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8. B. - Page 179 <br /> Resqonse A-11: The City in no way disnussed Clarlc's or BAAQNIDs fu�dings. Dr. Clarlc's <br /> coinments and opiiuons were ca�efi�lly considered by the City in light of BAAQNID's <br /> guidelines and methodology. The Final EIR discL�ssed in detail why the City a��d the City's <br /> air quality expei�t believe Dr. Clark's a��alysis to be flawed a��d provided detailed <br /> expla��ations on the EIR analysis which is based on BAAQMD guidelines (pages 42-46 and <br /> 59-70). As noted above, the City's air quality expert is based u� the Bay Area a��d has <br /> prepared numerous studies of this type throughout tlie Bay Area in fi�ll accordance with <br /> BAAQNID guidelines a�1d is thoroughly versed with the reqi�irements a�ld methodologies of <br /> BAAQNID. The proposed project is not Luuque or even unusual in regards to other housing <br /> projects along major roadways in the Bay Area atid the atialysis completed for the proposed <br /> project was prepared in the same maiu�er as all other a��alyses of this type completed by the <br /> City's e�pert. There was nothiiig in Dr. Clarlc's original coimnents that deinonstrated the <br /> City L�sed faL�lty methodology in its analysis a��d fl�e fact that Dr. Clark, using different <br /> inethodology and assumptions, arrived at a different conclusion in no way invalidates the <br /> City's analysis, which concluded the fi�ture project residents would be exposed to air toxic <br /> enussions just below BAAQMD's pL�blished thresholds. <br /> Comment A-12: The Air Quality Analysis Utilizes Contradictoiy Methodology a�7d Underestimates <br /> TAC Impacts. <br /> The City L�sed two different mefl�odologies to calculate TAC enussions dL�ring the construction phase <br /> and the operational phase of fl�e Project. There was no explanation as to why the City adopted two <br /> differing methodologies. According to Clark, the methodology adopted by the City to a��alyze <br /> impacts during the operational phase is flawed a�1d underestimates the Project impacts. <br /> To a�7alyze operational impacts, the City applied the Sensitivity Weightu7g Factor (SWF) to the <br /> cancer risk ulstead of tlie enzission rc�te for each year. The SWF is the age sensitivity factor <br /> inL�ltiplied by the length of exposure divided by the 70 year life spa�l. The nus�ipplic�ition of the <br /> SWF to the cancer rislc instead of the emission rate Lu�derestimates the potential health risk from <br /> roadway einissions. <br /> The problem with applying the SWF' to the ca�lcer risk instead of the emission rate is that according <br /> to the BAAQMD the age sensitivity factors are designed to u�crease to the 70 ye�cr �aver�age <br /> coficentr�ation of cheinicals to be a��alyzed. Accordulg to BAAQMD gL�ida��ce, u� order to estimate <br /> the 70-yea� a�erage enussions, the user would generally average the enussions e�tracted from the <br /> EMFAC model. BAAQMD reconunends a three step process that reqL�ires a sigiufica�lt number of <br /> compL�tations. <br /> Step 1. The first step is to develop sensitivity weightulg factors (SWF) that are the age <br /> sensitivity valL�es mL�ltiplied by the duration of fl�e exposure by the lifetime of the exposure. <br /> This is expressed as: <br /> Sensitivity Weighing Factor = ASF x Length of E�posure (year) / 70 year lifespan. <br /> The City complied with this step as Shov�nl in Appendix G. <br /> Step 2. The user then estimates 70 ye«r aver�ige erriission r«tes (emphasis added) by <br /> multiplying each SWF by fl�e corresponding emissions (grains/vehicle nule) for that year. <br /> 2580 El Cainino Real Residenrial Project 11 Response to Conmients Recei��ed on Final EIR <br /> Cin� of Red��ood Cin� Jannai� 2012 <br />