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Volatile Organic Chemical Emissions for Indoor Sources Using Environmental <br />Chambers," (CDPH, 2017), and use the procedure described earlier above (i.e. Pre - <br />Construction Building Material/Fumishing Formaldehyde Emissions Assessment) to <br />insure that the materials selected achieve acceptable cancer risks from material off gassing <br />of formaldehyde. <br />Outdoor Air Ventilation Impact. Another important finding of the CNHS, was that the <br />outdoor air ventilation rates in the homes were very low. Outdoor air ventilation is a very <br />important factor influencing the indoor concentrations of air contaminants, as it is the <br />primary removal mechanism of all indoor air generated contaminants. Lower outdoor air <br />exchange rates cause indoor generated air contaminants to accumulate to higher indoor air <br />concentrations. Many homeowners rarely open their windows or doors for ventilation as a <br />result of their concerns for security/safety, noise, dust, and odor concerns (Price, 2007). In <br />the CNHS field study, 32% of the homes did not use their windows during the 24-hour Test <br />Day, and 15% of the homes did not use their windows during the entire preceding week. <br />Most of the homes with no window usage were homes in the winter field session. Thus, a <br />substantial percentage of homeowners never open their windows, especially in the winter <br />season. The median 24-hour measurement was 0.26 air changes per hour (ach), with a range <br />of 0.09 ach to 5.3 ach. A total of 67% of the homes had outdoor air exchange rates below <br />the minimum California Building Code (2001) requirement of 0.35 ach. Thus, the relatively <br />tight envelope construction, combined with the fact that many people never open their <br />windows for ventilation, results in homes with low outdoor air exchange rates and higher <br />indoor air contaminant concentrations. <br />The 4"' and Mortimer Project located in Santa Ana, CA is close to roads with moderate to <br />high traffic (e.g., E. 4th Street, E. 5"' Street, French Street, Mortimer Street, and N. Minter <br />Street, etc.) as well as close to the AT&SF rail line. As a result of the outdoor vehicle traffic <br />noise, the Project site is likely to be a sound impacted site. <br />According to the 41' and Mortimer Project —Environmental Impact Report Addendum, SCH <br />#2006071100, (City of Santa Ana, 2020) the ambient noise level exceeds 65 dBA CNEL. <br />796145 <br />