UCLA Department of Environmental Engineering, February 5, 2002. Seminar on Successful Remediation Technologies focusing on Groundwater Remediation.
University Of Washington, Soil Science Program, Teaching Assistant for several courses including: Soil Chemistry, Organic Soil Amendments, and Soil Stability.
U.C. Berkeley, Environmental Science Program Teaching Assistant for Environmental Science 10.
Academic Grants Awarded:
California Integrated Waste Management Board. $41,000 grant awarded to UCLA Institute of the Environment.
Goal: To investigate effect of high carbon wood ash on volatile organic emissions from compost. 2001.
Synagro Technologies, Corona California: $10,000 grant awarded to San Diego State University.
Goal: investigate effect of biosolids for restoration and remediation of degraded coastal sage soils. 2000.
King County, Department of Research and Technology, Washington State. $100,000 grant awarded to University of Washington: Goal: To investigate odor emissions from biosolids application and the effect of polymers and ash on VOC emissions. 1998.
Northwest Biosolids Management Association, Washington State. $20,000 grant awarded to investigate effect of polymers and ash on VOC emissions from biosolids. 1997.
James River Corporation, Oregon: $10,000 grant was awarded to investigate the success of genetically engineered Poplar trees with resistance to round-up. 1996.
United State Forest Service, Tahoe National Forest: $15,000 grant was awarded to investigating fire ecology of the Tahoe National Forest. 1995.
Kellogg Foundation, Washington D.C. $500 grant was awarded to construct a large anaerobic digester on St. Kitts in West Indies. 1993
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Paul E. Rosenfeld, Ph.D. Page 8 of 10 June 2019
Deposition and/or Trial Testimony:
In the United States District Court For The District of New Jersey Duarte et al, Plaintiffs, vs. United States Metals Refining Company et. al. Defendant.
Case No.: 2:17-cv-01624-ES-SCM
Rosenfeld Deposition. 6-7-2019
In the United States District Court of Southern District of Texas Galveston Division M/T Carla Maersk, Plaintiffs, vs. Conti 168., Schiffahrts-GMBH & Co. Bulker KG MS “Conti Perdido” Defendant.
Case No.: 3:15-CV-00106 consolidated with 3:15-CV-00237 Rosenfeld Deposition. 5-9-2019
In The Superior Court of the State of California In And For The County Of Los Angeles – Santa Monica Carole-Taddeo-Bates et al., vs. Ifran Khan et al., Defendants Case No.: No. BC615636
Rosenfeld Deposition, 1-26-2019
In The Superior Court of the State of California In And For The County Of Los Angeles – Santa Monica The San Gabriel Valley Council of Governments et al. vs El Adobe Apts. Inc. et al., Defendants Case No.: No. BC646857
Rosenfeld Deposition, 10-6-2018; Trial 3-7-19
In United States District Court For The District of Colorado Bells et al. Plaintiff vs. The 3M Company et al., Defendants Case: No 1:16-cv-02531-RBJ
Rosenfeld Deposition, 3-15-2018 and 4-3-2018
In The District Court Of Regan County, Texas, 112th Judicial District Phillip Bales et al., Plaintiff vs. Dow Agrosciences, LLC, et al., Defendants Cause No 1923
Rosenfeld Deposition, 11-17-2017
In The Superior Court of the State of California In And For The County Of Contra Costa Simons et al., Plaintiffs vs. Chevron Corporation, et al., Defendants Cause No C12-01481
Rosenfeld Deposition, 11-20-2017
In The Circuit Court Of The Twentieth Judicial Circuit, St Clair County, Illinois Martha Custer et al., Plaintiff vs. Cerro Flow Products, Inc., Defendants Case No.: No. 0i9-L-2295
Rosenfeld Deposition, 8-23-2017
In The Superior Court of the State of California, For The County of Los Angeles Warrn Gilbert and Penny Gilber, Plaintiff vs. BMW of North America LLC Case No.: LC102019 (c/w BC582154)
Rosenfeld Deposition, 8-16-2017, Trail 8-28-2018
In the Northern District Court of Mississippi, Greenville Division Brenda J. Cooper, et al., Plaintiffs, vs. Meritor Inc., et al., Defendants Case Number: 4:16-cv-52-DMB-JVM
Rosenfeld Deposition: July 2017
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Paul E. Rosenfeld, Ph.D. Page 9 of 10 June 2019
In The Superior Court of the State of Washington, County of Snohomish Michael Davis and Julie Davis et al., Plaintiff vs. Cedar Grove Composting Inc., Defendants Case No.: No. 13-2-03987-5
Rosenfeld Deposition, February 2017
Trial, March 2017
In The Superior Court of the State of California, County of Alameda Charles Spain., Plaintiff vs. Thermo Fisher Scientific, et al., Defendants Case No.: RG14711115
Rosenfeld Deposition, September 2015
In The Iowa District Court In And For Poweshiek County
Russell D. Winburn, et al., Plaintiffs vs. Doug Hoksbergen, et al., Defendants Case No.: LALA002187
Rosenfeld Deposition, August 2015
In The Iowa District Court For Wapello County
Jerry Dovico, et al., Plaintiffs vs. Valley View Sine LLC, et al., Defendants Law No,: LALA105144 - Division A
Rosenfeld Deposition, August 2015
In The Iowa District Court For Wapello County
Doug Pauls, et al.,, et al., Plaintiffs vs. Richard Warren, et al., Defendants Law No,: LALA105144 - Division A
Rosenfeld Deposition, August 2015
In The Circuit Court of Ohio County, West Virginia
Robert Andrews, et al. v. Antero, et al.
Civil Action N0. 14-C-30000
Rosenfeld Deposition, June 2015
In The Third Judicial District County of Dona Ana, New Mexico Betty Gonzalez, et al. Plaintiffs vs. Del Oro Dairy, Del Oro Real Estate LLC, Jerry Settles and Deward DeRuyter, Defendants
Rosenfeld Deposition: July 2015
In The Iowa District Court For Muscatine County
Laurie Freeman et. al. Plaintiffs vs. Grain Processing Corporation, Defendant Case No 4980
Rosenfeld Deposition: May 2015
In the Circuit Court of the 17th Judicial Circuit, in and For Broward County, Florida Walter Hinton, et. al. Plaintiff, vs. City of Fort Lauderdale, Florida, a Municipality, Defendant.
Case Number CACE07030358 (26)
Rosenfeld Deposition: December 2014
In the United States District Court Western District of Oklahoma Tommy McCarty, et al., Plaintiffs, v. Oklahoma City Landfill, LLC d/b/a Southeast Oklahoma City Landfill, et al. Defendants.
Case No. 5:12-cv-01152-C
Rosenfeld Deposition: July 2014
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Paul E. Rosenfeld, Ph.D. Page 10 of 10 June 2019
In the County Court of Dallas County Texas
Lisa Parr et al, Plaintiff, vs. Aruba et al, Defendant.
Case Number cc-11-01650-E
Rosenfeld Deposition: March and September 2013
Rosenfeld Trial: April 2014
In the Court of Common Pleas of Tuscarawas County Ohio
John Michael Abicht, et al., Plaintiffs, vs. Republic Services, Inc., et al., Defendants Case Number: 2008 CT 10 0741 (Cons. w/ 2009 CV 10 0987) Rosenfeld Deposition: October 2012
In the United States District Court of Southern District of Texas Galveston Division Kyle Cannon, Eugene Donovan, Genaro Ramirez, Carol Sassler, and Harvey Walton, each Individually and on behalf of those similarly situated, Plaintiffs, vs. BP Products North America, Inc., Defendant.
Case 3:10-cv-00622
Rosenfeld Deposition: February 2012
Rosenfeld Trial: April 2013
In the Circuit Court of Baltimore County Maryland
Philip E. Cvach, II et al., Plaintiffs vs. Two Farms, Inc. d/b/a Royal Farms, Defendants Case Number: 03-C-12-012487 OT
Rosenfeld Deposition: September 2013
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EXHIBIT C
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1640 5th St.., Suite 204 Santa
Santa Monica, California 90401
Tel: (949) 887‐9013
Email: [email protected]
Matthew F. Hagemann, P.G., C.Hg., QSD, QSP
Geologic and Hydrogeologic Characterization
Industrial Stormwater Compliance
Investigation and Remediation Strategies
Litigation Support and Testifying Expert
CEQA Review
Education:
M.S. Degree, Geology, California State University Los Angeles, Los Angeles, CA, 1984.
B.A. Degree, Geology, Humboldt State University, Arcata, CA, 1982.
Professional Certifications:
California Professional Geologist
California Certified Hydrogeologist
Qualified SWPPP Developer and Practitioner
Professional Experience:
Matt has 25 years of experience in environmental policy, assessment and remediation. He spent nine years with the U.S. EPA in the RCRA and Superfund programs and served as EPA’s Senior Science Policy Advisor in the Western Regional Office where he identified emerging threats to groundwater from perchlorate and MTBE. While with EPA, Matt also served as a Senior Hydrogeologist in the oversight of the assessment of seven major military facilities undergoing base closure. He led numerous enforcement actions under provisions of the Resource Conservation and Recovery Act (RCRA) while also working with permit holders to improve hydrogeologic characterization and water quality monitoring.
Matt has worked closely with U.S. EPA legal counsel and the technical staff of several states in the application and enforcement of RCRA, Safe Drinking Water Act and Clean Water Act regulations. Matt has trained the technical staff in the States of California, Hawaii, Nevada, Arizona and the Territory of Guam in the conduct of investigations, groundwater fundamentals, and sampling techniques.
Positions Matt has held include:
•Founding Partner, Soil/Water/Air Protection Enterprise (SWAPE) (2003 – present); •Geology Instructor, Golden West College, 2010 – 2014;
•Senior Environmental Analyst, Komex H2O Science, Inc. (2000 ‐‐ 2003); 10-348
• Executive Director, Orange Coast Watch (2001 – 2004); • Senior Science Policy Advisor and Hydrogeologist, U.S. Environmental Protection Agency (1989– 1998);
• Hydrogeologist, National Park Service, Water Resources Division (1998 – 2000); • Adjunct Faculty Member, San Francisco State University, Department of Geosciences (1993 – 1998);
• Instructor, College of Marin, Department of Science (1990 – 1995); • Geologist, U.S. Forest Service (1986 – 1998); and
• Geologist, Dames & Moore (1984 – 1986).
Senior Regulatory and Litigation Support Analyst:
With SWAPE, Matt’s responsibilities have included:
• Lead analyst and testifying expert in the review of over 100 environmental impact reports since 2003 under CEQA that identify significant issues with regard to hazardous waste, water resources, water quality, air quality, Valley Fever, greenhouse gas emissions, and geologic hazards. Make recommendations for additional mitigation measures to lead agencies at the local and county level to include additional characterization of health risks and implementation of protective measures to reduce worker exposure to hazards from toxins and Valley Fever.
• Stormwater analysis, sampling and best management practice evaluation at industrial facilities. • Manager of a project to provide technical assistance to a community adjacent to a former Naval shipyard under a grant from the U.S. EPA.
• Technical assistance and litigation support for vapor intrusion concerns. • Lead analyst and testifying expert in the review of environmental issues in license applications for large solar power plants before the California Energy Commission. • Manager of a project to evaluate numerous formerly used military sites in the western U.S. • Manager of a comprehensive evaluation of potential sources of perchlorate contamination in Southern California drinking water wells.
• Manager and designated expert for litigation support under provisions of Proposition 65 in the review of releases of gasoline to sources drinking water at major refineries and hundreds of gas stations throughout California.
• Expert witness on two cases involving MTBE litigation. • Expert witness and litigation support on the impact of air toxins and hazards at a school. • Expert witness in litigation at a former plywood plant.
With Komex H2O Science Inc., Matt’s duties included the following:
• Senior author of a report on the extent of perchlorate contamination that was used in testimony by the former U.S. EPA Administrator and General Counsel. • Senior researcher in the development of a comprehensive, electronically interactive chronology of MTBE use, research, and regulation.
• Senior researcher in the development of a comprehensive, electronically interactive chronology of perchlorate use, research, and regulation.
• Senior researcher in a study that estimates nationwide costs for MTBE remediation and drinking water treatment, results of which were published in newspapers nationwide and in testimony against provisions of an energy bill that would limit liability for oil companies. • Research to support litigation to restore drinking water supplies that have been contaminated by MTBE in California and New York.
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• Expert witness testimony in a case of oil production‐related contamination in Mississippi. • Lead author for a multi‐volume remedial investigation report for an operating school in Los Angeles that met strict regulatory requirements and rigorous deadlines. 10-350
• Development of strategic approaches for cleanup of contaminated sites in consultation with clients and regulators.
Executive Director:
As Executive Director with Orange Coast Watch, Matt led efforts to restore water quality at Orange County beaches from multiple sources of contamination including urban runoff and the discharge of wastewater. In reporting to a Board of Directors that included representatives from leading Orange County universities and businesses, Matt prepared issue papers in the areas of treatment and disinfection of wastewater and control of the discharge of grease to sewer systems. Matt actively participated in the development of countywide water quality permits for the control of urban runoff and permits for the discharge of wastewater. Matt worked with other nonprofits to protect and restore water quality, including Surfrider, Natural Resources Defense Council and Orange County CoastKeeper as well as with business institutions including the Orange County Business Council.
Hydrogeology:
As a Senior Hydrogeologist with the U.S. Environmental Protection Agency, Matt led investigations to characterize and cleanup closing military bases, including Mare Island Naval Shipyard, Hunters Point Naval Shipyard, Treasure Island Naval Station, Alameda Naval Station, Moffett Field, Mather Army Airfield, and Sacramento Army Depot. Specific activities were as follows:
• Led efforts to model groundwater flow and contaminant transport, ensured adequacy of monitoring networks, and assessed cleanup alternatives for contaminated sediment, soil, and groundwater.
• Initiated a regional program for evaluation of groundwater sampling practices and laboratory analysis at military bases.
• Identified emerging issues, wrote technical guidance, and assisted in policy and regulation development through work on four national U.S. EPA workgroups, including the Superfund Groundwater Technical Forum and the Federal Facilities Forum.
At the request of the State of Hawaii, Matt developed a methodology to determine the vulnerability of groundwater to contamination on the islands of Maui and Oahu. He used analytical models and a GIS to show zones of vulnerability, and the results were adopted and published by the State of Hawaii and County of Maui.
As a hydrogeologist with the EPA Groundwater Protection Section, Matt worked with provisions of the Safe Drinking Water Act and NEPA to prevent drinking water contamination. Specific activities included the following:
• Received an EPA Bronze Medal for his contribution to the development of national guidance for the protection of drinking water.
• Managed the Sole Source Aquifer Program and protected the drinking water of two communities through designation under the Safe Drinking Water Act. He prepared geologic reports, conducted public hearings, and responded to public comments from residents who were very concerned about the impact of designation.
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• Reviewed a number of Environmental Impact Statements for planned major developments, including large hazardous and solid waste disposal facilities, mine reclamation, and water transfer.
Matt served as a hydrogeologist with the RCRA Hazardous Waste program. Duties were as follows:
• Supervised the hydrogeologic investigation of hazardous waste sites to determine compliance with Subtitle C requirements.
• Reviewed and wrote ʺpart Bʺ permits for the disposal of hazardous waste. • Conducted RCRA Corrective Action investigations of waste sites and led inspections that formed the basis for significant enforcement actions that were developed in close coordination with U.S.
EPA legal counsel.
• Wrote contract specifications and supervised contractor’s investigations of waste sites.
With the National Park Service, Matt directed service‐wide investigations of contaminant sources to prevent degradation of water quality, including the following tasks:
• Applied pertinent laws and regulations including CERCLA, RCRA, NEPA, NRDA, and the Clean Water Act to control military, mining, and landfill contaminants. • Conducted watershed‐scale investigations of contaminants at parks, including Yellowstone and Olympic National Park.
• Identified high‐levels of perchlorate in soil adjacent to a national park in New Mexico and advised park superintendent on appropriate response actions under CERCLA. • Served as a Park Service representative on the Interagency Perchlorate Steering Committee, a national workgroup.
• Developed a program to conduct environmental compliance audits of all National Parks while serving on a national workgroup.
• Co‐authored two papers on the potential for water contamination from the operation of personal watercraft and snowmobiles, these papers serving as the basis for the development of nation‐ wide policy on the use of these vehicles in National Parks. • Contributed to the Federal Multi‐Agency Source Water Agreement under the Clean Water Action Plan.
Policy:
Served senior management as the Senior Science Policy Advisor with the U.S. Environmental Protection Agency, Region 9. Activities included the following:
• Advised the Regional Administrator and senior management on emerging issues such as the potential for the gasoline additive MTBE and ammonium perchlorate to contaminate drinking water supplies.
• Shaped EPA’s national response to these threats by serving on workgroups and by contributing to guidance, including the Office of Research and Development publication, Oxygenates in Water: Critical Information and Research Needs.
• Improved the technical training of EPAʹs scientific and engineering staff. • Earned an EPA Bronze Medal for representing the region’s 300 scientists and engineers in negotiations with the Administrator and senior management to better integrate scientific principles into the policy‐making process.
• Established national protocol for the peer review of scientific documents. 10-352
Geology:
With the U.S. Forest Service, Matt led investigations to determine hillslope stability of areas proposed for timber harvest in the central Oregon Coast Range. Specific activities were as follows:
• Mapped geology in the field, and used aerial photographic interpretation and mathematical models to determine slope stability.
• Coordinated his research with community members who were concerned with natural resource protection.
• Characterized the geology of an aquifer that serves as the sole source of drinking water for the city of Medford, Oregon.
As a consultant with Dames and Moore, Matt led geologic investigations of two contaminated sites (later listed on the Superfund NPL) in the Portland, Oregon, area and a large hazardous waste site in eastern Oregon. Duties included the following:
• Supervised year‐long effort for soil and groundwater sampling. • Conducted aquifer tests.
• Investigated active faults beneath sites proposed for hazardous waste disposal.
Teaching:
From 1990 to 1998, Matt taught at least one course per semester at the community college and university levels:
• At San Francisco State University, held an adjunct faculty position and taught courses in environmental geology, oceanography (lab and lecture), hydrogeology, and groundwater contamination.
• Served as a committee member for graduate and undergraduate students. • Taught courses in environmental geology and oceanography at the College of Marin.
Matt taught physical geology (lecture and lab and introductory geology at Golden West College in Huntington Beach, California from 2010 to 2014.
Invited Testimony, Reports, Papers and Presentations:
Hagemann, M.F., 2008. Disclosure of Hazardous Waste Issues under CEQA. Presentation to the Public Environmental Law Conference, Eugene, Oregon.
Hagemann, M.F., 2008. Disclosure of Hazardous Waste Issues under CEQA. Invited presentation to U.S.
EPA Region 9, San Francisco, California.
Hagemann, M.F., 2005. Use of Electronic Databases in Environmental Regulation, Policy Making and Public Participation. Brownfields 2005, Denver, Coloradao.
Hagemann, M.F., 2004. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in Nevada and the Southwestern U.S. Presentation to a meeting of the American Groundwater Trust, Las Vegas, NV (served on conference organizing committee).
Hagemann, M.F., 2004. Invited testimony to a California Senate committee hearing on air toxins at schools in Southern California, Los Angeles.
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Brown, A., Farrow, J., Gray, A. and Hagemann, M., 2004. An Estimate of Costs to Address MTBE Releases from Underground Storage Tanks and the Resulting Impact to Drinking Water Wells.
Presentation to the Ground Water and Environmental Law Conference, National Groundwater Association.
Hagemann, M.F., 2004. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in Arizona and the Southwestern U.S. Presentation to a meeting of the American Groundwater Trust, Phoenix, AZ (served on conference organizing committee).
Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in the Southwestern U.S. Invited presentation to a special committee meeting of the National Academy of Sciences, Irvine, CA.
Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River. Invited presentation to a tribal EPA meeting, Pechanga, CA.
Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River. Invited presentation to a meeting of tribal repesentatives, Parker, AZ.
Hagemann, M.F., 2003. Impact of Perchlorate on the Colorado River and Associated Drinking Water Supplies. Invited presentation to the Inter‐Tribal Meeting, Torres Martinez Tribe.
Hagemann, M.F., 2003. The Emergence of Perchlorate as a Widespread Drinking Water Contaminant.
Invited presentation to the U.S. EPA Region 9.
Hagemann, M.F., 2003. A Deductive Approach to the Assessment of Perchlorate Contamination. Invited presentation to the California Assembly Natural Resources Committee.
Hagemann, M.F., 2003. Perchlorate: A Cold War Legacy in Drinking Water. Presentation to a meeting of the National Groundwater Association.
Hagemann, M.F., 2002. From Tank to Tap: A Chronology of MTBE in Groundwater. Presentation to a meeting of the National Groundwater Association.
Hagemann, M.F., 2002. A Chronology of MTBE in Groundwater and an Estimate of Costs to Address Impacts to Groundwater. Presentation to the annual meeting of the Society of Environmental Journalists.
Hagemann, M.F., 2002. An Estimate of the Cost to Address MTBE Contamination in Groundwater (and Who Will Pay). Presentation to a meeting of the National Groundwater Association.
Hagemann, M.F., 2002. An Estimate of Costs to Address MTBE Releases from Underground Storage Tanks and the Resulting Impact to Drinking Water Wells. Presentation to a meeting of the U.S. EPA and State Underground Storage Tank Program managers.
Hagemann, M.F., 2001. From Tank to Tap: A Chronology of MTBE in Groundwater. Unpublished report.
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Hagemann, M.F., 2001. Estimated Cleanup Cost for MTBE in Groundwater Used as Drinking Water.
Unpublished report.
Hagemann, M.F., 2001. Estimated Costs to Address MTBE Releases from Leaking Underground Storage Tanks. Unpublished report.
Hagemann, M.F., and VanMouwerik, M., 1999. Potential Water Quality Concerns Related to Snowmobile Usage. Water Resources Division, National Park Service, Technical Report.
VanMouwerik, M. and Hagemann, M.F. 1999, Water Quality Concerns Related to Personal Watercraft Usage. Water Resources Division, National Park Service, Technical Report.
Hagemann, M.F., 1999, Is Dilution the Solution to Pollution in National Parks? The George Wright Society Biannual Meeting, Asheville, North Carolina.
Hagemann, M.F., 1997, The Potential for MTBE to Contaminate Groundwater. U.S. EPA Superfund Groundwater Technical Forum Annual Meeting, Las Vegas, Nevada.
Hagemann, M.F., and Gill, M., 1996, Impediments to Intrinsic Remediation, Moffett Field Naval Air Station, Conference on Intrinsic Remediation of Chlorinated Hydrocarbons, Salt Lake City.
Hagemann, M.F., Fukunaga, G.L., 1996, The Vulnerability of Groundwater to Anthropogenic Contaminants on the Island of Maui, Hawaii. Hawaii Water Works Association Annual Meeting, Maui, October 1996.
Hagemann, M. F., Fukanaga, G. L., 1996, Ranking Groundwater Vulnerability in Central Oahu, Hawaii. Proceedings, Geographic Information Systems in Environmental Resources Management, Air and Waste Management Association Publication VIP‐61.
Hagemann, M.F., 1994. Groundwater Characterization and Cleanup at Closing Military Bases in California. Proceedings, California Groundwater Resources Association Meeting.
Hagemann, M.F. and Sabol, M.A., 1993. Role of the U.S. EPA in the High Plains States Groundwater Recharge Demonstration Program. Proceedings, Sixth Biennial Symposium on the Artificial Recharge of Groundwater.
Hagemann, M.F., 1993. U.S. EPA Policy on the Technical Impracticability of the Cleanup of DNAPL‐ contaminated Groundwater. California Groundwater Resources Association Meeting. 10-355
Hagemann, M.F., 1992. Dense Nonaqueous Phase Liquid Contamination of Groundwater: An Ounce of Prevention... Proceedings, Association of Engineering Geologists Annual Meeting, v. 35.
Other Experience:
Selected as subject matter expert for the California Professional Geologist licensing examination, 2009‐ 2011.
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VIA E-MAIL
May 31, 2022
Majna Dukic, Planning Manager
City of Rancho Mirage
69-825 Highway 111
Rancho Mirage, CA 92270
Em: [email protected]
Kristie Ramos, City Clerk
City of Rancho Mirage
69-825 Highway 111
Rancho Mirage, CA 92270
Em: [email protected]
RE: Highway 111 Specific Plan Environmental Impact Report SCH No. 2020069010 – Supplemental Comment Letter
Dear Majna Dukic and Kristie Ramos,
On behalf of the Southwest Regional Council of Carpenters (“SWRCC” or “Southwest Carpenters”), my Office is submitting these supplemental comments on the City of Rancho Mirage’s (“City” or “Lead Agency”) Draft Environmental Impact Report (“Draft EIR” or “DEIR”) for the Highway 111 Specific Plan (“Project”).
These supplemental comments fully incorporate by reference our prior comments submitted on March 14, 2022.
These supplemental comments note further errors in the Draft EIR, specifically related to the EIR’s air quality & greenhouse gas emission (“GHG”), as well as traffic impacts & vehicle miles traveled (“VMT”) analysis and baseline assumptions, as identified by our experts’ review. These supplemental comments also recommend additional mitigation measures for those areas of impact.
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I. THE DRAFT EIR VIOLATES CEQA AS IT UNDERSTATES
SIGNIFICANT AIR QUALITY & GHG IMPACTS DUE TO
ERRORS IN ANALYSIS AND BASELINE ASSUMPTIONS.
Based on the March 28, 2022 expert report from SWAPE’s Matt Hagemann and Paul E. Rosenfeld (see, Exhibit 1 [3/28/2022 SWAPE Expert Report]), the Draft EIR’s air quality & GHG analysis, baseline assumptions and mitigations measures are inadequate. SWAPE concludes:
An updated EIR should be prepared to adequately assess and mitigate the potential air quality and greenhouse gas impacts that buildout of the Specific Plan may have on the surrounding environment.
Exhibit 1, p. 1.
The reasons for SWAPE’s conclusion are: (1) the EIR’s failure to mitigate the cumulative impacts of air quality emissions which the EIR acknowledged; (2) the EIR’s inadequate evaluation and mitigation of GHG impacts, including improper deferred mitigation; and (3) the EIR’s failure to incorporate feasible mitigation measures for GHG emissions.
A. The EIR Failed to Mitigate Cumulative Air Quality Impacts.
SWAPE notes that the Draft EIR acknowledged potential cumulative impacts in air quality emissions but fails to identify mitigation measures for such impacts. SWAPE references the Draft EIR and states, in relevant parts:
[O]perational air quality emissions for the proposed Specific Plan have the potential to result in a cumulatively considerable net increase of CO, NOX, SOX, PM10, PM2.5, and ROG” (p. 2.4-15).
However, the DEIR fails to implement any mitigation intended to reduce the above-mentioned operational criteria air pollutant emissions. As such, the DEIR fails to adequately address and mitigate the Specific Plan’s cumulative air quality impacts and, as a result, should not be relied upon to determine Project significance.
Exhibit 1, p. 2.
CEQA specifically mandates analysis of cumulative impacts in the EIR. Public Resources Code § 21100; Guidelines § 15064(h). Guidelines § 15130(a) mandates:
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(a) An EIR shall discuss cumulative impacts of a project when the project’s incremental effect is cumulatively considerable, as defined in section 15065 (a)(3). Where a lead agency is examining a project with an incremental effect that is not “cumulatively considerable,” a lead agency need not consider that effect significant, but shall briefly describe its basis for concluding that the incremental effect is not cumulatively considerable.”
It is well-established that “[t]he purpose of CEQA is not to generate paper, but to compel government at all levels to make decisions with environmental consequences in mind.” Bozung v. LAFCO (1975) 13 Cal.3d 263; Guidelines § 15003(g). CEQA has four basic purposes, which include both an affirmative duty to inform and an affirmative duty to mitigate. Guidelines § 15002(a). An EIR – which is the highest level of CEQA analysis – is not a self-serving document; it 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.) Here, by failing to duly address and mitigate the acknowledged cumulative impacts of the Project, the Draft EIR failed CEQA’s affirmative and substantive duty to mitigate and violated CEQA. As stated by SWAPE, the EIR must be updated and recirculated to include mitigation measures for cumulative impacts and to conduct appropriate impacts analysis with those measures in place.
B. The EIR Failed to Adequately Analyze and Mitigate GHG Impacts.
In its letter, SWAPE notes the EIR’s failure to adequately address and mitigate GHG emissions. Specifically, SWAPE points out that EIR admits that the cumulative impacts of GHG emissions from individual projects may occur; yet, SWAPE notes that the mitigation of GHG impacts is improperly deferred and the mitigation measure for GHG emissions (MM GHG-3) is narrowly and improperly limited only to individual projects that require CEQA. Exhibit 1, p. 3.
The EIR’s failure to mitigate GHG cumulative impacts and its deferred mitigation focusing only on projects subject to CEQA review is crucial since the Project is a specific plan and will, by operation of law, exempt future individual projects from CEQA review, including under Government Code § 65457.
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CEQA prohibits deferral of mitigation measures and allows deferral of formulation of specific details of mitigation only in case such formulation of measures is impractical or infeasible to include during the Project’s environmental review and in case the agency commits to such mitigation and provides specific performance standards for same.
Guidelines § 15126.4(a)(1)(B).
SWAPE references the 2017 State Official General Plan Guidelines of the Office of Planning and Research (“OPR”), where the OPR specifically prohibits deferral of mitigation of cumulative impacts in general plan amendments or adoptions to later tiered environmental documents. SWAPE also notes that the planning process of amending general plans is, by law, similar to the amendment of a specific plan (under Government Code § 65453), as here.
Based on its analysis, SWAPE concludes that the EIR improperly and inadequately defers mitigation of GHG impacts and recommends to amend the EIR to ensure that (1) GHG emissions get mitigated regardless of whether they will require CEQA review and (2) such mitigation occurs before project approval rather than prior to issuance of building permits. SWAPE states, in pertinent parts:
As demonstrated above, OPR guidance indicates that lead agencies cannot defer the analysis of any significant effects, as future projects would likely not be required to conduct further environmental review. As such, MM GHG-3 should apply to all future projects under the proposed Specific Plan. Additionally, the evaluation of GHG impacts and the incorporation of additional mitigation measures should be conducted before individual project approval, not just prior to the issuance of grading or demolition permits. Until all future projects within the Specific Plan are required to conduct GHG analyses to adequately evaluate and mitigate GHG impacts, the DEIR should not be relied upon for Project significance.MM GHG- 3 should apply to all future projects under the proposed Specific Plan.
Exhibit 1, p. 3.
Accordingly, the EIR and its GHG mitigation measure, as drafted, violate CEQA in failing to mitigate and in improperly deferring mitigation measures.
The EIR, its proposed mitigation measures and the ultimate mitigation monitoring and reporting plan must be updated/drafted to include SWAPE’s recommendations, to ensure that the City complies with CEQA’s mitigation mandate as to GHG emissions 10-360
by making binding commitments to alleviate those impacts. (E.g., Napa Citizens for Honest Government v. Napa County Bd. of Supervisors (2001) 91 Cal.App.4th 342, 380 [Updated Specific Plan, however, makes no binding commitment to do anything to alleviate the impact the Project will have on traffic and housing].) C. The EIR Fails to Include All Feasible Mitigation Measures for GHG Emissions, Which Precludes Project Approval Under CEQA.
SWAPE found that the Draft EIR fails to incorporate all feasible mitigation, as mandated by CEQA:
According to CEQA Guidelines § 15096(g)(2): ‘When an EIR has been prepared for a project, the Responsible Agency shall not approve the project as proposed if the agency finds any feasible alternative or feasible mitigation measures within its powers that would substantially lessen or avoid any significant effect the project would have on the environment. (Exhibit 1, p. 4.)
As to GHG emissions, CEQA also requires to adequately disclose and quantify the impacts. Guidelines § 15183.5. It is not enough to conclude that impacts would be less with mitigation; the EIR must adequately analyze and calculate GHG impacts before and after mitigation and explain how it arrives at such conclusion.
Hence, to make the EIR compliant with CEQA, SWAPE recommends additional feasible mitigation measures for GHG operational impacts. Without such mitigation, the City will violate CEQA’s affirmative duty to mitigate impacts to the extent feasible and cannot legally approve the Project under CEQA. Public Resources Code § 21002.
The EIR must be updated to evaluate the impacts of GHG emissions upon implementation of those additional feasible mitigation measures recommended by SWAPE, and the ultimate mitigation monitoring and reporting program must be drafted to incorporate SWAPE’s recommended feasible mitigation measures.
II. THE DRAFT EIR VIOLATES CEQA AS IT UNDERSTATES THE
PROJECT’S TRAFFIC IMPACTS DUE TO ERRONEOUS VMT
ANALYSIS AND BASELINE ASSUMPTIONS.
Based on its April 7, 2022 expert report from traffic expert Norman L. Marshall, Smart Mobility (see, Exhibit 2 [4/7/2022 Smart Mobility Expert Report]), the Draft EIR for 10-361
the Project is inadequate and fatally flawed due to errors in the traffic analysis and related baseline assumptions.
Upon review of the Project’s Draft EIR, other related projects (e.g., Disney’s Cotino Project), and statistical data, Smart Mobility made specific findings; namely:
1) The DEIR VMT Calculations are invalid. The calculations include erroneous negative VMT for housing, and grossly inconsistent VMT between the project area and the City as a whole.
2) The City of Rancho Mirage has a large deficit of workforce housing.
There are 10,800 more service jobs in the City today than there are service workers living in the City. This deficit will get worse as Disney’s Cotino project and other developments are constructed.
Many Rancho Mirage workers commute more than 50 miles in each direction and some commute more than 100 miles.
3) More market rate housing in Rancho Mirage will greatly increase VMT. Given the affluent older population, each addition market- rate household requires approximately one additional service worker, and the additional commute VMT from that service worker must be considered in calculating the VMT impacts of the housing. 4) Constructing workforce housing in Rancho Mirage would reduce regional VMT. A valid analysis of the VMT impacts of the Highway 111 Specific Plan must draw a sharp contrast between market-rate housing and workforce housing and evaluate the VMT impacts of each separately.
5) Without enforceable commitments for a large portion of the increased residential entitlement to be workforce housing the Highway 111 Specific Plan will cause an excessive increase in VMT.
Exhibit 2, p. 1.
A. The Draft EIR’s VMT Analysis Contains Errors and Must Be Revised.
Smart Mobility found that the Draft EIR’s VMT calculations contained an error: the VMT analysis of the Project’s area and the City in general, with the Project, showed large and unsupported negative baseline assumptions for residential growth. Specifically, Smart Mobility reported that the EIR calculated the Project’s area VMT per 10-362
population, with the Project, to be “P = -23.9 VMT per person” and for the City in general, with the Project, to be “P = -2.0 VMT per person”. (Exhibit 2, pp. 2-3.) Simply put, the Draft EIR finds that, with the increase of residential development – and hence, population growth – traffic impacts will decrease. Smart Mobility found no explanation in the Draft EIR to support this negative finding of VMTs. Hence, Smart Mobility concluded the EIR contains errors and is invalid:
It is possible that the Riverside Transportation Analysis Model (RIVTAM) performs poorly in this part of Riverside County. It also is possible that the DEIR consultants misapplied the model. In either case, the DEIR VMT analysis is invalid.
Exhibit 2, p. 3.
Regardless of the source of the error, the EIR must be updated and its VMT analysis revised, to correct the error or explain how the increase of population can reasonably amount to decrease in VMT. Failure to do so will render the EIR fatally flawed and violating CEQA as to its analysis and baseline assumptions.
B. The Draft EIR’s VMT Analysis Understates Traffic VMT Impacts In Light of the Project’s Demographics and Lack of Workforce Housing.
Based on review of the Project’s and the City’s demographics and statistical data (Exhibit 2, pp. 3-6), Smart Mobility found that the Project’s proposed increase of market-rate housing will increase VMTs, contrary to the EIR’s baseline assumptions.
In particular, Smart Mobility found:
[T]here are 15,000 jobs in Rancho Mirage but less than 5,000 workers living in Rancho Mirage. The 15,000 jobs are primarily in the service sector, with 89% in one of the service categories including health care, accommodations and food services, retail, entertainment and recreation, and other services. However, only 55% of the workers living in Rancho Mirage are employed in those industries. There is a deficit of 10,800 service workers in Rancho Mirage today.
This includes a 3,900-worker deficit in the hospitality industry (adding together accommodations, food service, recreation, and entertainment).
Exhibit 2, pp. 4-5.
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In addition, Smart Mobility found:
These statistics show a largely older population with small households and few children, and a relatively small proportion of residents in the labor force. Rancho Mirage is a very affluent community with current average house prices exceeding $1.2 million.
Exhibit 2, pp. 3.
Smart Mobility also found that the majority of hospitality and service workers have an average salary of $16,000/year, cannot afford living in the Project area or the City and are hence long-distance commuters from 50-100 miles away.
Based on its thorough review of statistical data, Smart Mobility concluded that the EIR understates VMT impacts as it fails to consider the additional VMT of service workers upon increase of residential market-rate housing:
Therefore, in evaluating the impacts of adding to the number of market- rate housing units in Rancho Mirage, we must not only add the direct VMT impacts of an added housing unit but also add in the VMT impacts of another service worker. As illustrated in Figure 3, the VMT impacts of adding these service workers is very great.
The DEIR is disingenuous when it suggests that reallocating land from commercial to residential will reduce future VMT because adding to residential growth will also cause service job growth.
Exhibit 2, p. 7.
Smart Mobility also noted the fact that other similar projects, such as Disney’s Cotino project in the City, will cumulatively add to VMTs. (Exhibit 2, p. 7.) Hence, the Draft EIR is also inadequate as it understates these cumulative VMTs of the Project along with other related projects in the City.
To cure the above-noted EIR inadequacy, Smart Mobility recommended to revise the EIR’s analysis as follows:
A valid analysis of the VMT impacts of the Highway 111 Specific Plan must draw a sharp contrast between market-rate housing and workforce housing and evaluate the VMT impacts of each separately. Unless a large proportion of any additional residential entitlement is workforce housing, there will be a large increase in VMT.
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Exhibit 2, p. 8.
To comply with CEQA’s affirmative duty of good-faith disclosure and identification of impacts, the Draft EIR must be revised to include the above-noted analysis of VMT impacts per market-rate and workforce housing.
A. The Draft EIR Must Provide Feasible Mitigation Measures and Binding Commitments to Build More Workforce (or, Affordable) Housing to Mitigate the Project’s Reasonably Foreseeable Traffic Impacts.
In order to mitigate the Project’s traffic impacts in view of the City’s reallocation of more commercial land for residential development, Smart Mobility recommends to include a feasible mitigation measure: a specific binding commitment to build workforce (or, affordable) housing.
Reviewing the EIR, Smart Mobility found that its analysis is inadequate as it improperly equates or conflates density and affordability and appears to evade the affordability issue at all:
In the DEIR, the word “workforce” appears only once - noting that there is a 20% potential density bonus in the R-H/SP High Density Residential category. (DEIR, p. 36 of 900) There is no discussion of whether this bonus will be attractive enough that workforce housing will be constructed.
Similarly, the DEIR equates density and affordability: “The allowance of such high maximum density demonstrates that the City can provide a substantial number of future residential units that are marketrate affordable.” (DEIR p. 205 of 900) This excerpt raises several questions.
What is a “substantial number” of units? Is it 10, 100, 1000? What is “market-rate affordable”? Is it $1 million instead of $1.2 million? How does the higher allowed density translate into actual new housing units that would be affordable to the City’s workforce?
Exhibit 2, p. 8.
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To mitigate the excessive – and yet understated – VMT traffic impacts, Smart Mobility recommended specific enforceable commitments on the part of the City:
Without enforceable commitments for a large portion of the increased residential entitlement to be workforce housing the Highway 111 Specific Plan will cause an excessive increase in VMT.
Exhibit 2, p. 8.)
Thus, to comply with CEQA’s imposed duty to mitigate Project’s traffic impacts, the City must include enforceable commitments and devise incentives for project applicants to ensure that large part of the Project’s residential development will produce workforce (or, affordable) housing. Further, these incentives should not be in return for more density, since adding more density as mitigation will increase traffic impacts as well.
If the City has any questions or concerns, please feel free to contact my Office.
Sincerely,
Naira Soghbatyan
Attorneys for Southwest Regional
Council of Carpenters
Attached:
March 28, 2022 SWAPE Letter to Mitchell M. Tsai, Attorney At Law, re “Comments on the Highway 111 Specific Plan (SCH No. 2020069010)” (Exhibit 1); and April 7, 2022 Smart Mobility Letter to Mitchell M. Tsai, Attorney at Law, re “Comments on the Highway 111 Specific Plan DEIR” (Exhibit 2) 10-366
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 28, 2022
Naira Soghbatyan, Esq.
Mitchell M. Tsai, Attorney at Law
155 South El Molino Avenue Suite 104
Pasadena, CA 91101
Subject: Comments on the Highway 111 Specific Plan (SCH No. 2020069010) Dear Ms. Soghbatyan,
We have reviewed the January 2022 Draft Environmental Impact Report (“DEIR”) for the Highway 111 Specific Plan (“Specific Plan”) located in the City of Rancho Mirage (“City”). The Specific Plan proposes to include a total of 1,504 residential units and 5,351,868-square feet (“SF”) of commercial space on the 684-acre site.
Our review concludes that the DEIR fails to adequately evaluate the Specific Plan’s air quality and greenhouse gas impacts. As a result, emissions associated with construction and operation of the proposed Specific Plan are inadequately addressed. An updated EIR should be prepared to adequately assess and mitigate the potential air quality and greenhouse gas impacts that buildout of the Specific Plan may have on the surrounding environment.
Air Quality & Greenhouse Gases Inadequate Mitigation of Potentially Significant Operational Air Quality Impacts According to California Government Code 65453:
“A specific plan shall be prepared, adopted, and amended in the same manner as a general plan.”1
1 “ARTICLE 8. Specific Plans [65450 - 65457].” California Public Resources Code, 1985, available at:
https://leginfo.legislature.ca.gov/faces/codes_displaySection.xhtml?lawCode=GOV§ionNum=65453.#:~:text=( a)%20A%20specific%20plan%20shall,necessary%20by%20the%20legislative%20body. 10-367
As demonstrated above, specific plans are to be prepared in the same manner as general plans. The Governor’s Office of Planning and Research (“OPR”) published the State of California 2017 General Plan Guidelines, which assists local governments in preparing general plans.2 Regarding cumulative impacts, OPR guidance states:
“The EIR must analyze the cumulative effects of the plan’s land use designations, policies and programs on the environment.”3
Furthermore, OPR guidance states:
“The EIR must identify mitigation measures and alternatives to avoid or minimize potential impacts, to the extent feasible. The general plan EIR is a particularly useful tool for identifying measures to mitigate the cumulative effects of new development.”4 As demonstrated above, general plans, and consequently specific plans, are required to incorporate mitigation measures to reduce cumulative impacts. Thus, as the DEIR indicates that the Specific Plan’s operational air quality emissions have potentially significant cumulative impacts, mitigation measures should have been incorporated to reduce such impacts. Specifically, the DEIR states:
“[O]perational air quality emissions for the proposed Specific Plan have the potential to result in a cumulatively considerable net increase of CO, NOX, SOX, PM10, PM2.5, and ROG” (p. 2.4-15).
However, the DEIR fails to implement any mitigation intended to reduce the above-mentioned operational criteria air pollutant emissions. As such, the DEIR fails to adequately address and mitigate the Specific Plan’s cumulative air quality impacts and, as a result, should not be relied upon to determine Project significance. Inadequate Evaluation of Greenhouse Gas Impacts Regarding the Specific Plan’s greenhouse gas (“GHG”) impacts, the DEIR states:
“[I]ndividual projects developed under the proposed Specific Plan will be assessed on a case-by- case basis for potential impacts related to GHG emissions. While implementation of existing General Plan policies and programs and proposed Specific Plan policies and guidelines will help reduce GHG emissions, based on the GHG projections above, it is possible that the proposed Specific Plan would generate GHG emissions that could have a significant and unavoidable impact on the environment” (p. 2.4-20).
As demonstrated above, the Specific Plan concludes that “individual projects developed under the proposed Specific Plan will be assessed on a case-by-case basis for potential impacts related to GHG 2 “State of California 2017 General Plan Guidelines.” Governor’s Office of Planning and Research, 2017, available at: https://opr.ca.gov/docs/OPR_COMPLETE_7.31.17.pdf . 3 “State of California 2017 General Plan Guidelines.” Governor’s Office of Planning and Research, 2017, available at: https://opr.ca.gov/docs/OPR_COMPLETE_7.31.17.pdf , p. 271. 4 “State of California 2017 General Plan Guidelines.” Governor’s Office of Planning and Research, 2017, available at: https://opr.ca.gov/docs/OPR_COMPLETE_7.31.17.pdf , p. 271. 10-368
emissions” (p. 2.4-20). As such, the Specific Plan incorporates Mitigation Measure (“MM”) GHG-3, which states:
“GHG-3 CEQA Analysis: Sustainability Plan Measures
Projects that require CEQA analysis shall be required to conduct detailed impact analyses and incorporate mitigation measures into their designs using the City’s current Sustainability Plan prescribed reduction measures for achieving greenhouse gas emission reduction targets. All proposed mitigation measures shall be reviewed and approved by the City prior to the issuance of grading or demolition permits” (p. ES-8).
Thus, future projects that “require CEQA analysis” would conduct further GHG analyses and incorporate Project-specific mitigation measures. However, this is insufficient, as projects that are exempt from CEQA analysis would not be required to adhere to this mitigation measure. According to the above- mentioned State of California 2017 General Plan Guidelines:
“The general plan EIR need not be as detailed as an EIR for the specific projects that will follow (CEQA Guidelines § 15146). Its level of detail should reflect the level contained in the plan or plan element being considered (Rio Vista Farm Bureau Center v. County of Solano (1992) 5 Cal.App.4th 351). However, the lead agency cannot defer its analysis of any significant effect of the general plan to later-tiered EIRs (Stanislaus Natural Heritage Project v. County of Stanislaus (1996) 48 Cal.App.4th 182). “With a good and detailed analysis of the [general plan], many subsequent activities could be found to be within the scope of the project described in the [general plan] EIR, and no further environmental documents would be required.” (CEQA Guidelines § 15168(c) (5); see also id. at § 15183.3 (streamlining for infill projects))” (emphasis added).5
As demonstrated above, OPR guidance indicates that lead agencies cannot defer the analysis of any significant effects, as future projects would likely not be required to conduct further environmental review. As such, MM GHG-3 should apply to all future projects under the proposed Specific Plan.
Additionally, the evaluation of GHG impacts and the incorporation of additional mitigation measures should be conducted before individual project approval, not just prior to the issuance of grading or demolition permits. Until all future projects within the Specific Plan are required to conduct GHG analyses to adequately evaluate and mitigate GHG impacts, the DEIR should not be relied upon for Project significance. Failure to Implement All Feasible Mitigation to Reduce Emissions The DEIR determines that the Specific Plan’s operational GHG emissions would be significant-and- unavoidable. Specifically, the DEIR states:
5 “State of California 2017 General Plan Guidelines.” Governor’s Office of Planning and Research, 2017, available at: https://opr.ca.gov/docs/OPR_COMPLETE_7.31.17.pdf , p. 271. 10-369
“[T]he per capita emission rate for the proposed Specific Plan is 12.1 MTCO2e in 2040, which exceeds the statewide recommended targets (6 MTCO2e for 2030 and 2 MTCO2e for 2050) for AB 32 compliance. It is possible and expected that per capita emissions will decrease over the next 20 years due to future technology improvements, increased use of alternative modes of transportation, improved building efficiency, and increased use of renewable energy sources.
However, the elective use of alternative modes of transportation and future efficiency potentials cannot be confidently quantified and applied as a mitigation measure. Therefore, operational impacts as they currently stand are not in compliance with AB 32, and impacts will be significant and unavoidable” (p. 2.4-19).
However, while we agree that the Specific Plan’s GHG emissions would result in a significant GHG impact, the DEIR’s conclusion that these impacts are “significant and unavoidable” is incorrect.
According to CEQA Guidelines § 15096(g)(2):
“When an EIR has been prepared for a project, the Responsible Agency shall not approve the project as proposed if the agency finds any feasible alternative or feasible mitigation measures within its powers that would substantially lessen or avoid any significant effect the project would have on the environment.”
As demonstrated above, an impact can only be labeled as significant and unavoidable after all available, feasible mitigation is considered. Here, while the DEIR includes MM GHG-1 through GHG-2, the DEIR fails to implement all feasible mitigation (p. 2.4-21). Thus, the DEIR’s conclusion that the Specific Plan’s operational GHG impacts are significant-and-unavoidable is unsubstantiated. To reduce GHG impacts to the maximum extent possible, additional feasible mitigation measures should be incorporated, such as those suggested in the following section of this letter. The Specific Plan should not be approved until an updated EIR is prepared, incorporating all feasible mitigation to reduce operational emissions to less- than-significant levels. Feasible Mitigation Measures Available to Reduce Emissions Our analysis demonstrates that the Specific Plan results in potentially significant air quality and GHG impacts that should be mitigated further. As such, in an effort to reduce emissions, we identified several mitigation measures that are applicable to the proposed Specific Plan. Therefore, to reduce emissions, we recommend consideration of SCAG’s 2020 RTP/SCS PEIR’s Air Quality Project Level Mitigation Measures (“PMM-AQ-1”) and Greenhouse Gas Project Level Mitigation Measures (“PMM-GHG-1”), as described below: 6
6 “4.0 Mitigation Measures.” Connect SoCal Program Environmental Impact Report Addendum #1, September 2020, available at: https://scag.ca.gov/sites/main/files/file- attachments/fpeir_connectsocal_addendum_4_mitigationmeasures.pdf?1606004420, p. 4.0-2 – 4.0-10; 4.0-19 –
4.0-23; See also: “Certified Final Connect SoCal Program Environmental Impact Report.” Southern California Association of Governments (SCAG), May 2020, available at: https://scag.ca.gov/peir . 10-370
SCAG RTP/SCS 2020-2045
Air Quality Project Level Mitigation Measures – PMM-AQ-1:
In accordance with provisions of sections 15091(a)(2) and 15126.4(a)(1)(B) of the State CEQA Guidelines, a Lead Agency for a project can and should consider mitigation measures to reduce substantial adverse effects related to violating air quality standards. Such measures may include the following or other comparable measures identified by the Lead Agency:
m) Provide an operational water truck on-site at all times. Use watering trucks to minimize dust; watering should be sufficient to confine dust plumes to the project work areas. Sweep paved streets at least once per day where there is evidence of dirt that has been carried on to the roadway. n) Utilize existing power sources (e.g., power poles) or clean fuel generators rather than temporary power generators.
o) Develop a traffic plan to minimize traffic flow interference from construction activities. The plan may include advance public notice of routing, use of public transportation, and satellite parking areas with a shuttle service.
Schedule operations affecting traffic for off-peak hours. Minimize obstruction of through-traffic lanes. Provide a flag person to guide traffic properly and ensure safety at construction sites. p) As appropriate require that portable engines and portable engine-driven equipment units used at the project work site, with the exception of on-road and off-road motor vehicles, obtain CARB Portable Equipment Registration with the state or a local district permit. Arrange appropriate consultations with the CARB or the District to determine registration and permitting requirements prior to equipment operation at the site. q) Require projects within 500 feet of residences, hospitals, or schools to use Tier 4 equipment for all engines above 50 horsepower (hp) unless the individual project can demonstrate that Tier 4 engines would not be required to mitigate emissions below significance thresholds. r) Projects located within the South Coast Air Basin should consider applying for South Coast AQMD “SOON” funds which provides funds to applicable fleets for the purchase of commercially available low-emission heavy- duty engines to achieve near-term reduction of NOx emissions from in-use off-road diesel vehicles. s) Projects located within AB 617 communities should review the applicable Community Emissions Reduction Plan (CERP) for additional mitigation that can be applied to individual projects. t) Where applicable, projects should provide information about air quality related programs to schools, including the Environmental Justice Community Partnerships (EJCP), Clean Air Ranger Education (CARE), and Why Air Quality Matters programs.
y) Projects that will introduce sensitive receptors within 500 feet of freeways and other sources should consider installing high efficiency of enhanced filtration units, such as Minimum Efficiency Reporting Value (MERV) 13 or better. Installation of enhanced filtration units can be verified during occupancy inspection prior to the issuance of an occupancy permit.
z) Develop an ongoing monitoring, inspection, and maintenance program for the MERV filters. aa) Consult the SCAG Environmental Justice Toolbox for potential measures to address impacts to low-income and/or minority communities.
bb) The following criteria related to diesel emissions shall be implemented on by individual project sponsors as appropriate and feasible:
- Diesel nonroad vehicles on site for more than 10 total days shall have either (1) engines that meet EPA on road emissions standards or (2) emission control technology verified by EPA or CARB to reduce PM emissions by a minimum of 85%
- Diesel generators on site for more than 10 total days shall be equipped with emission control technology verified by EPA or CARB to reduce PM emissions by a minimum of 85%. - Nonroad diesel engines on site shall be Tier 2 or higher. - Diesel nonroad construction equipment on site for more than 10 total days shall have either (1) engines meeting EPA Tier 4 nonroad emissions standards or (2) emission control technology verified by EPA or 10-371
CARB for use with nonroad engines to reduce PM emissions by a minimum of 85% for engines for 50 hp and greater and by a minimum of 20% for engines less than 50 hp. - Emission control technology shall be operated, maintained, and serviced as recommended by the emission control technology manufacturer.
- Diesel vehicles, construction equipment, and generators on site shall be fueled with ultra-low sulfur diesel fuel (ULSD) or a biodiesel blend approved by the original engine manufacturer with sulfur content of 15 ppm or less.
- The construction contractor shall maintain a list of all diesel vehicles, construction equipment, and generators to be used on site. The list shall include the following:
i. Contractor and subcontractor name and address, plus contact person responsible for the vehicles or equipment.
ii. Equipment type, equipment manufacturer, equipment serial number, engine manufacturer, engine model year, engine certification (Tier rating), horsepower, engine serial number, and expected fuel usage and hours of operation.
iii. For the emission control technology installed: technology type, serial number, make, model, manufacturer, EPA/CARB verification number/level, and installation date and hour-meter reading on installation date.
- The contractor shall establish generator sites and truck-staging zones for vehicles waiting to load or unload material on site. Such zones shall be located where diesel emissions have the least impact on abutters, the general public, and especially sensitive receptors such as hospitals, schools, daycare facilities, elderly housing, and convalescent facilities. - The contractor shall maintain a monthly report that, for each on road diesel vehicle, nonroad construction equipment, or generator onsite, includes:
i. Hour-meter readings on arrival on-site, the first and last day of every month, and on off-site date.
ii. Any problems with the equipment or emission controls. iii. Certified copies of fuel deliveries for the time period that identify:
1. Source of supply
2. Quantity of fuel
3. Quantity of fuel, including sulfur content (percent by weight) cc) Project should exceed Title-24 Building Envelope Energy Efficiency Standards (California Building Standards Code). The following measures can be used to increase energy efficiency:
- Provide pedestrian network improvements, such as interconnected street network, narrower roadways and shorter block lengths, sidewalks, accessibility to transit and transit shelters, traffic calming measures, parks and public spaces, minimize pedestrian barriers. - Provide traffic calming measures, such as:
i. Marked crosswalks
ii. Count-down signal timers
iii. Curb extensions iv. Speed tables
iv. Raised crosswalks
v. Raised intersections
vi. Median islands
vii. Tight corner radii
viii. Roundabouts or mini-circles
ix. On-street parking
x. Chicanes/chokers
- Create urban non-motorized zones
- Provide bike parking in non-residential and multi-unit residential projects - Dedicate land for bike trails
- Limit parking supply through:
i. Elimination (or reduction) of minimum parking requirements ii. Creation of maximum parking requirements
iii. Provision of shared parking
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- Require residential area parking permit.
- Provide ride-sharing programs
i. Designate a certain percentage of parking spacing for ride sharing vehicles ii. Designating adequate passenger loading and unloading and waiting areas for ride-sharing vehicles
iii. Providing a web site or messaging board for coordinating rides iv. Permanent transportation management association membership and finding requirement.
Greenhouse Gas Project Level Mitigation Measures – PMM-GHG-1 In accordance with provisions of sections 15091(a)(2) and 15126.4(a)(1)(B) of the State CEQA Guidelines, a Lead Agency for a project can and should consider mitigation measures to reduce substantial adverse effects related to violating air quality standards. Such measures may include the following or other comparable measures identified by the Lead Agency:
b) Reduce emissions resulting from projects through implementation of project features, project design, or other measures, such as those described in Appendix F of the State CEQA Guidelines. c) Include off-site measures to mitigate a project’s emissions. d) Measures that consider incorporation of Best Available Control Technology (BACT) during design, construction and operation of projects to minimize GHG emissions, including but not limited to:
i. Use energy and fuel-efficient vehicles and equipment; ii. Deployment of zero- and/or near zero emission technologies; iii. Use lighting systems that are energy efficient, such as LED technology; iv. Use the minimum feasible amount of GHG-emitting construction materials; v. Use cement blended with the maximum feasible amount of flash or other materials that reduce GHG emissions from cement production;
vi. Incorporate design measures to reduce GHG emissions from solid waste management through encouraging solid waste recycling and reuse;
vii. Incorporate design measures to reduce energy consumption and increase use of renewable energy;
viii. Incorporate design measures to reduce water consumption; ix. Use lighter-colored pavement where feasible;
x. Recycle construction debris to maximum extent feasible; xi. Plant shade trees in or near construction projects where feasible; and xii. Solicit bids that include concepts listed above.
e) Measures that encourage transit use, carpooling, bike-share and car-share programs, active transportation, and parking strategies, including, but not limited to the following:
i. Promote transit-active transportation coordinated strategies; ii. Increase bicycle carrying capacity on transit and rail vehicles; iii. Improve or increase access to transit;
iv. Increase access to common goods and services, such as groceries, schools, and day care; v. Incorporate affordable housing into the project;
vi. Incorporate the neighborhood electric vehicle network; vii. Orient the project toward transit, bicycle and pedestrian facilities; viii. Improve pedestrian or bicycle networks, or transit service; ix. Provide traffic calming measures;
x. Provide bicycle parking;
xi. Limit or eliminate park supply;
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xii. Unbundle parking costs;
xiii. Provide parking cash-out programs;
xiv. Implement or provide access to commute reduction program; f) Incorporate bicycle and pedestrian facilities into project designs, maintaining these facilities, and providing amenities incentivizing their use; and planning for and building local bicycle projects that connect with the regional network;
g) Improving transit access to rail and bus routes by incentives for construction and transit facilities within developments, and/or providing dedicated shuttle service to transit stations; and h) Adopting employer trip reduction measures to reduce employee trips such as vanpool and carpool programs, providing end-of-trip facilities, and telecommuting programs including but not limited to measures that:
i. Provide car-sharing, bike sharing, and ride-sharing programs; ii. Provide transit passes;
iii. Shift single occupancy vehicle trips to carpooling or vanpooling, for example providing ride- matching services;
iv. Provide incentives or subsidies that increase that use of modes other than single-occupancy vehicle;
v. Provide on-site amenities at places of work, such as priority parking for carpools and vanpools, secure bike parking, and showers and locker rooms;
vi. Provide employee transportation coordinators at employment sites; vii. Provide a guaranteed ride home service to users of non-auto modes. i) Designate a percentage of parking spaces for ride-sharing vehicles or high-occupancy vehicles, and provide adequate passenger loading and unloading for those vehicles; j) Land use siting and design measures that reduce GHG emissions, including:
i. Developing on infill and brownfields sites;
ii. Building compact and mixed-use developments near transit; iii. Retaining on-site mature trees and vegetation, and planting new canopy trees; iv. Measures that increase vehicle efficiency, encourage use of zero and low emissions vehicles, or reduce the carbon content of fuels, including constructing or encouraging construction of electric vehicle charging stations or neighborhood electric vehicle networks, or charging for electric bicycles; and
v. Measures to reduce GHG emissions from solid waste management through encouraging solid waste recycling and reuse.
k) Consult the SCAG Environmental Justice Toolbox for potential measures to address impacts to low-income and/or minority communities. The measures provided above are also intended to be applied in low income and minority communities as applicable and feasible.
l) Require at least five percent of all vehicle parking spaces include electric vehicle charging stations, or at a minimum, require the appropriate infrastructure to facilitate sufficient electric charging for passenger vehicles and trucks to plug-in.
m) Encourage telecommuting and alternative work schedules, such as:
i. Staggered starting times
ii. Flexible schedules
iii. Compressed work weeks
n) Implement commute trip reduction marketing, such as:
i. New employee orientation of trip reduction and alternative mode options ii. Event promotions
iii. Publications
o) Implement preferential parking permit program
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p) Implement school pool and bus programs
q) Price workplace parking, such as:
i. Explicitly charging for parking for its employees;
ii. Implementing above market rate pricing;
iii. Validating parking only for invited guests;
iv. Not providing employee parking and transportation allowances; and v. Educating employees about available alternatives.
These measures offer a cost-effective, feasible way to incorporate lower-emitting design features into the proposed Specific Plan, which subsequently, reduce emissions released during construction and operation. An updated EIR should be prepared to include all feasible mitigation measures, as well as include updated air quality and GHG analyses to ensure that the necessary mitigation measures are implemented to reduce emissions to below thresholds. The updated EIR should also demonstrate a commitment to the implementation of these measures prior to the approval of the Specific Plan, to ensure that the Project’s significant emissions are reduced to the maximum extent possible. Disclaimer SWAPE has received limited discovery regarding this project. 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.
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Attachment A: Matt Hagemann CV
Attachment B: Paul E. Rosenfeld CV
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2656 29th Street, Suite 201
Santa Monica, CA 90405
Matt Hagemann, P.G, C.Hg.
(949) 887-9013
[email protected]
Matthew F. Hagemann, P.G., C.Hg., QSD, QSP
Geologic and Hydrogeologic Characterization
Investigation and Remediation Strategies
Litigation Support and Testifying Expert
Industrial Stormwater Compliance
CEQA Review
Education:
M.S. Degree, Geology, California State University Los Angeles, Los Angeles, CA, 1984.
B.A. Degree, Geology, Humboldt State University, Arcata, CA, 1982.
Professional Certifications:
California Professional Geologist
California Certified Hydrogeologist
Qualified SWPPP Developer and Practitioner
Professional Experience:
Matt has 30 years of experience in environmental policy, contaminant assessment and remediation, stormwater compliance, and CEQA review. He spent nine years with the U.S. EPA in the RCRA and Superfund programs and served as EPA’s Senior Science Policy Advisor in the Western Regional Office where he identified emerging threats to groundwater from perchlorate and MTBE. While with EPA, Matt also served as a Senior Hydrogeologist in the oversight of the assessment of seven major military facilities undergoing base closure. He led numerous enforcement actions under provisions of the Resource Conservation and Recovery Act (RCRA) and directed efforts to improve hydrogeologic characterization and water quality monitoring. For the past 15 years, as a founding partner with SWAPE, Matt has developed extensive client relationships and has managed complex projects that include consultation as an expert witness and a regulatory specialist, and a manager of projects ranging from industrial stormwater compliance to CEQA review of impacts from hazardous waste, air quality and greenhouse gas emissions.
Positions Matt has held include:
•Founding Partner, Soil/Water/Air Protection Enterprise (SWAPE) (2003 – present); •Geology Instructor, Golden West College, 2010 – 2104, 2017; •Senior Environmental Analyst, Komex H2O Science, Inc. (2000 ‐‐ 2003); Attachment A
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• Executive Director, Orange Coast Watch (2001 – 2004); • Senior Science Policy Advisor and Hydrogeologist, U.S. Environmental Protection Agency (1989– 1998);
• Hydrogeologist, National Park Service, Water Resources Division (1998 – 2000); • Adjunct Faculty Member, San Francisco State University, Department of Geosciences (1993 – 1998);
• Instructor, College of Marin, Department of Science (1990 – 1995); • Geologist, U.S. Forest Service (1986 – 1998); and
• Geologist, Dames & Moore (1984 – 1986).
Senior Regulatory and Litigation Support Analyst:
With SWAPE, Matt’s responsibilities have included:
• Lead analyst and testifying expert in the review of over 300 environmental impact reports and negative declarations since 2003 under CEQA that identify significant issues with regard to hazardous waste, water resources, water quality, air quality, greenhouse gas emissions, and geologic hazards. Make recommendations for additional mitigation measures to lead agencies at the local and county level to include additional characterization of health risks and implementation of protective measures to reduce worker exposure to hazards from toxins and Valley Fever.
• Stormwater analysis, sampling and best management practice evaluation at more than 100 industrial facilities.
• Expert witness on numerous cases including, for example, perfluorooctanoic acid (PFOA) contamination of groundwater, MTBE litigation, air toxins at hazards at a school, CERCLA compliance in assessment and remediation, and industrial stormwater contamination. • Technical assistance and litigation support for vapor intrusion concerns. • Lead analyst and testifying expert in the review of environmental issues in license applications for large solar power plants before the California Energy Commission. • Manager of a project to evaluate numerous formerly used military sites in the western U.S. • Manager of a comprehensive evaluation of potential sources of perchlorate contamination in Southern California drinking water wells.
• Manager and designated expert for litigation support under provisions of Proposition 65 in the review of releases of gasoline to sources drinking water at major refineries and hundreds of gas stations throughout California.
With Komex H2O Science Inc., Matt’s duties included the following:
• Senior author of a report on the extent of perchlorate contamination that was used in testimony by the former U.S. EPA Administrator and General Counsel. • Senior researcher in the development of a comprehensive, electronically interactive chronology of MTBE use, research, and regulation.
• Senior researcher in the development of a comprehensive, electronically interactive chronology of perchlorate use, research, and regulation.
• Senior researcher in a study that estimates nationwide costs for MTBE remediation and drinking water treatment, results of which were published in newspapers nationwide and in testimony against provisions of an energy bill that would limit liability for oil companies. • Research to support litigation to restore drinking water supplies that have been contaminated by MTBE in California and New York.
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• Expert witness testimony in a case of oil production‐related contamination in Mississippi. • Lead author for a multi‐volume remedial investigation report for an operating school in Los Angeles that met strict regulatory requirements and rigorous deadlines. • Development of strategic approaches for cleanup of contaminated sites in consultation with clients and regulators.
Executive Director:
As Executive Director with Orange Coast Watch, Matt led efforts to restore water quality at Orange County beaches from multiple sources of contamination including urban runoff and the discharge of wastewater. In reporting to a Board of Directors that included representatives from leading Orange County universities and businesses, Matt prepared issue papers in the areas of treatment and disinfection of wastewater and control of the discharge of grease to sewer systems. Matt actively participated in the development of countywide water quality permits for the control of urban runoff and permits for the discharge of wastewater. Matt worked with other nonprofits to protect and restore water quality, including Surfrider, Natural Resources Defense Council and Orange County CoastKeeper as well as with business institutions including the Orange County Business Council.
Hydrogeology:
As a Senior Hydrogeologist with the U.S. Environmental Protection Agency, Matt led investigations to characterize and cleanup closing military bases, including Mare Island Naval Shipyard, Hunters Point Naval Shipyard, Treasure Island Naval Station, Alameda Naval Station, Moffett Field, Mather Army Airfield, and Sacramento Army Depot. Specific activities were as follows:
• Led efforts to model groundwater flow and contaminant transport, ensured adequacy of monitoring networks, and assessed cleanup alternatives for contaminated sediment, soil, and groundwater.
• Initiated a regional program for evaluation of groundwater sampling practices and laboratory analysis at military bases.
• Identified emerging issues, wrote technical guidance, and assisted in policy and regulation development through work on four national U.S. EPA workgroups, including the Superfund Groundwater Technical Forum and the Federal Facilities Forum.
At the request of the State of Hawaii, Matt developed a methodology to determine the vulnerability of groundwater to contamination on the islands of Maui and Oahu. He used analytical models and a GIS to show zones of vulnerability, and the results were adopted and published by the State of Hawaii and County of Maui.
As a hydrogeologist with the EPA Groundwater Protection Section, Matt worked with provisions of the Safe Drinking Water Act and NEPA to prevent drinking water contamination. Specific activities included the following:
• Received an EPA Bronze Medal for his contribution to the development of national guidance for the protection of drinking water.
• Managed the Sole Source Aquifer Program and protected the drinking water of two communities through designation under the Safe Drinking Water Act. He prepared geologic reports, conducted 10-379
public hearings, and responded to public comments from residents who were very concerned about the impact of designation.
• Reviewed a number of Environmental Impact Statements for planned major developments, including large hazardous and solid waste disposal facilities, mine reclamation, and water transfer.
Matt served as a hydrogeologist with the RCRA Hazardous Waste program. Duties were as follows:
• Supervised the hydrogeologic investigation of hazardous waste sites to determine compliance with Subtitle C requirements.
• Reviewed and wrote ʺpart Bʺ permits for the disposal of hazardous waste. • Conducted RCRA Corrective Action investigations of waste sites and led inspections that formed the basis for significant enforcement actions that were developed in close coordination with U.S.
EPA legal counsel.
• Wrote contract specifications and supervised contractor’s investigations of waste sites.
With the National Park Service, Matt directed service‐wide investigations of contaminant sources to prevent degradation of water quality, including the following tasks:
• Applied pertinent laws and regulations including CERCLA, RCRA, NEPA, NRDA, and the Clean Water Act to control military, mining, and landfill contaminants. • Conducted watershed‐scale investigations of contaminants at parks, including Yellowstone and Olympic National Park.
• Identified high‐levels of perchlorate in soil adjacent to a national park in New Mexico and advised park superintendent on appropriate response actions under CERCLA. • Served as a Park Service representative on the Interagency Perchlorate Steering Committee, a national workgroup.
• Developed a program to conduct environmental compliance audits of all National Parks while serving on a national workgroup.
• Co‐authored two papers on the potential for water contamination from the operation of personal watercraft and snowmobiles, these papers serving as the basis for the development of nation‐ wide policy on the use of these vehicles in National Parks. • Contributed to the Federal Multi‐Agency Source Water Agreement under the Clean Water Action Plan.
Policy:
Served senior management as the Senior Science Policy Advisor with the U.S. Environmental Protection Agency, Region 9.
Activities included the following:
• Advised the Regional Administrator and senior management on emerging issues such as the potential for the gasoline additive MTBE and ammonium perchlorate to contaminate drinking water supplies.
• Shaped EPA’s national response to these threats by serving on workgroups and by contributing to guidance, including the Office of Research and Development publication, Oxygenates in Water: Critical Information and Research Needs.
• Improved the technical training of EPAʹs scientific and engineering staff. • Earned an EPA Bronze Medal for representing the region’s 300 scientists and engineers in negotiations with the Administrator and senior management to better integrate scientific 10-380
principles into the policy‐making process.
• Established national protocol for the peer review of scientific documents.
Geology:
With the U.S. Forest Service, Matt led investigations to determine hillslope stability of areas proposed for timber harvest in the central Oregon Coast Range. Specific activities were as follows:
• Mapped geology in the field, and used aerial photographic interpretation and mathematical models to determine slope stability.
• Coordinated his research with community members who were concerned with natural resource protection.
• Characterized the geology of an aquifer that serves as the sole source of drinking water for the city of Medford, Oregon.
As a consultant with Dames and Moore, Matt led geologic investigations of two contaminated sites (later listed on the Superfund NPL) in the Portland, Oregon, area and a large hazardous waste site in eastern Oregon. Duties included the following:
• Supervised year‐long effort for soil and groundwater sampling. • Conducted aquifer tests.
• Investigated active faults beneath sites proposed for hazardous waste disposal.
Teaching:
From 1990 to 1998, Matt taught at least one course per semester at the community college and university levels:
• At San Francisco State University, held an adjunct faculty position and taught courses in environmental geology, oceanography (lab and lecture), hydrogeology, and groundwater contamination.
• Served as a committee member for graduate and undergraduate students. • Taught courses in environmental geology and oceanography at the College of Marin.
Matt is currently a part time geology instructor at Golden West College in Huntington Beach, California where he taught from 2010 to 2014 and in 2017.
Invited Testimony, Reports, Papers and Presentations:
Hagemann, M.F., 2008. Disclosure of Hazardous Waste Issues under CEQA. Presentation to the Public Environmental Law Conference, Eugene, Oregon.
Hagemann, M.F., 2008. Disclosure of Hazardous Waste Issues under CEQA. Invited presentation to U.S.
EPA Region 9, San Francisco, California.
Hagemann, M.F., 2005. Use of Electronic Databases in Environmental Regulation, Policy Making and Public Participation. Brownfields 2005, Denver, Coloradao.
Hagemann, M.F., 2004. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in Nevada and the Southwestern U.S. Presentation to a meeting of the American Groundwater Trust, Las Vegas, NV (served on conference organizing committee).
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Hagemann, M.F., 2004. Invited testimony to a California Senate committee hearing on air toxins at schools in Southern California, Los Angeles.
Brown, A., Farrow, J., Gray, A. and Hagemann, M., 2004. An Estimate of Costs to Address MTBE Releases from Underground Storage Tanks and the Resulting Impact to Drinking Water Wells.
Presentation to the Ground Water and Environmental Law Conference, National Groundwater Association.
Hagemann, M.F., 2004. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in Arizona and the Southwestern U.S. Presentation to a meeting of the American Groundwater Trust, Phoenix, AZ (served on conference organizing committee).
Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in the Southwestern U.S. Invited presentation to a special committee meeting of the National Academy of Sciences, Irvine, CA.
Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River. Invited presentation to a tribal EPA meeting, Pechanga, CA.
Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River. Invited presentation to a meeting of tribal repesentatives, Parker, AZ.
Hagemann, M.F., 2003. Impact of Perchlorate on the Colorado River and Associated Drinking Water Supplies. Invited presentation to the Inter‐Tribal Meeting, Torres Martinez Tribe.
Hagemann, M.F., 2003. The Emergence of Perchlorate as a Widespread Drinking Water Contaminant.
Invited presentation to the U.S. EPA Region 9.
Hagemann, M.F., 2003. A Deductive Approach to the Assessment of Perchlorate Contamination. Invited presentation to the California Assembly Natural Resources Committee.
Hagemann, M.F., 2003. Perchlorate: A Cold War Legacy in Drinking Water. Presentation to a meeting of the National Groundwater Association.
Hagemann, M.F., 2002. From Tank to Tap: A Chronology of MTBE in Groundwater. Presentation to a meeting of the National Groundwater Association.
Hagemann, M.F., 2002. A Chronology of MTBE in Groundwater and an Estimate of Costs to Address Impacts to Groundwater. Presentation to the annual meeting of the Society of Environmental Journalists.
Hagemann, M.F., 2002. An Estimate of the Cost to Address MTBE Contamination in Groundwater (and Who Will Pay). Presentation to a meeting of the National Groundwater Association.
Hagemann, M.F., 2002. An Estimate of Costs to Address MTBE Releases from Underground Storage Tanks and the Resulting Impact to Drinking Water Wells. Presentation to a meeting of the U.S. EPA and State Underground Storage Tank Program managers.
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Hagemann, M.F., 2001. From Tank to Tap: A Chronology of MTBE in Groundwater. Unpublished report.
Hagemann, M.F., 2001. Estimated Cleanup Cost for MTBE in Groundwater Used as Drinking Water.
Unpublished report.
Hagemann, M.F., 2001. Estimated Costs to Address MTBE Releases from Leaking Underground Storage Tanks. Unpublished report.
Hagemann, M.F., and VanMouwerik, M., 1999. Potential W a t e r Quality Concerns Related to Snowmobile Usage. Water Resources Division, National Park Service, Technical Report.
VanMouwerik, M. and Hagemann, M.F. 1999, Water Quality Concerns Related to Personal Watercraft Usage. Water Resources Division, National Park Service, Technical Report.
Hagemann, M.F., 1999, Is Dilution the Solution to Pollution in National Parks? The George Wright Society Biannual Meeting, Asheville, North Carolina.
Hagemann, M.F., 1997, The Potential for MTBE to Contaminate Groundwater. U.S. EPA Superfund Groundwater Technical Forum Annual Meeting, Las Vegas, Nevada.
Hagemann, M.F., and Gill, M., 1996, Impediments to Intrinsic Remediation, Moffett Field Naval Air Station, Conference on Intrinsic Remediation of Chlorinated Hydrocarbons, Salt Lake City.
Hagemann, M.F., Fukunaga, G.L., 1996, The Vulnerability of Groundwater to Anthropogenic Contaminants on the Island of Maui, Hawaii. Hawaii Water Works Association Annual Meeting, Maui, October 1996.
Hagemann, M. F., Fukanaga, G. L., 1996, Ranking Groundwater Vulnerability in Central Oahu, Hawaii. Proceedings, Geographic Information Systems in Environmental Resources Management, Air and Waste Management Association Publication VIP‐61.
Hagemann, M.F., 1994. Groundwater Ch ar ac te r i z a t i o n and Cl ean up a t Closing Military Bases in California. Proceedings, California Groundwater Resources Association Meeting.
Hagemann, M.F. and Sabol, M.A., 1993. Role of the U.S. EPA in the High Plains States Groundwater Recharge Demonstration Program. Proceedings, Sixth Biennial Symposium on the Artificial Recharge of Groundwater.
Hagemann, M.F., 1993. U.S. EPA Policy on the Technical Impracticability of the Cleanup of DNAPL‐ contaminated Groundwater. California Groundwater Resources Association Meeting. 10-383
Hagemann, M.F., 1992. Dense Nonaqueous Phase Liquid Contamination of Groundwater: An Ounce of Prevention... Proceedings, Association of Engineering Geologists Annual Meeting, v. 35.
Other Experience:
Selected as subject matter expert for the California Professional Geologist licensing examinations, 2009‐2011.
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SOIL WATER AIR PROTECTION ENTERPRISE
2656 29th Street, Suite 201
Santa Monica, California 90405
Attn: Paul Rosenfeld, Ph.D.
Mobil: (310) 795-2335
Office: (310) 452-5555
Fax: (310) 452-5550
Email: [email protected]
Paul E. Rosenfeld, Ph.D. Page 1 of 10 October 2021
Paul Rosenfeld, Ph.D.Chemical Fate and Transport & Air Dispersion Modeling Principal Environmental Chemist Risk Assessment & Remediation Specialist Education
Ph.D. Soil Chemistry, University of Washington, 1999. Dissertation on volatile organic compound filtration.
M.S. Environmental Science, U.C. Berkeley, 1995. Thesis on organic waste economics.
B.A. Environmental Studies, U.C. Santa Barbara, 1991. Thesis on wastewater treatment.
Professional Experience
Dr. Rosenfeld has over 25 years’ experience conducting environmental investigations and risk assessments for evaluating impacts to human health, property, and ecological receptors. His expertise focuses on the fate and transport of environmental contaminants, human health risk, exposure assessment, and ecological restoration. Dr.
Rosenfeld has evaluated and modeled emissions from oil spills, landfills, boilers and incinerators, process stacks, storage tanks, confined animal feeding operations, industrial, military and agricultural sources, unconventional oil drilling operations, and locomotive and construction engines. His project experience ranges from monitoring and modeling of pollution sources to evaluating impacts of pollution on workers at industrial facilities and residents in surrounding communities. Dr. Rosenfeld has also successfully modeled exposure to contaminants distributed by water systems and via vapor intrusion.
Dr. Rosenfeld has investigated and designed remediation programs and risk assessments for contaminated sites containing lead, heavy metals, mold, bacteria, particulate matter, petroleum hydrocarbons, chlorinated solvents, pesticides, radioactive waste, dioxins and furans, semi- and volatile organic compounds, PCBs, PAHs, creosote, perchlorate, asbestos, per- and poly-fluoroalkyl substances (PFOA/PFOS), unusual polymers, fuel oxygenates (MTBE), among other pollutants. Dr. Rosenfeld also has experience evaluating greenhouse gas emissions from various projects and is an expert on the assessment of odors from industrial and agricultural sites, as well as the evaluation of odor nuisance impacts and technologies for abatement of odorous emissions. As a principal scientist at SWAPE, Dr. Rosenfeld directs air dispersion modeling and exposure assessments. He has served as an expert witness and testified about pollution sources causing nuisance and/or personal injury at sites and has testified as an expert witness on numerous cases involving exposure to soil, water and air contaminants from industrial, railroad, agricultural, and military sources.
Attachment B
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Paul E. Rosenfeld, Ph.D. Page 2 of 10 October 2021
Professional History:
Soil Water Air Protection Enterprise (SWAPE); 2003 to present; Principal and Founding Partner UCLA School of Public Health; 2007 to 2011; Lecturer (Assistant Researcher) UCLA School of Public Health; 2003 to 2006; Adjunct Professor UCLA Environmental Science and Engineering Program; 2002-2004; Doctoral Intern Coordinator UCLA Institute of the Environment, 2001-2002; Research Associate Komex H2O Science, 2001 to 2003; Senior Remediation Scientist National Groundwater Association, 2002-2004; Lecturer
San Diego State University, 1999-2001; Adjunct Professor Anteon Corp., San Diego, 2000-2001; Remediation Project Manager Ogden (now Amec), San Diego, 2000-2000; Remediation Project Manager Bechtel, San Diego, California, 1999 – 2000; Risk Assessor King County, Seattle, 1996 – 1999; Scientist
James River Corp., Washington, 1995-96; Scientist
Big Creek Lumber, Davenport, California, 1995; Scientist Plumas Corp., California and USFS, Tahoe 1993-1995; Scientist Peace Corps and World Wildlife Fund, St. Kitts, West Indies, 1991-1993; Scientist
Publications:
Remy, L.L., Clay T., Byers, V., Rosenfeld P. E. (2019) Hospital, Health, and Community Burden After Oil Refinery Fires, Richmond, California 2007 and 2012. Environmental Health. 18:48
Simons, R.A., Seo, Y. Rosenfeld, P., (2015) Modeling the Effect of Refinery Emission On Residential Property Value. Journal of Real Estate Research. 27(3):321-342
Chen, J. A, Zapata A. R., Sutherland A. J., Molmen, D.R., Chow, B. S., Wu, L. E., Rosenfeld, P. E., Hesse, R. C., (2012) Sulfur Dioxide and Volatile Organic Compound Exposure To A Community In Texas City Texas Evaluated Using Aermod and Empirical Data. American Journal of Environmental Science, 8(6), 622-632.
Rosenfeld, P.E. & Feng, L. (2011). The Risks of Hazardous Waste. Amsterdam: Elsevier Publishing.
Cheremisinoff, N.P., & Rosenfeld, P.E. (2011). Handbook of Pollution Prevention and Cleaner Production: Best Practices in the Agrochemical Industry, Amsterdam: Elsevier Publishing.
Gonzalez, J., Feng, L., Sutherland, A., Waller, C., Sok, H., Hesse, R., Rosenfeld, P. (2010). PCBs and Dioxins/Furans in Attic Dust Collected Near Former PCB Production and Secondary Copper Facilities in Sauget, IL.
Procedia Environmental Sciences. 113–125.
Feng, L., Wu, C., Tam, L., Sutherland, A.J., Clark, J.J., Rosenfeld, P.E. (2010). Dioxin and Furan Blood Lipid and Attic Dust Concentrations in Populations Living Near Four Wood Treatment Facilities in the United States. Journal of Environmental Health. 73(6), 34-46.
Cheremisinoff, N.P., & Rosenfeld, P.E. (2010). Handbook of Pollution Prevention and Cleaner Production: Best Practices in the Wood and Paper Industries. Amsterdam: Elsevier Publishing.
Cheremisinoff, N.P., & Rosenfeld, P.E. (2009). Handbook of Pollution Prevention and Cleaner Production: Best Practices in the Petroleum Industry. Amsterdam: Elsevier Publishing.
Wu, C., Tam, L., Clark, J., Rosenfeld, P. (2009). Dioxin and furan blood lipid concentrations in populations living near four wood treatment facilities in the United States. WIT Transactions on Ecology and the Environment, Air Pollution, 123 (17), 319-327.
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Tam L. K.., Wu C. D., Clark J. J. and Rosenfeld, P.E. (2008). A Statistical Analysis Of Attic Dust And Blood Lipid Concentrations Of Tetrachloro-p-Dibenzodioxin (TCDD) Toxicity Equivalency Quotients (TEQ) In Two Populations Near Wood Treatment Facilities. Organohalogen Compounds, 70, 002252-002255.
Tam L. K.., Wu C. D., Clark J. J. and Rosenfeld, P.E. (2008). Methods For Collect Samples For Assessing Dioxins And Other Environmental Contaminants In Attic Dust: A Review. Organohalogen Compounds, 70, 000527- 000530.
Hensley, A.R. A. Scott, J. J. J. Clark, Rosenfeld, P.E. (2007). Attic Dust and Human Blood Samples Collected near a Former Wood Treatment Facility. Environmental Research. 105, 194-197.
Rosenfeld, P.E., J. J. J. Clark, A. R. Hensley, M. Suffet. (2007). The Use of an Odor Wheel Classification for Evaluation of Human Health Risk Criteria for Compost Facilities. Water Science & Technology 55(5), 345-357.
Rosenfeld, P. E., M. Suffet. (2007). The Anatomy Of Odour Wheels For Odours Of Drinking Water, Wastewater, Compost And The Urban Environment. Water Science & Technology 55(5), 335-344.
Sullivan, P. J. Clark, J.J.J., Agardy, F. J., Rosenfeld, P.E. (2007). Toxic Legacy, Synthetic Toxins in the Food, Water, and Air in American Cities. Boston Massachusetts: Elsevier Publishing
Rosenfeld, P.E., and Suffet I.H. (2004). Control of Compost Odor Using High Carbon Wood Ash. Water Science and Technology. 49(9),171-178.
Rosenfeld P. E., J.J. Clark, I.H. (Mel) Suffet (2004). The Value of An Odor-Quality-Wheel Classification Scheme For The Urban Environment. Water Environment Federation’s Technical Exhibition and Conference (WEFTEC) 2004. New Orleans, October 2-6, 2004.
Rosenfeld, P.E., and Suffet, I.H. (2004). Understanding Odorants Associated With Compost, Biomass Facilities, and the Land Application of Biosolids. Water Science and Technology. 49(9), 193-199.
Rosenfeld, P.E., and Suffet I.H. (2004). Control of Compost Odor Using High Carbon Wood Ash, Water Science and Technology, 49( 9), 171-178.
Rosenfeld, P. E., Grey, M. A., Sellew, P. (2004). Measurement of Biosolids Odor and Odorant Emissions from Windrows, Static Pile and Biofilter. Water Environment Research. 76(4), 310-315.
Rosenfeld, P.E., Grey, M and Suffet, M. (2002). Compost Demonstration Project, Sacramento California Using High-Carbon Wood Ash to Control Odor at a Green Materials Composting Facility. Integrated Waste Management Board Public Affairs Office, Publications Clearinghouse (MS–6), Sacramento, CA Publication #442-02-008.
Rosenfeld, P.E., and C.L. Henry. (2001). Characterization of odor emissions from three different biosolids. Water Soil and Air Pollution. 127(1-4), 173-191.
Rosenfeld, P.E., and Henry C. L., (2000). Wood ash control of odor emissions from biosolids application. Journal of Environmental Quality. 29, 1662-1668.
Rosenfeld, P.E., C.L. Henry and D. Bennett. (2001). Wastewater dewatering polymer affect on biosolids odor emissions and microbial activity. Water Environment Research. 73(4), 363-367.
Rosenfeld, P.E., and C.L. Henry. (2001). Activated Carbon and Wood Ash Sorption of Wastewater, Compost, and Biosolids Odorants. Water Environment Research, 73, 388-393.
Rosenfeld, P.E., and Henry C. L., (2001). High carbon wood ash effect on biosolids microbial activity and odor.
Water Environment Research. 131(1-4), 247-262.
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Paul E. Rosenfeld, Ph.D. Page 4 of 10 October 2021
Chollack, T. and P. Rosenfeld. (1998). Compost Amendment Handbook For Landscaping. Prepared for and distributed by the City of Redmond, Washington State.
Rosenfeld, P. E. (1992). The Mount Liamuiga Crater Trail. Heritage Magazine of St. Kitts, 3(2).
Rosenfeld, P. E. (1993). High School Biogas Project to Prevent Deforestation On St. Kitts. Biomass Users Network, 7(1).
Rosenfeld, P. E. (1998). Characterization, Quantification, and Control of Odor Emissions From Biosolids Application To Forest Soil. Doctoral Thesis. University of Washington College of Forest Resources.
Rosenfeld, P. E. (1994). Potential Utilization of Small Diameter Trees on Sierra County Public Land. Masters thesis reprinted by the Sierra County Economic Council. Sierra County, California.
Rosenfeld, P. E. (1991). How to Build a Small Rural Anaerobic Digester & Uses Of Biogas In The First And Third World. Bachelors Thesis. University of California.
Presentations:
Rosenfeld, P.E., "The science for Perfluorinated Chemicals (PFAS): What makes remediation so hard?" Law Seminars International, (May 9-10, 2018) 800 Fifth Avenue, Suite 101 Seattle, WA.
Rosenfeld, P.E., Sutherland, A; Hesse, R.; Zapata, A. (October 3-6, 2013). Air dispersion modeling of volatile organic emissions from multiple natural gas wells in Decatur, TX. 44th Western Regional Meeting, American Chemical Society. Lecture conducted from Santa Clara, CA.
Sok, H.L.; Waller, C.C.; Feng, L.; Gonzalez, J.; Sutherland, A.J.; Wisdom-Stack, T.; Sahai, R.K.; Hesse, R.C.; Rosenfeld, P.E. (June 20-23, 2010). Atrazine: A Persistent Pesticide in Urban Drinking Water.
Urban Environmental Pollution. Lecture conducted from Boston, MA.
Feng, L.; Gonzalez, J.; Sok, H.L.; Sutherland, A.J.; Waller, C.C.; Wisdom-Stack, T.; Sahai, R.K.; La, M.; Hesse, R.C.; Rosenfeld, P.E. (June 20-23, 2010). Bringing Environmental Justice to East St. Louis, Illinois. Urban Environmental Pollution. Lecture conducted from Boston, MA.
Rosenfeld, P.E. (April 19-23, 2009). Perfluoroctanoic Acid (PFOA) and Perfluoroactane Sulfonate (PFOS) Contamination in Drinking Water From the Use of Aqueous Film Forming Foams (AFFF) at Airports in the United States. 2009 Ground Water Summit and 2009 Ground Water Protection Council Spring Meeting , Lecture conducted from Tuscon, AZ.
Rosenfeld, P.E. (April 19-23, 2009). Cost to Filter Atrazine Contamination from Drinking Water in the United States” Contamination in Drinking Water From the Use of Aqueous Film Forming Foams (AFFF) at Airports in the United States. 2009 Ground Water Summit and 2009 Ground Water Protection Council Spring Meeting . Lecture conducted from Tuscon, AZ.
Wu, C., Tam, L., Clark, J., Rosenfeld, P. (20-22 July, 2009). Dioxin and furan blood lipid concentrations in populations living near four wood treatment facilities in the United States. Brebbia, C.A. and Popov, V., eds., Air Pollution XVII: Proceedings of the Seventeenth International Conference on Modeling, Monitoring and Management of Air Pollution. Lecture conducted from Tallinn, Estonia.
Rosenfeld, P. E. (October 15-18, 2007). Moss Point Community Exposure To Contaminants From A Releasing Facility. The 23rd Annual International Conferences on Soils Sediment and Water. Platform lecture conducted from University of Massachusetts, Amherst MA.
Rosenfeld, P. E. (October 15-18, 2007). The Repeated Trespass of Tritium-Contaminated Water Into A Surrounding Community Form Repeated Waste Spills From A Nuclear Power Plant. The 23rd Annual International 10-388
Paul E. Rosenfeld, Ph.D. Page 5 of 10 October 2021
Conferences on Soils Sediment and Water. Platform lecture conducted from University of Massachusetts, Amherst MA.
Rosenfeld, P. E. (October 15-18, 2007). Somerville Community Exposure To Contaminants From Wood Treatment Facility Emissions. The 23rd Annual International Conferences on Soils Sediment and Water. Lecture conducted from University of Massachusetts, Amherst MA.
Rosenfeld P. E. (March 2007). Production, Chemical Properties, Toxicology, & Treatment Case Studies of 1,2,3- Trichloropropane (TCP). The Association for Environmental Health and Sciences (AEHS) Annual Meeting. Lecture conducted from San Diego, CA.
Rosenfeld P. E. (March 2007). Blood and Attic Sampling for Dioxin/Furan, PAH, and Metal Exposure in Florala, Alabama. The AEHS Annual Meeting. Lecture conducted from San Diego, CA.
Hensley A.R., Scott, A., Rosenfeld P.E., Clark, J.J.J. (August 21 – 25, 2006). Dioxin Containing Attic Dust And Human Blood Samples Collected Near A Former Wood Treatment Facility. The 26th International Symposium on Halogenated Persistent Organic Pollutants – DIOXIN2006. Lecture conducted from Radisson SAS Scandinavia Hotel in Oslo Norway.
Hensley A.R., Scott, A., Rosenfeld P.E., Clark, J.J.J. (November 4-8, 2006). Dioxin Containing Attic Dust And Human Blood Samples Collected Near A Former Wood Treatment Facility. APHA 134 Annual Meeting & Exposition. Lecture conducted from Boston Massachusetts.
Paul Rosenfeld Ph.D. (October 24-25, 2005). Fate, Transport and Persistence of PFOA and Related Chemicals.
Mealey’s C8/PFOA. Science, Risk & Litigation Conference. Lecture conducted from The Rittenhouse Hotel, Philadelphia, PA.
Paul Rosenfeld Ph.D. (September 19, 2005). Brominated Flame Retardants in Groundwater: Pathways to Human Ingestion, Toxicology and Remediation PEMA Emerging Contaminant Conference. Lecture conducted from Hilton Hotel, Irvine California.
Paul Rosenfeld Ph.D. (September 19, 2005). Fate, Transport, Toxicity, And Persistence of 1,2,3-TCP. PEMA Emerging Contaminant Conference. Lecture conducted from Hilton Hotel in Irvine, California.
Paul Rosenfeld Ph.D. (September 26-27, 2005). Fate, Transport and Persistence of PDBEs. Mealey’s Groundwater Conference. Lecture conducted from Ritz Carlton Hotel, Marina Del Ray, California.
Paul Rosenfeld Ph.D. (June 7-8, 2005). Fate, Transport and Persistence of PFOA and Related Chemicals.
International Society of Environmental Forensics: Focus On Emerging Contaminants. Lecture conducted from Sheraton Oceanfront Hotel, Virginia Beach, Virginia.
Paul Rosenfeld Ph.D. (July 21-22, 2005). Fate Transport, Persistence and Toxicology of PFOA and Related Perfluorochemicals. 2005 National Groundwater Association Ground Water And Environmental Law Conference.
Lecture conducted from Wyndham Baltimore Inner Harbor, Baltimore Maryland.
Paul Rosenfeld Ph.D. (July 21-22, 2005). Brominated Flame Retardants in Groundwater: Pathways to Human Ingestion, Toxicology and Remediation. 2005 National Groundwater Association Ground Water and Environmental Law Conference. Lecture conducted from Wyndham Baltimore Inner Harbor, Baltimore Maryland.
Paul Rosenfeld, Ph.D. and James Clark Ph.D. and Rob Hesse R.G. (May 5-6, 2004). Tert-butyl Alcohol Liability and Toxicology, A National Problem and Unquantified Liability. National Groundwater Association. Environmental Law Conference. Lecture conducted from Congress Plaza Hotel, Chicago Illinois.
Paul Rosenfeld, Ph.D. (March 2004). Perchlorate Toxicology. Meeting of the American Groundwater Trust.
Lecture conducted from Phoenix Arizona.
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Hagemann, M.F., Paul Rosenfeld, Ph.D. and Rob Hesse (2004). Perchlorate Contamination of the Colorado River.
Meeting of tribal representatives. Lecture conducted from Parker, AZ.
Paul Rosenfeld, Ph.D. (April 7, 2004). A National Damage Assessment Model For PCE and Dry Cleaners.
Drycleaner Symposium. California Ground Water Association. Lecture conducted from Radison Hotel, Sacramento, California.
Rosenfeld, P. E., Grey, M., (June 2003) Two stage biofilter for biosolids composting odor control. Seventh International In Situ And On Site Bioremediation Symposium Battelle Conference Orlando, FL.
Paul Rosenfeld, Ph.D. and James Clark Ph.D. (February 20-21, 2003) Understanding Historical Use, Chemical Properties, Toxicity and Regulatory Guidance of 1,4 Dioxane. National Groundwater Association. Southwest Focus Conference. Water Supply and Emerging Contaminants.. Lecture conducted from Hyatt Regency Phoenix Arizona.
Paul Rosenfeld, Ph.D. (February 6-7, 2003). Underground Storage Tank Litigation and Remediation. California CUPA Forum. Lecture conducted from Marriott Hotel, Anaheim California.
Paul Rosenfeld, Ph.D. (October 23, 2002) Underground Storage Tank Litigation and Remediation. EPA Underground Storage Tank Roundtable. Lecture conducted from Sacramento California.
Rosenfeld, P.E. and Suffet, M. (October 7- 10, 2002). Understanding Odor from Compost, Wastewater and Industrial Processes. Sixth Annual Symposium On Off Flavors in the Aquatic Environment. International Water Association. Lecture conducted from Barcelona Spain.
Rosenfeld, P.E. and Suffet, M. (October 7- 10, 2002). Using High Carbon Wood Ash to Control Compost Odor.
Sixth Annual Symposium On Off Flavors in the Aquatic Environment. International Water Association . Lecture conducted from Barcelona Spain.
Rosenfeld, P.E. and Grey, M. A. (September 22-24, 2002). Biocycle Composting For Coastal Sage Restoration.
Northwest Biosolids Management Association. Lecture conducted from Vancouver Washington..
Rosenfeld, P.E. and Grey, M. A. (November 11-14, 2002). Using High-Carbon Wood Ash to Control Odor at a Green Materials Composting Facility. Soil Science Society Annual Conference. Lecture conducted from Indianapolis, Maryland.
Rosenfeld. P.E. (September 16, 2000). Two stage biofilter for biosolids composting odor control. Water Environment Federation. Lecture conducted from Anaheim California.
Rosenfeld. P.E. (October 16, 2000). Wood ash and biofilter control of compost odor. Biofest. Lecture conducted from Ocean Shores, California.
Rosenfeld, P.E. (2000). Bioremediation Using Organic Soil Amendments. California Resource Recovery Association. Lecture conducted from Sacramento California.
Rosenfeld, P.E., C.L. Henry, R. Harrison. (1998). Oat and Grass Seed Germination and Nitrogen and Sulfur Emissions Following Biosolids Incorporation With High-Carbon Wood-Ash. Water Environment Federation 12th Annual Residuals and Biosolids Management Conference Proceedings. Lecture conducted from Bellevue Washington.
Rosenfeld, P.E., and C.L. Henry. (1999). An evaluation of ash incorporation with biosolids for odor reduction. Soil Science Society of America. Lecture conducted from Salt Lake City Utah.
Rosenfeld, P.E., C.L. Henry, R. Harrison. (1998). Comparison of Microbial Activity and Odor Emissions from Three Different Biosolids Applied to Forest Soil. Brown and Caldwell. Lecture conducted from Seattle Washington.
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Paul E. Rosenfeld, Ph.D. Page 7 of 10 October 2021
Rosenfeld, P.E., C.L. Henry. (1998). Characterization, Quantification, and Control of Odor Emissions from Biosolids Application To Forest Soil. Biofest. Lecture conducted from Lake Chelan, Washington.
Rosenfeld, P.E, C.L. Henry, R. Harrison. (1998). Oat and Grass Seed Germination and Nitrogen and Sulfur Emissions Following Biosolids Incorporation With High-Carbon Wood-Ash. Water Environment Federation 12th Annual Residuals and Biosolids Management Conference Proceedings. Lecture conducted from Bellevue Washington.
Rosenfeld, P.E., C.L. Henry, R. B. Harrison, and R. Dills. (1997). Comparison of Odor Emissions From Three Different Biosolids Applied to Forest Soil. Soil Science Society of America. Lecture conducted from Anaheim California.
Teaching Experience:
UCLA Department of Environmental Health (Summer 2003 through 20010) Taught Environmental Health Science 100 to students, including undergrad, medical doctors, public health professionals and nurses. Course focused on the health effects of environmental contaminants.
National Ground Water Association, Successful Remediation Technologies. Custom Course in Sante Fe, New Mexico. May 21, 2002. Focused on fate and transport of fuel contaminants associated with underground storage tanks.
National Ground Water Association; Successful Remediation Technologies Course in Chicago Illinois. April 1, 2002. Focused on fate and transport of contaminants associated with Superfund and RCRA sites.
California Integrated Waste Management Board, April and May, 2001. Alternative Landfill Caps Seminar in San Diego, Ventura, and San Francisco. Focused on both prescriptive and innovative landfill cover design.
UCLA Department of Environmental Engineering, February 5, 2002. Seminar on Successful Remediation Technologies focusing on Groundwater Remediation.
University Of Washington, Soil Science Program, Teaching Assistant for several courses including: Soil Chemistry, Organic Soil Amendments, and Soil Stability.
U.C. Berkeley, Environmental Science Program Teaching Assistant for Environmental Science 10.
Academic Grants Awarded:
California Integrated Waste Management Board. $41,000 grant awarded to UCLA Institute of the Environment.
Goal: To investigate effect of high carbon wood ash on volatile organic emissions from compost. 2001.
Synagro Technologies, Corona California: $10,000 grant awarded to San Diego State University.
Goal: investigate effect of biosolids for restoration and remediation of degraded coastal sage soils. 2000.
King County, Department of Research and Technology, Washington State. $100,000 grant awarded to University of Washington: Goal: To investigate odor emissions from biosolids application and the effect of polymers and ash on VOC emissions. 1998.
Northwest Biosolids Management Association, Washington State. $20,000 grant awarded to investigate effect of polymers and ash on VOC emissions from biosolids. 1997.
James River Corporation, Oregon: $10,000 grant was awarded to investigate the success of genetically engineered Poplar trees with resistance to round-up. 1996.
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Paul E. Rosenfeld, Ph.D. Page 8 of 10 October 2021
United State Forest Service, Tahoe National Forest: $15,000 grant was awarded to investigating fire ecology of the Tahoe National Forest. 1995.
Kellogg Foundation, Washington D.C. $500 grant was awarded to construct a large anaerobic digester on St. Kitts in West Indies. 1993
Deposition and/or Trial Testimony:
In the Circuit Court Of The Twentieth Judicial Circuit, St Clair County, Illinois Martha Custer et al., Plaintiff vs. Cerro Flow Products, Inc., Defendants Case No.: No. 0i9-L-2295
Rosenfeld Deposition, 5-14-2021
Trial, October 8-4-2021
In the Circuit Court of Cook County Illinois
Joseph Rafferty, Plaintiff vs. Consolidated Rail Corporation and National Railroad Passenger Corporation d/b/a AMTRAK,
Case No.: No. 18-L-6845
Rosenfeld Deposition, 6-28-2021
In the United States District Court For the Northern District of Illinois Theresa Romcoe, Plaintiff vs. Northeast Illinois Regional Commuter Railroad Corporation d/b/a METRA Rail, Defendants
Case No.: No. 17-cv-8517
Rosenfeld Deposition, 5-25-2021
In the Superior Court of the State of Arizona In and For the Cunty of Maricopa Mary Tryon et al., Plaintiff vs. The City of Pheonix v. Cox Cactus Farm, L.L.C., Utah Shelter Systems, Inc.
Case Number CV20127-094749
Rosenfeld Deposition: 5-7-2021
In the United States District Court for the Eastern District of Texas Beaumont Division Robinson, Jeremy et al Plaintiffs, vs. CNA Insurance Company et al.
Case Number 1:17-cv-000508
Rosenfeld Deposition: 3-25-2021
In the Superior Court of the State of California, County of San Bernardino Gary Garner, Personal Representative for the Estate of Melvin Garner vs. BNSF Railway Company.
Case No. 1720288
Rosenfeld Deposition 2-23-2021
In the Superior Court of the State of California, County of Los Angeles, Spring Street Courthouse Benny M Rodriguez vs. Union Pacific Railroad, A Corporation, et al.
Case No. 18STCV01162
Rosenfeld Deposition 12-23-2020
In the Circuit Court of Jackson County, Missouri
Karen Cornwell, Plaintiff, vs. Marathon Petroleum, LP, Defendant.
Case No.: 1716-CV10006
Rosenfeld Deposition. 8-30-2019
In the United States District Court For The District of New Jersey Duarte et al, Plaintiffs, vs. United States Metals Refining Company et. al. Defendant.
Case No.: 2:17-cv-01624-ES-SCM
Rosenfeld Deposition. 6-7-2019
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Paul E. Rosenfeld, Ph.D. Page 9 of 10 October 2021
In the United States District Court of Southern District of Texas Galveston Division M/T Carla Maersk, Plaintiffs, vs. Conti 168., Schiffahrts-GMBH & Co. Bulker KG MS “Conti Perdido” Defendant.
Case No.: 3:15-CV-00106 consolidated with 3:15-CV-00237 Rosenfeld Deposition. 5-9-2019
In The Superior Court of the State of California In And For The County Of Los Angeles – Santa Monica Carole-Taddeo-Bates et al., vs. Ifran Khan et al., Defendants Case No.: No. BC615636
Rosenfeld Deposition, 1-26-2019
In The Superior Court of the State of California In And For The County Of Los Angeles – Santa Monica The San Gabriel Valley Council of Governments et al. vs El Adobe Apts. Inc. et al., Defendants Case No.: No. BC646857
Rosenfeld Deposition, 10-6-2018; Trial 3-7-19
In United States District Court For The District of Colorado Bells et al. Plaintiff vs. The 3M Company et al., Defendants Case No.: 1:16-cv-02531-RBJ
Rosenfeld Deposition, 3-15-2018 and 4-3-2018
In The District Court Of Regan County, Texas, 112th Judicial District Phillip Bales et al., Plaintiff vs. Dow Agrosciences, LLC, et al., Defendants Cause No.: 1923
Rosenfeld Deposition, 11-17-2017
In The Superior Court of the State of California In And For The County Of Contra Costa Simons et al., Plaintiffs vs. Chevron Corporation, et al., Defendants Cause No C12-01481
Rosenfeld Deposition, 11-20-2017
In The Circuit Court Of The Twentieth Judicial Circuit, St Clair County, Illinois Martha Custer et al., Plaintiff vs. Cerro Flow Products, Inc., Defendants Case No.: No. 0i9-L-2295
Rosenfeld Deposition, 8-23-2017
In United States District Court For The Southern District of Mississippi Guy Manuel vs. The BP Exploration et al., Defendants
Case: No 1:19-cv-00315-RHW
Rosenfeld Deposition, 4-22-2020
In The Superior Court of the State of California, For The County of Los Angeles Warrn Gilbert and Penny Gilber, Plaintiff vs. BMW of North America LLC Case No.: LC102019 (c/w BC582154)
Rosenfeld Deposition, 8-16-2017, Trail 8-28-2018
In the Northern District Court of Mississippi, Greenville Division Brenda J. Cooper, et al., Plaintiffs, vs. Meritor Inc., et al., Defendants Case Number: 4:16-cv-52-DMB-JVM
Rosenfeld Deposition: July 2017
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Paul E. Rosenfeld, Ph.D. Page 10 of 10 October 2021
In The Superior Court of the State of Washington, County of Snohomish Michael Davis and Julie Davis et al., Plaintiff vs. Cedar Grove Composting Inc., Defendants Case No.: No. 13-2-03987-5
Rosenfeld Deposition, February 2017
Trial, March 2017
In The Superior Court of the State of California, County of Alameda Charles Spain., Plaintiff vs. Thermo Fisher Scientific, et al., Defendants Case No.: RG14711115
Rosenfeld Deposition, September 2015
In The Iowa District Court In And For Poweshiek County
Russell D. Winburn, et al., Plaintiffs vs. Doug Hoksbergen, et al., Defendants Case No.: LALA002187
Rosenfeld Deposition, August 2015
In The Circuit Court of Ohio County, West Virginia
Robert Andrews, et al. v. Antero, et al.
Civil Action N0. 14-C-30000
Rosenfeld Deposition, June 2015
In The Iowa District Court For Muscatine County
Laurie Freeman et. al. Plaintiffs vs. Grain Processing Corporation, Defendant Case No 4980
Rosenfeld Deposition: May 2015
In the Circuit Court of the 17th Judicial Circuit, in and For Broward County, Florida Walter Hinton, et. al. Plaintiff, vs. City of Fort Lauderdale, Florida, a Municipality, Defendant.
Case Number CACE07030358 (26)
Rosenfeld Deposition: December 2014
In the County Court of Dallas County Texas
Lisa Parr et al, Plaintiff, vs. Aruba et al, Defendant.
Case Number cc-11-01650-E
Rosenfeld Deposition: March and September 2013
Rosenfeld Trial: April 2014
In the Court of Common Pleas of Tuscarawas County Ohio
John Michael Abicht, et al., Plaintiffs, vs. Republic Services, Inc., et al., Defendants Case Number: 2008 CT 10 0741 (Cons. w/ 2009 CV 10 0987) Rosenfeld Deposition: October 2012
In the United States District Court for the Middle District of Alabama, Northern Division James K. Benefield, et al., Plaintiffs, vs. International Paper Company, Defendant.
Civil Action Number 2:09-cv-232-WHA-TFM
Rosenfeld Deposition: July 2010, June 2011
In the Circuit Court of Jefferson County Alabama
Jaeanette Moss Anthony, et al., Plaintiffs, vs. Drummond Company Inc., et al., Defendants Civil Action No. CV 2008-2076
Rosenfeld Deposition: September 2010
In the United States District Court, Western District Lafayette Division Ackle et al., Plaintiffs, vs. Citgo Petroleum Corporation, et al., Defendants.
Case Number 2:07CV1052
Rosenfeld Deposition: July 2009
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1 794 Sawnee Bean Road
Thetford Center VT 05075
Norman Marshall, President
(802) 356-2969
[email protected]
April 7, 2022
Mitchell M. Tsai
139 South Hudson Avenue Suite 200
Pasadena, CA 91101
Subject: Comments on the Highway 111 Specific Plan DEIR Dear Mr. Tsai
I have reviewed vehicle miles traveled (VMT) impacts in the Draft Environmental Impact Report dated January 2022 (“DEIR”). I make the following findings:
1) The DEIR VMT Calculations are invalid. The calculations include erroneous negative VMT for housing, and grossly inconsistent VMT between the project area and the City as a whole. 2) The City of Rancho Mirage has a large deficit of workforce housing. There are 10,800 more service jobs in the City today than there are service workers living in the City. This deficit will get worse as Disney’s Cotino project and other developments are constructed. Many Rancho Mirage workers commute more than 50 miles in each direction and some commute more than 100 miles.
3) More market rate housing in Rancho Mirage will greatly increase VMT. Given the affluent older population, each addition market-rate household requires approximately one additional service worker, and the additional commute VMT from that service worker must be considered in calculating the VMT impacts of the housing.
4) Constructing workforce housing in Rancho Mirage would reduce regional VMT. A valid analysis of the VMT impacts of the Highway 111 Specific Plan must draw a sharp contrast between market-rate housing and workforce housing and evaluate the VMT impacts of each separately. 5) Without enforceable commitments for a large portion of the increased residential entitlement to be workforce housing the Highway 111 Specific Plan will cause an excessive increase in VMT. 10-395
2 The DEIR VMT Calculations are Invalid
The calculations include erroneous negative VMT for housing, and grossly inconsistent VMT between the project area and the City as a whole.
The DEIR asserts that the Project will result in less future VMT than the No Project alternative. It states:
Per the VMT Analysis, the currently adopted land use table (2017 General Plan) will generate approximately 1,275,319 daily VMT and 465,491,435 annual VMT, and the proposed 2040 land use table will generate approximately 1,121,638 daily VMT and 409,397,870 annual VMT. (DEIR p. 2-4-12)
These numbers are documented in the DEIR table reproduced below. (DEIR, p. 896 of 900)
These numbers can be restated in the two of two equations where “P” represents population and “E” represents employment:
Without Project 8,044 x P + 11,388 x E = 1,275,319 VMT With Project: 10,199 x P + 10,596 x E = 1,121,638
This restatement includes two equations and two unknowns, and the values of P and E can be solved for using standard high school algebra.
P = -23.9 VMT per person
E = 128.9 VMT per person
The values in the DEIR table reproduced above imply that adding a person reduces VMT by 23.9 and adding an employee adds 128.9 VMT. The large negative value for population is so unrealistic that it must be an error. Even if there is an extreme jobs-housing imbalance and that adding workforce housing will substitute for workers commuting extremely long distances, adding population would still increase VMT because the majority of household VMT is for non- work trips. I examine the jobs/housing balance question in a later section of this letter.
A DEIR table on the next page extends the geographic analysis to include all of Rancho Mirage City. (DEIR, p. 897 of 900)
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3 Somehow, the VMT totals in Table 4 for the entire City are lower than the VMT totals for the project area only in Table 3. The VMT per Service Population numbers are less than a quarter as high. These differences are a sign of serious errors in the VMT estimates.
Solving again for P and E using the numbers in Table 4.
P = -2.0 VMT per person
E = 31.2 VMT per person
The negative number for population again appears to be an error.
It is possible that the Riverside Transportation Analysis Model (RIVTAM) performs poorly in this part of Riverside County. It also is possible that the DEIR consultants misapplied the model. In either case, the DEIR VMT analysis is invalid.
The Rancho Mirage Has a Large Deficit of Workforce Housing Current Rancho Mirage demographic facts from the U.S. Census Bureau1 include:
• Population in 2020: 16,999
• Persons 65 years and over: 50.4%
• Persons under 18 years, percent 7.7%
• Households: 9,637
• Persons per household: 1.91
• In civilian labor force, total, percent of population:41.5% These statistics show a largely older population with small households and few children, and a relatively small proportion of residents in the labor force.
Rancho Mirage is a very affluent community with current average house prices exceeding $1.2 million.2
1 https://www.census.gov/quickfacts/fact/table/ranchomiragecitycalifornia,lahabraheightscitycalifornia,chowchillac itycalifornia/AGE135219
2 Kevin Stanley Realtor, March 8, 2022. https://kevinstanley.net/greater-palm-springs-real-estate-housing-report . 10-397
4 The combination of an older affluent population and extraordinarily high housing prices have created a huge deficit in workforce housing.3
The U.S. Census Bureau publishes Longitudinal Employer-Household Dynamics (LEHD) Origin-Destination Employment Statistics (LODES) data that provide detailed geographic data about workers, jobs, and commutes. Figure 1 compares the data for jobs in Rancho Mirage and workers living in Rancho Mirage.
Figure 1: Rancho Mirage Jobs vs. Workers Living in Rancho Mirage
As shown in Figure 1, there are 15,000 jobs in Rancho Mirage but less than 5,000 workers living in Rancho Mirage. The 15,000 jobs are primarily in the service sector, with 89% in one of the service categories including health care, accommodations and food services, retail, entertainment and recreation, and other services. However, only 55% of the workers living in Rancho Mirage are employed in those industries. There is a deficit of 10,800 service workers in Rancho Mirage today.
3 Ingrassia, Jake, KESQ. Affordable housing crisis amplifies as more luxury developments come to the valley, March 15, 2022. https://kesq.com/news/2022/03/15/affordable-housing-crisis-amplifies-as-more-luxury-developments- come-to-the-valley/
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5 This includes a 3,900-worker deficit in the hospitality industry (adding together accommodations, food service, recreation, and entertainment).
The Coachella Valley Economic Partnership has summarized income data showing that the average income per hospitality worker is less than $16,000 per year (Figure 2).
Figure 2: Average Income Per Coachella Valley Worker by Major Industry Sectors4
Obviously, these hospitality workers earning less than $16,000 per year are not able to buy $1.2 million houses. Instead, they end up making long commuters and generating excessive VMT. Residential locations of those working in Rancho Mirage are mapped in Figure 3.
4 Coachella Valley Economic Partnership. Average income for workers in the Coachella valley, https://cvep.com/average-income-for-workers-in-the-coachella- valley/?utm_source=rss&utm_medium=rss&utm_campaign=average -income-for-workers-in-the-coachella-valley# 10-399
6 Figure 3: Residential Locations of Those Rancho Mirage Workforce (LODES data) – Each red dot represents one commuter, City of Rancho Mirage shown in blue
As shown in Figure 3, Rancho Mirage workers commute long distances from all other southern California. Many of these commutes are longer than 50 miles and some are longer than 100 miles.
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7 More Market Rate Housing in Rancho Mirage Will Greatly Increase VMT The DEIR VMT analysis pretends that future employment in Rancho Mirage will build out to whatever level is allowed by land use regulations. In reality, Rancho Mirage has a service economy and jobs will be added in proportion to the growth in housing, hotels and resorts. The proposed reallocation of land away from commercial to residential is an indication that the market doesn’t require all of the land that is currently allocated to commercial use.
As discussed above, the City of Rancho Mirage has less than 10,000 households but over 13,000 service workers. Some of these service workers work at hotels and resorts, but most are providing services to the Rancho Mirage population. Therefore, it appears that with the older affluent population of Rancho Mirage, it takes about one service worker, on average, to serve one household.
Therefore, in evaluating the impacts of adding to the number of market-rate housing units in Rancho Mirage, we must not only add the direct VMT impacts of an added housing unit but also add in the VMT impacts of another service worker. As illustrated in Figure 3, the VMT impacts of adding these service workers is very great.
The DEIR is disingenuous when it suggests that reallocating land from commercial to residential will reduce future VMT because adding to residential growth will also cause service job growth.
This workforce housing problem is growing even worse. In a recent report:
The national spotlight fell on the Coachella Valley in February when Disney announced its new residential-living business would debut its first master planned community here in Rancho Mirage.
Cotino is slated to be the first development of its kind from Storyliving, Disney’s new venture into the housing business. The proposal includes 1,700 homes, a 400-room hotel, and shopping and dining spots centered around a 24-acre lagoon meant to mimic a beachfront oasis in the desert. The city of Rancho Mirage—long associated with high- end resort living—called it “one of the most significant master-planned projects in Rancho Mirage history.”5
The Cotino project alone likely will require at least 2,000 additional service workers, with few, if any living in the planned development, and also few living in Rancho Mirage unless a large amount of workforce housing is constructed.
5 Daniels, Melissa. Civic Solutions: As Resort Life Proliferates, What About Affordable Housing? Civic Independent, March 8, 2022. https://cvindependent.com/2022/03/civic-solutions-as-resort-life-proliferates-what-about- affordable-housing/
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8 Workforce Housing in Rancho Mirage Would Reduce Regional VMT Workforce housing that reduces commute lengths to Rancho Mirage jobs would reduce regional VMT even though there likely would be more local VMT including both work and non-work trips.
A valid analysis of the VMT impacts of the Highway 111 Specific Plan must draw a sharp contrast between market-rate housing and workforce housing and evaluate the VMT impacts of each separately.
Unless a large proportion of any additional residential entitlement is workforce housing, there will be a large increase in VMT.
In the DEIR, the word “workforce” appears only once - noting that there is a 20% potential density bonus in the R-H/SP High Density Residential category. (DEIR, p. 36 of 900) There is no discussion of whether this bonus will be attractive enough that workforce housing will be constructed.
Similarly, the DEIR equates density and affordability: “The allowance of such high maximum density demonstrates that the City can provide a substantial number of future residential units that are market- rate affordable.” (DEIR p. 205 of 900) This excerpt raises several questions. What is a “substantial number” of units? Is it 10, 100, 1000? What is “market-rate affordable”? Is it $1 million instead of $1.2 million? How does the higher allowed density translate into actual new housing units that would be affordable to the City’s workforce?
Without enforceable commitments for a large portion of the increased residential entitlement to be workforce housing the Highway 111 Specific Plan will cause an excessive increase in VMT.
Sincerely,
Norman L. Marshall
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9 Resume
NORMAN L. MARSHALL, PRESIDENT
[email protected]
EDUCATION:
Master of Science in Engineering Sciences, Dartmouth College, Hanover, NH, 1982 Bachelor of Science in Mathematics, Worcester Polytechnic Institute, Worcester, MA, 1977 PROFESSIONAL EXPERIENCE: (32 Years, 18 at Smart Mobility, Inc.) Norm Marshall helped found Smart Mobility, Inc. in 2001. Prior to this, he was at RSG for 14 years where he developed a national practice in travel demand modeling. He specializes in analyzing the relationships between the built environment and travel behavior and doing planning that coordinates multi-modal transportation with land use and community needs.
Regional Land Use/Transportation Scenario Planning
Portland Area Comprehensive Transportation System (PACTS) – the Portland Maine Metropolitan Planning Organization. Updating regional travel demand model with new data (including AirSage), adding a truck model, and multiclass assignment including differentiation between cash toll and transponder payments.
Loudoun County Virginia Dynamic Traffic Assignment – Enhanced subarea travel demand model to include Dynamic Traffic Assignment (Cube). Model being used to better understand impacts of roadway expansion on induced travel.
Vermont Agency of Transportation-Enhanced statewide travel demand model to evaluate travel impacts of closures and delays resulting from severe storm events. Model uses innovate Monte Carlo simulations process to account for combinations of failures.
California Air Resources Board – Led team including the University of California in $250k project that reviewed the ability of the new generation of regional activity-based models and land use models to accurately account for greenhouse gas emissions from alternative scenarios including more compact walkable land use and roadway pricing. This work included hands-on testing of the most complex travel demand models in use in the U.S. today.
Climate Plan (California statewide) – Assisted large coalition of groups in reviewing and participating in the target setting process required by Senate Bill 375 and administered by the California Air Resources Board to reduce future greenhouse gas emissions through land use measures and other regional initiatives.
Chittenden County (2060 Land use and Transportation Vision Burlington Vermont region) – led extensive public visioning project as part of MPO’s long-range transportation plan update.
Flagstaff Metropolitan Planning Organization – Implemented walk, transit and bike models within regional travel demand model. The bike model includes skimming bike networks including on-road and off-road bicycle facilities with a bike level of service established for each segment.
Chicago Metropolis Plan and Chicago Metropolis Freight Plan (6-county region)— developed alternative transportation scenarios, made enhancements in the regional travel demand model, and used the enhanced 10-403
10 model to evaluate alternative scenarios including development of alternative regional transit concepts.
Developed multi-class assignment model and used it to analyze freight alternatives including congestion pricing and other peak shifting strategies.
Municipal Planning
City of Grand Rapids – Michigan Street Corridor – developed peak period subarea model including non- motorized trips based on urban form. Model is being used to develop traffic volumes for several alternatives that are being additional analyzed using the City’s Synchro model
City of Omaha - Modified regional travel demand model to properly account for non-motorized trips, transit trips and shorter auto trips that would result from more compact mixed-use development. Scenarios with different roadway, transit, and land use alternatives were modeled.
City of Dublin (Columbus region) – Modified regional travel demand model to properly account for non- motorized trips and shorter auto trips that would result from more compact mixed-use development. The model was applied in analyses for a new downtown to be constructed in the Bridge Street corridor on both sides of an historic village center.
City of Portland, Maine – Implemented model improvements that better account for non-motorized trips and interactions between land use and transportation and applied the enhanced model to two subarea studies.
City of Honolulu – Kaka’ako Transit Oriented Development (TOD) – applied regional travel demand model in estimating impacts of proposed TOD including estimating internal trip capture.
City of Burlington (Vermont) Transportation Plan – Led team that developing Transportation Plan focused on supporting increased population and employment without increases in traffic by focusing investments and policies on transit, walking, biking and Transportation Demand Management.
Transit Planning
Regional Transportation Authority (Chicago) and Chicago Metropolis 2020 – evaluated alternative 2020 and 2030 system-wide transit scenarios including deterioration and enhance/expand under alternative land use and energy pricing assumptions in support of initiatives for increased public funding.
Capital Metropolitan Transportation Authority (Austin, TX) Transit Vision – analyzed the regional effects of implementing the transit vision in concert with an aggressive transit-oriented development plan developed by Calthorpe Associates. Transit vision includes commuter rail and BRT.
Bus Rapid Transit for Northern Virginia HOT Lanes (Breakthrough Technologies, Inc and Environmental Defense.) – analyzed alternative Bus Rapid Transit (BRT) strategies for proposed privately-developing High Occupancy Toll lanes on I-95 and I-495 (Capital Beltway) including different service alternatives (point-to-point services, trunk lines intersecting connecting routes at in-line stations, and hybrid).
Roadway Corridor Planning
I-30 Little Rock Arkansas – Developed enhanced version of regional travel demand model that integrates TransCAD with open source Dynamic Traffic Assignment (DTA) software, and used to model I-30 alternatives.
Freeway bottlenecks are modeled much more accurately than in the base TransCAD model. 10-404
11 South Evacuation Lifeline (SELL) – In work for the South Carolina Coastal Conservation League, used Dynamic Travel Assignment (DTA) to estimate evaluation times with different transportation alternatives in coastal South Caroline including a new proposed freeway.
Hudson River Crossing Study (Capital District Transportation Committee and NYSDOT) – Analyzing long term capacity needs for Hudson River bridges which a special focus on the I-90 Patroon Island Bridge where a microsimulation VISSIM model was developed and applied.
PUBLICATIONS AND PRESENTATIONS (partial list)
DTA Love: Co-leader of workshop on Dynamic Traffic Assignment at the June 2019 Transportation Research Board Planning Applications Conference.
Forecasting the Impossible: The Status Quo of Estimating Traffic Flows with Static Traffic Assignment and the Future of Dynamic Traffic Assignment. Research in Transportation Business and Management 2018.
Assessing Freeway Expansion Projects with Regional Dynamic Traffic Assignment. Presented at the August 2018 Transportation Research Board Tools of the Trade Conference on Transportation Planning for Small and Medium Sized Communities.
Vermont Statewide Resilience Modeling. With Joseph Segale, James Sullivan and Roy Schiff. Presented at the May 2017 Transportation Research Board Planning Applications Conference.
Assessing Freeway Expansion Projects with Regional Dynamic Traffic Assignment. Presented at the May 2017 Transportation Research Board Planning Applications Conference.
Pre-Destination Choice Walk Mode Choice Modeling. Presented at the May 2017 Transportation Research Board Planning Applications Conference.
A Statistical Model of Regional Traffic Congestion in the United States, presented at the 2016 Annual Meeting of the Transportation Research Board.
MEMBERSHIPS/AFFILIATIONS
Associate Member, Transportation Research Board (TRB)
Member and Co-Leader Project for Transportation Modeling Reform, Congress for the New Urbanism (CNU)
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69 .
0 8
'
N
8 9
°
4 4
'
1 6
"
E
32 .
2 1
'
∆=
0 4
°
4 7
'
4 0
"
R=
9 8
9 .
5 0
'
82 .
8 0
'
=
5 3
°
4 0
'
2 8
"
R
=
4 5
8 .
0 0
'
4 2
9 .
0 5
'
=22°56'29" R=550.00' 220.22'
=0 9 °0 3 '3 8 " R =1 5 0 0 .0 0 ' 2 3 7 .2 0 '
=
5 8
°
0 7
'
3 8
"
R
=
3 9
0 .
0 0
'
3 95
.
66'
=87°19'35" R=200.00' 304.83'
=
4 8°3
1'3
5 " R
=
5 75
.
0 0
'
4 8
6 .
9 9
'
=1
8°37'55" R=1610.50' 523.72'
∆=
1 9
°
1 8
'
1 0
"
R=
3 4
0 .
0 0
'
11 4
.
5 4
'
∆=
1 8
°
2 2
'
1 4
"
R=
2 4
0 .
0 0
'
76 .
9 5
'
∆=
1 3
3 °
4 5
'
3 4
"
R=
5 0
.
0 0
'
11 6
.
7 3
'
∆=
1 0
5 °
1 5
'
4 7
"
R=
6 5
.
0 0
'
11 9
.
4 2
'
∆=
2 3
°
1 5
'
0 8
"
R=
2 1
0 .
0 0
'
85 .
2 2
'
∆=
1 6
°
4 0
'
4 9
"
R=
2 4
5 .
0 0
'
71 .
3 3
'
∆=
1 7
°
4 1
'
1 3
"
R
=
1 3
6 .
1 4
'
4 2
.
0 3
'
N
4 2
°
1 4
'
1 3
"
E
82 .
9 8
'
∆=
1 7
°
4 1
'
1 3
"
R
=
1 6
0 .
0 4
'
4 9
.
4 0
'
N
5 0
°
4 0
'
1 1
"
W
36 .
4 1
'
∆=
1 2
°
5 4
'
5 9
"
R=
7 4
9 .
5 0
'
16 8
.
9 6
'
N
1 0
°
3 4
'
2 6
"
W
86 .
4 5
'
N
4 2
°
3 0
'
3 0
"
W
95 .
0 0
'
R
=
1 5
0 .
0 '
R = 283.5'
R = 300.0'
R = 250.0'
R
=
1 1
6 0
.
0 '
R
=
1 2
9 3
.
5 '
R
=
4 0
0 .
0 '
R
=
2 6
6 .
5 '
R = 500.0'
R = 1 7 8 .0 '
R = 25 0.0'
R = 2 0 0 .0 '
R = 2 0 0 .0 '
R
= 1
0 0
0 .
0 '
R
=
1 0
0 0.
0'
R = 1000.0'
R = 3 0 0 .0 '
R = 1000.0'
R
=
1 0
0 0
.
0 '
R
=
3 0
0 .
0 '
R
=
1 6
0 0
.
0 '
R
=
7 0
0 .
0 '
R = 1 8 0 .0 '
R
=
8 0
0 .
0 '
R
=
5 0
0 .
0 '
R = 285.0'
R
=
3 0
0 .
0 '
R
= 1
0 0
0 .
0 '
R
=
5 0
0 .
0 '
R = 5 0 0 .0 '
R
=
1 2
9 3
.
5 '
A
L
L
E
Y
"
E
"
A
L
L
E
Y
"
A
"
28 '
47'23'
15 '
33 '
15 '
15'33'15'
15'33'15'
15'
33'
5'
24'
5'
EX
.
2 4
'
A
C
C
E
S
S
E
A
S
E
M
E
N
T
P
E
R
RE
C
O
R
D
M
A
P
N
O
.
3 7
5 6
3 EX
.
2 4
'
A
C
C
E
S
S
E
A
S
E
M
E
N
T
P
E
R
RE
C
O
R
D
M
A
P
N
O
.
3 7
5 6
3 1
0 5
'
1 0
5 '
56'
1 0
5 '
8 9
'
58'
1 2
0 '
67'
9 9
'
1 25
'
8 1 '
L
O
T
"
C
"
0 .
0 5
A
C
.
53'
1 0
8 '
6 6 '
1 0
6 '
107
'
105'
4 9
'105'
4 9
'
105'
6 6
'
81'
4 1
'
4 8
'
48'
38'
6 8
'
6 8
'
8 6
'
5 6'
32'
56 '
56 '
105
'
56 '
56 '
105
'
56 '
58 '
105
'
105'
43'
3 1
'
35 '
102'
55'
88'
43 '
126'
49'
50 '
12'
32 '
87'
50 '
50 '
105
'
58 '
58 '
49 '
53 '
105
'
45'
105
'
49'
55 '
2 8
'
27'
114'
50 '
54'
49'
74'
1 1
0'
79 '
48 '
72 '
81'
57 '
57 '
105
'
57 '
105
'
55 '
106'
105
'
3 8 '
51 '
51 '
107
'
51 '
107
'
50 '
107'
107
'
107
'
48'
50 '
109'
54 '
50 '
106
'
50 '
50 '
106
'
50 '
50 '
106'50
'
50 '
106
'
50 '
50 '
106
'
85 '
106
'
41'
90'
3 7
'
50 '
106'
64'
55'
67'
1 0
5 '
9 1
'
1 0
5 '
55'
1 0
5 '
1 0
5 '
6 9 '
1 0
7 '
51'
1 0
5 '
50'
50'
1 0
5 '
8 7
'
54'
4 9 '
4 9
'
105'
4 9
'
105'
4 9
'
105
'
5 0
'
105
'
8 1 '
6 5
'
82'
105'
4 8
'
105'
5 5
'
105'
5 5
'
8 3
'
36'
6 8
'
105'
4 4
'
81'
5 1
'
105'
5 0
'
105'
4 9
'
80'
4 3
'
7 0
'
5 4
'
38'
39'
112
'
4 9
'
109
'
88 '
4 9'
9 2
'
4 5'
36'
8 5 '
106
'
6 5
'
5 0
'
106
'
5 0
'
110
'
40 '
50 '
110
'
45'
110
'
1 6
'
115
'
1 2
0'
5 0
'
112'
6 6
'
6 5
'
19 0
42 ,
5 5
9 S
F
0. 9
8 A
C
.
E
E
E
E
D
E
D
E
D
D
R=300.0'
D
D
D
D
E
E
D
D
E
E
D
D
E
E
60 '
25 '
2 4
'
D D
3 3
'
125'135'
135'
5 3
'
135'
53'
135'
145'62'
14 5
'
1 4
5 '
62'
1 4
5 '
6 2 '
1 4
5 '
62'
14 5
'
62'
14 5
'
13 5
'
53'
135
'
5 3'
135
'
5 3
'
135'
6 0
'
6 0
'
135'
9 0
'
9 0'
90'
109'109'
1 0 9 '
1 0 9'
109'
90'
9 0
'
5 3
'
8 9
'
8 7
'
135'
37 9
'
44'
41 2
'
5 4
'
61'
1 0
5 '
56'
50'
46'
1 0
5 '
1 0
8 '
1 0
5 '
51 '
105
'
51 '
105
'
51 '
105
'
51 '
105
'
51 '
105'
105
'51
'
105
'
105
'
56 '
105
'
56 '
105
'
56 '
105
'
1 07'
76 '
105'60
'
105
'60
'
105
'
71 '
106
'
105'
67 '
117'
105'
105
'
105
'58
'
105
'58
'
10 5
'59
'
1 0
5'
72'
69'
59'
PR
O
P
.
1 5
'
L
A
N
D
S
C
A
P
E
&
P.
U
.
E
.
E
A
S
E
M
E
N
T
(
T
Y
P
.
)
PR
O
P
.
1 5
'
L
A
N
D
S
C
A
P
E
&
P.
U
.
E
.
E
A
S
E
M
E
N
T
(
T
Y
P
.
)
G
G
AA
B
B
1 0
5 '
27'
52'
59'
50'
1 0
5 '
9 9
'
8 3
'
7 6
'
4 0
'
5 1
'
4 1'
7 9 '
46 '
3 8
'
R = 195.5'
71 '
R = 1000.0'
R
=
1 0
3 6
.
0 '
R = 1
5 9
4.0'
R = 7
6 6.0'
R = 1006.0'
R = 7
0 0.0'
R = 3
00.0'
R = 300
.0'
R = 300.0'
69 '
71 '
105'
107
'
67 '
79'
3 9 '
50'
R
=
1 2
9 3
.
5 '
15 4
5,
7 7
5 S
F
15 3
5,
7 7
5 S
F
15 2
5,
7 7
5 S
F
15 1
5,
7 7
5 S
F
15 8
5,
7 7
5 S
F
15 7
5,
7 7
5 S
F
15 6
5,
7 7
5 S
F
15 5
5,
7 7
5 S
F
55 '
105
'
55 '
55 '
105
'55
'
55 '
105
'
55 '
55 '
105
'55
'
105
'
55 '
55 '
105
'
55 '
55 '
105
'
55 '
55 '
105
'
55 '
105
'
55 '
105'
LO
T
"
O
"
31 ,
6 8
2 S
F
0. 7
3 A
C
.
LO
T
"
N
"
24 ,
9 4
5 S
F
0. 5
7 A
C
.
E
E
R = 700.0'
AL
L
E
Y
"
H
"
24'
24'
TID
E
S
W
E
L
L
W
A
Y
BR
I
L
L
I
A
N
C
E
AVENUE
33'
71 '
105
'
71 '
81'
15 '
33 '
15 '
8 3
'
22 8
'
180
'
3 1
8 '
26 4
'
555
'
54'
15 4
'
4 58'
271'
2 9
2 '
1 1
2 7
'
6 6
9 '
1 5
'
1 5
'
PR
O
P
.
T
E
M
P
O
R
A
R
Y
EM
E
R
G
E
N
C
Y
AC
C
E
S
S
PO
I
N
T
PR
O
P
.
T
E
M
P
O
R
A
R
Y
A
C
C
E
S
S
D
R
I
V
E
W
A
Y
WI
T
H
G
A
T
E
&
K
N
O
X
B
O
X
F F
PR
O
P
.
T
E
M
P
O
R
A
R
Y
EM
E
R
G
E
N
C
Y
A
C
C
E
S
S
E
E
24'
=
5 1
°
0 1
'
3 6
"
R
=
1 0
1 9
.
5 0
'
9 0
7 .
9 5
'
LO
T
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M
"
3,
7 7
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F
0. 0
9 A
C
.
LO
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U
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3,
7 5
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F
0. 0
9 A
C
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LO
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G
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2,
3 2
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F
0. 0
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C
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LO
T
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L
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3,
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F
0. 0
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C
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K
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4,
2 9
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0. 1
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C
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LO
T
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3,
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0. 0
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C
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LO
T
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S
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3,
6 4
1 S
F
0. 0
8 A
C
.
LO
T
"
H
"
15 ,
9 0
4 S
F
0. 3
7 A
C
.
LO
T
"
Q
"
13 ,
1 6
6 S
F
0. 3
0 A
C
.
LO
T
"
P
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15 ,
0 1
1 S
F
0. 3
4 A
C
.
LO
T
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I
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2,
2 7
9 S
F
0. 0
5 A
C
.
PR
O
P
.
C
V
W
D
W
E
L
L
S
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PR
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R
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B
A
S
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PR
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P
.
2 4
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A
C
C
E
S
S
EA
S
E
M
E
N
T
C
C
G
G
MONTEREY AVENUE
FR
A
N
K
S
I
N
A
T
R
A
D
R
I
V
E
GE
R
A
L
D
F
O
R
D
D
R
I
V
E
BOB HOPE DRIVE
PH
A
S
E
1 B
&
1 C
LO
T
3 2
8 &
3 2
9 PE
R
T
R
.
N
O
.
3 7
8 5
6 /
LO
T
7 &
8 P
E
R
TR
.
N
O
.
3 7
5 6
3 60
'
(
P
R
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J
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C
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S
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D
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)
60 '
(
B
Y
O
T
H
E
R
S
)
12 0
'
(
U
L
T
I
M
A
T
E
R
/
W
)
16 '
8'
8'
45 '
13 '
12 '
20 '
7'
13 '
12 '
20 '
7'
45 '
25 '
EX
.
EX
.
P
A
V
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P
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PR
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1 0
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W
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B
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16 '
16 '
33 '
*1
5 '
M
I
N
.
*1
5 '
M
I
N
.
5'
5'
5'
5'
2'
MI
N
.
5'
5'
2'
MI
N
.
6'
6'
3'
43 '
C
V
W
D
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A
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T
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'
17 .
5 '
17 .
5 '
3'
2'
2. 5
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5. 5
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10 '
10 '
*NO
T
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:
P
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PR
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24 6
(
E
)
24 7
(
E
)
24 8
(
E
)
24 9
(
E
)
25 0
(
E
)
17 7
(
E
)
17 6
(
E
)
(E
)
15 9
(
E
)
31 0
30 9
30 8
30 7
17 5
(E
)
17 4
(E
)
17 3
(E
)
17 2
(E
)
17 1
(E
)
17 0
16 4
(
E
)
(E
)
16 3
(E
)
16 2
(E
)
16 1
(E
)
16 9
(E
)
16 8
(E
)
16 7
(E
)
16 6
(E
)
16 5
16 0
(
E
)
(E
)
18 1
(E
)
18 0
(E
)
17 9
(E
)
17 8
(E
)
19 2
(E
)
19 3
(E
)
19 4
(E
)
19 5
(E
)
19 6
19 7
(
E
)
19 8
(
E
)
(E
)
18 6
(E
)
18 5
(E
)
18 4
(E
)
18 3
(E
)
18 2
(E
)
19 1
(E
)
19 0
(E
)
18 9
(E
)
18 8
(E
)
18 7
(E
)
21 3
(E
)
21 2
(E
)
21 1
(E
)
21 0
(E
)
20 9
(E
)
20 8
(E
)
20 7
(E
)
20 6
(E
)
20 5
(E
)
20 4
(E
)
20 3
(E
)
20 2
(E
)
20 1
(E
)
20 0
19 9
(
E
)
26 4
(
F
)
26 3
(
F
)
26 2
(
F
)
26 1
(
F
)
26 0
(
F
)
(F
)
32 0
(F
)
31 9
(F
)
31 8
31 7
(
F
)
(F
)
32 4
(F
)
32 5
(F
)
32 6
(F
)
32 7
(F
)
26 9
(F
)
27 0
(F
)
27 1
(F
)
26 5
(F
)
26 6
(F
)
26 7
(F
)
26 8
25 7
(
F
)
(F
)
25 8
(F
)
25 9
(F
)
25 6
(F
)
25 5
(F
)
25 4
(F
)
25 3
(F
)
25 2
(F
)
25 1
(F
)
31 6
32 3
(
E
)
(E
)
32 2
(F
)
31 5
(F
)
31 4
55 (
A
)
56 (
A
)
57 (
A
)
58 (
A
)
59 (
A
)
60 (
A
)
61 (
A
)
62 (
A
)
63 (
A
)
64 (
A
)
65 (
A
)
66 (
A
)
67 (
A
)
68 (
A
)
47 (
A
)
48 (
A
)
49 (
A
)
50 (
A
)
51 (
A
)
52 (
A
)
53 (
A
)
54 (
A
)
34 (
B
)
35 (
B
)
36 (
B
)
37 (
B
)
38 (
B
)
39 (
B
)
40 (
B
)
41 (
B
)
42 (
B
)
43 (
B
)
44 (
B
)
45 (
B
)
46 (
B
)
69 (
B
)
70 (
B
)
71 (
B
)
72 (
B
)
73 (
B
)
74 (
B
)
75 (
B
)
76 (
B
)
77 (
B
)
78 (
B
)
79 (
B
)
25 (
B
)
26 (
B
)
27 (
B
)
28 (
B
)
29 (
B
)
30 (
B
)
31 (
B
)
32 (
B
)
33 (
B
)
19 (
C
)
20 (
C
)
21 (
C
)
22 (
C
)
23 (
C
)
24 (
C
)
17 (
C
)
16 (
C
)
15 (
C
)
14 (
C
)
18 (
C
)
12 (
C
)
13 (
C
)
6(
C
)
7(
C
)
8(
C
)
9(
C
)
10 (
C
)
11 (
C
)
5(
C
)
4(
C
)
3(
C
)
2(
C
)
1(
C
)
89 (
C
)
88 (
C
)
87 (
C
)
86 (
C
)
85 (
C
)
84 (
C
)
83 (
C
)
82 (
C
)
81 (
C
)
80 (
C
)
14 5
(
C
)
14 6
(
C
)
22 0
(
C
)
21 9
(
C
)
21 8
(
C
)
21 7
(
C
)
21 6
(
C
)
21 5
(
C
)
21 4
(
C
)
23 7
(
D
)
23 8
(
D
)
23 9
(
D
)
24 0
(
D
)
24 1
(
D
)
23 6
(
D
)
23 5
(
D
)
23 4
(
D
)
24 2
(
D
)
24 3
(
D
)
23 3
(
D
)
27 7
(
D
)
27 8
(
D
)
27 9
(
D
)
28 0
(
D
)
28 1
28 2
(
D
)
28 3
(
D
)
27 5
(
D
)
27 6
(
D
)
28 4
(
D
)
28 5
(
D
)
28 6
(
D
)
28 7
(
D
)
28 8
(
D
)
28 9
(
D
)
(D
)
(
D
)
(
D
)
(D
)
(D
)
(D
)
(D
)
(D
)
23 2
(
D
)
23 1
(
D
)
23 0
(
D
)
22 9
(
D
)
22 8
(
D
)
22 7
(
D
)
22 6
(
D
)
22 5
(
D
)
22 4
(
D
)
22 3
(
D
)
22 2
(
D
)
22 1
(
D
)
15 3
(
D
)
15 4
(
D
)
15 5
(
D
)
15 6
(
D
)
13 0
(
D
)
13 1
(
D
)
13 2
(
D
)
13 3
(
D
)
12 8
(
D
)
12 7
(
D
)
12 6
(
D
)
12 9
(
D
)
15 7
(
D
)
15 8
(
D
)
12 5
(
D
)
12 2
(
D
)
13 7
(
D
)
13 6
(
D
)
13 5
(
D
)
13 4
(
D
)
13 8
(
D
)
(D
)
(D
)
(D
)
(D
)
(D
)
(D
)
(D
)
(D
)
(D
)
(D
)
15 1
(
D
)
15 2
(
D
)
96 (
D
)
95 (
D
)
94 (
D
)
93 (
D
)
92 (
D
)
91 (
D
)
90 (
D
)
97 (
D
)
98 (
D
)
99 (
D
)
10 0
(
D
)
10 1
(
D
)
10 2
(
D
)
10 3
(
D
)
10 4
(
D
)
10 5
(
D
)
10 6
(
D
)
10 7
(
D
)
10 8
(
D
)
10 9
(
D
)
11 0
(
D
)
11 1
(
D
)
11 2
(
D
)
11 3
(
D
)
11 4
(
D
)
(D
)
(D
)
(D
)
(D
)
11 9
(
D
)
(D
)
12 1
(
D
)
29 0
2 9
1 2
9 2
29 3
29 4
29 5
29 6
29 7
12 0
11 5
11 6
11 7
11 8
(D
)
12 4
(D
)
12 3
13 9
14 0
14 1
14 2
14 3
14 4
14 7
14 8
14 9
15 0
(D
)
43 (D
)
39 41
(
D
)
30 (
D
)
29 (
D
)
28 (
D
)
27 (
D
)
26 (
D
)
(E
)
23 (E
)
24 (E
)
25 47
(
E
)
(E
)
44 (E
)
38 (E
)
35 (E
)
34 (E
)
33 32
(
E
)
31 (
E
)
(E
)1
(E
)2
(E
)3
(E
)4
(E
)5
(E
)6
(E
)7
(E
)8
(E
)9
(E
)
10 (E
)
11 (E
)
12 (E
)
13 (E
)
14 (E
)
15 16
(
E
)
17 (
E
)
18 (
E
)
42 (
F
)
40 (
F
)
93 (
F
)
94 (
F
)
95 (
F
)
96 (
F
)
97 (
F
)
98 (
F
)
87 (
F
)
88 (
F
)
89 (
F
)
90 (
F
)
91 (
F
)
92 (
F
)
73 (
F
)
74 (
F
)
75 (
F
)
76 (
F
)
77 (
F
)
78 (
F
)
68 (
F
)
69 (
F
)
70 (
F
)
71 (
F
)
72 (
F
)
(F
)
36 (F
)
37 (F
)
46 (F
)
45 (F
)
19 (F
)
20 (F
)
21 (F
)
22 (F
)
55 (F
)
54 (F
)
53 (F
)
52 51
(
F
)
50 (
F
)
(F
)
56 (F
)
57 (F
)
58 49
(
F
)
48 (
F
)
(G
)
17 1
(G
)
17 2
(G
)
17 3
(G
)
17 4
(G
)
16 7
(G
)
16 8
(
G
)
16 9
(G
)
17 0
(G
)
16 3
(G
)
16 4
(G
)
16 5
(G
)
16 6
(G
)
15 9
(G
)
16 0
(G
)
16 1
(G
)
16 2
(G
)
14 4
(G
)
14 5
(G
)
14 6
(G
)
14 7
(G
)
14 8
(G
)
14 9
(G
)
15 0
(G
)
13 7
(
G
)
13 8
(G
)
13 9
(G
)
14 0
(G
)
14 1
(G
)
14 2
(G
)
14 3
(G
)
11 5
(G
)
11 4
(G
)
11 3
(G
)
11 2
(G
)
11 1
(G
)
84 (G
)
83 (G
)
82 (G
)
81 (G
)
64 (G
)
63 (G
)
62 (G
)
61 (G
)
60 59
(
G
)
(G
)
67 (G
)
66 (G
)
65 80
(
G
)
79 (
G
)
86 (
G
)
85 (
G
)
10 1
(
G
)
10 0
(
G
)
99 (
G
)
10 7
(
G
)
10 6
(
G
)
10 5
(
G
)
(G
)
11 0
(G
)
10 9
(G
)
10 8
(G
)
11 9
(G
)
11 8
(G
)
11 7
(G
)
11 6
(G
)
12 3
(G
)
12 4
(G
)
12 5
(G
)
12 6
(G
)
12 7
(G
)
12 8
(G
)
12 9
(G
)
12 2
(G
)
12 1
(G
)
12 0
(G
)
13 0
(G
)
13 1
(G
)
13 2
(G
)
13 3
(G
)
13 4
(G
)
13 5
(G
)
13 6
(G
)
10 4
(G
)
10 3
(G
)
10 2
(G
)
17 5
(G
)
17 6
(G
)
17 7
(
G
)
17 8
(G
)
17 9
(G
)
18 0
(G
)
18 1
(G
)
18 2
(G
)
18 3
(G
)
18 4
(G
)
18 5
(G
)
18 6
(G
)
18 7
18 8
WE
L
L
S
I
T
E
MONTEREY AVENUE
TT
M
N
O
.
37 8
5 6
TT
M
N
O
.
3 8
2 9
1 18
9 19
0 19
1 (D
)
(G
)
15 5
(G
)
15 6
(G
)
15 7
(G
)
15 8
(G
)
15 1
(G
)
15 2
(G
)
15 3
(G
)
15 4
34 2
0 0
B
o
b
H
o
p
e
D
r
i
v
e
,
R
a
n
c
h
o
M
i
r
a
g
e
,
C
A
9 2
2 7
0 76
0 .
3 2
0 .
9 8
1 1
ms
a
c
o
n
s
u
l
t
i
n
g
i
n
c
.
c
o
m
MS
A
CO
N
S
U
L
T
I
N
G
,
I
N
C
.
>
P
L
A
N
N
I
N
G
>
C
I
V
I
L
E
N
G
I
N
E
E
R
I
N
G
>
L
A
N
D
S
U
R
V
E
Y
I
N
G
PH
A
S
E
1 (
T
R
.
3 7
8 5
6 )
/
P
H
A
S
E
1 B
&
1 C
(
T
R
.
3 8
2 9
1 )
:
R
E
S
I
D
E
N
T
I
A
L
L
O
T
T
Y
P
E
S
SE
C
T
I
O
N
3 1
/
C
O
T
I
N
O
AP
R
I
L
1 8
,
2 0
2 2
PH
A
S
E
1 (
T
T
M
N
O
.
3 7
8 5
6 )
-
R
E
S
I
D
E
N
T
I
A
L
L
O
T
T
Y
P
E
S
LO
T
T
Y
P
E
MI
N
I
M
U
M
L
O
T
DI
M
E
N
S
I
O
N
S
TR
A
C
T
M
A
P
NU
M
B
E
R
S
P
E
R
MI
N
.
D
I
M
E
N
S
I
O
N
S
TR
A
C
T
M
A
P
L
O
T
LO
T
S
T
A
N
D
A
R
D
S
SP
E
C
I
F
I
C
P
L
A
N
CO
U
N
T
LO
T
%
LA
R
G
E
L
O
T
(
A
)
13 5
F
T
X
2 0
0 F
T
47 -
6 8
22 7
%
LA
R
G
E
L
O
T
(
B
)
25 -
4 6
&
6 9
-
7 9
33 1
0 %
LA
R
G
E
L
O
T
(
C
)
43 1
3 %
CO
N
V
E
N
T
I
O
N
A
L
L
O
T
(
D
)
11 3
3 4
%
CO
N
V
E
N
T
I
O
N
A
L
L
O
T
(
E
)
68 2
1 %
CO
N
V
E
N
T
I
O
N
A
L
L
O
T
(
F
)
48 1
5 %
21 4
-
2 2
0 1-
2 4
,
8 0
-
8 9
,
1 4
5 ,
1 4
6 &
22 1
-
2 4
3 &
2 7
5 -
2 9
7 90
-
1 4
4 ,
1 4
7 -
1 5
8 ,
27 2
-
2 7
4 &
3 2
1 -
3 2
3 15
9 -
2 1
3 ,
2 4
4 -
2 5
0 ,
31 0
-
3 2
0 &
3 2
4 -
3 2
7 25
1 -
2 7
1 ,
2 9
8 -
3 0
6 ,
PH
A
S
E
1 B
&
1 C
(
T
T
M
N
O
.
3 8
2 9
1 )
-
R
E
S
I
D
E
N
T
I
A
L
L
O
T
T
Y
P
E
S
LO
T
T
Y
P
E
MI
N
I
M
U
M
L
O
T
DI
M
E
N
S
I
O
N
S
TR
A
C
T
M
A
P
NU
M
B
E
R
S
P
E
R
MI
N
.
D
I
M
E
N
S
I
O
N
S
TR
A
C
T
M
A
P
L
O
T
LO
T
S
T
A
N
D
A
R
D
S
SP
E
C
I
F
I
C
P
L
A
N
CO
U
N
T
LO
T
%
CO
N
V
E
N
T
I
O
N
A
L
L
O
T
(
D
)
8 4%
CO
N
V
E
N
T
I
O
N
A
L
L
O
T
(
E
)
29 1
6 %
CO
N
V
E
N
T
I
O
N
A
L
L
O
T
(
F
)
44 2
4 %
CL
U
S
T
E
R
L
O
T
(
G
)
10 6
5 6
%
44 &
4 7
1-
1 8
,
2 3
-
2 5
,
3 1
-
3 5
,
3 8
,
45 ,
4 6
,
4 8
,
4 9
,
5 0
-
5 8
,
19 -
2 2
,
3 6
,
3 7
,
4 0
,
4 2
,
68 -
7 8
&
8 7
-
9 8
26 -
3 0
,
3 9
,
4 1
&
4 3
59 -
6 7
,
7 9
-
8 6
&
9 9
-
1 8
7 TO
T
A
L
-
32 7
1 0
0 %
-
-
N.
T
.
S
.
TO
T
A
L
-
TB
D
T
B
D
-
-TB
D
18 8
-
1 9
1 -
TB
D
T
B
D
TB
D
SU
B
T
O
T
A
L
-
-
-
18 7
1 0
0 %
27 ,
0 0
0 S
F
12 0
F
T
X
1 5
0 F
T
18 ,
0 0
0 S
F
90 F
T
X
1 4
0 F
T
12 ,
6 0
0 S
F
70 F
T
X
1 3
0 F
T
9,
1 0
0 S
F
60 F
T
X
1 2
0 F
T
7,
2 0
0 S
F
50 F
T
X
1 1
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