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Screening Health Risk Assessment for 3370 Hopyard Road Project As shown,the maximum combined cancer risk and PM2.5 impacts from combined off-site sources of TAC emissions is estimated to result in impacts to sensitive receptors less than the thresholds of significance. As a result, impacts would be considered less than significant. References Bay Area Air Quality Management District(BAAQMD), 2009. CEQA Thresholds Options and Justification Report,(2009). Available: http://www.baagmd.gov/—/media/files/planning-and-research/cega/revised- draft-ceqa-thresholds justification-report-oct-2009.pdf?la=en. Accessed December 2017. , 2012a. California Environmental Quality Act Air Quality Guidelines,(2012). Available: http://www.baagmd.gov/plans-and-climate/california-environmental-quality-act-cega/updated-ceqa- guidelines. Accessed December 2017. , 2012b. Stationary Source Screening Analysis Tool, (2012). Available: http://www.baagmd.gov/plans-and-climate/california-environmental-quality-act-cega/cega-tools. Accessed December 2017. ,2015. Roadway Screening Analysis Calculator,(2015). Available: http://www.baagmd.gov/plans- and-climate/california-environmental-quality-act-cega/cega-tools. Accessed December 2017. , 2017. California Environmental Quality Act Air Quality Guidelines,(2017). Available: http://www.baagmd.gov//media/files/pl anni ng-and-research/cega/cega_gu i del i nes_may2017- pdf.pdf?la=en. Accessed December 2017. City of Pleasanton, General Plan—2005 Pleasanton Plan 2025, Circulation Element,(2005). Federal Highway Administration(FHWA), 2017. Time-of-Day Modeling Procedures: State-of-the-Practice, State-of-the-Art, (2017).Available at: http://www.fhwa.dot.gov/planning/tmip/publ ications/other_reports/tod_model ing_procedures/ch02.cfm. Accessed December 2017. CWIN\53247\1016910.1/Yountville Hill Winery Project 5 ESA/MSRGOO1AQ