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PC - Item 3B - Exhibit F - Appendix A AQ GHG and Energy Urban Planning ■ Due Diligence ■ Entitlements ■ CEQA/NEPA ■ Development Services ■ Management ■ Public Outreach 2355 Main Street, Suite 100 ■ Irvine, CA 92614 949.794.1180 ■ info@epdsolutions.com This technical memorandum presents an analysis of the air quality, energy, and greenhouse gas (GHG) impact for the proposed Mission Villas Residential Development (project), located on Mission Drive east of Walnut Grove Avenue in the City of Rosemead. The project proposes the construction of 29 single family homes and eight townhomes with common open space and landscaping on a 3.435-acre site. The site is mostly vacant, with approximately 2,000 sf of concrete pavement on the south and west side of the project site. To support the CEQA document for the proposed project, this report analyzes the proposed project’s construction and operational impacts to air quality (emission of criterial pollutants) emissions using the California Emissions Estimator Model (CalEEMod v. 2022.1) land use emission model. Table 1 shows the estimated construction schedule, which is expected to last about 11 months. Table 1. Construction Schedule Activity Start Date End Date Total Days Demolition 3/1/2023 3/2/2023 2 Site Preparation 3/3/2023 3/8/2023 5 Grading 3/9/2023 3/17/2023 8 Building Construction 3/18/2023 12/11/2023 230 Paving 12/12/2023 1/1/2024 18 Architectural Coating 1/2/2024 1/22/2024 18 Summary of Air Quality, Energy and GHG Impacts Air Quality: The project’s maximum daily emissions (regional and local) for construction and operation of the project would not exceed SCAQMD’s regional thresholds of significance. In addition, all construction activities would comply with applicable SCAQMD rules and regulations, including Rule 403 to minimize fugitive PM dust emissions, Rule 445 preventing woodfire stoves, and Rule 1113 which allows only Low-Volatile Organic Compounds (VOC) paints. Projects that do not exceed the regional thresholds are assumed to not have a significant impact on a project level and cumulative level. Therefore, the proposed project would have less than significant air quality impacts. Energy: The project’s energy consumption for construction does not have any unusual characteristics and is not less efficient compared with other similar construction sites. The operation of the project is also similar to other residential projects and would comply with Title 24 as well as all applicable City business and energy codes and ordinances. To: City of Rosemead, Planning Division From: Alex J. Garber Date: 7/29/2022 Re: Air Quality, Energy, and Greenhouse Gas Impact Analysis for the Mission Villas Residential Development Mission Villas Residential Development Air Quality/Energy/GHG Summary 2 GHG: Finally, the proposed project’s GHG emissions of 613 MTCO2e per year are below the existing operation and the SCAQMD significance threshold of 3,000 MTCO2e per year for residential projects. Therefore, the project has a less then significant impact on GHG emissions. Air Quality Impact Tables Regional Emissions The SCAQMD has adopted maximum daily emission thresholds1 (pounds/day) for the criteria pollutants during construction and operation of a project. While incremental regional air quality impacts of an individual project are generally very small and difficult to measure, SCAQMDs regional maximum emission thresholds set standards to reduce the burden of SCAQMD to attain and maintain ambient air quality standards. The regional thresholds apply to the criteria pollutants mentioned above and can be found in Table 2 and Table 3 along with the CalEEMod projects emissions. These emission thresholds include the project emissions generated both from onsite sources (such as off-road construction equipment and fugitive dust) and offsite sources (vehicle travel leaving and arriving to the site). As can be seen in Table 2 and Table 3, the project would have less then significant regional air quality impacts. Table 2. Regional Construction Emission Estimates Construction Activity Maximum Daily Regional Emissions (pounds/day) ROG NOx CO SOx PM10 PM2.5 2023 Demolition 2.9 28.3 24.9 0.0 1.7 1.2 Site Prep 4.0 39.7 35.5 0.1 6.9 4.3 Grading 2.1 20.1 20.7 0.0 2.8 1.8 Building Construction 1.4 13.1 15.7 0.0 0.6 0.6 Paving 1.1 8.5 10.5 0.0 0.4 0.4 Maximum Daily Emissions 4.0 39.7 35.5 0.1 6.9 4.3 2024 Paving 1.1 8.2 10.5 0.0 0.4 0.4 Architectural Coating 31.3 1.2 1.5 0.0 0.0 0.0 Maximum Daily Emissions 31.3 8.2 10.5 0.0 0.4 0.4 Maximum Daily Emission 2023-2024 31.3 39.7 35.5 0.1 6.9 4.3 SCAQMD Significance Thresholds 75 100 550 150 150 55 Threshold Exceeded? No No No No No No Table 3. Regional Operational Emission Estimates Operational Activity Maximum Daily Regional Emissions (pounds/day) ROG NOx CO SOx PM10 PM2.5 Area 2.2 0.6 2.4 0.0 0.1 0.1 Energy 0.0 0.6 0.3 0.0 0.1 0.1 Mobile 1.3 1.1 11.6 0.0 0.9 0.2 Total Project Operational Emissions 3.5 2.4 14.2 0.0 1.0 0.3 SCAQMD Significance Thresholds 55 55 550 150 150 55 Threshold Exceeded? No No No No No No Local Emissions 1 SCAQMD April 2019. Found at http://www.aqmd.gov/docs/default-source/ceqa/handbook/scaqmd-air-quality- significance-thresholds.pdf Mission Villas Residential Development Air Quality/Energy/GHG Summary 3 Localized significance thresholds (LSTs) were also adopted by the SCAQMD due to project-related construction or operational air emissions having the potential to exceed the state and national air quality standards in the project vicinity, while not exceeding the regional emission significance thresholds adopted by the SCAQMD. These thresholds set the maximum rates of daily construction or operational emissions from a project site that would not exceed a national or State ambient air quality standard2. The differences between regional thresholds and LSTs are as follows: 1. Regional thresholds include all sources of project construction and operational emissions generated from onsite and offsite emission sources whereas the LSTs only consider the emissions generated from onsite emission sources. 2. LSTs only apply to CO, NOx, PM10, and PM2.5, while regional thresholds include both ROG and SOx. 3. Regional Thresholds apply to emission sources located anywhere within the SCAQMD whereas the LSTs are location dependent and also depend on the size of the project, and emission location relative to the nearest sensitive receptor. A sensitive receptor is defined as an individual who is most susceptible to negative health affects when exposed to air pollutants including children, the elderly, and adults with chronic health issues. Such receptors include residences, schools, elderly care centers, and hospitals. SCAQMD provides screening look up tables (Appendix C of the SCAQMD 2008 Final Localized Significance Threshold Methodology)3 for projects that disturb less than or equal to 5 acres in size in a day. These tables were created to easily determine if the daily emissions of NOx, CO, PM10, and PM2.5 from a project could result in a significant impact to the local air quality. The thresholds are determined by: • Source receptor area (SRA), the geographic area within the SCAQMD that can act as both a source of emissions and a receptor of emission impacts (project is located within SRA 11, South San Gabriel Valley), • Size of the project, • Distance to the nearest sensitive receptor. The phase with the most ground disturbance would be the grading phase, which would grade 2.5 acres per day. The thresholds for 2 acres from Appendix C were used for a conservative analysis. Distance to the nearest sensitive receptor also determines the emission thresholds. The sensitive receptors closest to the project include residential homes northwest of the project boundary, about 1.35 meters (4.43 feet) from the property line. These receptors (distance from the project property line to the residential structure) are less than the minimum distance provided in the lookup tables (25 meters). Therefore, 25 meters (82 feet) was used. Table 4 shows the thresholds and estimated maximum daily construction emissions for the proposed project. As seen in Table 4, the proposed project has a less then significant localized construction air quality impact. 2 SCAQMD 2008: Final Localized Significance Threshold Methodology. Referenced on 9/3/2020 at http://www.aqmd.gov/docs/defaultsource/ceqa/handbook/localized-significance-thresholds/final-lst- methodology-document.pdf 3 SCAQMD 2008: Final Localized Significance Threshold Methodology Appendix C. Referenced on 9/16/2020 at http://www.aqmd.gov/docs/default-source/ceqa/handbook/localized-significance-thresholds/appendix-c-mass- rate-lst-look-up-tables.pdf?sfvrsn=2 Mission Villas Residential Development Air Quality/Energy/GHG Summary 4 Table 4. Localized Construction Emission Estimates Construction Activity Maximum Daily Regional Emissions (pounds/day) NOx CO PM10 PM2.5 2022 Demolition 27.3 23.5 1.7 1.2 Site Prep 39.7 35.5 6.9 4.3 Grading 20.0 19.7 2.8 1.8 Building Construction 12.8 14.3 0.6 0.6 Paving 8.5 10.5 0.4 0.4 Maximum Daily Emissions 39.7 35.5 6.9 4.3 2023 Paving 8.2 10.5 0.4 0.4 Architectural Coating 1.2 1.5 0.0 0.0 Maximum Daily Emissions 8.2 10.5 0.4 0.4 Maximum Daily Emission 2023-2024 39.7 35.5 6.9 4.3 SCAQMD Significance Thresholds 121 1,031 7 5 Threshold Exceeded? No No No No According to the SCAQMD LST methodology, LSTs apply to project stationary mobile sources. Projects that involve mobile sources that spend long periods queuing and idling at a site, such as transfer facilities or warehousing and distribution buildings, have the potential to exceed the operational localized significance thresholds. The proposed project would operate 37 residential units, which do not involve vehicles idling or queueing for long periods. Therefore, due to the lack of significant stationary source emissions, impacts related to operational localized significance thresholds would be less than significant. Energy The State CEQA Guidelines do not have specific thresholds for Energy consumption. Rather, the question in Appendix G: VI Energy (a) asks, “[Does the proposed project] Result in potentially significant environmental impact due to wasteful, inefficient, or unnecessary consumption of energy resources during project construction or operation?”. Therefore, for the purpose of this analysis, a significant impact would occur if: • The Project design and/or location encourages wasteful, inefficient, and unnecessary consumption of energy, especially fossil fuels such as coal, natural gas, and petroleum, as well as the use of fuel by vehicles anticipated to travel to and from the project. The following assumptions were used to calculate the energy consumption of the proposed project: • The project’s construction and operational energy consumption would be provided by Southern California Edison Company. • Construction equipment fuel consumption derived from ARB Offroad2021 emission model • Fuel Consumption from vehicle travel derived from ARB EMFAC2021 emission model • Electrical and natural gas usage derived from the CalEEMod model Construction Electricity and Natural Gas Usage: Due to the project size and the fact that construction is temporary, the electricity used would be substantially less than that required for project operation and would have a negligible contribution to the project’s overall energy consumption. The electric power used would be for as-necessary lighting and electronic equipment such as computers inside temporary construction trailers. Natural gas is not anticipated to be needed for construction activities. Any consumption of natural gas would be minor and negligible in comparison to the operation of the proposed project. Petroleum Fuel Usage: Mission Villas Residential Development Air Quality/Energy/GHG Summary 5 The construction equipment associated with construction activities (off-road/heavy duty vehicles) would rely on diesel fuel as would vendor and haul trucks involved in delivering building materials and removing the demolition debris from the project site. Construction workers would travel to and from the project site throughout the duration of construction, and for a conservative analysis it is assumed that construction workers would travel in gasoline-powered passenger vehicles. Table 5 shows the total fuel consumption and horsepower-hour data contained within the ARB OffRoad2021 emission model for specific types of diesel construction equipment. It should be noted that the total fuel consumption is a conservative analysis and would likely overstate the amount of fuel usage, as specific construction equipment is not expected to operate during the duration of the construction activity (i.e., crane). Table 6 summarizes the project’s construction vehicle fuel usage based on vehicle miles traveled and fuel usage factors contained in the ARB EMFAC2021. The trips included are worker vehicles, vendor vehicles, and haul vehicles. Table 7 shows the overall fuel consumption for construction of the proposed project. Mission Villas Residential Development Air Quality/Energy/GHG Summary 6 Table 5. Construction Equipment Fuel Usage Activity Equipment Number Hours per day Horse- power Load Factor Days of Construction Total Horsepower- hours Fuel Rate (gal/hp-hr) Fuel Use (gallons) Demolition Rubber Tired Dozers 2 8 367 0.4 2 4,698 0.020615155 97 Concrete/Industrial Saws 1 8 33 0.73 2 385 0.041912413 16 Excavators 3 8 36 0.38 2 657 0.019868435 13 Site Preparation Rubber Tired Dozers 3 8 367 0.4 5 17,616 0.020615155 363 Tractors/Loaders/Backhoes 4 8 84 0.37 5 4,973 0.019155948 95 Grading Graders 1 8 148 0.41 8 3,884 0.021167864 82 Excavators 1 8 36 0.38 8 876 0.019868435 17 Tractors/Loaders/Backhoes 3 8 84 0.37 8 5,967 0.019155948 114 Rubber Tired Dozers 1 8 367 0.4 8 9,395 0.020615155 194 Model Building Construction Cranes 1 8 367 0.29 230 195,831 0.014896922 2,917 Forklifts 3 8 82 0.2 230 90,528 0.010444038 945 Generator Sets 1 8 14 0.74 230 19,062 0.042356362 807 Tractors/Loaders/Backhoes 1 8 84 0.37 230 57,187 0.019155948 1,095 Welder 3 8 46 0.45 230 114,264 0.025848623 2,954 Paving Tractors/Loaders/Backhoes 1 8 84 0.37 18 4,476 0.019155948 86 Cement and Mortar Mixers 2 8 10 0.56 18 1,613 0.019767572 32 Pavers 1 8 81 0.42 18 4,899 0.021536901 106 Paving Equipment 2 8 89 0.36 18 9,228 0.01846541 170 Rollers 2 8 36 0.38 18 3,940 0.019837453 78 Architectural Coating Air Compressors 1 8 78 0.48 18 5,391 0.027606329 149 Total 10,233 Mission Villas Residential Development Air Quality/Energy/GHG Summary 7 Table 6. Estimated Project Vehicle Fuel Usage Construction Source Number VMT Fuel Rate Gallons of Diesel Fuel Gallons of Gasoline Fuel Haul Trucks 56 1,120 5.96 188 0 Vendor Trucks 4 9,384 8.87 1,058 0 Worker Vehicles 72 80,179 25.91 0 3,095 Total 1,246 3,095 Table 7. Total Construction Fuel Usage Construction Source Gallons of Diesel Fuel Gallons of Gasoline Fuel Construction Vehicles 1,246 3,095 Off-road Construction Equipment 10,233 0 Total 11,479 3,095 Operation The operation of the proposed project would consume electricity, natural gas, and petroleum. The net energy consumption can be found in Table 8 below. Electricity and natural gas consumption were found in the Annual CalEEMod Output Sheets attached. The gasoline consumption rates utilize the same assumptions that were used for the worker vehicles. Table 8. Annual Operational Energy Requirements Operational Source Energy Usage Electricity (Kilowatt-Hours) Project 252,539 Natural Gas (Thousands British Thermal Units) Project 1,242,170 Petroleum (gasoline) Consumption Annual VMT Gallons of Gasoline Fuel Project 1,127,736 43,533 Conclusion The proposed project has no unusual characteristics that would make the construction fuel and energy consumption associated with construction of the project less efficient compared with other similar construction sites throughout the state. The consumption would also be temporary and localized. Operation of the 29 single family and eight townhome residential units would comply with all the energy efficiency requirements under Title 24 and all applicable City business and energy codes ordinances. Therefore, the construction and operation of the project would result in a less than significant impact for inefficient, wasteful, or unnecessary energy use, and no mitigation would be required. Greenhouse Gas SCAQMD has convened a Greenhouse Gas Emissions (GHG) CEQA Significance Threshold Working Group to help lead agencies determine significance thresholds for GHG emissions when SCAQMD is not the lead agency. The last working group was held September 2010 (Meeting No. 15)4 and proposed a tiered approach, equivalent to the existing consistency determination requirements in CEQA Guidelines Sections 15064(h)(3), 15125(d), or 15152(a). The most recent proposal issued in Meeting No. 15 uses a tiered approach, Tier 1 to Tier 5, to evaluate potential GHG impacts from various uses. This assessment will apply 4 SCAQMD 2010. Minutes of the GHG CEQA Significance Threshold Stakeholder Working Group #15. Referenced on 9/21/2020 at: http://www.aqmd.gov/docs/default-source/ceqa/handbook/greenhouse-gases-(ghg)-ceqa- significance-thresholds/year-2008-2009/ghg-meeting-15/ghg-meeting-15-minutes.pdf Mission Villas Residential Development Air Quality/Energy/GHG Summary 8 the Tier 3: Numerical Screening Thresholds approach. Tier three consists of screening values in metric tons of carbon dioxide equivalent (MTCO2e) (converting other greenhouse gasses to an equivalent impact of CO2), which the lead agency can choose, but must be consistent with all projects within its jurisdiction. A project’s construction emissions are averaged over 30 years and are added to the project’s operational emissions. If a project’s emissions are below one of the following screening thresholds, then the project impact would be is less than significant: • Option 1: All land use types: 3,000 MTCO2e per year • Option 2: Based on land use type: residential: 3,500 MTCO2e per year; commercial: 1,400 MTCO2e per year; or mixed use: 3,000 MT CO2e per year Executive Order S-3-05’s year 2050 goal is the basis of SCAQMD’ draft Tier 3 screening level thresholds. The objective of the Executive Order is to contribute to capping worldwide CO2 concentrations at 450 ppm, stabilizing global climate change. The City of Tustin utilizes Option 1, and therefore the threshold is 3,000 MTCO2e per year. The project’s construction GHG emissions are shown in Table 9 and the overall construction and operational emissions are shown in Table 10 These emissions were calculated using the CalEEMod Model. The construction emissions are amortized over 30 years. As shown in Table 10, the net GHG emissions are 613 MTCO2e per year, below the existing operation and the 3,000 MTCO2e per year. Therefore, the project would have a less than significant GHG impact. Table 9. Project Construction GHG Emissions Activity Annual GHG Emissions (MTCO2e) 2023 369 2024 2 Total Emissions 371 Total Emissions Amortized Over 30 Years 12 Table 10. Total GHG Emissions Activity Annual GHG Emissions (MTCO2e) Project Operational Emissions Mobile 412 Area 10 Energy 172 Water 4 Waste 3 Total Project Gross Operation Emissions 601 Project Construction Emissions 12 Total Emissions 613 Significance Threshold 3,000 Threshold Exceeded? No Mission Villas Residential Development Air Quality/Energy/GHG Summary 9 Figure 1: Project Site Plan Mission Villas Residential Development Air Quality/Energy/GHG Summary 10 CalEEMod Output Sheets Mission Villas Residential Development Air Quality/Energy/GHG Summary 11 Fuel Calculations