A - Ex B Final EIR — San Leandro City Council, May 5, 2025 (part 2 of 3)

Access to the project site would be from the existing driveway on Doolittle Drive in the southwest area of the site, and from an existing driveway the end of Hester Street in the northern area of the site. The proposed project would include reconstruction of the driveways to meet City standards and current ADA requirements. Additionally, a new, second, driveway to the site would be constructed at the end of Hester Street, providing a total of three driveways. A total of 204 parking spaces would be provided on-site for passenger vehicles, which would be located primarily in a new surface parking lot on the west side of the proposed building. Approximately 59 parking spaces sized for tractor trailers would be on the north side of the warehouse. A total of 24 bicycle parking spaces would be provided.

The project would require a Use Permit, Site Plan Review, Height Exception, Building Permit, Grading Permit, and Tree Removal Permit.

The project may also require approval(s) from the Federal Aviation Administration and the Department of Toxic Substances Control.

NOA of DEIR, p. 1.

Local 713 represents thousands of union carpenters in Alameda County and has a strong interest in well-ordered land use planning and in addressing the environmental impacts of development projects.

Individual members of Local 713 live, work, and recreate in the City and surrounding communities and would be directly affected by the Project’s environmental impacts.

Local 713 expressly reserves the right to supplement these comments at or prior to hearings on the Project, and at any later hearing and proceeding related to this Project.

Gov. Code, § 65009, subd. (b); Pub. Res. Code, § 21177, subd. (a); see Bakersfield Citizens for Local Control v. Bakersfield (2004) 124 Cal.App.4th 1184, 1199-1203; see also Galante Vineyards v. Monterey Water Dist. (1997) 60 Cal.App.4th 1109, 1121.

Local 713 incorporates by reference all comments related to the Project or its CEQA review, including the Environmental Impact Report. See Citizens for Clean Energy v City of Woodland (2014) 225 Cal.App.4th 173, 191 (finding that any party who has objected to the project’s environmental documentation may assert any issue timely raised by other parties).
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Moreover, Local 713 requests that the City provide notice for any and all notices referring or related to the Project issued under the California Environmental Quality Act (CEQA) (Pub. Res. Code, § 21000 et seq.), and the California Planning and Zoning Law (“Planning and Zoning Law”) (Gov. Code, §§ 65000–65010). California Public Resources Code Sections 21092.2, and 21167(f) and California Government Code Section 65092 require agencies to mail such notices to any person who has filed a written request for them with the clerk of the agency’s governing body.

I. THE CITY SHOULD REQUIRE THE USE OF A LOCAL
WORKFORCE TO BENEFIT THE COMMUNITY’S ECONOMIC

DEVELOPMENT AND ENVIRONMENT
The City should require the Project to be built by contractors who participate in a Joint Labor-Management Apprenticeship Program approved by the State of California and make a commitment to hiring a local workforce.

Community benefits such as local hire can also be helpful to reduce environmental impacts and improve the positive economic impact of the Project. Local hire provisions requiring that a certain percentage of workers reside within 10 miles or less of the Project site can reduce the length of vendor trips, reduce greenhouse gas emissions, and provide localized economic benefits. As environmental consultants Matt Hagemann and Paul E. Rosenfeld note:
[A]ny local hire requirement that results in a decreased worker trip length from the default value has the potential to result in a reduction of construction-related GHG emissions, though the significance of the reduction would vary based on the location and urbanization level of the project site.

March 8, 2021 SWAPE Letter to Mitchell M. Tsai re Local Hire Requirements and Considerations for Greenhouse Gas Modeling.

Workforce requirements promote the development of skilled trades that yield sustainable economic development. As the California Workforce Development Board and the University of California, Berkeley Center for Labor Research and Education concluded:
[L]abor should be considered an investment rather than a cost—and investments in growing, diversifying, and upskilling California’s workforce can positively affect returns on climate mitigation efforts. In other words, 218
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well-trained workers are key to delivering emissions reductions and moving California closer to its climate targets.1
Furthermore, workforce policies have significant environmental benefits given that they improve an area’s jobs-housing balance, decreasing the amount and length of job commutes and the associated greenhouse gas (GHG) emissions. In fact, on May 7, 2021, the South Coast Air Quality Management District found that that the “[u]se of a local state-certified apprenticeship program” can result in air pollutant reductions.2

Locating jobs closer to residential areas can have significant environmental benefits.

As the California Planning Roundtable noted in 2008:

People who live and work in the same jurisdiction would be more likely to take transit, walk, or bicycle to work than residents of less balanced communities and their vehicle trips would be shorter. Benefits would include potential reductions in both vehicle miles traveled and vehicle hours traveled.3
Moreover, local hire mandates and skill-training are critical facets of a strategy to reduce vehicle miles traveled (VMT). As planning experts Robert Cervero and Michael Duncan have noted, simply placing jobs near housing stock is insufficient to achieve VMT reductions given that the skill requirements of available local jobs must match those held by local residents.4 Some municipalities have even tied local hire and 1 California Workforce Development Board (2020) Putting California on the High Road: A Jobs and Climate Action Plan for 2030 at p. ii, available at https://laborcenter.berkeley.edu/
wp-content/uploads/2020/09/Putting-California-on-the-High-Road.pdf. 2 South Coast Air Quality Management District (May 7, 2021) Certify Final Environmental Assessment and Adopt Proposed Rule 2305 – Warehouse Indirect Source Rule – Warehouse Actions and Investments to Reduce Emissions Program, and Proposed Rule 316 – Fees for Rule 2305, Submit Rule 2305 for Inclusion Into the SIP, and Approve Supporting Budget Actions, available at http://www.aqmd.gov/docs/defaultsource/Agendas/Governing-Board/2021/2021-May7-027.pdf?sfvrsn=10. 3 California Planning Roundtable (2008) Deconstructing Jobs-Housing Balance at p. 6, available at https://cproundtable.org/static/media/uploads/publications/cpr-jobshousing.pdf 4 Cervero, Robert and Duncan, Michael (2006) Which Reduces Vehicle Travel More: JobsHousing Balance or Retail-Housing Mixing? Journal of the American Planning Association 72 (4), 475-490, 482, available at http://reconnectingamerica.org/assets/Uploads/UTCT825.pdf. 219
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other workforce policies to local development permits to address transportation issues. Cervero and Duncan note that:

In nearly built-out Berkeley, CA, the approach to balancing jobs and housing is to create local jobs rather than to develop new housing. The city’s First Source program encourages businesses to hire local residents, especially for entry- and intermediate-level jobs, and sponsors vocational training to ensure residents are employment-ready. While the program is voluntary, some 300 businesses have used it to date, placing more than 3,000 city residents in local jobs since it was launched in 1986. When needed, these carrots are matched by sticks, since the city is not shy about negotiating corporate participation in First Source as a condition of approval for development permits.

Recently, the State of California verified its commitment towards workforce development through the Affordable Housing and High Road Jobs Act of 2022, otherwise known as Assembly Bill No. 2011 (“AB2011”). AB2011 amended the Planning and Zoning Law to allow ministerial, by-right approval for projects being built alongside commercial corridors that meet affordability and labor requirements.

The City should consider utilizing local workforce policies and requirements to benefit the local area economically and to mitigate greenhouse gas, improve air quality, and reduce transportation impacts.

II. THE CALIFORNIA ENVIRONMENTAL QUALITY ACT
CEQA is a California statute designed to inform decision-makers and the public about the potential significant environmental effects of a project. 14 California Code of Regulations (“CEQA Guidelines”), § 15002, subd. (a)(1).5 At its core, its purpose is to “inform the public and its responsible officials of the environmental consequences of their decisions before they are made. Thus, the EIR ‘protects not only the environment but also informed self-government[.]’” Citizens of Goleta Valley v.

Board of Supervisors (1990) 52 Cal.3d 553, 564 (internal citation omitted). 5 The CEQA Guidelines, codified in Title 14 of the California Code of Regulations, section 15000 et seq., are regulatory guidelines promulgated by the state Natural Resources Agency for the implementation of CEQA. Pub. Res. Code, § 21083. The CEQA Guidelines are given “great weight in interpreting CEQA except when . . . clearly unauthorized or erroneous.” Center for Biological Diversity v. Dept. of Fish & Wildlife (2015) 62 Cal.4th 204, 217. 220
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CEQA directs public agencies to avoid or reduce environmental damage, when possible, by requiring alternatives or mitigation measures. CEQA Guidelines, § 15002, subds. (a)(2)-(3); see also Berkeley Keep Jets Over the Bay Committee v. Board of Port Commissioners of the City of Oakland (2001) 91 Cal.App.4th 1344, 1354; Laurel Heights Improvement Assn. v. Regents of University of California (1988) 47 Cal.3d 376, 400. The Environmental Impact Report (EIR) serves to provide public agencies and the public in general with information about the effect that a proposed project is likely to have on the environment and to “identify ways that environmental damage can be avoided or significantly reduced.” CEQA Guidelines, § 15002, subd. (a)(2).

A public agency must prepare an EIR whenever substantial evidence supports a “fair argument” that a proposed project “may have a significant effect on the environment.” Pub. Res. Code, §§ 21100, 21151; CEQA Guidelines, §§ 15002, subds. (f)(1)-(2), 15063; No Oil, supra, 13 Cal.App.3d at p. 75; Communities for a Better Environment v. California Resources Agency (2002) 103 Cal.App.4th 98, 111-112. If the project has a significant effect on the environment, the agency may approve the project only upon finding that it has “eliminated or substantially lessened all significant effects on the environment where feasible” and that any unavoidable significant effects on the environment are “acceptable due to overriding concerns” specified in Public Resources Code section 21081. See CEQA Guidelines, §§ 15092, subds. (b)(2)(A)-(B).

Essentially, should a lead agency be presented with a fair argument that a project may have a significant effect on the environment, the lead agency shall prepare an EIR even though it may also be presented with other substantial evidence that the project will not have a significant effect. CEQA Guidelines, §§ 15064(f)(1)-(2); see No Oil, supra, 13 Cal.App.3d at p. 75 (internal citations and quotations omitted). Substantial evidence includes “enough relevant information and reasonable inferences from this information that a fair argument can be made to support a conclusion, even though other conclusions might also be reached.” CEQA Guidelines, § 15384, subd. (a).

The EIR has been described as “an environmental ‘alarm bell’ whose purpose it is to alert the public and its responsible officials to environmental changes before they have reached ecological points of no return.” Berkeley Keep Jets Over the Bay v. Bd. of Port Comm’rs. (2001) 91 Cal. App. 4th 1344, 1354 (“Berkeley Jets”); County of Inyo v. Yorty (1973) 32 Cal. App. 3d 795, 810.
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The preparation and circulation of an EIR is more than a set of technical hurdles for agencies and developers to overcome. Communities for a Better Environment v. Richmond (2010) 184 Cal.App.4th 70, 80 (quoting Vineyard Area Citizens for Responsible Growth, Inc. v. City of Rancho Cordova (2007) 40 Cal.4th 412, 449-450). The EIR’s function is to ensure that government officials who decide to build or approve a project do so with a full understanding of the environmental consequences and, equally important, that the public is assured those consequences have been considered. Id. For the EIR to serve these goals it must present information so that the foreseeable impacts of pursuing the project can be understood and weighed, and the public must be given an adequate opportunity to comment on that presentation before the decision to go forward is made. Id.

A strong presumption in favor of requiring preparation of an EIR is built into CEQA.

This presumption is reflected in what is known as the “fair argument” standard under which an EIR must be prepared whenever substantial evidence in the record supports a fair argument that a project may have a significant effect on the environment. Quail Botanical Gardens Found., Inc. v. City of Encinitas (1994) 29 Cal.App.4th 1597, 1602; Friends of “B” St. v. City of Hayward (1980) 106 Cal.3d 988, 1002.

The fair argument test stems from the statutory mandate that an EIR be prepared for any project that “may have a significant effect on the environment.” Pub. Res. Code, § 21151; see No Oil, Inc. v. City of Los Angeles (1974) 13 Cal.App.3d 68, 75 (hereafter, “No Oil”); accord Jensen v. City of Santa Rosa (2018) 23 Cal.App.5th 877, 884 (hereafter, “Jensen”). Under this test, if a proposed project is not exempt and may cause a significant effect on the environment, the lead agency must prepare an EIR. Pub. Res.

Code, §§ 21100, subd. (a), 21151; CEQA Guidelines, §§ 15064, subds. (a)(1), (f)(1). An EIR may be dispensed with only if the lead agency finds no substantial evidence in the initial study or elsewhere in the record that the project may have a significant effect on the environment. Parker Shattuck Neighbors v. Berkeley City Council (2013) 222 Cal.App.4th 768, 785. In such a situation, the lead agency must adopt a negative declaration. Pub. Res. Code, § 21080, subd. (c)(1); CEQA Guidelines, §§ 15063, subd. (b)(2), 15064, subd. (f)(3).
“Significant effect upon the environment” is defined as “a substantial or potentially substantial adverse change in the environment.” Pub. Res. Code, § 21068; CEQA Guidelines, § 15382. A project may have a significant effect on the environment if there is a reasonable probability that it will result in a significant impact. No Oil, supra, 222
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13 Cal.App.3d at p. 83 fn. 16; see Sundstrom v. County of Mendocino (1988) 202 Cal.App.3d 296, 309 (hereafter, “Sundstrom”). If any aspect of the project may result in a significant impact on the environment, an EIR must be prepared even if the overall effect of the project is beneficial. CEQA Guidelines, § 15063, subd. (b)(1); see County Sanitation Dist. No. 2 v. County of Kern (2005) 127 Cal.App.4th 1544, 1580.

This standard sets a “low threshold” for preparation of an EIR. Consolidated Irrigation Dist. v. City of Selma (2012) 204 Cal.App.4th 187, 207; Nelson v. County of Kern (2010) 190 Cal.App.4th 252; Pocket Protectors v. City of Sacramento (2004) 124 Cal.App.4th 903, 928; Bowman v. City of Berkeley (2004) 122 Cal.App.4th 572, 580; Citizen Action to Serve All Students v. Thornley (1990) 222 Cal.App.3d 748, 754; Sundstrom, supra, 202 Cal.App.3d at p. 310; No Oil, supra, 13 Cal.App.3d at p. 84; County Sanitation, supra, 127 Cal.App.4th at p. 1579. If substantial evidence in the record supports a fair argument that the project may have a significant environmental effect, the lead agency must prepare an EIR even if other substantial evidence before it indicates the project will have no significant effect. See Jensen, supra, 23 Cal.App.5th at p. 886; Clews Land & Livestock v. City of San Diego (2017) 19 Cal.App.5th 161, 183; Stanislaus Audubon Society, Inc. v. County of Stanislaus (1995) 33 Cal.App.4th 144, 150; Brentwood Assn. for No Drilling, Inc. v. City of Los Angeles (1982) 134 Cal.App.3d 491; Friends of “B” St., 106 Cal.App.3d 988; CEQA Guidelines, § 15064, subd. (f)(1). It “requires the preparation of an EIR where there is substantial evidence that any aspect of the project, either individually or cumulatively, may cause a significant effect on the environment, regardless of whether the overall effect of the project is adverse or beneficial[.]” County Sanitation, supra, 127 Cal.App.4th at p. 1580 (quoting CEQA Guidelines, § 15063, subd. (b)(1)).

Evidence supporting a fair argument of a significant environmental impact triggers preparation of an EIR regardless of whether the record contains contrary evidence.

League for Protection of Oakland’s Architectural and Historical Resources v. City of Oakland (1997) 52 Cal.App.4th 896, 904-905. “Where the question is the sufficiency of the evidence to support a fair argument, deference to the agency’s determination is not appropriate[.]” County Sanitation, supra, 127 Cal.App.4th at p. 1579 (quoting Sierra Club v. County of Sonoma (1992) 6 Cal.App.4th 1307, 1317-1318).

The agency or the court should not weigh expert testimony or decide on the credibility of such evidence—this is the EIR’s responsibility. As stated in Pocket Protectors v. City of Sacramento (2004):
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Unlike the situation where an EIR has been prepared, neither the lead agency nor a court may “weigh” conflicting substantial evidence to determine whether an EIR must be prepared in the first instance.

Guidelines section 15064, subdivision (f)(1) provides in pertinent part: if a lead agency is presented with a fair argument that a project may have a significant effect on the environment, the lead agency shall prepare an EIR even though it may also be presented with other substantial evidence that the project will not have a significant effect. Thus, as Claremont itself recognized, [c]onsideration is not to be given contrary evidence supporting the preparation of a negative declaration.
124 Cal.App.4th 903, 935 (internal citations and quotations omitted).

In cases where it is not clear whether there is substantial evidence of significant environmental impacts, CEQA mandates erring on the side of a “preference for resolving doubts in favor of environmental review.” Mejia v. City of Los Angeles (2005) 130 Cal.App.4th 322, 332 “The foremost principle under CEQA is that the Legislature intended the act to be interpreted in such manner as to afford the fullest possible protection to the environment within the reasonable scope of the statutory language. Friends of Mammoth v. Bd. of Supervisors (1972) 8 Cal.3d 247, 259.

Further, it is the duty of the lead agency, not the public, to conduct the proper environmental studies. “The agency should not be allowed to hide behind its own failure to gather relevant data.” Sundstrom, supra, 202 Cal.App.3d at p. 311. “Deficiencies in the record may actually enlarge the scope of fair argument by lending a logical plausibility to a wider range of inferences.” Ibid; see also Gentry v. City of Murrieta (1995) 36 Cal.App.4th 1359, 1382 (lack of study enlarges the scope of the fair argument which may be made based on the limited facts in the record).

Thus, refusal to complete recommended studies lowers the already low threshold to establish a fair argument. The court may not exercise its independent judgment on the omitted material by determining whether the ultimate decision of the lead agency would have been affected had the law been followed. Environmental Protection Information Center v. Cal. Dept. of Forestry (2008) 44 Cal.4th 459, 486 (internal citations and quotations omitted). The remedy for this deficiency would be for the trial court to issue a writ of mandate. Ibid.
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While the courts review an EIR using an ‘abuse of discretion’ standard, the reviewing court is not to uncritically rely on every study or analysis presented by a project proponent in support of its position. Berkeley Keep Jets, supra, 91 Cal.App.4th at p. 1355 (quoting Laurel Heights, supra, 47 Cal.3d at pp. 391, 409 fn. 12) (internal quotations omitted). A clearly inadequate or unsupported study is entitled to no judicial deference. Ibid. Drawing this line and determining whether the EIR complies with CEQA’s information disclosure requirements presents a question of law subject to independent review by the courts. Sierra Club v. County of Fresno (2018) 6 Cal.5th 502, 515; Madera Oversight Coalition, Inc. v. County of Madera (2011) 199 Cal.App.4th 48, 102, 131. As the First District Court of Appeal has previously stated, prejudicial abuse of discretion occurs if the failure to include relevant information precludes informed decision-making and informed public participation, thereby thwarting the statutory goals of the EIR process. Berkeley Keep Jets, supra, 91 Cal.App.4th at p. 1355 (internal quotations omitted).

Both the review for failure to follow CEQA’s procedures and the fair argument test are questions of law, thus, the de novo standard of review applies. Vineyard Area Citizens for Responsible Growth v. City of Rancho Cordova (2007) 40 Cal.4th 412, 435.

Whether the agency’s record contains substantial evidence that would support a fair argument that the project may have a significant effect on the environment is treated as a question of law. Consolidated Irrigation Dist., supra, 204 Cal.App.4th at p. 207; Kostka and Zischke, Practice Under the Environmental Quality Act (2017, 2d ed.) at § 6.76.

III. THE DEIR IS INADEQUATE UNDER CEQA
A. The DEIR Fails to Support Its Findings with Substantial Evidence When new information is brought to light showing that an impact previously discussed in the DEIR but found to be insignificant with or without mitigation in the DEIR’s analysis has the potential for a significant environmental impact supported by substantial evidence, the DEIR must consider and resolve the conflict in the evidence.

See Visalia Retail, L.P. v. City of Visalia (2018) 20 Cal. App. 5th 1, 13, 17; see also Protect the Historic Amador Waterways v. Amador Water Agency (2004) 116 Cal. App. 4th 1099, 1109. While a lead agency has discretion to formulate standards for determining significance and the need for mitigation measures—the choice of any standards or thresholds of significance must be “based to the extent possible on scientific and factual data and an exercise of reasoned judgment based on substantial evidence.

CEQA Guidelines § 15064(b); Cleveland Nat'l Forest Found. v. San Diego Ass'n of Gov'ts 225
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(2017) 3 Cal. App. 5th 497, 515; Mission Bay Alliance v. Office of Community Inv. & Infrastructure (2016) 6 Cal. App. 5th 160, 206. And when there is evidence that an impact could be significant, an EIR cannot adopt a contrary finding without providing an adequate explanation along with supporting evidence. East Sacramento Partnership for a Livable City v. City of Sacramento (2016) 5 Cal. App. 5th 281, 302.

In addition, a determination that regulatory compliance will be sufficient to prevent significant adverse impacts must be based on a project-specific analysis of potential impacts and the effect of regulatory compliance. In Californians for Alternatives to Toxics v.

Department of Food & Agric. (2005) 136 Cal. App. 4th 1, the court set aside an EIR for a statewide crop disease control plan because it did not include an evaluation of the risks to the environment and human health from the proposed program but simply presumed that no adverse impacts would occur from use of pesticides in accordance with the registration and labeling program of the California Department of Pesticide Regulation. See also Ebbetts Pass Forest Watch v Department of Forestry & Fire Protection (2008) 43 Cal. App. 4th 936, 956 (fact that Department of Pesticide Regulation had assessed environmental effects of certain herbicides in general did not excuse failure to assess effects of their use for specific timber harvesting project).

1. The Project’s Initial Study Omits Critical Supporting Information Regarding the Project’s Energy Use Impacts, Fails to Adopt a Correct Threshold of Significance, and Improperly Finds that the Project’s Energy Use Impacts
Would Be Less Than Significant
Environmental documents must provide technical details, not merely conclusory findings, to support their determinations. [A]n EIR shall include summarized technical data, maps, plot plans, diagrams, and similar relevant information sufficient to permit full assessment of significant environmental impacts by reviewing agencies and members of the public. CEQA Guidelines § 15147; San Franciscans for Reasonable Growth v. City & County of San Francisco (1987) 193 Cal.App.3d 1544. 1549 (“All technical data, however, need not be included in the body of report, but may be relegated to appendices [citation omitted] or may be contained in separate source documents which are not formally a part of the document.”). An EIR shall cite all documents used in its preparation . . . .” CEQA Guidelines § 15148. An environmental document may incorporate by reference another document so long as the document is made available for inspection to the public. CEQA Guidelines § 15150.
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Here, the Project’s Initial Study (Appendix A to DEIR) concludes that the Project’s energy use impacts will be less than significant and therefore no mitigation is required.

See Appendix A to DEIR, pp. 59-65. However, the City premises this determination regarding the threshold of significance on faulty analysis whereby it compares the Project’s anticipated net increase in energy uses to the estimated energy uses of all of Alameda County. See Appendix A to DEIR at p. 59. The City then applies this improper underlying assumption in making the determination that the proposed Project’s anticipated energy uses will have no significant energy use impacts. Id.

As such, the EIR fails to provide substantial evidence to support utilizing the estimated energy use of the entirety of Alameda County as a threshold of significance.

Thresholds of significance are “identifiable, quantitative, qualitative or performance level of a particular environmental effect.” (CEQA Guidelines 15064.7.) While a lead agency has discretion to set thresholds of significance to determine whether an adverse environmental impact should be classified as “significant” or “less than significant”, a lead agency’s choice of an appropriate threshold must be based upon scientific and factual data to the extent possible and supported by substantial evidence Mission Bay Alliance v. Office of Community Inv. & Infrastructure (2016) 6 Cal.App.5th 160, 206; CEQA Guidelines § 15064.) When there is evidence that an impact may be significant, an EIR may not find the impact to be less than significant without an adequate explanation and supporting evidence. (East Sacramento Partnership for a Livable City v. City of Sacramento (2016) 5 Cal. App.5th 281, 300 – 02.) A threshold of significance may not be “impermissibly lenient.” (Endangered Habitats League, Inc. v.

County of Orange (2005) 131 Cal.App.5th 777, 791.)
Here, comparing the Project’s anticipated energy use impacts to the energy use of all of Alameda County is unjustified. The more pertinent, legally appropriate, and proportional analysis in assessing the Project’s energy use impacts would be for the DEIR to consider the percentage increase in energy use that the Project presents compared to the current, existing energy uses within the Project site. Moreover, the DEIR should analyze and present the Project’s proportional contribution to the City’s overall energy use, which it also fails to do.

The foregoing statistical calculations, and the City’s demonstrated lack of analysis of them, amounts to significant new information associated with the Project’s energy use impacts. This analysis must be performed for the City to properly assess the Project’s 227
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anticipated energy use impacts and to thereby determine whether implementation of mitigation measures is warranted.

As set forth in Sundstrom, on this issue, the City “should not be allowed to hide behind its own failure to gather relevant data.” 202 Cal.App.3d at p. 311. The City’s selection of energy use for all Alameda County as the basis for comparison of the Project’s anticipated energy uses is without justification, and is therefore arbitrary and capricious.

This inadequate study conducted by the City on this issue will be entitled to no judicial deference in any CEQA challenge brought against the Project’s DEIR/FEIR. See Laurel Heights, supra, 47 Cal.3d at pp. 391, 409 fn. 12) (internal quotations omitted).

Additionally, the Initial Study admits that Project would utilize natural gas for heating purposes. Appendix A to DEIR, p. 62. Meanwhile, the Bay Area Air Quality Management District’s (“BAAQMD”) 2022 CEQA Thresholds for Evaluating the Significance of Climate Impacts From Land Use Projects and Plans guidance document (which the City has adopted) provides that inclusion of natural gas plumbing and/or appliances in new construction gives rise to potentially significant impacts with regard to a project’s greenhouse gas emissions. See BAAQMD 2022 CEQA Guidelines, Ch. 6, Sec. 6.2.1 – Land Use Project Design Elements, pp. 6-3 – 6-4. To that end, the installation and use of natural gas for heating purposes at the Project will also arguably result in inefficient consumption of energy by the Project during its operation (i.e., a potentially significant energy impact).

Based on the foregoing, and in spite of the conclusions set forth in the DEIR, there is substantial evidence of the potential for the Project’s energy use to present a significant environmental impact. As such, the DEIR must, at a minimum, be revised and recirculated consider and resolve this conflict in the evidence. See Visalia Retail, supra, 20 Cal. App. 5th at 17; see also Amador Waterways, supra, (2004) 116 Cal. App. 4th at 1109.

Furthermore, and as discussed below in connection with the Project’s Greenhouse Gas Emissions impacts, there are a litany of additional mitigation measures that could be incorporated in the Project in order to curb its GHG emissions impacts, many of which would also reduce the Project’s Energy Use (and Air Quality) impacts as well.

Incorporating the energy use mitigation measures proposed below is feasible and justified for the Project. The DEIR’s failure to do so, in conjunction with its faulty energy use impact analysis, violates CEQA.
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2. The DEIR Improperly Fails to Deploy Mitigation Measures for the Project’s Greenhouse Gas Emissions Impacts
Similar to the deficiencies identified above regarding the DEIR’s faulty analysis of the Project’s projected energy use, the DEIR fails to properly analyze and mitigate the impacts associated with the Project’s projected greenhouse gas (“GHG”) emissions.

Indeed, despite concluding that the Project will lead to significant and unavoidable GHG impacts in operation, the DEIR does not supply any estimated calculations of the GHG emissions that the Project will produce, either in the construction phase or the operation phase. Further, based on the appendices to the DEIR, no GHG impact technical study for the Project has been conducted. Thus, the DEIR provides no demonstrable analysis of the threshold of significance applicable to the Project’s increase in GHG emissions. Rather, the EIR arbitrarily and summarily concludes that the Project’s GHG impacts in the operation are significant and unavoidable (and less than significant in the construction phase), and that no mitigation measures are feasible.

As stated in the Office of Planning Research’s (“OPR”) technical advisory in 2018:

VMT and Greenhouse Gas Emissions Reduction. Senate Bill 32 (Pavley, 2016) requires California to reduce greenhouse gas (GHG) emissions 40 percent below 1990 levels by 2030, and Executive Order B-16-12 provides a target of 80 percent below 1990 emissions levels for the transportation sector by 2050.

Despite the Project’s clear GHG emissions impact in direct contravention of SB 32’s GHG reduction goals, the DEIR draws the conclusion that the Project’s GHG impacts are significant and cannot be mitigated because of the 9th Circuit’s recent decision in California Restaurant Association v. City of Berkeley. However, the DEIR makes no effort to otherwise reduce the Project’s GHG impacts through other specific project design features aimed at reducing GHG emissions. In this regard, the DEIR mistakes a federal court ruling concerning federal preemption of natural gas supply regulations as grounds to excuse the City from the CEQA requirement of endeavoring to ensure that the Project’s otherwise significant and unavoidable GHG emissions impacts are reduced to the maximum extent feasible.

Moreover, the Project is not consistent with the CARB 2022 Scoping Plan. Indeed, the first action item in the Scoping Plan is reduce GHG emissions “40% below 1990 229
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levels by 2030.”6 The CARB Scoping Plan also sets forth the action item that new residential and commercial buildings will have “[a]ll electric appliances beginning 2026 (residential) and 2029 (commercial), contributing to 6 million heat pumps installed statewide by 2030.”7
Despite the clear path presented by the CARB Scoping Plan for reducing GHG emissions, the DEIR declines to hold the Project to that standard, and instead deflects its responsibility to identify and mitigate GHG emissions impacts pursuant to CEQA’s mandate.

It is the City’s obligation, as lead agency, to ensure that the Project’s environmental impacts have first been properly analyzed and then mitigated to a less than significant level wherever possible. Local 713 submits that the Project’s implementation of the additional potential mitigation measures set forth below (where applicable), as delineated by the California Air Pollution Control Officers Association’s Quantifying Greenhouse Gas Mitigation Measures, would contribute toward the goal of reducing the Project’s GHG emission impacts to the maximum extent possible:
6 California Air Resources Board 2022 Scoping Plan at p. 72; https://ww2.arb.ca.gov/sites/default/files/2023-04/2022-sp.pdf 7 Id. at p. 75 230
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(See Quantifying Greenhouse Gas Mitigation Measures, Tables 6-1 to 6-9, California Air Pollution Control Officers Association (CAPCOA), August 2010.8 )
It is entirely feasible for the EIR to incorporate a substantial proportion of the foregoing measures for the Project as mandatory forms of mitigation against the 8 Available at: http://www.aqmd.gov/docs/default-source/ceqa/handbook/capcoaquantifying-greenhouse-gas-mitigation-measures.pdf 236
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Project’s potentially significant greenhouse gas impacts (as well as energy use and air quality impacts). The EIR cannot permissibly deflect its obligations to mitigate such impacts merely by hiding behind the 9th Circuit’s ruling in California Restaurant Association v. City of Berkeley. More is required, and as currently constituted, the DEIR’s improper analysis and lack of appropriate mitigation on GHG impacts violates CEQA.

3. The DEIR’s Biological Resources Mitigation Measure Is Insufficient.

The Project’s Initial Study and DEIR notes that up to 5 city street trees may require removal at the north edge of the Project site at the terminus of Hester Street.

Appendix A to DEIR, Initial Study, p. 51. In order to mitigate the Project’s potentially significant impacts to nesting birds in said street trees, the Initial Study imposes mitigation measure BIO-1, which requires, among other things, that pre-construction nesting surveys be conducted during the nesting season. Id. at p. 52. However, the mitigation measure defines the nesting period as February-September, contrary to the California Department of Fish and Wildlife’s (“CDFW”) finding that raptor nesting may commence before and/or after this timeframe.9
Further investigation of the information contained on the CDFW’s “California Outdoors Q&A” webpage reveals that the boundaries of bird nesting season in California are broad and variable: “[N]esting season can vary based on location and species of bird, and in some parts of the state, birds nest year-round.”10 This added qualification by CDFW regarding bird nesting season is consistent with, and underscores, CDFW’s separate finding that raptor nesting in the Project’s geographic region can and does occur outside the more general bird nesting period of February-September sought by the DEIR in BIO-1. Moreover, CDFW’s collective findings on this issue confirm the inadequacy of the City’s proposed mitigation measure for the Project.
9 “…[S]ome species of raptors (e g. owls, hawks, etc.) may commence nesting activities in January.” See CDFW November 18, 2021 letter to City of Adelanto, available at https://files.ceqanet.opr.ca.gov/273819-1/attachment/
zo76RgD7dUdj5BLJTEhEMdf74g6f100RrKiWBQSquhFFe5l0X53rLsbLSGMPRXgXM4 AaYnJSTfZB6JpY0 10 See CDFW California Outdoors Q&A – Nesting Birds https://wildlife.ca.gov/COQA/ ArticlePage/2/tag/conflict#gsc.tab=0
237
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Accordingly, the nesting period and survey plan set forth in the MM-BIO-1 must, at a minimum, be revised to account for CDFW’s findings pertaining to the raptor nesting season within the Project’s geographic region. Absent such revision, the proposed mitigation measure and, by extension, the DEIR will be in direct violation of the CEQA Guidelines.

4. The DEIR’s Noise/Vibration Mitigation Measures Are
Inadequate and Fail to Incorporate Requisite Analysis
The Project’s DEIR finds that construction of the Project will result in a potentially significant impact with respect to groundborne vibration. Specifically, the DEIR indicates that the Project’s construction would generate groundborne vibration that would exceed thresholds of structural damage at nearby existing buildings. DEIR at p.

4.3-18. In an effort to address these potential significant impacts, the DEIR implements Mitigation Measure NOI-2, which states as follows:

Static Roller Requirement. The project applicant and/or its construction contractors shall use of a static roller in lieu of a vibratory roller for paving activities within 15 feet of the existing off-site buildings to the north and west of the project site. City staff shall verify that this requirement is incorporated into construction plans prior to issuance of a building permit and verified in the field.

DEIR at p. 4.3-20.

However, the calculations associated with MM-NOI-2 do not include any analysis of the impacts of vibratory roller use between 10 feet and 25 feet of distance from existing off-site buildings. See Appendix F to DEIR at pp. 3-5, Table 1. Meanwhile, MM-NOI-2 only requires use of a static (non-vibratory) roller within 15 feet of neighboring sensitive receptors. Thus, the DEIR’s analysis with regard to MM-NOI-2 is inadequate to support the measure, in that the DEIR does not clearly indicate that the vibration caused by use a vibratory roller starting at 15 feet of distance from neighboring structures would be less than the prescribed threshold of 0.5 in/sec PPV for vibration-induced structural damage. Moreover, the DEIR also does not otherwise provide a clear delineation for the minimum safe distance for use of a vibratory roller in the context of proximity to off-site structures.

Further analysis is required to demonstrate that no significant impact will occur to neighboring industrial structures via use of vibratory roller starting at 15 feet distance 238
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away and greater. Accordingly, the DEIR must be revised and recirculated to reflect this appropriate analysis, and MM-NOI-2 should be adjusted accordingly, if necessary, in order to protect neighboring structures from damage.

IV. CONCLUSION
Based on the foregoing concerns, the City should require revision and recirculation of the DEIR for the Project pursuant to CEQA. Absent doing so, the DEIR in its current form directly violates CEQA in multiple respects. If the City should have any questions or concerns, please do not hesitate to contact this office.

Sincerely,
____________________________
Jeremy Herwitt
Attorneys for Carpenters Local 713
Attached:

March 8, 2021 SWAPE Letter to Mitchell M. Tsai re Local Hire Requirements and Considerations for Greenhouse Gas Modeling (Exhibit A); Air Quality and GHG Expert Paul Rosenfeld CV (Exhibit B); Air Quality and GHG Expert Matt Hagemann CV (Exhibit C) 239

EXHIBIT A
240
1 2656 29th Street, Suite 201
Santa Monica, CA 90405
Matt Hagemann, P.G, C.Hg.
(949) 887-9013
[email protected]
Paul E. Rosenfeld, PhD
(310) 795-2335
[email protected]
March 8, 2021
Mitchell M. Tsai
155 South El Molino, Suite 104
Pasadena, CA 91101
Subject: Local Hire Requirements and Considerations for Greenhouse Gas Modeling Dear Mr. Tsai,
Soil Water Air Protection Enterprise (“SWAPE”) is pleased to provide the following draft technical report explaining the significance of worker trips required for construction of land use development projects with respect to the estimation of greenhouse gas (“GHG”) emissions. The report will also discuss the potential for local hire requirements to reduce the length of worker trips, and consequently, reduced or mitigate the potential GHG impacts.

Worker Trips and Greenhouse Gas Calculations
The California Emissions Estimator Model (“CalEEMod”) is a “statewide land use emissions computer model designed to provide a uniform platform for government agencies, land use planners, and environmental professionals to quantify potential criteria pollutant and greenhouse gas (GHG) emissions associated with both construction and operations from a variety of land use projects.”1 CalEEMod quantifies construction-related emissions associated with land use projects resulting from off-road construction equipment; on-road mobile equipment associated with workers, vendors, and hauling; fugitive dust associated with grading, demolition, truck loading, and on-road vehicles traveling along paved and unpaved roads; and architectural coating activities; and paving.2
The number, length, and vehicle class of worker trips are utilized by CalEEMod to calculate emissions associated with the on-road vehicle trips required to transport workers to and from the Project site during construction.3 1 “California Emissions Estimator Model.” CAPCOA, 2017, available at: http://www.aqmd.gov/caleemod/home. 2 “California Emissions Estimator Model.” CAPCOA, 2017, available at: http://www.aqmd.gov/caleemod/home. 3 “CalEEMod User’s Guide.” CAPCOA, November 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/01_user-39-s-guide2016-3-2_15november2017.pdf?sfvrsn=4, p. 34. 241
2 Specifically, the number and length of vehicle trips is utilized to estimate the vehicle miles travelled (“VMT”) associated with construction. Then, utilizing vehicle-class specific EMFAC 2014 emission factors, CalEEMod calculates the vehicle exhaust, evaporative, and dust emissions resulting from construction-related VMT, including personal vehicles for worker commuting.4
Specifically, in order to calculate VMT, CalEEMod multiplies the average daily trip rate by the average overall trip length (see excerpt below):
“VMTd = Σ(Average Daily Trip Rate i * Average Overall Trip Length i) n Where:
n = Number of land uses being modeled.”5
Furthermore, to calculate the on-road emissions associated with worker trips, CalEEMod utilizes the following equation (see excerpt below):
“Emissionspollutant = VMT * EFrunning,pollutant
Where:

Emissionspollutant = emissions from vehicle running for each pollutant VMT = vehicle miles traveled
EFrunning,pollutant = emission factor for running emissions.” 6 Thus, there is a direct relationship between trip length and VMT, as well as a direct relationship between VMT and vehicle running emissions. In other words, when the trip length is increased, the VMT and vehicle running emissions increase as a result. Thus, vehicle running emissions can be reduced by decreasing the average overall trip length, by way of a local hire requirement or otherwise.

Default Worker Trip Parameters and Potential Local Hire Requirements As previously discussed, the number, length, and vehicle class of worker trips are utilized by CalEEMod to calculate emissions associated with the on-road vehicle trips required to transport workers to and from the Project site during construction.7In order to understand how local hire requirements and associated worker trip length reductions impact GHG emissions calculations, it is important to consider the CalEEMod default worker trip parameters. CalEEMod provides recommended default values based on site-specific information, such as land use type, meteorological data, total lot acreage, project type and typical equipment associated with project type. If more specific project information is known, the user can change the default values and input projectspecific values, but the California Environmental Quality Act (“CEQA”) requires that such changes be justified by substantial evidence.8 The default number of construction-related worker trips is calculated by multiplying the 4 “Appendix A Calculation Details for CalEEMod.” CAPCOA, October 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/02_appendix-a2016-3-2.pdf?sfvrsn=6, p. 14-15. 5 “Appendix A Calculation Details for CalEEMod.” CAPCOA, October 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/02_appendix-a2016-3-2.pdf?sfvrsn=6, p. 23. 6 “Appendix A Calculation Details for CalEEMod.” CAPCOA, October 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/02_appendix-a2016-3-2.pdf?sfvrsn=6, p. 15. 7 “CalEEMod User’s Guide.” CAPCOA, November 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/01_user-39-s-guide2016-3-2_15november2017.pdf?sfvrsn=4, p. 34. 8 CalEEMod User Guide, available at: http://www.caleemod.com/, p. 1, 9. 242
3 number of pieces of equipment for all phases by 1.25, with the exception of worker trips required for the building construction and architectural coating phases.9Furthermore, the worker trip vehicle class is a 50/25/25 percent mix of light duty autos, light duty truck class 1 and light duty truck class 2, respectively.”10 Finally, the default worker trip length is consistent with the length of the operational home-to-work vehicle trips.11 The operational home-to-work vehicle trip lengths are:
“[B]ased on the location and urbanization selected on the project characteristic screen. These values were supplied by the air districts or use a default average for the state. Each district (or county) also assigns trip lengths for urban and rural settings” (emphasis added). 12 Thus, the default worker trip length is based on the location and urbanization level selected by the User when modeling emissions. The below table shows the CalEEMod default rural and urban worker trip lengths by air basin (see excerpt below and Attachment A).13
Worker Trip Length by Air Basin
Air Basin Rural (miles) Urban (miles)
Great Basin Valleys 16.8 10.8
Lake County 16.8 10.8
Lake Tahoe 16.8 10.8
Mojave Desert 16.8 10.8
Mountain Counties 16.8 10.8
North Central Coast 17.1 12.3
North Coast 16.8 10.8
Northeast Plateau 16.8 10.8
Sacramento Valley 16.8 10.8
Salton Sea 14.6 11
San Diego 16.8 10.8
San Francisco Bay Area 10.8 10.8
San Joaquin Valley 16.8 10.8
South Central Coast 16.8 10.8
South Coast 19.8 14.7
Average 16.47 11.17
Minimum 10.80 10.80
Maximum 19.80 14.70
Range 9.00 3.90
9 “CalEEMod User’s Guide.” CAPCOA, November 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/01_user-39-s-guide2016-3-2_15november2017.pdf?sfvrsn=4, p. 34. 10 “Appendix A Calculation Details for CalEEMod.” CAPCOA, October 2017, available at:
http://www.aqmd.gov/docs/default-source/caleemod/02_appendix-a2016-3-2.pdf?sfvrsn=6, p. 15. 11 “Appendix A Calculation Details for CalEEMod.” CAPCOA, October 2017, available at:
http://www.aqmd.gov/docs/default-source/caleemod/02_appendix-a2016-3-2.pdf?sfvrsn=6, p. 14. 12 “Appendix A Calculation Details for CalEEMod.” CAPCOA, October 2017, available at:
http://www.aqmd.gov/docs/default-source/caleemod/02_appendix-a2016-3-2.pdf?sfvrsn=6, p. 21. 13 “Appendix D Default Data Tables.” CAPCOA, October 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/05_appendix-d2016-3-2.pdf?sfvrsn=4, p. D-84 – D-86. 243
4 As demonstrated above, default rural worker trip lengths for air basins in California vary from 10.8- to 19.8- miles, with an average of 16.47 miles. Furthermore, default urban worker trip lengths vary from 10.8- to 14.7- miles, with an average of 11.17 miles. Thus, while default worker trip lengths vary by location, default urban worker trip lengths tend to be shorter in length. Based on these trends evident in the CalEEMod default worker trip lengths, we can reasonably assume that the efficacy of a local hire requirement is especially dependent upon the urbanization of the project site, as well as the project location.

Practical Application of a Local Hire Requirement and Associated Impact To provide an example of the potential impact of a local hire provision on construction-related GHG emissions, we estimated the significance of a local hire provision for the Village South Specific Plan (“Project”) located in the City of Claremont (“City”). The Project proposed to construct 1,000 residential units, 100,000-SF of retail space, 45,000-SF of office space, as well as a 50-room hotel, on the 24-acre site. The Project location is classified as Urban and lies within the Los Angeles-South Coast County. As a result, the Project has a default worker trip length of 14.7 miles.14 In an effort to evaluate the potential for a local hire provision to reduce the Project’s construction-related GHG emissions, we prepared an updated model, reducing all worker trip lengths to 10 miles (see Attachment B). Our analysis estimates that if a local hire provision with a 10-mile radius were to be implemented, the GHG emissions associated with Project construction would decrease by approximately 17% (see table below and Attachment C).

Local Hire Provision Net Change
Without Local Hire Provision
Total Construction GHG Emissions (MT CO2e) 3,623
Amortized Construction GHG Emissions (MT CO2e/year) 120.77 With Local Hire Provision
Total Construction GHG Emissions (MT CO2e) 3,024
Amortized Construction GHG Emissions (MT CO2e/year) 100.80 % Decrease in Construction-related GHG Emissions 17%
As demonstrated above, by implementing a local hire provision requiring 10 mile worker trip lengths, the Project could reduce potential GHG emissions associated with construction worker trips. More broadly, any local hire requirement that results in a decreased worker trip length from the default value has the potential to result in a reduction of construction-related GHG emissions, though the significance of the reduction would vary based on the location and urbanization level of the project site.

This serves as an example of the potential impacts of local hire requirements on estimated project-level GHG emissions, though it does not indicate that local hire requirements would result in reduced construction-related GHG emission for all projects. As previously described, the significance of a local hire requirement depends on the worker trip length enforced and the default worker trip length for the project’s urbanization level and location.
14 “Appendix D Default Data Tables.” CAPCOA, October 2017, available at: http://www.aqmd.gov/docs/defaultsource/caleemod/05_appendix-d2016-3-2.pdf?sfvrsn=4, p. D-85. 244
5 Disclaimer
SWAPE has received limited discovery. Additional information may become available in the future; thus, we retain the right to revise or amend this report when additional information becomes available. Our professional services have been performed using that degree of care and skill ordinarily exercised, under similar circumstances, by reputable environmental consultants practicing in this or similar localities at the time of service. No other warranty, expressed or implied, is made as to the scope of work, work methodologies and protocols, site conditions, analytical testing results, and findings presented. This report reflects efforts which were limited to information that was reasonably accessible at the time of the work, and may contain informational gaps, inconsistencies, or otherwise be incomplete due to the unavailability or uncertainty of information obtained or provided by third parties.

Sincerely,
Matt Hagemann, P.G., C.Hg.

Paul E. Rosenfeld, Ph.D.
245
Location Type Location Name Rural H-W
(miles)
Urban H-W
(miles)
Air Basin Great Basin 16.8 10.8
Air Basin Lake County 16.8 10.8
Air Basin Lake Tahoe 16.8 10.8
Air Basin Mojave Desert 16.8 10.8
Air Basin Mountain 16.8 10.8
Air Basin North Central 17.1 12.3
Air Basin North Coast 16.8 10.8
Air Basin Northeast 16.8 10.8
Air Basin Sacramento 16.8 10.8
Air Basin Salton Sea 14.6 11
Air Basin San Diego 16.8 10.8
Air Basin San Francisco 10.8 10.8
Air Basin San Joaquin 16.8 10.8
Air Basin South Central 16.8 10.8
Air Basin South Coast 19.8 14.7
Air District Amador County 16.8 10.8
Air District Antelope Valley 16.8 10.8
Air District Bay Area AQMD 10.8 10.8
Air District Butte County 12.54 12.54
Air District Calaveras 16.8 10.8
Air District Colusa County 16.8 10.8
Air District El Dorado 16.8 10.8
Air District Feather River 16.8 10.8
Air District Glenn County 16.8 10.8
Air District Great Basin 16.8 10.8
Air District Imperial County 10.2 7.3
Air District Kern County 16.8 10.8
Air District Lake County 16.8 10.8
Air District Lassen County 16.8 10.8
Air District Mariposa 16.8 10.8
Air District Mendocino 16.8 10.8
Air District Modoc County 16.8 10.8
Air District Mojave Desert 16.8 10.8
Air District Monterey Bay 16.8 10.8
Air District North Coast 16.8 10.8
Air District Northern Sierra 16.8 10.8
Air District Northern

16.8 10.8
Air District Placer County 16.8 10.8
Air District Sacramento 15 10
Attachment A
246
Air District San Diego 16.8 10.8
Air District San Joaquin

16.8 10.8
Air District San Luis Obispo 13 13
Air District Santa Barbara 8.3 8.3
Air District Shasta County 16.8 10.8
Air District Siskiyou County 16.8 10.8
Air District South Coast 19.8 14.7
Air District Tehama County 16.8 10.8
Air District Tuolumne 16.8 10.8
Air District Ventura County 16.8 10.8
Air District Yolo/Solano 15 10
County Alameda 10.8 10.8
County Alpine 16.8 10.8
County Amador 16.8 10.8
County Butte 12.54 12.54
County Calaveras 16.8 10.8
County Colusa 16.8 10.8
County Contra Costa 10.8 10.8
County Del Norte 16.8 10.8
County El Dorado-Lake 16.8 10.8
County El Dorado- 16.8 10.8
County Fresno 16.8 10.8
County Glenn 16.8 10.8
County Humboldt 16.8 10.8
County Imperial 10.2 7.3
County Inyo 16.8 10.8
County Kern-Mojave 16.8 10.8
County Kern-San 16.8 10.8
County Kings 16.8 10.8
County Lake 16.8 10.8
County Lassen 16.8 10.8
County Los Angeles- 16.8 10.8
County Los Angeles- 19.8 14.7
County Madera 16.8 10.8
County Marin 10.8 10.8
County Mariposa 16.8 10.8
County Mendocino- 16.8 10.8
County Mendocino- 16.8 10.8
County Mendocino- 16.8 10.8
County Mendocino- 16.8 10.8
County Merced 16.8 10.8
County Modoc 16.8 10.8
County Mono 16.8 10.8
County Monterey 16.8 10.8
County Napa 10.8 10.8
247
County Nevada 16.8 10.8
County Orange 19.8 14.7
County Placer-Lake 16.8 10.8
County Placer-Mountain 16.8 10.8
County Placer- 16.8 10.8
County Plumas 16.8 10.8
County Riverside- 16.8 10.8
County Riverside-

19.8 14.7
County Riverside-Salton 14.6 11
County Riverside-South 19.8 14.7
County Sacramento 15 10
County San Benito 16.8 10.8
County San Bernardino- 16.8 10.8
County San Bernardino- 19.8 14.7
County San Diego 16.8 10.8
County San Francisco 10.8 10.8
County San Joaquin 16.8 10.8
County San Luis Obispo 13 13
County San Mateo 10.8 10.8
County Santa Barbara-

8.3 8.3
County Santa Barbara-

8.3 8.3
County Santa Clara 10.8 10.8
County Santa Cruz 16.8 10.8
County Shasta 16.8 10.8
County Sierra 16.8 10.8
County Siskiyou 16.8 10.8
County Solano- 15 10
County Solano-San 16.8 10.8
County Sonoma-North 16.8 10.8
County Sonoma-San 10.8 10.8
County Stanislaus 16.8 10.8
County Sutter 16.8 10.8
County Tehama 16.8 10.8
County Trinity 16.8 10.8
County Tulare 16.8 10.8
County Tuolumne 16.8 10.8
County Ventura 16.8 10.8
County Yolo 15 10
County Yuba 16.8 10.8
Statewide Statewide 16.8 10.8
248
Air Basin Rural (miles) Urban (miles)
Great Basin Valleys 16.8 10.8
Lake County 16.8 10.8
Lake Tahoe 16.8 10.8
Mojave Desert 16.8 10.8
Mountain Counties 16.8 10.8
North Central Coast 17.1 12.3
North Coast 16.8 10.8
Northeast Plateau 16.8 10.8
Sacramento Valley 16.8 10.8
Salton Sea 14.6 11
San Diego 16.8 10.8
San Francisco Bay Area 10.8 10.8
San Joaquin Valley 16.8 10.8
South Central Coast 16.8 10.8
South Coast 19.8 14.7
Average 16.47 11.17
Mininum 10.80 10.80
Maximum 19.80 14.70
Range 9.00 3.90
Worker Trip Length by Air Basin
249

1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population General Office Building 45.00 1000sqft 1.03 45,000.00 0 High Turnover (Sit Down Restaurant) 36.00 1000sqft 0.83 36,000.00 0 Hotel 50.00 Room 1.67 72,600.00 0
Quality Restaurant 8.00 1000sqft 0.18 8,000.00 0
Apartments Low Rise 25.00 Dwelling Unit 1.56 25,000.00 72 Apartments Mid Rise 975.00 Dwelling Unit 25.66 975,000.00 2789 Regional Shopping Center 56.00 1000sqft 1.29 56,000.00 0

1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
9 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 33

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2028
CO2 Intensity
(lb/MWhr)
702.44 CH4 Intensity 0.029
(lb/MWhr)
N2O Intensity 0.006
(lb/MWhr)
Village South Specific Plan (Proposed)
Los Angeles-South Coast County, Annual
CalEEMod Version: CalEEMod.2016.3.2 Page 1 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual Attachment B
250
Project Characteristics - Consistent with the DEIR's model.

Land Use - See SWAPE comment regarding residential and retail land uses.

Construction Phase - See SWAPE comment regarding individual construction phase lengths.

Demolition - Consistent with the DEIR's model. See SWAPE comment regarding demolition.

Vehicle Trips - Saturday trips consistent with the DEIR's model. See SWAPE comment regarding weekday and Sunday trips.

Woodstoves - Woodstoves and wood-burning fireplaces consistent with the DEIR's model. See SWAPE comment regarding gas fireplaces.

Energy Use -
Construction Off-road Equipment Mitigation - See SWAPE comment on construction-related mitigation.

Area Mitigation - See SWAPE comment regarding operational mitigation measures.

Water Mitigation - See SWAPE comment regarding operational mitigation measures.

Table Name Column Name Default Value New Value
tblFireplaces FireplaceWoodMass 1,019.20 0.00
tblFireplaces FireplaceWoodMass 1,019.20 0.00
tblFireplaces NumberWood 1.25 0.00
tblFireplaces NumberWood 48.75 0.00
tblVehicleTrips ST_TR 7.16 6.17
tblVehicleTrips ST_TR 6.39 3.87
tblVehicleTrips ST_TR 2.46 1.39
tblVehicleTrips ST_TR 158.37 79.82
tblVehicleTrips ST_TR 8.19 3.75
tblVehicleTrips ST_TR 94.36 63.99
tblVehicleTrips ST_TR 49.97 10.74
tblVehicleTrips SU_TR 6.07 6.16
tblVehicleTrips SU_TR 5.86 4.18
tblVehicleTrips SU_TR 1.05 0.69
tblVehicleTrips SU_TR 131.84 78.27
CalEEMod Version: CalEEMod.2016.3.2 Page 2 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 251

2.0 Emissions Summary
tblVehicleTrips SU_TR 5.95 3.20
tblVehicleTrips SU_TR 72.16 57.65
tblVehicleTrips SU_TR 25.24 6.39
tblVehicleTrips WD_TR 6.59 5.83
tblVehicleTrips WD_TR 6.65 4.13
tblVehicleTrips WD_TR 11.03 6.41
tblVehicleTrips WD_TR 127.15 65.80
tblVehicleTrips WD_TR 8.17 3.84
tblVehicleTrips WD_TR 89.95 62.64
tblVehicleTrips WD_TR 42.70 9.43
tblWoodstoves NumberCatalytic 1.25 0.00
tblWoodstoves NumberCatalytic 48.75 0.00
tblWoodstoves NumberNoncatalytic 1.25 0.00
tblWoodstoves NumberNoncatalytic 48.75 0.00
tblWoodstoves WoodstoveDayYear 25.00 0.00
tblWoodstoves WoodstoveDayYear 25.00 0.00
tblWoodstoves WoodstoveWoodMass 999.60 0.00
tblWoodstoves WoodstoveWoodMass 999.60 0.00
CalEEMod Version: CalEEMod.2016.3.2 Page 3 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 252

2.1 Overall Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2021 0.1713 1.8242 1.1662 2.4000e0030.4169 0.0817 0.4986 0.1795 0.0754 0.2549 0.0000 213.1969 213.1969 0.0601 0.0000 214.6993 2022 0.6904 4.1142 6.1625 0.0189 1.3058 0.1201 1.4259 0.3460 0.1128 0.4588 0.0000 1,721.682 6 1,721.682
6 0.1294 0.0000 1,724.918
7 2023 0.6148 3.3649 5.6747 0.0178 1.1963 0.0996 1.2959 0.3203 0.0935 0.4138 0.0000 1,627.529 5 1,627.529
5 0.1185 0.0000 1,630.492
5 2024 4.1619 0.1335 0.2810 5.9000e0040.0325 6.4700e0030.0390 8.6300e0036.0400e0030.0147 0.0000 52.9078 52.9078 8.0200e0030.0000 53.1082 Maximum 4.1619 4.1142 6.1625 0.0189 1.3058 0.1201 1.4259 0.3460 0.1128 0.4588 0.0000 1,721.682 6 1,721.682
6 0.1294 0.0000 1,724.918
7 Unmitigated Construction
CalEEMod Version: CalEEMod.2016.3.2 Page 4 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 253

2.1 Overall Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2021 0.1713 1.8242 1.1662 2.4000e0030.4169 0.0817 0.4986 0.1795 0.0754 0.2549 0.0000 213.1967 213.1967 0.0601 0.0000 214.6991 2022 0.6904 4.1142 6.1625 0.0189 1.3058 0.1201 1.4259 0.3460 0.1128 0.4588 0.0000 1,721.682 3 1,721.682
3 0.1294 0.0000 1,724.918
3 2023 0.6148 3.3648 5.6747 0.0178 1.1963 0.0996 1.2959 0.3203 0.0935 0.4138 0.0000 1,627.529 1 1,627.529
1 0.1185 0.0000 1,630.492
1 2024 4.1619 0.1335 0.2810 5.9000e0040.0325 6.4700e0030.0390 8.6300e0036.0400e0030.0147 0.0000 52.9077 52.9077 8.0200e0030.0000 53.1082 Maximum 4.1619 4.1142 6.1625 0.0189 1.3058 0.1201 1.4259 0.3460 0.1128 0.4588 0.0000 1,721.682 3 1,721.682
3 0.1294 0.0000 1,724.918
3 Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Quarter Start Date End Date Maximum Unmitigated ROG + NOX (tons/quarter) Maximum Mitigated ROG + NOX (tons/quarter) 1 9-1-2021 11-30-2021 1.4103 1.4103
2 12-1-2021 2-28-2022 1.3613 1.3613
3 3-1-2022 5-31-2022 1.1985 1.1985
4 6-1-2022 8-31-2022 1.1921 1.1921
5 9-1-2022 11-30-2022 1.1918 1.1918
6 12-1-2022 2-28-2023 1.0774 1.0774
7 3-1-2023 5-31-2023 1.0320 1.0320
8 6-1-2023 8-31-2023 1.0260 1.0260
CalEEMod Version: CalEEMod.2016.3.2 Page 5 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 254

2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 5.1437 0.2950 10.3804 1.6700e0030.0714 0.0714 0.0714 0.0714 0.0000 220.9670 220.9670 0.0201 3.7400e003222.5835 Energy 0.1398 1.2312 0.7770 7.6200e0030.0966 0.0966 0.0966 0.0966 0.0000 3,896.073 2 3,896.073
2 0.1303 0.0468 3,913.283
3 Mobile 1.5857 7.9962 19.1834 0.0821 7.7979 0.0580 7.8559 2.0895 0.0539 2.1434 0.0000 7,620.498 6 7,620.498
6 0.3407 0.0000 7,629.016
2 Waste 0.0000 0.0000 0.0000 0.0000 207.8079 0.0000 207.8079 12.2811 0.0000 514.8354 Water 0.0000 0.0000 0.0000 0.0000 29.1632 556.6420 585.8052 3.0183 0.0755 683.7567 Total 6.8692 9.5223 30.3407 0.0914 7.7979 0.2260 8.0240 2.0895 0.2219 2.3114 236.9712 12,294.18 07 12,531.15
19 15.7904 0.1260 12,963.47
51 Unmitigated Operational
9 9-1-2023 11-30-2023 1.0265 1.0265
10 12-1-2023 2-29-2024 2.8857 2.8857
11 3-1-2024 5-31-2024 1.6207 1.6207
Highest 2.8857 2.8857
CalEEMod Version: CalEEMod.2016.3.2 Page 6 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 255

3.0 Construction Detail
Construction Phase
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 7 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 256
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 9/1/2021 10/12/2021 5 30
2 Site Preparation Site Preparation 10/13/2021 11/9/2021 5 20 3 Grading Grading 11/10/2021 1/11/2022 5 45
4 Building Construction Building Construction 1/12/2022 12/12/2023 5 500 5 Paving Paving 12/13/2023 1/30/2024 5 35
6 Architectural Coating Architectural Coating 1/31/2024 3/19/2024 5 35 OffRoad Equipment
Residential Indoor: 2,025,000; Residential Outdoor: 675,000; Non-Residential Indoor: 326,400; Non-Residential Outdoor: 108,800; Striped Parking Area: 0 (Architectural Coating ±sqft)
Acres of Grading (Site Preparation Phase): 0
Acres of Grading (Grading Phase): 112.5
Acres of Paving: 0
CalEEMod Version: CalEEMod.2016.3.2 Page 8 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 257
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Demolition Concrete/Industrial Saws 1 8.00 81 0.73
Demolition Excavators 3 8.00 158 0.38
Demolition Rubber Tired Dozers 2 8.00 247 0.40
Site Preparation Rubber Tired Dozers 3 8.00 247 0.40
Site Preparation Tractors/Loaders/Backhoes 4 8.00 97 0.37 Grading Excavators 2 8.00 158 0.38
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Scrapers 2 8.00 367 0.48
Grading Tractors/Loaders/Backhoes 2 8.00 97 0.37
Building Construction Cranes 1 7.00 231 0.29
Building Construction Forklifts 3 8.00 89 0.20
Building Construction Generator Sets 1 8.00 84 0.74
Building Construction Tractors/Loaders/Backhoes 3 7.00 97 0.37 Building Construction Welders 1 8.00 46 0.45
Paving Pavers 2 8.00 130 0.42
Paving Paving Equipment 2 8.00 132 0.36
Paving Rollers 2 8.00 80 0.38
Architectural Coating Air Compressors 1 6.00 78 0.48
Trips and VMT
CalEEMod Version: CalEEMod.2016.3.2 Page 9 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 258

3.2 Demolition - 2021
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0496 0.0000 0.0496 7.5100e0030.0000 7.5100e0030.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0475 0.4716 0.3235 5.8000e0040.0233 0.0233 0.0216 0.0216 0.0000 51.0012 51.0012 0.0144 0.0000 51.3601 Total 0.0475 0.4716 0.3235 5.8000e0040.0496 0.0233 0.0729 7.5100e0030.0216 0.0291 0.0000 51.0012 51.0012 0.0144 0.0000 51.3601 Unmitigated Construction On-Site

3.1 Mitigation Measures Construction
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Demolition 6 15.00 0.00 458.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Site Preparation 7 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 801.00 143.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 160.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 10 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 259

3.2 Demolition - 2021
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 1.9300e0030.0634 0.0148 1.8000e0043.9400e0031.9000e0044.1300e0031.0800e0031.8000e0041.2600e0030.0000 17.4566 17.4566 1.2100e0030.0000 17.4869 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 9.7000e0047.5000e0048.5100e0032.0000e0052.4700e0032.0000e0052.4900e0036.5000e0042.0000e0056.7000e0040.0000 2.2251 2.2251 7.0000e0050.0000 2.2267 Total 2.9000e0030.0641 0.0233 2.0000e0046.4100e0032.1000e0046.6200e0031.7300e0032.0000e0041.9300e0030.0000 19.6816 19.6816 1.2800e0030.0000 19.7136 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0496 0.0000 0.0496 7.5100e0030.0000 7.5100e0030.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0475 0.4716 0.3235 5.8000e0040.0233 0.0233 0.0216 0.0216 0.0000 51.0011 51.0011 0.0144 0.0000 51.3600 Total 0.0475 0.4716 0.3235 5.8000e0040.0496 0.0233 0.0729 7.5100e0030.0216 0.0291 0.0000 51.0011 51.0011 0.0144 0.0000 51.3600 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 11 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 260

3.3 Site Preparation - 2021
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 7.7000e0046.0000e0046.8100e0032.0000e0051.9700e0032.0000e0051.9900e0035.2000e0041.0000e0055.4000e0040.0000 1.7801 1.7801 5.0000e0050.0000 1.7814 Total 7.7000e0046.0000e0046.8100e0032.0000e0051.9700e0032.0000e0051.9900e0035.2000e0041.0000e0055.4000e0040.0000 1.7801 1.7801 5.0000e0050.0000 1.7814 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.1807 0.0000 0.1807 0.0993 0.0000 0.0993 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0389 0.4050 0.2115 3.8000e0040.0204 0.0204 0.0188 0.0188 0.0000 33.4357 33.4357 0.0108 0.0000 33.7060 Total 0.0389 0.4050 0.2115 3.8000e0040.1807 0.0204 0.2011 0.0993 0.0188 0.1181 0.0000 33.4357 33.4357 0.0108 0.0000 33.7060 Mitigated Construction On-Site
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3.4 Grading - 2021
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.1741 0.0000 0.1741 0.0693 0.0000 0.0693 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0796 0.8816 0.5867 1.1800e0030.0377 0.0377 0.0347 0.0347 0.0000 103.5405 103.5405 0.0335 0.0000 104.3776 Total 0.0796 0.8816 0.5867 1.1800e0030.1741 0.0377 0.2118 0.0693 0.0347 0.1040 0.0000 103.5405 103.5405 0.0335 0.0000 104.3776 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 14 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 263

3.4 Grading - 2021
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.6400e0031.2700e0030.0144 4.0000e0054.1600e0033.0000e0054.2000e0031.1100e0033.0000e0051.1400e0030.0000 3.7579 3.7579 1.1000e0040.0000 3.7607 Total 1.6400e0031.2700e0030.0144 4.0000e0054.1600e0033.0000e0054.2000e0031.1100e0033.0000e0051.1400e0030.0000 3.7579 3.7579 1.1000e0040.0000 3.7607 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.1741 0.0000 0.1741 0.0693 0.0000 0.0693 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0796 0.8816 0.5867 1.1800e0030.0377 0.0377 0.0347 0.0347 0.0000 103.5403 103.5403 0.0335 0.0000 104.3775 Total 0.0796 0.8816 0.5867 1.1800e0030.1741 0.0377 0.2118 0.0693 0.0347 0.1040 0.0000 103.5403 103.5403 0.0335 0.0000 104.3775 Mitigated Construction On-Site
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3.4 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0807 0.0000 0.0807 0.0180 0.0000 0.0180 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0127 0.1360 0.1017 2.2000e0045.7200e0035.7200e0035.2600e0035.2600e0030.0000 19.0871 19.0871 6.1700e0030.0000 19.2414 Total 0.0127 0.1360 0.1017 2.2000e0040.0807 5.7200e0030.0865 0.0180 5.2600e0030.0233 0.0000 19.0871 19.0871 6.1700e0030.0000 19.2414 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 16 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 265

3.4 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 2.8000e0042.1000e0042.4400e0031.0000e0057.7000e0041.0000e0057.7000e0042.0000e0041.0000e0052.1000e0040.0000 0.6679 0.6679 2.0000e0050.0000 0.6684 Total 2.8000e0042.1000e0042.4400e0031.0000e0057.7000e0041.0000e0057.7000e0042.0000e0041.0000e0052.1000e0040.0000 0.6679 0.6679 2.0000e0050.0000 0.6684 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0807 0.0000 0.0807 0.0180 0.0000 0.0180 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0127 0.1360 0.1017 2.2000e0045.7200e0035.7200e0035.2600e0035.2600e0030.0000 19.0871 19.0871 6.1700e0030.0000 19.2414 Total 0.0127 0.1360 0.1017 2.2000e0040.0807 5.7200e0030.0865 0.0180 5.2600e0030.0233 0.0000 19.0871 19.0871 6.1700e0030.0000 19.2414 Mitigated Construction On-Site
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3.5 Building Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.2158 1.9754 2.0700 3.4100e0030.1023 0.1023 0.0963 0.0963 0.0000 293.1324 293.1324 0.0702 0.0000 294.8881 Total 0.2158 1.9754 2.0700 3.4100e0030.1023 0.1023 0.0963 0.0963 0.0000 293.1324 293.1324 0.0702 0.0000 294.8881 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 18 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 267

3.5 Building Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0527 1.6961 0.4580 4.5500e0030.1140 3.1800e0030.1171 0.0329 3.0400e0030.0359 0.0000 441.9835 441.9835 0.0264 0.0000 442.6435 Worker 0.4088 0.3066 3.5305 0.0107 1.1103 8.8700e0031.1192 0.2949 8.1700e0030.3031 0.0000 966.8117 966.8117 0.0266 0.0000 967.4773 Total 0.4616 2.0027 3.9885 0.0152 1.2243 0.0121 1.2363 0.3278 0.0112 0.3390 0.0000 1,408.795 2 1,408.795
2 0.0530 0.0000 1,410.120
8 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.2158 1.9754 2.0700 3.4100e0030.1023 0.1023 0.0963 0.0963 0.0000 293.1321 293.1321 0.0702 0.0000 294.8877 Total 0.2158 1.9754 2.0700 3.4100e0030.1023 0.1023 0.0963 0.0963 0.0000 293.1321 293.1321 0.0702 0.0000 294.8877 Mitigated Construction On-Site
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3.5 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.1942 1.7765 2.0061 3.3300e0030.0864 0.0864 0.0813 0.0813 0.0000 286.2789 286.2789 0.0681 0.0000 287.9814 Total 0.1942 1.7765 2.0061 3.3300e0030.0864 0.0864 0.0813 0.0813 0.0000 286.2789 286.2789 0.0681 0.0000 287.9814 Unmitigated Construction On-Site
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3.5 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0382 1.2511 0.4011 4.3000e0030.1113 1.4600e0030.1127 0.0321 1.4000e0030.0335 0.0000 417.9930 417.9930 0.0228 0.0000 418.5624 Worker 0.3753 0.2708 3.1696 0.0101 1.0840 8.4100e0031.0924 0.2879 7.7400e0030.2957 0.0000 909.3439 909.3439 0.0234 0.0000 909.9291 Total 0.4135 1.5218 3.5707 0.0144 1.1953 9.8700e0031.2051 0.3200 9.1400e0030.3292 0.0000 1,327.336 9 1,327.336
9 0.0462 0.0000 1,328.491
6 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.1942 1.7765 2.0061 3.3300e0030.0864 0.0864 0.0813 0.0813 0.0000 286.2785 286.2785 0.0681 0.0000 287.9811 Total 0.1942 1.7765 2.0061 3.3300e0030.0864 0.0864 0.0813 0.0813 0.0000 286.2785 286.2785 0.0681 0.0000 287.9811 Mitigated Construction On-Site
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3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 6.7100e0030.0663 0.0948 1.5000e0043.3200e0033.3200e0033.0500e0033.0500e0030.0000 13.0175 13.0175 4.2100e0030.0000 13.1227 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 6.7100e0030.0663 0.0948 1.5000e0043.3200e0033.3200e0033.0500e0033.0500e0030.0000 13.0175 13.0175 4.2100e0030.0000 13.1227 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 22 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 271

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.7000e0042.7000e0043.1200e0031.0000e0051.0700e0031.0000e0051.0800e0032.8000e0041.0000e0052.9000e0040.0000 0.8963 0.8963 2.0000e0050.0000 0.8968 Total 3.7000e0042.7000e0043.1200e0031.0000e0051.0700e0031.0000e0051.0800e0032.8000e0041.0000e0052.9000e0040.0000 0.8963 0.8963 2.0000e0050.0000 0.8968 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 6.7100e0030.0663 0.0948 1.5000e0043.3200e0033.3200e0033.0500e0033.0500e0030.0000 13.0175 13.0175 4.2100e0030.0000 13.1227 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 6.7100e0030.0663 0.0948 1.5000e0043.3200e0033.3200e0033.0500e0033.0500e0030.0000 13.0175 13.0175 4.2100e0030.0000 13.1227 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 23 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 272

3.6 Paving - 2024
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0109 0.1048 0.1609 2.5000e0045.1500e0035.1500e0034.7400e0034.7400e0030.0000 22.0292 22.0292 7.1200e0030.0000 22.2073 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0109 0.1048 0.1609 2.5000e0045.1500e0035.1500e0034.7400e0034.7400e0030.0000 22.0292 22.0292 7.1200e0030.0000 22.2073 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 24 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 273

3.6 Paving - 2024
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 5.9000e0044.1000e0044.9200e0032.0000e0051.8100e0031.0000e0051.8200e0034.8000e0041.0000e0054.9000e0040.0000 1.4697 1.4697 4.0000e0050.0000 1.4706 Total 5.9000e0044.1000e0044.9200e0032.0000e0051.8100e0031.0000e0051.8200e0034.8000e0041.0000e0054.9000e0040.0000 1.4697 1.4697 4.0000e0050.0000 1.4706 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0109 0.1048 0.1609 2.5000e0045.1500e0035.1500e0034.7400e0034.7400e0030.0000 22.0292 22.0292 7.1200e0030.0000 22.2073 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0109 0.1048 0.1609 2.5000e0045.1500e0035.1500e0034.7400e0034.7400e0030.0000 22.0292 22.0292 7.1200e0030.0000 22.2073 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 25 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 274

3.7 Architectural Coating - 2024
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0101 6.9900e0030.0835 2.8000e0040.0307 2.3000e0040.0309 8.1500e0032.2000e0048.3700e0030.0000 24.9407 24.9407 6.1000e0040.0000 24.9558 Total 0.0101 6.9900e0030.0835 2.8000e0040.0307 2.3000e0040.0309 8.1500e0032.2000e0048.3700e0030.0000 24.9407 24.9407 6.1000e0040.0000 24.9558 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 4.1372 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 3.1600e0030.0213 0.0317 5.0000e0051.0700e0031.0700e0031.0700e0031.0700e0030.0000 4.4682 4.4682 2.5000e0040.0000 4.4745 Total 4.1404 0.0213 0.0317 5.0000e0051.0700e0031.0700e0031.0700e0031.0700e0030.0000 4.4682 4.4682 2.5000e0040.0000 4.4745 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 27 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 276

4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile

3.7 Architectural Coating - 2024
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0101 6.9900e0030.0835 2.8000e0040.0307 2.3000e0040.0309 8.1500e0032.2000e0048.3700e0030.0000 24.9407 24.9407 6.1000e0040.0000 24.9558 Total 0.0101 6.9900e0030.0835 2.8000e0040.0307 2.3000e0040.0309 8.1500e0032.2000e0048.3700e0030.0000 24.9407 24.9407 6.1000e0040.0000 24.9558 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 28 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 277
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 1.5857 7.9962 19.1834 0.0821 7.7979 0.0580 7.8559 2.0895 0.0539 2.1434 0.0000 7,620.498 6 7,620.498
6 0.3407 0.0000 7,629.016
2 Unmitigated 1.5857 7.9962 19.1834 0.0821 7.7979 0.0580 7.8559 2.0895 0.0539 2.1434 0.0000 7,620.498 6 7,620.498
6 0.3407 0.0000 7,629.016
2 4.2 Trip Summary Information

4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Apartments Low Rise 145.75 154.25 154.00 506,227 506,227 Apartments Mid Rise 4,026.75 3,773.25 4075.50 13,660,065 13,660,065 General Office Building 288.45 62.55 31.05 706,812 706,812 High Turnover (Sit Down Restaurant) 2,368.80 2,873.52 2817.72 3,413,937 3,413,937 Hotel 192.00 187.50 160.00 445,703 445,703
Quality Restaurant 501.12 511.92 461.20 707,488 707,488 Regional Shopping Center 528.08 601.44 357.84 1,112,221 1,112,221 Total 8,050.95 8,164.43 8,057.31 20,552,452 20,552,452
CalEEMod Version: CalEEMod.2016.3.2 Page 29 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 278
Miles Trip % Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by Apartments Low Rise 14.70 5.90 8.70 40.20 19.20 40.60 86 11 3 Apartments Mid Rise 14.70 5.90 8.70 40.20 19.20 40.60 86 11 3 General Office Building 16.60 8.40 6.90 33.00 48.00 19.00 77 19 4 High Turnover (Sit Down
Restaurant)

16.60 8.40 6.90 8.50 72.50 19.00 37 20 43
Hotel 16.60 8.40 6.90 19.40 61.60 19.00 58 38 4
Quality Restaurant 16.60 8.40 6.90 12.00 69.00 19.00 38 18 44 Regional Shopping Center 16.60 8.40 6.90 16.30 64.70 19.00 54 35 11

5.0 Energy Detail

5.1 Mitigation Measures Energy

4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Apartments Low Rise 0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 Apartments Mid Rise 0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 General Office Building 0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 High Turnover (Sit Down
Restaurant)

0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 Hotel 0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 Quality Restaurant 0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 Regional Shopping Center 0.543088 0.044216 0.209971 0.116369 0.014033 0.006332 0.021166 0.033577 0.002613 0.001817 0.005285 0.000712 0.000821 Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Page 30 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 279
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Electricity
Mitigated

0.0000 0.0000 0.0000 0.0000 0.0000 2,512.646
5 2,512.646
5 0.1037 0.0215 2,521.635
6 Electricity
Unmitigated

0.0000 0.0000 0.0000 0.0000 0.0000 2,512.646
5 2,512.646
5 0.1037 0.0215 2,521.635
6 NaturalGas
Mitigated

0.1398 1.2312 0.7770 7.6200e0030.0966 0.0966 0.0966 0.0966 0.0000 1,383.426 7 1,383.426
7 0.0265 0.0254 1,391.647
8 NaturalGas
Unmitigated

0.1398 1.2312 0.7770 7.6200e0030.0966 0.0966 0.0966 0.0966 0.0000 1,383.426 7 1,383.426
7 0.0265 0.0254 1,391.647
8 CalEEMod Version: CalEEMod.2016.3.2 Page 31 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 280

1.30613e
+007

0.0704 0.6018 0.2561 3.8400e0030.0487 0.0487 0.0487 0.0487 0.0000 696.9989 696.9989 0.0134 0.0128 701.1408 General Office
Building
468450 2.5300e0030.0230 0.0193 1.4000e0041.7500e0031.7500e0031.7500e0031.7500e0030.0000 24.9983 24.9983 4.8000e0044.6000e00425.1468 High Turnover (Sit
Down Restaurant)

8.30736e
+006

0.0448 0.4072 0.3421 2.4400e0030.0310 0.0310 0.0310 0.0310 0.0000 443.3124 443.3124 8.5000e0038.1300e003445.9468 Hotel 1.74095e
+006

9.3900e0030.0853 0.0717 5.1000e0046.4900e0036.4900e0036.4900e0036.4900e0030.0000 92.9036 92.9036 1.7800e0031.7000e00393.4557 Quality
Restaurant

1.84608e
+006

9.9500e0030.0905 0.0760 5.4000e0046.8800e0036.8800e0036.8800e0036.8800e0030.0000 98.5139 98.5139 1.8900e0031.8100e00399.0993 Regional
Shopping Center
91840 5.0000e0044.5000e0033.7800e0033.0000e0053.4000e0043.4000e0043.4000e0043.4000e0040.0000 4.9009 4.9009 9.0000e0059.0000e0054.9301 Total 0.1398 1.2312 0.7770 7.6200e0030.0966 0.0966 0.0966 0.0966 0.0000 1,383.426 8 1,383.426
8 0.0265 0.0254 1,391.647
8 Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 32 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 281

1.30613e
+007

8.30736e
+006

0.0448 0.4072 0.3421 2.4400e0030.0310 0.0310 0.0310 0.0310 0.0000 443.3124 443.3124 8.5000e0038.1300e003445.9468 Hotel 1.74095e
+006

9.3900e0030.0853 0.0717 5.1000e0046.4900e0036.4900e0036.4900e0036.4900e0030.0000 92.9036 92.9036 1.7800e0031.7000e00393.4557 Quality
Restaurant

1.84608e
+006

9.9500e0030.0905 0.0760 5.4000e0046.8800e0036.8800e0036.8800e0036.8800e0030.0000 98.5139 98.5139 1.8900e0031.8100e00399.0993 Regional
Shopping Center
91840 5.0000e0044.5000e0033.7800e0033.0000e0053.4000e0043.4000e0043.4000e0043.4000e0040.0000 4.9009 4.9009 9.0000e0059.0000e0054.9301 Total 0.1398 1.2312 0.7770 7.6200e0030.0966 0.0966 0.0966 0.0966 0.0000 1,383.426 8 1,383.426
8 0.0265 0.0254 1,391.647
8 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 33 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 282

5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Apartments Low
Rise
106010 33.7770 1.3900e0032.9000e00433.8978
Apartments Mid
Rise

3.94697e
+006
1,257.587
9 0.0519 0.0107 1,262.086
9 General Office
Building
584550 186.2502 7.6900e0031.5900e003186.9165
High Turnover (Sit
Down Restaurant)

6.1 Mitigation Measures Area

6.0 Area Detail

5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Apartments Low
Rise
106010 33.7770 1.3900e0032.9000e00433.8978
Apartments Mid
Rise

3.94697e
+006
1,257.587
9 0.0519 0.0107 1,262.086
9 General Office
Building
584550 186.2502 7.6900e0031.5900e003186.9165
High Turnover (Sit
Down Restaurant)

1.58904e
+006
506.3022 0.0209 4.3200e003508.1135
Hotel 550308 175.3399 7.2400e0031.5000e003175.9672
Quality
Restaurant
353120 112.5116 4.6500e0039.6000e004112.9141
Regional
Shopping Center
756000 240.8778 9.9400e0032.0600e003241.7395
Total 2,512.646
5 0.1037 0.0215 2,521.635
6 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 35 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 284
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 5.1437 0.2950 10.3804 1.6700e0030.0714 0.0714 0.0714 0.0714 0.0000 220.9670 220.9670 0.0201 3.7400e003222.5835 Unmitigated 5.1437 0.2950 10.3804 1.6700e0030.0714 0.0714 0.0714 0.0714 0.0000 220.9670 220.9670 0.0201 3.7400e003222.5835

6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating

0.4137 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products

7.1 Mitigation Measures Water

7.0 Water Detail

0.4137 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products

4.3998 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 0.0206 0.1763 0.0750 1.1200e0030.0143 0.0143 0.0143 0.0143 0.0000 204.1166 204.1166 3.9100e0033.7400e003205.3295 Landscaping 0.3096 0.1187 10.3054 5.4000e0040.0572 0.0572 0.0572 0.0572 0.0000 16.8504 16.8504 0.0161 0.0000 17.2540 Total 5.1437 0.2950 10.3804 1.6600e0030.0714 0.0714 0.0714 0.0714 0.0000 220.9670 220.9670 0.0201 3.7400e003222.5835 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 37 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 286
Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 585.8052 3.0183 0.0755 683.7567
Unmitigated 585.8052 3.0183 0.0755 683.7567
CalEEMod Version: CalEEMod.2016.3.2 Page 38 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 287

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Apartments Low
Rise

1.62885 /

1.02688

10.9095 0.0535 1.3400e00312.6471
Apartments Mid
Rise

63.5252 /

40.0485
425.4719 2.0867 0.0523 493.2363
General Office
Building

7.99802 /

4.90201

53.0719 0.2627 6.5900e00361.6019
High Turnover (Sit
Down Restaurant)

10.9272 /

0.697482

51.2702 0.3580 8.8200e00362.8482
Hotel 1.26834 /

0.140927

6.1633 0.0416 1.0300e0037.5079
Quality
Restaurant

2.42827 /

0.154996

11.3934 0.0796 1.9600e00313.9663
Regional
Shopping Center

4.14806 /

2.54236

27.5250 0.1363 3.4200e00331.9490
Total 585.8052 3.0183 0.0755 683.7567
Unmitigated
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8.1 Mitigation Measures Waste

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Apartments Low
Rise

1.62885 /

1.02688

10.9095 0.0535 1.3400e00312.6471
Apartments Mid
Rise

63.5252 /

40.0485
425.4719 2.0867 0.0523 493.2363
General Office
Building

7.99802 /

4.90201

53.0719 0.2627 6.5900e00361.6019
High Turnover (Sit
Down Restaurant)

10.9272 /

0.697482

51.2702 0.3580 8.8200e00362.8482
Hotel 1.26834 /

0.140927

6.1633 0.0416 1.0300e0037.5079
Quality
Restaurant

2.42827 /

0.154996

11.3934 0.0796 1.9600e00313.9663
Regional
Shopping Center

4.14806 /

2.54236

27.5250 0.1363 3.4200e00331.9490
Total 585.8052 3.0183 0.0755 683.7567
Mitigated

8.0 Waste Detail
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Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 207.8079 12.2811 0.0000 514.8354
Unmitigated 207.8079 12.2811 0.0000 514.8354
Category/Year
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8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Apartments Low
Rise

11.5 2.3344 0.1380 0.0000 5.7834
Apartments Mid
Rise
448.5 91.0415 5.3804 0.0000 225.5513
General Office
Building

41.85 8.4952 0.5021 0.0000 21.0464
High Turnover (Sit
Down Restaurant)
428.4 86.9613 5.1393 0.0000 215.4430
Hotel 27.38 5.5579 0.3285 0.0000 13.7694
Quality
Restaurant

7.3 1.4818 0.0876 0.0000 3.6712
Regional
Shopping Center

58.8 11.9359 0.7054 0.0000 29.5706
Total 207.8079 12.2811 0.0000 514.8354
Unmitigated
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8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Apartments Low
Rise

11.5 2.3344 0.1380 0.0000 5.7834
Apartments Mid
Rise
448.5 91.0415 5.3804 0.0000 225.5513
General Office
Building

41.85 8.4952 0.5021 0.0000 21.0464
High Turnover (Sit
Down Restaurant)
428.4 86.9613 5.1393 0.0000 215.4430
Hotel 27.38 5.5579 0.3285 0.0000 13.7694
Quality
Restaurant

7.3 1.4818 0.0876 0.0000 3.6712
Regional
Shopping Center

58.8 11.9359 0.7054 0.0000 29.5706
Total 207.8079 12.2811 0.0000 514.8354
Mitigated

9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type

10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type CalEEMod Version: CalEEMod.2016.3.2 Page 43 of 44 Date: 1/6/2021 1:52 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Annual 292

11.0 Vegetation
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
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1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
9 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 33

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2028
CO2 Intensity
(lb/MWhr)
702.44 CH4 Intensity 0.029
(lb/MWhr)
N2O Intensity 0.006
(lb/MWhr)
Village South Specific Plan (Proposed)
Los Angeles-South Coast County, Summer
CalEEMod Version: CalEEMod.2016.3.2 Page 1 of 35 Date: 1/6/2021 1:54 PM Village South Specific Plan (Proposed) - Los Angeles-South Coast County, Summer 294
Project Characteristics - Consistent with the DEIR's model.