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Central Pointe Mixed -Use Development Project <br />November 9, 2020 <br />Page 9 of 14 <br />the Project -related emissions, existing, existing and projected future emissions from local <br />PM2.5 sources upon the outdoor air concentrations at the Project site. Id. No analysis has <br />been conducted of the significant cumulative health impacts that will result to residents <br />and employees at the Project. <br />Mr. Offermann concludes that this significant environmental impact should be <br />analyzed in an EIR and mitigation measures should be imposed to reduce the risk of <br />formaldehyde exposure. Id., p. 4. Mr. Offermann identifies mitigation measures that are <br />available to reduce these significant health risks, including the installation of air filters and <br />a requirement that the applicant use only composite wood materials (e.g. hardwood <br />plywood, medium density fiberboard, particleboard) for all interior finish systems that are <br />made with CARB approved no -added formaldehyde (NAF) resins in the buildings' <br />interiors. Id., p. 12. <br />Mr. Offermann relies in part on the study by Singer et al. published in 2020 to <br />calculate of the Projects emissions. This study analyzed the indoor concentrations of <br />formaldehyde for homes built between 2011 and 2015, and since only Phase 2 composite <br />wood products were permitted for sale after July 2012, most of the homes in the Singer <br />study were constructed with CARB Phase 2 compliant materials. See id., p. 3. The Singer <br />study shows that homes built after 2009 with CARB Phase 2 Formaldehyde ATCM <br />materials had lower indoor formaldehyde concentrations of 22.4 pg/m3 (18.2 ppb) as <br />compared to a median of 36 pg/m3 found in the 2007 California New Home Study. See id. <br />While these buildings had a lower median formaldehyde concentration and cancer risk, <br />the median lifetime cancer risk for homes built with CARB Phase 2 compliant composite <br />wood products still greatly exceeded the OEHHA 10 in a million cancer risk threshold. Id. <br />Mr. Offermann relies in part on the indoor formaldehyde concentrations determined in the <br />2020 Singer study to conclude that the Project will have similar indoor concentrations of <br />formaldehyde as observed in the Singer study and exceed the CEQA significance <br />threshold for airborne cancer risk because the building materials and furnishings <br />commonly found in homes that release formaldehyde are also found in multi -family <br />residential buildings and commercial buildings. The 2020 Singer study and resulting <br />finding that a project's compliance with CARB Phase 2 compliant materials is not enough <br />to get a project below the cancer risk threshold is new information that was not previously <br />available of substantial importance, which was not known and could not have been known <br />with the exercise of reasonable diligence at the time the 2007 MEMU EIR or the 2018 <br />MEMU SEIR were certified as complete, showing that the Project will have a significant <br />health risk impact from its indoor air quality not discussed in the MEMU EIR. Therefore, <br />the City must prepare a subsequent EIR for the Project. <br />The City has a duty to investigate issues relating to a project's potential <br />environmental impacts, especially those issues raised by an expert's comments. See Cty. <br />Sanitation Dist. No. 2 v. Cty. of Kern, (2005) 127 Cal.AppAth 1544, 1597-98 ("under <br />CEQA, the lead agency bears a burden to investigate potential environmental impacts"). <br />In addition to assessing the Project's potential health impacts to residents and workers, <br />Mr. Offermann identifies the investigatory path that the City should be following in <br />developing an EIR to more precisely evaluate the Projects' future formaldehyde <br />emissions and establishing mitigation measures that reduce the cancer risk below the <br />