /> Context: To assess whether the Project would have project-level <br /> The IHSP EIR would have described � �mpacts or contribute to any cumulative impact,ESA will: �ssumptions: <br /> the IHSP air quality setting that would � ; . Air quality and health risk <br /> aiso apply to the Project,specifically ' Construction � effects from TACs will be <br /> information regarding the attainment � � based on BAAQMD <br /> status for the state and federal ' • For construction health risk,ESA will qualitatively discuss `= 2010/2011 thresholds and <br /> ambient air quality standards for ` the potential for concentrations of diesel particulate matter CEQA Guidelines. <br /> ozone and particulate matter,and for � (DPM)and fine particulates(PM2.5)for construction to pase <br /> carbon monoxide;ambient particulate ! lifetime cancer nsk to the nearest sensitive receptors.ESA . The Project would be <br /> standards and policies and Best ; anticipates that the risk from construction TACs would be developed in phases,but <br /> Practices relevant to construction screened out from the EIR due to the distance of the project fully completed and <br /> activities;sources of toxic air � site from the nearest potential receptors,which are operational by 2040. <br /> contaminants(TACs);and existing or � residential and various uses that could occur within the <br /> planned sources of odors.The IHSP ; inner Harbor-1(IH-1)area of the IHSP(approximately 1,000 • No odor-producing uses are <br /> EIR will also have identified potential feet from the project site or IH-2 area).The assessment will proposed. <br /> program level effects and mitigation present the necessary information to demonstrate the . The IHSP could result in <br /> measures. potential for adverse risk during construction. � outdoor reaeation uses <br /> Construction activities and operation ± Q rations E within the Open Space(OS) <br /> of the Project would generate air � or Public Facilities(PF) <br /> pollutant emissions,potentially in • The analysis will present the daily opera6onal emissions of � areas of the IHSP. <br /> proximity to future sensitive receptors. ;, ROG,NOX,PM�o and PMzs for the Pro�ect and current ' Development of the Project <br /> significance thresholds for each.The analysis will input the is assumed to be <br /> The Project would be developed in an 's', Project vehide trip generation rates(provided in the Traffic constructed prior to the <br /> area that includes existing emissions Study)into CaIEEMod(Version 2013.2.2),accounting for development of new <br /> generating uses,including heavy any modal split adjustment factors. potential outdoor reaeation <br /> industrial uses,nearby highways and ; , Conduct an assessment of potential cumulative exposure to uses. <br /> active railroad tracks. localized excess cancer risks from existing sources of diesel ; <br /> The Project is not considered to ` particulate matter(DPM)as well as increases in fine <br /> include sensitive receptors(e.g., � particulate matter(PM2.5)concentrations at proposed <br /> residences,schools,medical facilities), sensitive receptors.ESA does not propose to conduct a <br /> nor are sensitive receptor existing or � model run for TAC assessment;it will apply the BAAQMD <br /> proposed in proximity to the project methodology of assessing TAC impacts based on the <br /> site. cumulative contribution of data provided by BAAQMD. <br /> ''' • ESA will apply the CaIEEMod defaults for all other inputs <br /> (except that any fireplaces will be assumed to be natural <br /> gas-fired only.ESA will also modify default inputs for any <br /> project-spec��c inputs that the project sponsor may provide. <br /> • Identify any sources of TACs associated with the Project <br /> itself,however,because the Project dces not include <br /> sensitive receptors,ESA will not conduct a model run or <br /> BAAQMD methodology to assess TAC impacts to proposed <br /> on-site receptors. <br /> _ _ --�-�... -- - - - - -- .. __ �....�. <br /> 5.3 Biological Resources <br /> Context: To assess whether the Project would have project-level �Assumptions: <br /> The IHSP EIR would have described ! �mpacts or contribute to any cumulative impact,ESA will: � . No protocol-level surveys for <br /> the IHSP biological resources setting � state or federally listed <br /> that would also apply to the Project, • Speafy any special status species habitats on the project � wildlife will be required for <br /> specifically information re�arding site,conduct a habitat-level site reconnaissance survey to ! this project-level analysis. <br /> special status species habitats;federal, ; identify and characterize any terrestrial biological : <br /> state,and local policies and regulations ' communities within and adjacent to the Project site,and if ` • No formal wetland <br /> (State and federal Endangered Species '; any exists,assess their potential to support sensitive plants, � delineation will be required <br /> Acts,MacAteer-Petns Act,Section 404 ; wildlife and their habitat.To ensure project-level clearance, � <br /> and 401 of the Clean Water Act,Rivers : the plan-level reconnaissance conducted for the Baseline <br /> � arbors Act,Mi rato Bird Trea Study m support of the IHSP wiil be refined to address the <br /> and H g ry ty � <br /> REV:06-15-15 VR <br /> Page 10 of 18 <br /> ATTY/AGR.Amend No. 2/ESA Inner Harbor EIR Amendment No.2 <br />