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<br />Sequoia Ecological Consulting, Inc. <br />CalVTP Project-Specific Analysis and Addendum <br />Augustin Bernal Community Park Fuel Reduction <br />November 2025 <br />4-13 <br /> <br /> <br />4.3.1.3. Impact AQ-3 <br />This impact does not apply to the treatment project because no NOA, ultramafic rock outcrops, serpentine <br />soils, or former asbestos mines are mapped in or near the treatment area, and no serpentine soils or <br />serpentine outcrops were observed during biological reconnaissance surveys (USGS 2011, 2017; Sequoia <br />2025). <br />4.3.1.4. Impact AQ-4 <br />Prescribed burning during initial and maintenance treatments could expose people to toxic air <br />contaminants. The potential to expose people to toxic air contaminants from prescribed burning was <br />examined in the PEIR and found to be potentially significant because such burns release smoke containing <br />fine particulate matter and other harmful compounds that can affect respiratory and cardiovascular <br />health, especially in areas near sensitive populations or regions already experiencing poor air quality. The <br />duration and parameters of the prescribed burns are within the scope of the activities addressed in the <br />PEIR, and within the BAAB, air quality conditions are consistent with those analyzed in the PEIR for <br />Alameda County and Pleasanton. Therefore, the potential for exposure to toxic air contaminants is also <br />within the scope of the PEIR. SPRs applicable to these treatment activities are AD-4, AQ -1, AQ -2, AQ -3, <br />and AQ-6. All feasible measures to prevent and minimize smoke emissions, as well as exposure to smoke, <br />are included in SPRs; however, this impact would remain significant and unavoidable, as explained in the <br />PEIR. <br />The inclusion of approximately 93 acres of land that is outside the CalVTP treatable landscape in the <br />proposed treatment area constitutes a change to the geographic extent presented in the PEIR. However, <br />within the boundary of the project area, the air quality conditions present and air basin in the areas <br />outside the treatable landscape are essentially the same as those within the treatable landscape. <br />Therefore, the air quality impact is also the same, as described above. This determination is consistent <br />with the PEIR and would not constitute a substantially more severe significant impact than what was <br />covered in the PEIR. <br />4.3.1.5. Impact AQ-5 <br />The use of vehicles and mechanical equipment during initial and maintenance treatments could expose <br />people to objectionable odors from diesel exhaust. The PEIR determined that the potential for exposing <br />individuals to diesel exhaust odors is less than significant, as these odors are typically short-lived, confined <br />to specific areas, and classified as nuisance pollutants rather than health risks. Additionally, treatment <br />activities are brief and spread out, reducing the likelihood of sustained exposure near sensitive locations. <br />This impact is within the scope of the PEIR because the exposure potential and the proposed activities, as <br />well as the associated equipment and duration of use, are consistent with those analyzed in the PEIR. SPRs