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AgdaPkt 2017-04-03 Joint SA PFA
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AgdaPkt 2017-04-03 Joint SA PFA
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Last modified
5/11/2017 10:44:41 AM
Creation date
3/30/2017 4:41:02 PM
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Template:
CC Index
CC Index - Document Type
Agenda Packet
Meeting Type
Joint
Agency Type
City Council and Successor Agency and Public Financing Authority
Date
4/3/2017
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Attachment 1: Health Impact Evaluation Methodology <br /> <br />A health risk assessment (HRA) for exposure to TACs requires the application of a risk characterization model to <br />the results from the air dispersion model to estimate potential health risk at each sensitive receptor location. The <br />State of California Office of Environmental Health Hazard Assessment (OEHHA) and CARB develop <br />recommended methods for conducting health risk assessments. The most recent OEHHA risk assessment guidelines <br />were published in February of 2015.19 These guidelines incorporate substantial changes designed to provide for <br />enhanced protection of children, as required by State law, compared to previous published risk assessment <br />guidelines. CARB has provided additional guidance on implementing OEHHA’s recommended methods.20 This <br />health risk assessment used the recent 2015 OEHHA risk assessment guidelines and CARB guidance. While the <br />OEHHA guidelines use substantially more conservative assumptions than the current BAAQMD guidelines, <br />BAAQMD has not formally adopted recommended procedures for applying the newest OEHHA guidelines. <br />BAAQMD is in the process of developing new guidance and has developed proposed HRA Guidelines as part of the <br />proposed amendments to Regulation 2, Rule 5: New Source Review of Toxic Air Contaminants.21 Exposure <br />parameters from the OEHHA guidelines and newly proposed BAAQMD HRA Guidelines were used in this <br />evaluation. <br /> <br />Cancer Risk <br /> <br />Potential increased cancer risk from inhalation of TACs are calculated based on the TAC concentration over the <br />period of exposure, inhalation dose, the TAC cancer potency factor, and an age sensitivity factor to reflect the <br />greater sensitivity of infants and children to cancer causing TACs. The inhalation dose depends on a person’s <br />breathing rate, exposure time and frequency of exposure, and the exposure duration. These parameters vary <br />depending on the age, or age range, of the persons being exposed and whether the exposure is considered to occur at <br />a residential location or other sensitive receptor location. <br /> <br />The current OEHHA guidance recommends that cancer risk be calculated by age groups to account for different <br />breathing rates and sensitivity to TACs. Specifically, they recommend evaluating risks for the third trimester of <br />pregnancy to age zero, ages zero to less than two (infant exposure), ages two to less than 16 (child exposure), and <br />ages 16 to 70 (adult exposure). Age sensitivity factors (ASFs) associated with the different types of exposure are an <br />ASF of 10 for the third trimester and infant exposures, an ASF of 3 for a child exposure, and an ASF of 1 for an <br />adult exposure. Also associated with each exposure type are different breathing rates, expressed as liters per <br />kilogram of body weight per day (L/kg-day). As recommended by the BAAQMD, 95th percentile breathing rates are <br />used for the third trimester and infant exposures, and 80th percentile breathing rates for child and adult exposures. <br />Additionally, CARB and the BAAQMD recommend the use of a residential exposure duration of 30 years for <br />sources with long-term emissions (e.g., roadways). <br /> <br />Under previous OEHHA and BAAQMD HRA guidance, residential receptors are assumed to be at their home 24 <br />hours a day, or 100 percent of the time. In the 2015 Risk Assessment Guidance, OEHHA includes adjustments to <br />exposure duration to account for the fraction of time at home (FAH), which can be less than 100 percent of the time, <br />based on updated population and activity statistics. The FAH factors are age-specific and are: 0.85 for third <br />trimester of pregnancy to less than 2 years old, 0.72 for ages 2 to less than 16 years, and 0.73 for ages 16 to 70 years. <br />BAAQMD recommends using these FAH factors for residential exposures. <br /> <br />Functionally, cancer risk is calculated using the following parameters and formulas: <br /> <br />Cancer Risk (per million) = CPF x Inhalation Dose x ASF x ED/AT x FAH x 106 <br />Where: <br />CPF = Cancer potency factor (mg/kg-day)-1 <br /> ASF = Age sensitivity factor for specified age group <br /> <br />19 OEHHA, 2015. Air Toxics Hot Spots Program Risk Assessment Guidelines, The Air Toxics Hot Spots Program Guidance <br />Manual for Preparation of Health Risk Assessments. Office of Environmental Health Hazard Assessment. February. <br />20 CARB, 2015. Risk Management Guidance for Stationary Sources of Air Toxics. July 23. <br />21 BAAQMD, 2016. Workshop Report. Proposed Amendments to Air District Regulation 2, Rule 5: New Source Review of <br />Toxic Air Contaminants. Appendix C. Proposed Air District HRA Guidelines. January 2016. <br /> <br />8.A. - Page 96
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