Cupertino City Council
December 16, 2025

3.4.1.4 EMERGENCY ACCESS
The proposed project will not alter the existing circulation pattern on Stevens Creek Boulevard. The proposed internal roadways will be constructed to 24 to 39 feet wide, consistent with the CMC and Cupertino Fire Department’s requirements, and will provide emergency vehicles with sufficient space to access each of the residential units on-site. Therefore, the proposed project will not result in inadequate emergency access.

3.4.2 Noise
The analysis presented in this section is based in part on the Noise Technical Memorandum prepared for the proposed project and appended as Appendix C, Noise Analysis, to this document.

Pursuant to the CEQA Statute (Public Resources Code) Section 21085, for residential projects, the effects of noise generated by project occupants and their guests on human beings is not a significant effect on the environment. Accordingly, this section evaluates the noise from construction equipment, buildings, and vehicles.

The noise environment in the project vicinity is primarily characterized by vehicular traffic along Stevens Creek Boulevard to the north of the project site. Operations and activities from adjacent commercial, institutional, and residential uses also contribute to the existing noise environment in the project vicinity.

The closest existing noise-sensitive receptors to the project site are the adjacent single-family residences to the south of the project site along Richwood Drive.

3.4.2.1 AMBIENT NOISE LEVELS
Construction Impacts
According to CMC Section 10.48.053, Grading, Construction and Demolition, construction is allowed during “daytime hours” (7:00 a.m. to 8:00 p.m. Monday through Friday, and 9:00 a.m. to 6:00 p.m. on weekends) and exempt from the City’s daytime and nighttime maximum noise level limits, provided that such construction activities do not exceed 80 dBA at the nearest affected property or individual equipment items do not exceed 87 dBA at 25 feet. Only one of these two criteria must be met. In addition, construction is prohibited on holidays and within 750 feet of residential areas on weekends, holidays, and during the nighttime, unless a special exception has been granted, and during nighttime hours unless it meets the nighttime noise level standards. Even with these restrictions, project construction would temporarily increase ambient noise. However, noise levels would subside again after construction is completed. 541
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Noise generated by on-site construction equipment is based on the type of equipment used, its location relative to sensitive receptors, and the timing and duration of noise-generating activities. Each stage of construction involves different kinds of equipment and has distinct noise characteristics. Noise levels from construction activities are typically dominated by the loudest pieces of equipment. The dominant noise source of construction equipment is typically the engine, although work-piece noise (such as dropping of materials) can also be noticeable.

The noise produced at each construction stage is determined by combining the contributions from each piece of equipment used at a given time, while accounting for the on-going time-variations of noise emissions (commonly referred to as the usage factor) to determine the Leq noise levels. Heavy equipment, such as a bulldozer, can have maximum, short-duration noise levels of up to 85 dBA at 50 feet. However, overall noise emissions vary considerably, depending on what specific activity is being performed at any given moment. Noise attenuation due to distance, the number and type of equipment, and the load and power requirements to accomplish tasks at each construction phase would result in different noise levels from construction activities at a given receptor. Since noise from construction equipment is intermittent and diminishes at a rate of at least 6 dBA per doubling of distance (conservatively ignoring other attenuation effects from air absorption, ground effects, and/or shielding/scattering effects), the average noise levels at noise-sensitive receptors could vary considerably, because mobile construction equipment would move around the site with different loads and power requirements. Noise levels from project-related construction activities were calculated from the simultaneous use of all applicable construction equipment at spatially averaged distances (i.e., from the acoustical center of the general construction site or phase) to the property line of the nearest receptors. Although construction may occur across the entire phase area, the center of construction activities best represents the potential construction-related noise levels from multiple pieces of equipment at the various sensitive receptors. This is represented by the center of the entire construction site for activities such as paving, demolition, site preparation, and grading, which are expected to take place across the entire site. Other activities, such as building construction and architectural coating are expected to occur in a focused area of the construction site. Distances for these activities were measured from the nearest sensitive receptor to the nearest phase of potential focused construction activity. The expected construction equipment mix was estimated and categorized by construction activity and the three loudest equipment per activity phase using the Federal Highway Administration Roadway Construction Noise Model (RCNM). The associated, aggregate noise levels, grouped by construction activity, are summarized in Table 3-1, Project-Related Construction Noise, dBA Leq Noise Levels. As shown in Table 3-1, construction noise levels would not exceed 80 dBA Leq at nearby sensitive receptor locations, therefore complying with the City’s construction noise limit.
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TABLE 3-1 PROJECT-RELATED CONSTRUCTION NOISE, DBA LEQ NOISE LEVELS Construction
Activity
Reference Noise
Level
Residential/Daycare
Receptor to the
West
Residential
Receptor to the
South
Residential
Receptor to the
Southwest
Distance 50 feet 250 feet 280 feet 180 feet
Demolition 84 73 69 73
Site Prep 84 73 69 73
Grading 83 72 68 72
Paving 79 67 64 68
Building Construction 79 77 74 77
Architectural Coating 74 72 69 72
Maximum dBA Leq 77 74 77
Exceeds 80 dBA Leq Threshold? No No No
Note: Distances were measured using Google Earth (2025).

Source: Federal Highway Administration’s Roadway Construction Noise Model software.

CMC Chapter 17.04, Standard Environmental Protection Requirements, identifies standard environmental protection requirements that all construction projects must meet. Specifically, the project applicant will be required to comply with CMC Sections 17.04.050(G)(1) and 17.04.050(G)(2) listed here, which will minimize impacts related to construction noise:

CMC Section 17.04.050(G)(1), Notice and Signage. At least 10 days prior to the start of any demolition, ground disturbing, or construction activities, because the project site is between 0.25 to 0.5 acres, the project applicant shall send notices shall be sent to off-site businesses and residents within 250 feet of the project site. The notification shall include a brief description of the project, the activities that would occur, the hours when activity would occur, and the construction period’s overall duration. The notification should include the telephone numbers of the contractor’s authorized representatives that are assigned to respond in the event of a noise or vibration complaint. The project applicant shall provide the City with evidence of mailing of the notice, upon request. Additionally, the at least 10 days prior to the start of construction activities, a sign shall be posted at the entrance(s) to the job site, clearly visible to the public, which includes permitted construction days and hours, as well as the telephone numbers of the City’s and contractor’s authorized representatives that are assigned to respond in the event of a noise or vibration complaint. If the authorized contractor’s representative receives a complaint, they shall investigate, take appropriate corrective action, and report the action to the City within three business days of receiving the complaint.

CMC Section 17.04.050(G)(2), Manage Noise During Construction. a. The project applicant and contractors shall prepare and submit a Construction Noise Control Plan to the City’s Planning Department for review and approval prior to issuance of the first permit. The 543
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Construction Noise Plan shall demonstrate compliance with daytime and nighttime decibel limits pursuant to Chapter 10.48 (Community Noise Control) of Cupertino Municipal Code. The details of the Construction Noise Control Plan shall be included in the applicable construction documents and implemented by the on-site Construction Manager. Noise reduction measures selected and implemented shall be based on the type of construction equipment used on the site, distance of construction activities from sensitive receptor(s), site terrain, and other features on and surrounding the site (e.g., trees, built environment) and may include, but not be limited to, temporary construction noise attenuation walls, high quality mufflers. During the entire active construction period, the Construction Noise Control Plan shall demonstrate that compliance with the specified noise control requirements for construction equipment and tools will reduce construction noise in compliance with the City’s daytime and nighttime decibel limits. b. Select haul routes that avoid the greatest amount of sensitive use areas and submit to the City of Cupertino Public Works Department for approval prior to the start of the construction phase. c. Signs will be posted at the job site entrance(s), within the on-site construction zones, and along queueing lanes (if any) to reinforce the prohibition of unnecessary engine idling. All other equipment will be turned off if not in use for more than 5 minutes. d. During the entire active construction period and to the extent feasible, the use of noise producing signals, including horns, whistles, alarms, and bells will be for safety warning purposes only. The construction manager will use smart back-up alarms, which automatically adjust the alarm level based on the background noise level or switch off back-up alarms and replace with human spotters in compliance with all safety requirements and law.

Pursuant to CMC Section 17.04.050(G)(2), the proposed project would be required to prepare and implement a noise control plan to ensure compliance with daytime and nighttime decibel limits in the CMC.

Therefore, the proposed project will not increase ambient noise levels in the vicinity of the project in excess of standards established in the CMC during the construction phase.

Operational Impact
Stationary-Source Noise
Noise from sources such as people talking and using outdoor common areas or property maintenance may contribute to the total noise environment within the direct vicinity of the proposed project site. However, these types of noise are commonly associated with uses that already exist on the project site and surrounding uses. CMC Section 10.48.040, Daytime and Nighttime Maximum Noise Levels, sets the maximum noise level at the site of a receiving residential property to be 60 dBA during the daytime and 50 dBA during the nighttime and 65 dBA during the daytime and 55 dBA during the nighttime at the site of a receiving nonresidential property. Noise associated with landscape maintenance activities is exempt from 544
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the provisions of the CMC, provided said activities take place between the hours of 7:00 a.m. to 8:00 p.m. on weekdays, and 9:00 a.m. to 6:00 p.m. on weekends and holidays.

The project’s common space area is in the center of the proposed project, approximately 170 feet north of the nearest residence on Richwood Drive. A typical conversation between two people 3 feet apart is 60 dBA.43 At a distance of 170 feet, noise levels would attenuate to approximately 25 dBA. Therefore, noise from typical use of the open space area would result in noise levels less than the CMC Section 10.48.040 nighttime 50 dBA limit for residential uses.

The proposed townhomes are anticipated to have mechanical heating, ventilation, and air conditioning (HVAC) equipment on the ground next to units or on the on the rooftop. The exterior mechanical and HVAC equipment associated with the proposed townhomes are expected to be similar to the existing commercial uses on the site or quieter. Because mechanical specifications for these proposed units are not yet available, it is conservatively assumed that noise from these units would be up to 72 dBA Leq at a distance of 3 feet and that they could be located within approximately 45 feet from the nearest residential property lines to the west. At this distance, the sound pressure level associated with a common HVAC unit would be approximately 48 dBA at the nearest noise sensitive receptor. Therefore, the noise level associated with HVAC in the backyards of the future residential units would not exceed the CMC Section 10.48.040 standards, which limit nighttime noise to 50 dBA at nearby residential uses.

Traffic Noise
The proposed project would generate an increase of 100 net new trips per day with 15 new AM peak hour trips compared to existing daily trips attributed to the existing shopping center at the project site. A project will normally have a significant effect on the environment related to traffic noise if it substantially increases the ambient noise levels for adjoining areas. Most people can detect changes in sound levels of approximately 3 dBA under normal, quiet conditions, and changes of 1 to 3 dBA under quiet, controlled conditions. Changes of less than 1 dBA are usually indiscernible. A change of 5 dBA is readily discernible to most people in an outdoor environment. Noise levels above 65 dBA CNEL are normally unacceptable at sensitive receptor locations such as residences, schools, and noise environments in these areas would be considered degraded. Based on this, a significant impact would occur if traffic noise increases by 3 dBA.

Traffic noise increases were calculated using a version of the Federal Highway Administration RD-77-108 Traffic Noise Prediction Model. The traffic noise prediction model takes into account the following inputs:
average daily traffic volumes; vehicle mix; speeds; number of lanes; and day, evening, and night traffic splits.

Existing traffic noise estimates are based on the City of Cupertino’s baseline roadway volumes modeled for 43 Engineering ToolBox, 2005, Voice Level at Distance, https://www.engineeringtoolbox.com/voice-level-d_938.html, accessed June 6, 2025.
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the General Plan 2040 and Zoning Code Amendments Environmental Assessment in April 2024. 44 Project
trips were provided by Hexagon Transportation Consultants Inc.45 Traffic noise modeling does not account for existing masonry walls at adjacent residential property lines. Table 3-2, Project-Related Increases in Traffic Noise, dBA CNEL at 50 Feet, shows that the addition of proposed project trips would result in an increase of less than 1 dBA over existing conditions. Therefore, project traffic would not result in a significant noise impact.

TABLE 3-2 PROJECT-RELATED INCREASES IN TRAFFIC NOISE, DBA CNEL AT 50 FEET Roadway
Segment Traffic Noise Increase
From To
Existing
No Project
Existing with
Proposed Project Difference
Stevens Creek Boulevard Tantau Avenue Portal Avenue 70 70 <1 Wolfe Road I-280 Overpass Stevens Creek Boulevard 72 72 <1 Miller Avenue
Stevens Creek
Boulevard Mitty Way 69 69 <1
Sources: Hexagon Transportation Consultants, Inc., September 24, 2025, Transportation Analysis for the Proposed Residential Development at 10065- 10075 East Estates Drive in Cupertino, CA (see Appendix B, Transportation Analysis, of this document); City of Cupertino, April 2024, General Plan 2040 and Zoning Code Amendments Environmental Assessment, Table 4.11-6, Baseline Roadway Noise Levels, https://www.cupertino.gov/files/assets/city/v/2/departments/documents/community-development/planning/general-plan/current-gpdocuments/cupgp_appendix_g_2024update_9-30-2024_reduced_size.pdf.

3.4.2.2 GROUNDBORNE VIBRATION
Potential vibration impacts associated with construction projects are usually related to the use of heavy construction equipment during the demolition phase of construction. Construction can generate varying degrees of ground vibration depending on the construction procedures and equipment. Construction equipment generates vibration that spreads through the ground and diminishes with distance from the source. The effect on buildings in the vicinity of the construction site varies depending on soil type, ground strata, and receptor-building construction. The effects from vibration can range from no perceptible effects at the lowest vibration levels, to low rumbling sounds and perceptible vibrations at moderate levels, to slight structural damage at the highest levels. Vibration from construction activities rarely reaches the levels that can damage structures. Table 3-3, Vibration Levels at Nearby Structures, summarizes vibration levels for typical construction equipment at the nearest structures to the project site. As noted in Table 3-3, the vibratory roller, which would be used during paving activities on project streets, would produce the highest levels of vibration. Therefore, the distances shown in Table 3-3 reflect the distance from the nearest off-site buildings to the nearest paved street area shown on the proposed site plan. 44 City of Cupertino, April 2024, General Plan 2040 and Zoning Code Amendments Environmental Assessment, Table 4.11-6, Baseline Roadway Noise Levels, https://www.cupertino.gov/files/assets/city/v/2/departments/documents/communitydevelopment/planning/general-plan/current-gp-documents/cupgp_appendix_g_2024update_9-30-2024_reduced_size.pdf. 45 Hexagon Transportation Consultants, Inc., September 24, 2025, Transportation Analysis for the Proposed Residential Development at 10065-10075 East Estates Drive in Cupertino, CA (see Appendix B, Transportation Analysis, of this document). 546
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TABLE 3-3 VIBRATION LEVELS AT NEARBY STRUCTURES
Equipment
Inches/Second Peak Particle Velocity
Residential/Daycare Receptor
to the West (80 Feet)
Residential Receptor to the
South (130 Feet)
Commercial Uses to the
West (145 Feet)
Vibratory Roller 0.037 0.018 0.015
Hoe Ram 0.016 0.008 0.006
Large Bulldozer 0.016 0.008 0.006
Caisson Drilling 0.016 0.008 0.006
Loaded Trucks 0.013 0.006 0.005
Small Bulldozer 0.006 0.003 0.003
Jackhammer 0.001 0.000 0.000
Note: As measured from the center of the nearest street on the project site to the nearest off-site building.

Source: Federal Transit Administration, September 2018, Transit Noise and Vibration Impact Assessment Manual, https://www.transit.dot.gov/sites/fta.dot.gov/files/docs/research-innovation/118131/transit-noise-and-vibration-impact-assessment-manual-ftareport-no-0123_0.pdf.

The nearest structure to the site’s construction activities, the residential/daycare building to the southwest, is approximately 80 feet from the nearest proposed project construction activities. At this distance, construction vibration would attenuate to 0.037 inches per second peak particle velocity (in/sec PPV) or less. Vibration levels at the other nearby residence 130 feet south of the project site and the commercial uses to the west would also attenuate to 0.018 in/sec PPV or less. Therefore, proposed construction activities would not exceed the City’s vibration standard of 0.2 in/sec PPV or 0.12 in/sec PPV (for historic structures) at nearby off-site structures.

CMC Chapter 17.04, Standard Environmental Protection Requirements, identifies standard environmental protection requirements that all construction projects must meet. Specifically, the project applicant will be required to comply with CMC Section 17.04.050(G)(3), which will minimize impacts related to construction vibration:

CMC Section 17.04.050(G)(3), Manage Vibrations During Construction. In the event pile driving is required, the project applicant shall:
a. Notify all vibration-sensitive receptors within 300 feet of the project site of the schedule 10 days prior to its commencement and include the contact information for the person responsible for responding to complaints on site.
b. The project applicant shall retain a qualified acoustical consultant or structural engineer, to prepare and implement a Construction Vibration Monitoring Plan, which is subject to third-party peer review under the direction of the City at the applicant’s cost, for areas within 100 feet for pile driving, 25 feet for vibratory roller, or 15 feet for other heavy equipment (e.g., bulldozer); and for historical structures: within 135 feet for pile driving, 40 feet for vibratory roller, or 20 feet for other 547
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heavy equipment. The plan shall include surveying the condition of existing structures; and determining the number, type, and location of vibration sensors and establish a vibration velocity limit (as determined based on a detailed review of the proposed building), method (including locations and instrumentation) for monitoring vibrations during construction, location of notices displaying the contact information for on-site coordination and complaints on site, and method for alerting responsible persons who have the authority to halt construction should limits be exceeded or damaged observed.
c. Submit final monitoring reports to the City upon completion of vibration related construction activities.
d. Conduct a post-survey on any structure where either monitoring has indicated high vibration levels or complaints that damage has occurred are received.
e. The project applicant shall be responsible for appropriate repairs as determined by the qualified acoustical consultant or structural engineer where damage has occurred as a result of construction activities.

Should the proposed project require the use of the construction equipment listed in CMC Section

17.04.050(G)(3)(b) within the specified distances to receptors, it will be required to prepare a Construction and Vibration Monitoring Plan by a qualified acoustical consultant to ensure that no damage due to vibration from construction equipment would occur. Therefore, the proposed project will not result in an increase in excessive ground-borne vibration.

3.4.2.3 AIRPORT NOISE
Because the project site is not within two miles of a private or public use airport, which is the standard for assessing noise impacts under CEQA, the proposed project will not result in the exposure of people residing or working in the project area to excessive noise levels associated with the proximity of an airport.

3.4.3 Air Quality
The analysis presented in this section is based in part on the Air Quality Technical Memorandum and Health Risk Assessment prepared for the proposed project and appended as Appendix D, Air Quality Analysis, to this document.

The analysis of the proposed project’s air quality impacts follows the guidance and methodologies recommended in the Bay Area Air District (Air District)46 2022 CEQA Air Quality Guidelines. CEQA allows the significance criteria established by the applicable air quality management or air pollution control district to be used to assess impacts of a project on air quality. The guidelines provide recommended procedures for 46 Formerly known as the Bay Area Air Quality Management District (BAAQMD) 548
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evaluating potential air impacts during the environmental review process, consistent with CEQA requirements, and include recommended thresholds of significance, mitigation measures, and background air quality information.

Attainment Status of the Air Basin
The proposed project is in the San Francisco Bay Area Air Basin (Air Basin) under the jurisdiction of the Air District, which regulates air quality in the San Francisco Bay Area. Within the Air Basin, ambient air quality standards for ozone, carbon monoxide (CO), nitrogen dioxide (NO2), sulfur dioxide (SO2), particulate matter (PM10, PM2.5), and lead (Pb) have been set by both the State of California and the federal government. The State has also set standards for sulfate and visibility. The Air Basin is under State nonattainment status for ozone and particulate matter (both PM10 and PM2.5) standards. The Air Basin is classified as nonattainment for the federal ozone 8-hour standard and nonattainment for the federal 24-hour standard for PM2.5. 47 Air Quality Plans
The Air District is directly responsible for reducing emissions from area, stationary, and mobile sources in the Air Basin to achieve national and California Ambient Air Quality Standards (AAQS). The Air District’s 2017 Clean Air Plan is a regional and multiagency effort to reduce air pollution in the Air Basin. 48 A consistency
determination with the air quality management plan plays an important role in local agency project review by linking local planning and individual projects to the 2017 Clean Air Plan. It fulfills the CEQA goal of informing decision makers of the environmental efforts of the project under consideration early enough to ensure that air quality concerns are fully addressed. It also provides the local agency with ongoing information as to whether they are contributing to the clean air goals in the 2017 Clean Air Plan.

Regional Significance Thresholds
As described previously, the Air Basin is currently designated a nonattainment area for California and National O3, California and National PM2.5, and California PM10 air quality standards. Any project that produces a significant project-level regional air quality impact in an area that is in nonattainment adds to the cumulative impact. Due to the extent of the area potentially impacted by cumulative-plus-project emissions (the Air Basin), a project is cumulatively significant when project-related emissions exceed the Air District’s emissions thresholds.
47 Bay Area Air District, 2025, Air Quality Standards and Attainment Status, https://www.baaqmd.gov/about-airquality/research-and-data/air-quality-standards-and-attainment-status, accessed February 12, 2025. 48 Bay Area Air District. April 19, 2017, Final 2017 Clean Air Plan, https://www.baaqmd.gov/~/media/files/planning-andresearch/plans/2017-clean-air-plan/attachment-a_-proposed-final-cap-vol-1-pdf.pdf. 549
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The Air District has identified thresholds of significance for criteria pollutant emissions and criteria air pollutant precursors, including reactive organic gas (ROG), NOX, PM10, and PM2.5. Development projects below the significance thresholds would not generate sufficient criteria pollutant emissions to violate any air quality standard or contribute substantially to an existing or projected air quality violation.

CO Hotspots
Congested intersections have the potential to create elevated concentrations of CO, referred to as CO hotspots. The significance criteria for CO hotspots are based on the California AAQS for CO, which are 9.0 ppm (8-hour average) and 20.0 ppm (1-hour average). With the turnover of older vehicles, introduction of cleaner fuels, and implementation of control technology, the SFBAAB is in attainment of the California and national AAQS, and CO concentrations in the SFBAAB have steadily declined. Because CO concentrations have improved, the Air District does not require a CO hotspot analysis if the following criteria are met:
 The project is consistent with an applicable congestion management program established by the County Congestion Management Agency for designated roads or highways, the regional transportation plan, and local congestion management agency plans.
 The project would not increase traffic volumes at affected intersections to more than 44,000 vehicles per hour.
 The project traffic would not increase traffic volumes at affected intersection to more than 24,000 vehicles per hour where vertical and/or horizontal mixing is substantially limited (e.g., tunnel, parking garage, bridge underpass, natural or urban street canyon, below-grade roadway).

Health Risk
The Air District’s significance thresholds for local community risk and hazard impacts apply to both the siting of a new source and to the siting of a new receptor. Local community risk and hazard impacts are associated with TACs and PM2.5 because emissions of these pollutants can have significant health impacts at the local level. The proposed project would generate TACs and PM2.5 during construction activities that could elevate concentrations of air pollutants at the nearby receptors. The thresholds for construction-related local community risk and hazard impacts are the same as for project operations. The Air District has adopted screening tables for air toxics evaluation during construction. Construction-related TAC and PM2.5 impacts are addressed on a case-by-case basis, taking into consideration the specific construction-related characteristics of each project and proximity to off-site and on-site receptors, as applicable.

Project-level emissions of TACs or PM2.5 from individual sources that exceed any of the thresholds listed below are considered a potentially significant community health risk in the absence of a qualified community risk reduction plan:
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 An excess (i.e., increased) cancer risk level of more than 10 in one million  Noncancer (i.e., chronic or acute) hazard index greater than 1.0  An incremental increase of greater than 0.3 micrograms per cubic meter (µg/m3 ) annual average PM2.5
Cumulative sources represent the combined total risk values of each of the individual sources within the 1,000-foot evaluation zone. A project would have a cumulatively considerable impact if the aggregate total of all past, present, and foreseeable future sources within a 1,000-foot radius from the fence line of a source or location of a receptor, plus the contribution from the project, exceeds any of the following in the absence of a qualified community risk reduction plan:
 An excess cancer risk level of more than 100 in one million (from all sources)  Chronic noncancer hazard index (from all local sources) greater than 10.0  0.8 µg/m3 annual average PM2.5 (from all local sources)

3.4.3.2 CONSISTENCY WITH APPLICABLE AIR QUALITY PLANS
The regional emissions inventory for the Air Basin is compiled by the Air District. Regional population, housing, and employment projections developed by the Association of Bay Area Governments (ABAG) are based, in part, on cities’ general plan land use designations. These projections form the foundation for the emissions inventory of the 2017 Clean Air Plan. These demographic trends are incorporated into Plan Bay Area 2050, compiled by ABAG and the Metropolitan Transportation Commission (MTC) to determine priority transportation projects and vehicle miles traveled in the Bay Area. The 2017 Clean Air Plan strategy is based on projections from local general plans. Projects that are consistent with the local general plan are considered consistent with the air quality-related regional plan. Large projects that exceed regional employment, population, and housing planning projections have the potential to be inconsistent with the regional inventory compiled as part of the 2017 Clean Air Plan.

The proposed residential uses would be consistent with the Commercial/Residential land use designation of the General Plan. Additionally, under CEQA Guidelines Section 15206,49 the proposed project is not considered a regionally significant project that would affect regional vehicle miles traveled and warrant intergovernmental review by ABAG and MTC. Additionally, the proposed project would serve the existing community and not induce substantial unplanned population growth. Lastly, as shown in Table 3-5, the proposed project would not generate operational emissions that would exceed the Air District’s emissions thresholds. These thresholds are established to identify projects that have the potential to generate a substantial amount of criteria air pollutants. Because the proposed project would not exceed these thresholds, the proposed project would not be considered by the Air District to be a substantial emitter of 49 Pursuant to CEQA Guidelines Section 15206(b)(2)(A), a proposed residential development of more than 500 dwelling units would be considered a project of statewide, regional, or areawide significance. 551
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criteria air pollutants. Therefore, the proposed project would not conflict with or obstruct implementation of the 2017 Clean Air Plan.

3.4.3.3 CUMULATIVELY CONSIDERABLE NET INCREASE CRITERIA POLLUTANT Construction Impacts
Construction activities produce combustion emissions from various sources, such as on-site heavy-duty construction vehicles, vehicles hauling materials to and from the site, and motor vehicles transporting the construction crew. Site preparation activities produce course fugitive dust (PM10) and fine fugitive dust (PM2.5) from demolition and soil-disturbing activities, such as grading and excavation. Air pollutant emissions from construction activities on-site will vary daily as construction activity levels change.

Construction activities associated with the proposed project will result in emissions of ROG, NOX, PM10, and PM2.5.

CMC Chapter 17.04, Standard Environmental Protection Requirements, identifies standard environmental protection requirements that all construction projects must meet. Specifically, the project applicant will be required to comply with CMC Sections 17.04.050(A)(1), 17.04.050(A)(3), and 17.04.050(A)(4) as listed here, which will minimize impacts from construction:

CMC Section 17.04.050(A)(1), Control Fugitive Dust During Construction. Projects shall implement the Bay Area Air Quality Management District Basic Control Measures included in the latest version of BAAQMD’s CEQA Air Quality Guidelines, as subsequently revised, supplemented, or replaced, to control fugitive dust (i.e., particulate matter, PM2.5 and PM10) during demolition, ground-disturbing activities, and/or construction. The project applicant shall include these measures in the applicable construction documents, prior to issuance of the first permit.

CMC Section 17.04.050(A)(3), Control Construction Exhaust. Projects that disturb more than one-acre and are more than two months in duration, shall implement the following measures and the project applicant shall include them in the applicable construction document, prior to issuance of the first permit:
a. Utilize off-road diesel-powered construction equipment that is rated by the U.S. Environmental Protection Agency (EPA) as Tier 4 or higher for equipment more than 25 horsepower. Any emissions control device used by the contractor shall achieve emissions reductions that are no less than what could be achieved by a Tier 4 interim emissions standard for a similarly sized engine, as defined by the California Air Resources Board’s (CARB) regulations. Applicable construction documents shall clearly show the selected emission reduction strategy for construction equipment over 25 horsepower.
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b. Ensure that the construction contractor shall maintain a list of all operating equipment in use on the project site for verification by the City. The construction equipment list shall state the makes, models, and number of construction equipment on-site.
c. Ensure that all equipment shall be properly serviced and maintained in accordance with the manufacturer’s recommendations.

CMC Section 17.04.050(A)(4), Control Volatile Organic Compound Emissions from Paint. Project shall use low VOC-paint (i.e., 50 grams per [g/l] or less) for interior and exterior wall architectural coatings.

The project applicant shall include the use of low-VOC paint in the applicable construction documents prior to issuance of the first permit.

In reference to CMC Section 17.04.050(A)(1), the Air District considers all impacts related to fugitive dust emissions from construction to be less than significant with implementation of the Air District’s best management practices. The current best management practices that are required to be implemented by the project applicant are listed herein:
 All exposed surfaces (e.g., parking areas, staging areas, soil piles, graded areas, and unpaved access roads) shall be watered two times per day.
 All haul trucks transporting soil, sand, or other loose material off-site shall be covered.  All visible mud or dirt tracked-out onto adjacent public roads shall be removed using wet power vacuum street sweepers at least once per day. The use of dry power sweeping is prohibited.  All vehicle speeds on unpaved roads shall be limited to 15 miles per hour.  All roadways, driveways, and sidewalks to be paved shall be completed as soon as possible.  Building pads shall be laid as soon as possible after grading unless seeding or soil binders are used.  Idling times shall be minimized either by shutting equipment off when not in use or reducing the maximum idling time to five minutes (as required by the California airborne toxics control measure Title 13, Section 2485 of California Code of Regulations). Clear signage shall be provided for construction workers at all access points.
 All construction equipment shall be maintained and properly tuned in accordance with the manufacturer’s specifications. All equipment shall be checked by a certified mechanic and determined to be running in proper condition prior to operation.
 A publicly visible sign shall be posted with the telephone number and person to contact at the City of Cupertino regarding dust complaints. This person shall respond and take corrective action within 48 hours. The phone number shall also be visible to ensure compliance with applicable regulations. 553
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Construction is anticipated to occur from Summer 2026 to 2028. For the purposes of this analysis, a 21- month construction schedule was utilized, with construction starting in August 2026 and lasting until May 2028. Based on information provided by the applicant, construction activities are expected to occur 11 hours a day Monday through Friday and 9 hours a day on Saturdays.

Construction emissions were estimated using CalEEMod version 2022.1. Table 3-4, Construction Criteria Air Pollutant Emissions, shows the average daily construction emissions of ROG, NOX, PM10 exhaust, and PM2.5 exhaust during construction of the proposed project. As indicated in Table 3-4, average project construction emissions will not exceed the Air District’s significance thresholds. Therefore, the proposed project will not result in a cumulatively considerable net increase of criteria air pollutants during the construction phase.

TABLE 3-4 CONSTRUCTION CRITERIA AIR POLLUTANT EMISSIONS

ROG NOX
Exhaust
PM10
Fugitive
PM10
Exhaust
PM2.5
Fugitive
PM2.5
Criteria Air Pollutants (tons/year)
2026 <1 <1 <1 <1 <1 <1
2027 <1 1 <1 <1 <1 <1
2028 <1 <1 <1 <1 <1 <1
Total <1 1 <1 1 <1 <1
Criteria Air Pollutants (average lbs/day)
a
Average Daily Emissions 2 5 <1 2 <1 <1
Air District Average Daily
Threshold 54 54 BMPs 82 BMPs 54
Exceeds Threshold? No No No No No No
Notes: Modeling assumes compliance with Cupertino Municipal Code (CMC) Sections 17.04.050(A)(1), 17.04.050(A)(3), and 17.04.050(A)(4). Specific to CMC Section 17.04.050(A)(3), modeling for the proposed project assumes that all equipment over 25 horsepower used during construction activities will meet Tier 4 Interim standards as a conservative analysis. a. Average daily emissions are based on the total construction emissions divided by the total number of active construction days. The total number of construction days is estimated to be about 548 days.

Source: CalEEMod Version 2022.1, Air District, 2023 (see Appendix D, Air Quality Analysis, of this document) Operational Impacts
Typical long-term air pollutant emissions are generated by area sources (e.g., landscape fuel use, aerosols, architectural coatings, and asphalt pavement), energy use (natural gas), and mobile sources (i.e., on-road vehicles). Types of land uses that typically generate substantial quantities of criteria air pollutants and toxic air contaminants include industrial (stationary sources), manufacturing, and warehousing (truck idling) land uses. These types of major air pollutant emissions sources are not included as part of the proposed project.

As described in Section 2.4.4, Utilities and Public Service Providers, the proposed project will be designed as 100 percent electric, which will also be a condition of approval, and will not include stationary sources that emit toxic air contaminants or generate a significant amount of heavy-duty truck trips (a source of diesel particulate matter).
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Table 3-5, Operational Criteria Air Pollutant Emissions, shows average daily emissions of ROG, NOX, total PM10, and total PM2.5 during operation of the project. As indicated in Table 3-5, operational emissions will not exceed the Air District’s significance thresholds. Therefore, the proposed project will not result in cumulatively considerable net increase of criteria air pollutants during operation.

TABLE 3-5 OPERATIONAL CRITERIA AIR POLLUTANT EMISSIONS
ROG NOX PM10 Exhaust PM2.5 Exhaust
Criteria Air Pollutants (tons/year)
Total 1 <1 <1 <1
Air District Thresholds (tons/year) 10 10 15 10
Exceeds Threshold? No No No No
Criteria Air Pollutants (average lbs/day)a
Area 3 <1 <1 <1
Energy <1 <1 <1 <1
On Road Mobile <1 <1 <1 <1
Total 4 <1 <1 <1
Air District Thresholds (pounds/day) 54 54 82 54
Exceeds Threshold? No No No No
Note: Emissions may not total to 100 percent due to rounding. a. Average daily emissions are based on the annual operational emissions divided by 365 days.

Source: See Appendix D, Air Quality Analysis, of this document.

Carbon Monoxide Hotspots
Areas of vehicle congestion have the potential to create pockets of CO, called hotspots. These pockets have the potential to exceed the State’s 1-hour standard of 20 parts per million (ppm) or the 8-hour standard of 9 ppm.

Under existing and future vehicle emission rates, a project would have to increase traffic volumes at a single intersection by more than 44,000 vehicles per hour—or 24,000 vehicles per hour where vertical and/or horizontal mixing is substantially limited—to generate a significant CO impact. The proposed project will result in 100 net new daily vehicle trips (15 AM peak hour trips).50 Thus, the proposed project will not increase traffic volumes at affected intersections by more than 44,000 vehicles per hour or 24,000 vehicles per hour where vertical and/or horizontal mixing is substantially limited.51 The proposed project will not have the potential to substantially increase CO hotspots at intersections in the project vicinity. Therefore, the proposed project will not increase CO concentration at intersections. 50 Hexagon Transportation Consultants, Inc., September 24, 2025, Transportation Analysis for the Proposed Residential Development at 10065-10075 East Estates Drive in Cupertino, CA (see Appendix B, Transportation Analysis, of this document). 51 Bay Area Air District, 2022, California Environmental Quality Act Air Quality Guidelines. 555
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3.4.3.4 SENSITIVE RECEPTORS
Project impacts related to increased health risk can occur by generating emissions of TACs and air pollutants.

Construction activity under the proposed project will generate dust and equipment exhaust that can affect nearby sensitive receptors. The proposed project will include a stationary source of air pollutants and TACs in the form of an emergency generator and will also generate some traffic consisting of mostly light-duty gasoline-powered vehicles, which will produce TAC and air pollutant emissions.

The closest existing sensitive receptors to the project site are at the adjacent single-family residences and daycare to the south and southwest, respectively. The nearest school receptor is a private academy (Fusion Academy Cupertino) located in the shopping mall adjacent to the project site, approximately 450 feet to the west.

Health risk impacts were addressed by predicting increased cancer risk, the increase in annual PM2.5 concentrations, and by computing the Hazard Index for noncancer health risks. The project’s maximally exposed receptor (MER) is identified as the sensitive receptor that is most impacted by the project’s construction and operation. The cancer risk MER is at the residence/daycare southwest of the project site and the annual PM2.5 MER is at the shopping center approximately 80 feet west of the project site.

Table 3-6, Construction Risk Summary, summarizes the maximum cancer risks, PM2.5 concentrations, and health Hazard Index for construction-related activities. As shown in Table 3-6, for non-carcinogenic effects, the chronic hazard index identified for each toxicological endpoint equaled less than one for each identified receptor, which is within acceptable limits. Cancer risk for the worker, daycare, and K-12 student receptors were each calculated to be less than 1 in one million, which would not exceed the 10 in one million significance threshold. However, with the use of Tier 4 Interim equipment, cancer risk for the residential MER from project-related construction emissions was calculated to be approximately 18 in one million, which would exceed the 10 in one million significance threshold. Similarly, with the use of Tier 4 Interim equipment, the annual average PM2.5 concentration at the worker MER would reach 0.303 µg/m3 , which
would exceed the Air District’s significance threshold of 0.3 µg/m3 . However, as discussed in Section 2.4.5,
Demolition, Grading, and Construction, in compliance with CMC Section 17.04.050(A)(3), the project applicant has voluntarily committed to the use of Tier 4 Final equipment, which will also be a condition of approval. With the use of Tier 4 Final equipment, cancer risk for the residential MER from project-related construction emissions would be 6.45 in one million, under the Air District’s significance threshold. Similarly, the annual average PM2.5 concentration at the worker MER would reach 0.27 µg/m3 , which is also under
the Air District’s significance threshold.
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TABLE 3-6 CONSTRUCTION RISK SUMMARY

Cancer Risk
(per million) Chronic Hazards PM2.5 (μg/m3)
Use of Tier 4 Interim Equipment
MER – K-12 Student1 <1 <0.1 0.02
MER – Daycare 7.98 <0.1 0.12
MER – Resident 17.96 <0.1 0.28
MER – Worker <1 <0.1 0.303
Air District Threshold 10 1.0 0.30
Exceeds Threshold? Yes No Yes
Use of Tier 4 Final Equipment
MER – Resident 6.45 <0.1 0.25
MER – Worker <1 <0.1 0.27
Air District Threshold 10 1.0 0.30
Exceeds Threshold? No No No
Note: Cancer risk calculated using 2015 California Office of Environmental Health Hazard Assessment’s Health Risk Assessment Guidance Manual.

1. While risks were calculated for each type of student receptor separately (including preschool, elementary school, middle school, and high school), these results report the highest risk among all student receptor types, the middle school student receptors at Fusion Academy Cupertino.

In addition to a project-level health risk assessment, the Air District recommends assessing the potential cumulative impacts from sources of TACs within 1,000 feet of a project. The existing TACs that the Air District recommends a cumulative analysis include permitted stationary sources, marine sources, roadway sources, rail sources, and highway sources. Risks from permitted stationary sources within 1,000 feet of the project site can be identified using the Air District’s Stationary Source Screening Map.52 The residential MER was utilized in the cumulative community risk assessment as it represents the greatest impact to nearby receptors during project construction. No marine or rail risks are shown in the cumulative health risk assessment as no marine or rail activities occur within 1,000 feet of the project site.

Table 3-7, Cumulative Community Risk Summary, summarizes the existing TAC source risks at the residential MER from mitigated project construction emissions in combination with existing TAC sources within 1,000 feet of the project site. As shown therein, the proposed project’s construction emissions with Tier 4 Final equipment combined with existing TAC emissions within 1,000 feet do not exceed the Air District’s cumulative community health risk significance thresholds at the residential MER location. 52 Bay Area Air District, updated August 1, 2024, Stationary Source Screening Map, https://baaqmd.maps.arcgis.com/apps/webappviewer/index.html?id=845658c19eae4594b9f4b805fb9d89a3. 557
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TABLE 3-7 CUMULATIVE COMMUNITY RISK SUMMARY
Source Source Type
Distance
to MER1
Cancer Risk
(per million)
Chronic
Hazards
PM2.5
(µg/m3)

Project Impacts
Project Construction2 Diesel Construction
Equipment - 6.45 <0.1 0.25
Permitted Stationary Source Impacts
Boyett Petroleum Boyett Site #18
(Facility ID 112405-1)
Gas Dispensing
Facility
158 2.08 0.01 0.00
Roadway & Highway Impacts
Air District-Provided Roadway Values3 Vehicles - 11.70 <0.1 0.41 Cumulative Health Impacts
Cumulative Project Health Impacts 20.23 <0.1 0.66
Air District Threshold 100 10.0 0.80
Exceeds Threshold? No No No
Notes: MER = Maximally Exposed Receptor

1. Values expressed in feet. Residential MER is a residence adjacent to the southwestern project boundary.

2. Includes use of Tier 4 Final equipment.

3. Air District-provided values correspond with risks experienced at the residential MER.

3.4.3.5 ODORS
Construction activities could also generate odors from construction equipment, such as diesel exhaust, and VOCs from architectural coatings and paving activities. However, these odors will be temporary and limited to the construction period. By the time such emissions reach any sensitive receptor sites, they would be diluted well below any level of air quality concern.

The type of facilities that are typically considered to have objectionable odors include wastewater treatments plants, compost facilities, landfills, solid waste transfer stations, fiberglass manufacturing facilities, paint/coating operations (e.g., auto body shops), dairy farms, petroleum refineries, asphalt batch plants, chemical manufacturing, and food manufacturing facilities.53 The proposed project consists of residential development, which is not considered a type of land use typically associated in generating objectionable odors that would affect a substantial number of people. Therefore, the proposed project will not create objectionable odors affecting a substantial number of people. 53 Bay Area Air District, 2022. California Environmental Quality Act Air Quality Guidelines. 558
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3.4.3.6 GREENHOUSE GAS EMISSIONS
A project does not generate enough greenhouse gas (GHG) emissions on its own to influence global climate change; therefore, this section measures the proposed project contribution to the cumulative environmental impact associated with GHG emissions. Development of the proposed project will contribute to climate change through direct and indirect GHG emissions from the construction activities needed to implement the proposed project, which will generate a short-term increase in GHG emissions.

Construction Impacts
The Air District does not have thresholds of significance for construction-related GHG emissions, which are one-time, short-term emissions and therefore will not significantly contribute to the long-term cumulative GHG emissions impacts of the proposed project. Implementation of the Air District’s basic construction best management practices required pursuant to CMC Section 17.04.050(A)(1) will reduce GHG emissions by reducing the amount of construction vehicle idling and by requiring the use of properly maintained equipment. Therefore, project construction impacts associated with GHG emissions will be reduced to the extent feasible, as required by the Air District.

Operational Impacts
The proposed project will generate a net increase of 209 daily weekday trips compared to existing on-site land uses. Because transportation emissions will generate the majority of GHG emissions associated with the proposed project, this net increase in daily trips will not substantially increase GHG emissions in the city.

Additionally, the new buildings will be more energy efficient than the existing structures and will be built to achieve the latest Title 24 Building and Energy-Efficiency Standards.

The Air District has the following thresholds for land use projects in analyzing GHG emissions impacts; projects must include conditions listed under either Criterion A or B:

A. Projects must include, at a minimum, the follow project design elements:

1. Buildings
a. The project will not include natural gas appliances or natural gas plumbing (in both residential and nonresidential development).
b. The project will not result in any wasteful, inefficient, or unnecessary energy usage as determined by the analysis required under CEQA Section 21100(b)(3) and Section 15126.2(b) of the State CEQA Guidelines.

2. Transportation
a. Achieve a reduction in project-generated vehicle miles traveled (VMT) below the regional average consistent with the current version of the California Climate Change Scoping Plan (currently 15 percent) or meet a locally adopted Senate Bill 743 VMT target, reflecting the 559
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recommendations provided in the Governor’s Office of Land Use and Climate Innovation's Technical Advisory on Evaluating Transportation Impacts in CEQA:
i. Residential projects: 15 percent below the existing VMT per capita ii. Office projects: 15 percent below the existing VMT per employee iii. Retail projects: no net increase in existing VMT
b. Achieve compliance with off-street electric vehicle requirements in the most recently adopted version of CALGreen Tier 2.

B. Projects must be consistent with a local GHG reduction strategy that meets the criteria under State CEQA Guidelines Section 15183.5(b).

As described herein, the proposed project will meet the conditions listed under Criterion B, for being consistent with a locally adopted GHG reduction strategy. In addition, it will not include natural gas appliances or plumbing, or result in any wasteful, inefficient, or unnecessary energy usage, as previously explained. Other applicable plans adopted for the purpose of reducing GHG emissions include the California Air Resources Board’s (CARB) Climate Change Scoping Plan (Scoping Plan) and Plan Bay Area 2050. A consistency analysis with these plans is also presented herein.

Cupertino Climate Action Plan
The Cupertino Climate Action Plan 2.0 (CAP 2.0) is a strategic planning document that identifies sources of GHG emissions in the city’s boundaries, presents current and future emissions estimates, identifies a GHG reduction target for future years, and presents strategic goals, measures, and actions to reduce emissions from the energy, transportation, land use, water, solid waste, and green infrastructure sectors.

A specific project proposal is considered consistent with the Cupertino CAP 2.0 if it does not conflict with the required GHG reduction measures contained in the adopted CAP. Project consistency with the adopted GHG reduction measures is shown in Table 3-8, Cupertino Climate Action Plan Consistency Matrix.

TABLE 3-8 CUPERTINO CLIMATE ACTION PLAN CONSISTENCY MATRIX Measure Consistency
Measure BE-1 Reduce non-SVCE usage rate to 2
percent for residential and 10 percent for commercial
by 2030 and maintain through 2040.

Consistent. As described in Chapter 2, Project Description, the proposed project will comply with the current California Building and Energy Efficiency Standards to reduce energy consumptions.

Measure BE-4 Require new residential and commercial
development to be all-electric at time of construction.

Consistent. As described in Chapter 2, Project Description, the proposed project will be fully electric.
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TABLE 3-8 CUPERTINO CLIMATE ACTION PLAN CONSISTENCY MATRIX Measure Consistency
Measure TR-1 Develop and implement an Active
Transportation Plan to achieve 15 percent of active
transportation mode share by 2030 and 23 percent by
2040.

Consistent. The City is the responsible party for this measure. As described in Chapter 2, Project Description, while the proposed project does not propose any new bicycle lanes or routes, the site is accessible from the existing Enhanced Bike Lane on Stevens Creek Boulevard. As such, the proposed project will not conflict with the City’s 2016 Bicycle Transportation Plan. Pedestrians will also have access to the site via the existing sidewalks that will connect to the pedestrian network surrounding the project site. Therefore, the proposed project will promote and will not obstruct these alternative modes of transportation.

Measure TR-2 Implement public and shared transit
programs to achieve 29 percent of public transit mode
share by 2030 and maintain through 2040.

Consistent. The City is the party responsible for this measure. The closest bus stop to the project site is approximately 0.02 miles (115 feet) away, on the north side of Stevens Creek Boulevard. The nearest transit stop is located 0.05 miles (280 feet) away, on the west side of Miller Avenue, which provides stops with a bus frequency of service interval of 15 to 20 minutes during the peak weekday commute periods along VTA bus route 23 and Rapid Transit 523.

Measure TR-3 Increase zero-emission vehicle (ZEV)
adoption to 35 percent for passenger vehicles and 20
percent for commercial vehicles by 2030 and 100
percent for all vehicles by 2040.

Consistent. The proposed project will result in an increase in land use intensity in a portion of the city that has access to existing transportation infrastructure and services, including the VTA bus routes 23, 25, 51, 55, and Rapid Transit 523. To encourage transition to electric vehicles (EVs), the proposed project will be required to install EV charging stations pursuant to the City’s code. The proposed project will be conditioned by the City to install six Level 2 EV Ready Circuits and six Level 1 EV Ready Circuits, one of each in each of the townhome units, and therefore will be consistent with this standard to increase this to the minimum of EVcapable charging spaces to comply with the voluntary Tier 2 standards of CALGreen, as required by the Air District.

Measure W-1 Implement SB 1383 requirements and
reduce communitywide landfilled organics 75 percent
by 2025 and inorganic waste 35 percent by 2030 and
reduce all waste 90 percent by 2040.

Consistent. The City is the party responsible for implementing this measure. As described in Chapter 2, Project Description, the proposed project will include compost and green waste disposal services through the City’s contracts with Recology South Bay. The proposed project will not conflict with implementation of this measure.

Measure W-2 Reduce overall waste disposed to
garbage, recycling, and compost per capita by 15
percent by 2035.

Consistent. The City is the party responsible for implementing this measure. As described in Chapter 2, Project Description, the proposed project will include compost and green waste disposal services through the City’s contracts with Recology South Bay. The proposed project will not conflict with implementation of this measure.
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TABLE 3-8 CUPERTINO CLIMATE ACTION PLAN CONSISTENCY MATRIX Measure Consistency
Measure W-3 Meet or exceed the SB 1383 recycled
organics products procurement requirements and
sequester or avoid at least 0.018 MT CO2e per person
by through 2045.

Consistent. The City is the party responsible for implementing this measure. As described in Chapter 2, Project Description, the proposed project will include compost and green waste disposal services through the City’s contracts with Recology South Bay. The proposed project will not conflict with implementation of this measure.

Measure WW-2 Reduce per capita water consumption
15 percent compared to 2019 levels by 2030 and
maintain through 2040
Consistent. The proposed project will comply with Senate Bill (SB) X7-7, which requires California to achieve a 20 percent reduction in urban percapita water use by 2020 and will implement best management practices for water conservation to achieve the City’s water conservation goals. As described in Chapter 2, Project Description, the project incorporates low water-use groundcovers, shrubs, and trees throughout the project site. All landscape zones will be irrigated as required by the Cupertino Landscape Ordinance, and water uses will be tailored to meet CALGreen Building Standards, which requires water conservation and requires new buildings to reduce water consumption by 20 percent. The proposed project will not conflict with implementation of this measure.

Measure CS-1 Increase carbon sequestration through
tree planting by developing and implementing an
Urban Forest Management Plan.

Consistent. The City is the party responsible for this measure. As described in Chapter 2, Project Description, the proposed project will increase landscaping on-site. This will increase tree canopy over the buildings and hardscaped areas, reducing energy needed to cool the buildings. The proposed project will include 3,720 square feet of on-site bioretention facilities that will hold and treat stormwater before dispersal to the City’s off-site storm drain infrastructure. Furthermore, the project will comply with the Santa Clara Valley Urban Runoff Pollution Prevention Program C.3 and CMC Chapter 9.18, Stormwater Pollution Prevention and Watershed Protection, to ensure ongoing compliance with the City’s municipal stormwater and urban runoff requirements. The proposed project will not conflict with implementation of this measure.

Notes: Measures BE-2 and BE-3 apply to existing development and are not applicable. Measure TR-4 is a city measure to re-focus transportation infrastructure in the city that is not applicable on a project-level. Measure CS-2 is for open space projects that can sequester carbon dioxide (CO2), and therefore, is not directly applicable to the project.

Source: City of Cupertino, August 2022, City of Cupertino Climate Action Plan 2.0.

Development in Cupertino, including the proposed project, is required to adhere to City-adopted policy provisions, including those contained in the adopted CAP 2.0. The City ensures that the provisions of the Cupertino CAP 2.0 are incorporated into projects and their permits through development review and applications of conditions of approval as applicable. Additionally, as previously stated, the proposed project will replace the older structures with newer, more energy-efficient structures that achieve the most recent California Building and Energy-Efficiency Standards and water-efficiency standards. 562
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Furthermore, CMC Chapter 17.04, Standard Environmental Protection Requirements, identifies standard environmental protection requirements that all construction projects must meet. Specifically, the project applicant will be required to comply with CMC Section 17.04.050(C), which will minimize stormwater runoff:

CMC Section 17.04.050(C), Reduce Greenhouse Gas Emissions (GHG) and Energy Use. The project applicant shall complete the City of Cupertino Climate Action Plan – Development Project Consistency Checklist, for review and approval by the City Environment and Sustainability Department prior to issuance of the first permit, to demonstrate how the project is consistent with the Cupertino Climate Action Plan, as subsequently revised, supplemented, or replaced, in order to reduce greenhouse gas emissions and conserve energy.

Therefore, the proposed project will be consistent with Cupertino CAP 2.0.

CARB’s Scoping Plan
CARB’s Scoping Plan outlines the State’s strategies to reduce GHG emissions in accordance with the targets established under SB 32, Assembly Bill (AB) 32, and Executive Order (EO) B-55-18. The Scoping Plan is applicable to State agencies and is not directly applicable to cities/counties and individual projects.

Nonetheless, the Scoping Plan has been the primary tool that is used to develop performance-based and efficiency-based CEQA criteria and GHG reduction targets for climate action planning efforts. CARB recently released the 2022 Scoping Plan to address measures to achieve the State’s carbon neutrality goals under EO B-55-18.

Statewide strategies to reduce GHG emissions in the 2017 Climate Change Scoping Plan include implementing SB 350, which expands the Renewable Portfolio Standards to 50 percent by 2030 and doubles energy-efficiency savings; expanding the Low Carbon Fuel Standards (LCFS) to 18 percent by 2030; implementing the Mobile Source Strategy to deploy zero-electric vehicle buses and trucks; implementing the Sustainable Freight Action Plan; implementing the Short-Lived Climate Pollutant Reduction Strategy, which reduces methane and hydrofluorocarbons to 40 percent below 2013 levels by 2030, and black carbon emissions to 50 percent below 2013 levels by 2030; continuing to implement SB 375; creating a post-2020 Cap-and-Trade Program; and developing an Integrated Natural and Working Lands Action Plan to secure California’s land base as a net carbon sink.

Statewide strategies to reduce GHG emissions include the low carbon fuel standards, California Appliance Energy Efficiency regulations, California Renewable Energy Portfolio standard, changes in the CAFE standards, and other early-action measures as necessary to ensure the State is on target to achieve the GHG emissions-reduction goals of SB 32, AB 32, and EO B-55-18. In addition, new buildings are required to comply with the current Building Energy-Efficiency Standards and CALGreen. The Cupertino CAP 2.0 is consistent with the statewide GHG reduction strategy and therefore complying with the CAP 2.0 will ensure the proposed project complies with the CARB Scoping Plan. The project’s GHG emissions will be reduced 563
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from compliance with statewide measures that have been adopted since SB 32, AB 32, and EO B-55-18 were adopted.

Plan Bay Area
Plan Bay Area 2050 is the Bay Area’s RTP/SCS that identifies a sustainable vision for the Bay Area. To achieve the MTC/ABAG’s sustainable vision for the Bay Area, the Plan Bay Area 2050 land use concept plan for the region concentrates the majority of new population and employment growth in the region in PDAs. An overarching goal of the regional plan is to concentrate development in areas where there are existing services and infrastructure rather than allocate new growth to outlying areas where substantial transportation investments would be necessary to achieve the per-capita passenger vehicle, VMT, and associated GHG emissions reductions. The project site is in a Santa Clara VTA City Cores, Corridors, and Station Areas PDA and the proposed project is an infill development project that will result in an increase in land use intensity in a portion of the city that has access to existing infrastructure and services, including transit service. Therefore, the proposed project will be consistent with Plan Bay Area 2050.

3.4.4 Water Quality

3.4.4.1 WATER QUALITY STANDARDS
The City, as a participant in the Santa Clara Valley Urban Runoff Pollution Prevention Program, which is regulated by the NPDES Program, is committed to reducing pollutants entering waterways. Below is a discussion of the proposed project’s compliance with water quality standards.

Construction Impacts
Because the proposed project is greater than one acre, it will be required to comply with the General Permit for Stormwater Discharges Associated with Construction and Land Disturbance Activity (Construction General Permit). The proposed project will also be required to comply with the Regional Water Board Municipal Regional Permit (MRP), because it will create more than 10,000 square feet of impervious surfaces. The proposed project is required to comply with the Santa Clara Valley Urban Runoff Pollution Prevention Program C.3 requirements, which include minimization of impervious surfaces, measures to detain or infiltrate runoff from peak flows to match pre-development conditions, and agreements to ensure that the stormwater treatment and flow-control facilities are maintained in perpetuity. Compliance with applicable regulations will ensure that the proposed project will not result in adverse impacts to water quality during the construction period.
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Operational Impacts
As stated previously, the proposed project will be required to comply with the MRP. Furthermore, stormwater from implementation of the proposed project will be directed to the existing stormwater system, in addition to being filtered through the 3,720 square feet of on-site bioretention areas as described in Section 2.4.4.3, Stormwater Management. Therefore, the proposed project will continue to minimize pollutant runoff from the project site and will not result in adverse water quality impacts during operation.

3.4.4.2 GROUNDWATER
The proposed project will connect to the existing water lines on-site and will not use groundwater at the site. Additionally, as described in Section 2.4.4.3, Stormwater Management, the proposed project will include 3,720 square feet of on-site bioretention areas, which will allow water to percolate into the groundwater basin below the project site. Therefore, the proposed project will not deplete groundwater supplies or interfere substantially with groundwater recharge.

3.4.4.3 DRAINAGE PATTERNS
Stormwater runoff from the project site is channeled into a storm drain under Stevens Creek Boulevard.

Stormwater from Cupertino is eventually discharged into San Francisco Bay. As described in Section 2.4.4.3, Stormwater Management, the proposed project includes 3,720 square feet of on-site bioretention areas and will result in a decrease of approximately 26,200 square feet of impervious surfaces. The proposed project will be required to comply with the Santa Clara Valley Urban Runoff Pollution Prevention Program C.3 requirements, which include minimization of impervious surfaces, measures to detain or infiltrate runoff from peak flows to match pre-development conditions, and agreements to ensure that the stormwater treatment and flow-control facilities are maintained in perpetuity.

Additionally, CMC Chapter 17.04, Standard Environmental Protection Requirements, identifies standard environmental protection requirements that all construction projects must meet. Specifically, the project applicant will be required to comply with CMC Section 17.04.050(F), which will minimize stormwater runoff:

CMC Section 17.04.050(F), Control Stormwater Runoff Contamination. The project applicant shall demonstrate compliance with Chapter 9.18 (Stormwater Pollution Prevention and Watershed Protection) of the Cupertino Municipal Code, to the satisfaction of the City of Cupertino. All identified stormwater runoff control measures shall be included in the applicable construction documents.

CMC Chapter 9.18 is intended to provide regulations and give legal effect to certain requirements of the NPDES permit, which requires erosion and siltation-control measures, issued to the City. Therefore, compliance with the CMC and Santa Clara Valley Urban Runoff Pollution Prevention Program C.3 requirements will ensure that the proposed project will not substantially alter the existing drainage pattern of the site or area.
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3.4.4.4 INUNDATION
The project site is not in a 100-year flood zone or special flood hazard area as mapped by the Federal Emergency Management Agency (FEMA). Additionally, the project site is also not in an area subject to tsunami, seiche, or dam failure inundation. Therefore, the proposed project will not risk release of pollutants due to project inundation.

3.5 CEQA GUIDELINES SECTION 15332(E): UTILITIES AND PUBLIC

SERVICES
For the following reasons, the project site can be adequately served by all required utilities and public services and therefore meets the criteria of CEQA Guidelines Section 15332(e).

The project site is in an urban area already served by all necessary municipal utilities (i.e., stormwater, water, wastewater, solid waste) and public services (i.e., police and fire).

3.5.1 Stormwater
The project site is served by existing stormwater sewer systems, and the proposed project will not require additional or modified stormwater sewer systems. As described in Section 2.4.4.3, Stormwater Management, the proposed project will also implement 3,720 square feet of on-site bioretention areas to reduce or slow stormwater runoff and will result in a decrease of approximately 26,200 square feet of impervious surfaces. Therefore, the proposed project will reduce demand to stormwater infrastructure when compared to existing conditions and will not result in significant impacts to stormwater utilities.

3.5.2 Water
The project site is in the CWS service area. Water service to the project site will be provided by the existing water lines on Stevens Creek Boulevard and East Estates Drive. No new connections will be needed and are not proposed as part of the proposed project. As shown in the water supply evaluation included in Appendix G, Environmental Assessment, of the Cupertino General Plan, which evaluated the project site being developed at a greater density (80 dwelling units per acre) than what is proposed (25 dwelling units per acre), CWS predicts that there will be sufficient water supplies to meet citywide demand through year 2040 during normal, single-dry, and multiple-dry years.54 Furthermore, the project applicant will be required to comply with CMC Chapter 17.04, Standard Environmental Protection Requirements. Specifically, the project 54 City of Cupertino, April 2024, Cupertino General Plan Community Vision 2015-2040, Appendix G, General Plan 2040 and Zoning Code Amendments Environmental Assessment, Table 4.15-3, Cal Water PAS Supply and Demand Comparison: 2025 to 2040 (AFY), https://www.cupertino.gov/Your-City/Departments/Community-Development/Planning/General-Plan/General-PlanCommunity-Vision, accessed March 18, 2025. 566
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applicant will be required to comply with CMC Section 17.04.050(I)(2), which will ensure adequate water supply and infrastructure:

CMC Section 17.04.050(I)(2), Ensure Adequate Water Supply and Infrastructure. The project applicant shall obtain written approval from the appropriate water service provider for water connections, service capability, and location and layout of water lines and backflow preventers, prior to issuance of the first permit.

This will ensure that the existing system can support the proposed project. Therefore, the proposed project will not result in significant impacts to water utilities.

3.5.3 Wastewater
The project site is in the CSD service area, and wastewater will be treated at SJ/SCWPCP. Wastewater generated by the proposed project will be collected by the existing sanitary sewer main along Stevens Creek Boulevard. As shown in the wastewater evaluation included in Appendix G, Environmental Assessment, of the Cupertino General Plan, which evaluated the project site being developed at a greater density (80 dwelling units per acre) than what is proposed (25 dwelling units per acre), CSD has sufficient capacity for buildout of the General Plan. As shown, the increase in wastewater demand due to future potential development from the General Plan is estimated to be approximately 0.41 million gallons per day (mgd). As of 2020, the SJ/SCWPCP is treating 110 mgd with a permitted capacity of 167 mgd. Therefore, the wastewater treatment facility has a residual capacity of 57 mgd and the addition of 0.41 mgd from implementation of the General Plan buildout is only 0.7 percent of the residual capacity. 55 The project applicant will be required to comply with CMC Chapter 17.04, Standard Environmental Protection Requirements. Specifically, the project applicant will be required to comply with CMC Section

17.04.050(I)(1), which will minimize potential impacts to the sewer system:

CMC Section 17.04.050(I)(1), Manage Wastewater Inflow and Infiltration to Sewer System. Project applicants shall implement the following measures to reduce wastewater flow:
a. The project applicant shall demonstrate, to the satisfaction of the City of Cupertino and Cupertino Sanitary District (CSD) that the project would not exceed the peak wet weather flow capacity of the Santa Clara sanitary sewer system by implementing one or more of the following methods:
i. Reduce inflow and infiltration in the CSD system to reduce peak wet weather flows, or 55 City of Cupertino, April 2024, Cupertino General Plan Community Vision 2015-2040, Appendix G, General Plan 2040 and Zoning Code Amendments Environmental Assessment, Table 4.15-6, Increase in Wastewater Demand with Proposed Modified Project, https://www.cupertino.gov/Your-City/Departments/Community-Development/Planning/General-Plan/General-PlanCommunity-Vision, accessed March 18, 2025. 567
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ii. Increase on-site water reuse, such as increased grey water use, or reduce water consumption of the fixtures used within the proposed project, or other methods that are measurable and reduce sewer generation rates to acceptable levels, to the satisfaction of the CSD.
b. The project’s estimated wastewater generation shall be calculated using the current generation rates used by the CSD unless alternative (i.e., lower) generation rates achieved by the project are substantiated by the project applicant based on evidence to the satisfaction of the CSD. c. The project applicant shall obtain a letter of clearance from the Cupertino Sanitary District and provide a copy of the letter of clearance to the City prior to issuance of the first permit.

This will ensure that the existing system can support the proposed project. Therefore, the proposed project will not result in significant impacts to wastewater utilities.

3.5.4 Solid Waste
The City contracts with Recology to provide solid waste collection services to residents in the city. Solid waste is collected by Recology and deposited at the Newby Island Sanitary Landfill in Milpitas. The proposed project site is already served by solid waste services and will continue to be served by Recology under the proposed project. As shown in the solid waste evaluation included in Appendix G, Environmental Assessment, of the Cupertino General Plan, which evaluated the project site being developed at a greater density (80 dwelling units per acre) than what is proposed (25 dwelling units per acre), the Newby Island Sanitary Landfill has sufficient capacity for buildout of the General Plan. As shown, an increase of 8.8 tons per day from implementation of the General Plan buildout would be 0.4 percent of the current residual capacity of Newby Island Sanitary Landfill. 56 The proposed project will not result in an excess of solid waste that will not be able to be accommodated under existing services.

3.5.5 Public Services Providers
The primary purpose of the public services impact analysis is to examine the impacts associated with physical improvements to public service facilities required to maintain acceptable service ratios, response times, or other performance objectives. Public service facilities need improvements (i.e., construction, renovation, or expansion) as demand for services increase. Increased demand is typically driven by increases in population. The proposed project will have a significant environmental impact if it exceeds the 56 City of Cupertino, April 2024, Cupertino General Plan Community Vision 2015-2040, Appendix G, General Plan 2040 and Zoning Code Amendments Environmental Assessment, Table 4.15-7, Increase in Solid Waste Generation with Proposed Modified Project, https://www.cupertino.gov/Your-City/Departments/Community-Development/Planning/General-Plan/General-PlanCommunity-Vision, accessed March 18, 2025. 568
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ability of public service providers to adequately serve residents, thereby requiring construction of new facilities or modification of existing facilities.

The proposed project is in an area already served by public service providers. Through developer impact fees, development of the proposed project will support the City’s public services funds that are used, in part, to maintain City services. Likewise, and pursuant to SB 50,57 the project applicant will be required to pay the school impact fees required for residential development to offset impacts to the school district. As shown in the public services evaluation included in Appendix G, Environmental Assessment, of the Cupertino General Plan, which evaluated the project site being developed at a greater density (80 dwelling units per acre) than what is proposed (25 dwelling units per acre), impacts to public service providers (fire protection, police, schools, libraries, and parks) were found to be less than significant at General Plan buildout. Therefore, the proposed project will not result in an increase in demand that will prevent public service providers from adequately serving residents.
57 Senate Bill 50 amended California Government Code Section 65995, which contains limitations on Education Code Section 17620, the statute that authorizes school districts to assess development fees within school district boundaries. 569
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4. Exceptions
In addition to analyzing the applicability of CEQA Guidelines Section 15332 (Class 32), this document assesses whether any of the exceptions to categorical exemptions identified in CEQA Guidelines Section 15300.2 (Exceptions) apply to the proposed project. The following analysis compares the criteria in CEQA Guidelines Section 15300.2 (Exceptions) to the project, and concludes, based on substantial evidence, that none of the exceptions are applicable to the project, and that the project is categorically exempt from CEQA pursuant to CEQA Guidelines Sections 15300 and 15332.

4.1 CEQA GUIDELINES SECTION 15300.2(A): LOCATION
Classes 3, 4, 5, 6, and 11 are qualified by consideration of where the project is to be located – a project that is ordinarily insignificant in its impact on the environment may, in a particularly sensitive environment, be significant. Therefore, these classes are considered to apply to all instances, except where the project may impact an environmental resource of hazardous or critical concern where designated, precisely mapped, and officially adopted pursuant to law by federal, State, or local agencies.

The proposed project does not qualify for an exemption under Classes 3, 4, 5, 6, or 11. The project site is in an urban developed area and is not in a sensitive environment. In addition, the proposed project will not result in any impacts on an environmental resource of hazardous or critical concern. Therefore, the exception under CEQA Guidelines Section 15300.2(a) does not apply to the proposed project.

4.2 CEQA GUIDELINES SECTION 15300.2(B): CUMULATIVE IMPACT All exemptions for these classes are inapplicable when the cumulative impact of successive projects of the same type in the same place, over time, is significant.

The project site is in a developed urban neighborhood that is already served by utilities and public services, as well as transportation. As discussed in Section 3.4, CEQA Guidelines Section 15332(d): Traffic, Noise, Air Quality, or Water Quality, the proposed project will not result in significant impacts pertaining to traffic, noise, air quality, or water quality. Any construction effects will be temporary, confined to the project vicinity, and reduced to the extent feasible through compliance with the CMC and applicable regulations.

Therefore, the exception under CEQA Guidelines Section 15300.2(b) does not apply to the proposed project.
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4.3 CEQA GUIDELINES SECTION 15300.2(C): SIGNIFICANT EFFECT A categorical exemption shall not be used for an activity where there is a reasonable possibility that the activity will have a significant effect on the environment due to unusual circumstances.

Neither the CEQA Statute nor the State CEQA Guidelines provide a definition of "unusual circumstances." However, the courts have provided guidance in determining what constitutes unusual circumstances. In Berkeley Hillside Preservation et al v. City of Berkeley et al. (2015), the California Supreme Court stated, "A party invoking the [Section 15300.2(c)] exception may establish an unusual circumstance without evidence of an environmental effect, by showing that the project has some feature that distinguishes it from others in the exempt class, such as its size or location [emphasis added]." This Supreme Court decision established a two-pronged test for determining whether the Section 15300.2(c) exception applies. Under this test, the lead agency must first determine whether an unusual circumstance exists and then, if an unusual circumstance does exist, must apply the fair argument standard to determine whether there is a reasonable possibility that the proposed project would produce a significant effect due to that circumstance.

There are no known unusual circumstances applicable to the project that could result in a significant effect on the environment. The proposed project consists of the demolition of the existing commercial building on the project site and the construction of 55 new residential townhome units and 10 ADUs on a 2.72-acre project site at 10065 East Estates Drive in the central region of the city near the intersection of Stevens Creek Boulevard and Wolfe Road. The proposed project will not result in a change in the existing land use or zoning designations or introduce a new activity to the area that could result in a significant effect on the environment. Therefore, neither the size nor the location of the project site is unusual.

With respect to the existing conditions, as discussed in Section 2.2, Existing Conditions, One Hour Dry Cleaners operated a dry-cleaning business at 10045 East Estates Drive using PCE as a dry-cleaning solvent between the 1960s and 2010. Due to the presence of PCE, believed to be associated with the former drycleaning operations, in soil and soil gas, the project site is listed as an open cleanup program site under the oversight of SCCDEH and is listed on the State Water Quality Control Board’s GeoTracker website. However, the City recognizes that sites subject to redevelopment may contain hazardous materials or contaminated soils are not unusual and, as described in Section 1.2, Standard Environmental Protection Requirements, updated the CMC to include Chapter 17.04, that set forth a uniform set of standards that apply to every project in Cupertino to address hazardous materials, further supporting that the One Hour Dry Cleaners is not an unusual circumstance. The project applicant will be required to comply with CMC Chapter 17.04 Specifically, the project applicant will be required to comply with CMC Section 17.05.050(B) listed below, which will require soil remediation:
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CMC Section 17.04.050(B), Hazardous Materials Permit Requirements.

Soil Remediation Required. If a Focused or other Phase II ESA, as required pursuant to Section

17.04.040(B)(1), identifies an unacceptable or a potentially unacceptable health risk, the project applicant shall, depending on the contaminant, contact either the Environmental Protection Agency (EPA), Department of Toxic Substances Control (DTSC), Regional Water Quality Control Board (RWQCB) or local Certified Unified Program Agency (CUPA). The project applicant shall enter into a regulatory agency oversight program with an appropriate regulatory agency, or an established voluntary oversight program alternative with an appropriate regulatory agency, as determined by the City, and follow the regulatory agency’s recommended response actions until the agency reaches a no further action determination, prior to issuance of any permit for a project that allows ground disturbing activity.

With mandatory compliance with CMC Section 17.04.050(B), the proposed project would obtain written clearance from the SCCDEH prior to the issuance of any building permits confirming that the project site has been adequately investigated and remediated for contamination associated with the former drycleaning operations and would not have a significant effect on the environment due to site contamination.

Therefore, the exception under CEQA Guidelines Section 15003.2(b) does not apply to the proposed project.

4.4 CEQA GUIDELINES SECTION 15300.2(D): SCENIC HIGHWAYS A categorical exemption shall not be used for a project that may result in damage to scenic resources, including, but not limited to, trees, historic buildings, rock outcroppings, or similar resources, within a highway officially designated as a state scenic highway. This does not apply to improvements that are required as mitigation by an adopted negative declaration or certified environmental impact report (EIR).

The proposed project will not affect a resource within a State Scenic Highway. The nearest scenic highway, State Route 9, is over five miles south of the project site. The nearest eligible State Scenic Highway, I-280, is approximately 0.5 miles northeast of the project site, with urban development between.58 The project site is not visible from I-280. Additionally, the project site and surrounding area are already developed.

Therefore, no scenic resources within view of a State Scenic Highway will be altered as part of the project. 58 California Department of Transportation, 2025, California State Scenic Highway System Map, https://caltrans.maps.arcgis.com/apps/webappviewer/index.html?id=465dfd3d807c46cc8e8057116f1aacaa, accessed May 8, 2025.
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4.5 CEQA GUIDELINES SECTION 15300.2(E): HAZARDOUS WASTE SITES A categorical exemption shall not be used for a project on a site that is included on any list compiled pursuant to Section 65962.5 of the Government Code.

California Government Code Section 65962.5 requires the California Environmental Protection Agency (CalEPA) to compile, maintain, and update specified lists of hazardous material release sites. CEQA requires the lead agency to consult the lists compiled pursuant to Government Code Section 65962.5 to determine whether a project and any alternatives are identified.
59 The required lists of hazardous material release sites are commonly referred to as the “Cortese List” named after the legislator who authored the legislation.

Because the statute was enacted more than 20 years ago, some of the provisions refer to agency activities that were conducted many years ago and are no longer being implemented and, in some cases, the information required in the Cortese List does not exist. Those requesting a copy of the Cortese Lists are now referred directly to the appropriate information resources contained on internet websites hosted by the boards or departments referenced in the statute, including California Department of Toxic Substance Control’s (DTSC) online EnviroStor database and the State Water Resources Control Board’s (SWRCB) online GeoTracker database. These two databases include hazardous material release sites, along with other categories of sites or facilities specific to each agency’s jurisdiction.

The project site is listed as an open cleanup program site on the State Water Quality Control Board’s GeoTracker website.60 However, the project site is not included on the Hazardous Waste and Substances Site List (Cortese) pursuant to Government Code Section 65962.5 as of November 2025.61 Additionally, the project site is not listed on any of the following CalEPA’s Cortese List Data Resources:62  List of Hazardous Waste and Substances sites from DTSC EnviroStor database63  List of Leaking Underground Storage Tank Sites from SWRCB’s GeoTracker64 59 California Public Resources Code Section 21092.6.
60 State Water Resources Control Board, 2024, GeoTracker, https://geotracker.waterboards.ca.gov/profile_report.asp?global_id=T10000021095, accessed November 11, 2025. 61 California Department of Toxic Substances Control, 2025, Hazardous Waste and Substances Site List (Cortese), https://www.envirostor.dtsc.ca.gov/public/search?cmd=search&reporttype=CORTESE&site_type=CSITES,FUDS&status=ACT,BKLG ,COM&reporttitle=HAZARDOUS+WASTE+AND+SUBSTANCES+SITE+LIST+%28CORTESE%29, accessed November 11, 2025. 62 California Environmental Protection Agency, 2025, Cortese List Data Resources, https://calepa.ca.gov/SiteCleanup/CorteseList/, accessed November 11, 2025. 63 California Department of Toxic Substances Control, 2025, Hazardous Waste and Substances Site List (Cortese), https://www.envirostor.dtsc.ca.gov/public/search?cmd=search&reporttype=CORTESE&site_type=CSITES,FUDS&status=ACT,BKLG ,COM&reporttitle=HAZARDOUS+WASTE+AND+SUBSTANCES+SITE+LIST+%28CORTESE%29, accessed November 11, 2025. 64 State Water Resources Control Board, 2025, GeoTracker, https://geotracker.waterboards.ca.gov/search?CMD=search&case_number=&business_name=&main_street_name=&city=&zip= &county=&SITE_TYPE=LUFT&oilfield=&STATUS=&BRANCH=&MASTER_BASE=&Search=Search, accessed November 11, 2025. 574
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 List of solid waste disposal sites identified by SWRCB with waste constituents above hazardous waste levels outside the waste management unit65
 List of “active” Cease and Desist Orders and Cleanup and Abatement Orders from SWRCB66  List of hazardous waste facilities subject to corrective action pursuant to Section 25187.5 of the Health and Safety Code, identified by DTSC67
Therefore, the exception under CEQA Guidelines Section 15300.2(e) does not apply to the proposed project.

4.6 CEQA GUIDELINES SECTION 15300.2(F): HISTORICAL RESOURCES A categorical exemption shall not be used for a project that may cause a substantial adverse change in the significance of a historical resource.

No historic resources exist in the vicinity of the project site. There is also no known sensitivity for archaeological or paleontological resources on the site. However, the site may contain previously unknown subsurface archaeological and paleontological deposits. The proposed project will comply with Land Use and Community Design Element Policy 2-72 in the General Plan, which requires compliance with City, State, and federal historic preservation laws, regulations, and codes, including laws related to archaeological resources. In particular, the proposed project will be required to comply with CEQA Guidelines Section 15064.5(e), which specifies procedures to be used in the event of a discovery of Native American human remains on non-federal land. Additionally, CMC Chapter 17.04, Standard Environmental Protection Requirements, identifies standard environmental protection requirements that all construction projects must meet. Specifically, the project applicant will be required to comply with CMC Sections 17.04.050(E)(1),

17.04.050(E)(2), and 17.04.050(H), which will minimize impacts to archaeological resources, tribal cultural resources, and paleontological resources:

CMC Section 17.04.050(E)(1), Protect Archaeological Resources and Tribal Cultural Resources. For all projects requiring ground-disturbing activities on land with no known archaeological or tribal cultural resources that has not been previously disturbed and/or where ground-disturbing activities would occur at a greater depth or affect a greater area than previously disturbed, the following shall be required:
65 California Environmental Protection Agency, 2025, Sites Identified with Waste Constituents Above Hazardous waste Levels Outside the Waste Management Unit, https://calepa.ca.gov/wp-content/uploads/2016/10/SiteCleanup-CorteseListCurrentList.pdf, accessed November 11, 2025. 66 California Environmental Protection Agency, 2025, List of “active” CDO and CAO from Water Board, https://calepa.ca.gov/wp-content/uploads/2016/10/SiteCleanup-CorteseList-CDOCAOList.xlsx, accessed November 11, 2025. 67 California Environmental Protection Agency, 2025, Cortese List: Section 65962.5(a), https://calepa.ca.gov/sitecleanup/corteselist/section-65962-5a/, accessed November 11, 2025. 575
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a. Areas with No Known Cultural Resources. For all projects within areas where there are no known cultural resources, prior to soil disturbance, the project applicant shall provide written verification, including the materials provided to contractors and construction crews, to the City confirming that contractors and construction crews have been notified of basic archaeological site indicators, the potential for discovery of archaeological resources, laws pertaining to these resources, and procedures for protecting these resources as follows:
i. Basic archaeological site indicators that may include, but are not limited to, darker than surrounding soils of a friable nature; evidence of fires (ash, charcoal, fire affected rock or earth); concentrations of stone, bone, or shellfish; artifacts of stone, bone, or shellfish; evidence of living surfaces (e.g., floors); and burials, either human or animal. ii. The potential for undiscovered archaeological resources or tribal cultural resources on site. iii. The laws protecting these resources and associated penalties, including, but not limited to, the Native American Graves Protection and Repatriation Act of 1990, Public Resources Code Section 5097, and California Health and Safety Code Section 7050 and Section 7052. iv. The protection procedures to follow should construction crews discover cultural resources during project-related earthwork, include the following:

1. All soil disturbing work within 25 feet of the find shall cease.

2. The project applicant shall retain a qualified archaeologist to provide and implement a plan for survey, subsurface investigation, as needed, to define the deposit, and assessment of the remainder of the site within the project area to determine whether the resource is significant and would be affected by the project.

3. Any potential archaeological or tribal cultural resources found during construction activities shall be recorded on appropriate California Department of Parks and Recreation forms by a qualified archaeologist. If the resource is a tribal cultural resource, the consulting archaeologist shall consult with the appropriate tribe, as determined by the Native American Heritage Commission, to evaluate the significance of the resource and to recommend appropriate and feasible avoidance, testing, preservation or mitigation measures, in light of factors such as the significance of the find, proposed project design, costs, and other considerations. The archeologist shall perform this evaluation in consultation with the tribe.
b. Areas with Known Cultural Resources. For all projects within areas of known cultural resources as documented in the 2015 General Plan EIR Table 4.4-2, Cultural Resources in the Project Study Area and Vicinity, as subsequently revised, supplemented, or replaced by the City, and the archaeological or tribal cultural resources cannot be avoided, in addition to the requirements in Section E.1.a for all construction projects with ground-disturbing activities, the following additional actions shall be implemented prior to ground disturbance:
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i. The project applicant shall retain a qualified archaeologist to conduct a subsurface investigation of the project site, and to ascertain the extent of the deposit of any buried archaeological materials relative to the project’s area of potential effects, in consultation with a tribal representative as applicable. The archaeologist shall prepare a site record and file it with the California Historical Resource Information System and the City of Cupertino. ii. If the resource extends into the project’s area of potential effects as determined by the archaeologist, the resource shall be evaluated by a qualified archaeologist to determine if the resource is eligible for listing on the California Register of Historical Resources. If the qualified archaeologist determines that the resource is not eligible, no further action is required unless there is a discovery of additional resources during construction (as required above for all construction projects with ground-disturbing activities). If the qualified archaeologist determines that the resource is eligible, the qualified archaeologist shall identify ways to minimize the effect which the project applicant shall implement. A written report of the results of investigations and mitigations shall be prepared by the qualified archaeologist and filed with the California Historic Resources Information System Northwest Information Center and the City of Cupertino.

CMC Section 17.04.050(E)(2), Protect Human Remains and Native American Burials. The project applicant shall comply with California Health and Safety Code Section 7050.5 and California Public Resources Code Section 5097.98.
a. In the event of discovering human remains during construction activities, there shall be no further excavation or disturbance of the site within a 100-foot radius of the remains, or any nearby area reasonably suspected to overlie adjacent remains.
b. The Santa Clara County Coroner shall be notified immediately and shall make a determination as to whether the remains are Native American.
c. If the Santa Clara County Coroner determines that the remains are not subject to his authority, he shall notify the Native American Heritage Commission (NAHC) within 24 hours. d. The NAHC shall attempt to identify descendants (Most Likely Descendant) of the deceased Native American.
e. The Most Likely Descendant has 48 hours following access to the project site to make recommendations or preferences regarding the disposition of the remains. If the Most Likely Descendant does not make recommendations within 48 hours after being allowed access to the project site, the owner shall, with appropriate dignity, reinter the remains in an area of the property secure from further disturbance and provide documentation about this determination and the location of the remains to the NAHC and the City of Cupertino. Alternatively, if the owner does not accept the Most Likely Descendant’s recommendations, the owner or the descendent may request mediation by the NAHC. Construction shall halt until the mediation has concluded. 577
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CMC Section 17.04.050(H), Protect Paleontological Resources During Construction. If paleontological resources are encountered during ground disturbing and/or other construction activities, all construction shall be temporarily halted or redirected to allow a qualified paleontologist, which shall be retained by the project applicant, to assess the find for significance. If paleontological resources are found to be significant, the paleontological monitor shall determine appropriate actions, in coordination with a qualified paleontologist, City staff, and property owner. Appropriate actions may include, but are not limited to, a mitigation plan formulated pursuant to guidelines developed by the Society of Vertebrate Paleontology and implemented to appropriately protect the significance of the resource by preservation, documentation, and/or removal, prior to recommencing activities. Measures may include, but are not limited to, salvage of unearthed fossil remains and/or traces (e.g., tracks, trails, burrows); screen washing to recover small specimens; preparation of salvaged fossils to a point of being ready for curation (e.g., removal of enclosing matrix, stabilization and repair of specimens, and construction of reinforced support cradles); and identification, cataloging, curation, and provision for repository storage of prepared fossil specimens.

With mandatory compliance with CMC Sections 17.04.050(E)(1), 17.04.050(E)(2), and 17.04.050(H), the proposed project will not result in significant impacts to unknown archaeological, tribal cultural, or paleontological resources. Therefore, the exception under CEQA Guidelines Section 15003.2(f) does not apply to the proposed project.
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5. Conclusion
As discussed in Chapter 3, Exemption, of this document, the proposed project meets the criteria for categorically exempt in-fill development projects in CEQA Guidelines Section 15332 and because, as discussed previously, none of the exceptions to the categorical exemptions in CEQA Guidelines Section 15300.2 apply, and it will not have a significant effect on the environment pursuant to CEQA, this analysis finds that a Notice of Exemption is appropriate for the proposed project. 579
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6. List of Preparers

CITY OF CUPERTINO
Luke Connolly, Assistant Director of Community Development Piu Ghosh, Planning Manager
Gian Martire, Senior Planner, Project Manager

PLACEWORKS
Terri McCracken, Principal, Principal-in-Charge
Vivian Kha, Associate II, Project Manager
Chris Shields, Senior Associate, Noise
Lance Park, Senior Associate, Air Quality and Greenhouse Gas Emissions Lexis Zimny, Associate, Air Quality, Greenhouse Gas Emissions, and Noise 581
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IDLEWILD TOWNHOMES PROJECT CEQA EXEMPTION

CITY OF CUPERTINO

6. List of Preparers
PlaceWorks Page 72
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A PPENDIX A

E NVIRONMENTAL S ITE A SSESSMENT
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Copyright © 2025 by ENGEO Incorporated. This document
may not be reproduced in whole or in part by any means
whatsoever, nor may it be quoted or excerpted without the express written consent of ENGEO Incorporated.

IDLEWILD SHOPPING CENTER

CUPERTINO, CALIFORNIA

PHASE I ENVIRONMENTAL SITE ASSESSMENT

SUBMITTED TO
Mr. Rob Connolly
Toll Brothers, Inc.
6800 Koll Center Parkway, Suite 320
Pleasanton, CA 94566-7053

PREPARED BY
ENGEO Incorporated
June 11, 2025
PROJECT NO.
22934.000.001
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GEOTECHNICAL

ENVIRONMENTAL

WATER RESOURCES

CONSTRUCTION SERVICES

COASTAL/MARINE GEOTECHNICS
2633 Camino Ramon, Suite 250  San Ramon, CA 94583  (925) 866-9000  [email protected] www.engeo.com
Project No.
22934.000.001
June 11, 2025
Mr. Rob Connolly
Toll Brothers, Inc.
6800 Koll Center Parkway, Suite 320
Pleasanton, CA 94566-7053
Subject: Idlewild Shopping Center
19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive
Cupertino, California

PHASE I ENVIRONMENTAL SITE ASSESSMENT
Dear Mr. Connolly:

We are pleased to present our phase I environmental site assessment of the subject property (Property) located in Cupertino, California. The attached report includes a description of the site assessment activities, along with our findings, opinions, and conclusions regarding the Property.

We have the specific qualifications based on education, training, and experience to assess the nature, history, and setting of the Property. We have prepared this phase I environmental site assessment in general accordance with United States Environmental Protection Agency (USEPA) Standards and Practices for All Appropriate Inquiries (AAI) Final Rule set forth in 40 Code of Federal Regulations (CFR) Part 312 (USEPA, 2021a) and the American Society for Testing and Materials (ASTM) E1527-21: Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process (ASTM International, 2021). We declare that, to the best of our professional knowledge and belief, the responsible charge for this study meets the definition of Environmental Professional as defined in Section 312.10 of 40 CFR Part 312 and ASTM E1527-21.

We are pleased to be of service to you on this project. If you have any questions concerning the contents of our report, please contact us.

Sincerely,
ENGEO Incorporated
Jenna Keith, PE Nadine Periat, PG
jk/np/jf
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TABLE OF CONTENTS

LETTER OF TRANSMITTAL
EXECUTIVE SUMMARY ................................................................................................ 1

1.0 INTRODUCTION.................................................................................................. 4

1.1 PURPOSE OF PHASE I ENVIRONMENTAL SITE ASSESSMENT .................................. 4

1.2 USER-PROVIDED INFORMATION.................................................................................... 5

1.3 DETAILED SCOPE OF SERVICES.................................................................................... 5

1.4 NON-SCOPE SERVICES ................................................................................................... 5

1.5 SITE LOCATION AND DESCRIPTION .............................................................................. 5

1.6 CURRENT USE OF PROPERTY AND ADJOINING PROPERTIES ................................. 6

2.0 PHYSICAL SETTING........................................................................................... 6

2.1 TOPOGRAPHY, GEOLOGY, AND HYDROGEOLOGY..................................................... 6

2.2 OIL AND GAS ..................................................................................................................... 7

2.3 INDOOR AIR QUALITY ...................................................................................................... 7

3.0 PREVIOUS ENVIRONMENTAL REPORTS......................................................... 8

4.0 RECORDS REVIEW .......................................................................................... 17

4.1 PROPERTY RECORDS ................................................................................................... 17

4.1.1 Title Report/Ownership ........................................................................................ 17

4.1.2 Environmental Liens and Activity and Use Limitations ........................................ 18

4.2 HISTORICAL RECORD SOURCES................................................................................. 18

4.2.1 Historical Topographic Maps, Aerial Photographs, and Sanborn Maps .............. 18

4.2.2 City Directory........................................................................................................ 19

4.3 ENVIRONMENTAL DATABASE RECORD SOURCES ................................................... 21

4.3.1 Property Database Records................................................................................. 21

4.3.2 Adjoining and Nearby Property Database Records ............................................. 22

4.4 REGULATORY AGENCY FILES AND RECORDS .......................................................... 25

4.5 PER- AND POLYFLUOROALKYL SUBSTANCES .......................................................... 26

5.0 SITE RECONNAISSANCE................................................................................. 27

5.1 METHODOLOGY.............................................................................................................. 27

5.2 SITE AND ADJOINING PROPERTIES SETTING............................................................ 27

5.3 SITE CONDITIONS........................................................................................................... 27

5.4 INTERIOR OBSERVATIONS ........................................................................................... 28

5.5 ASBESTOS, LEAD, AND PCB-CONTAINING BUILDING MATERIALS.......................... 29

6.0 INTERVIEWS ..................................................................................................... 29

6.1 USER INTERVIEW ........................................................................................................... 29

6.2 KEY SITE MANAGER INTERVIEW.................................................................................. 29

7.0 FINDINGS AND OPINIONS ............................................................................... 30

7.1 FINDINGS......................................................................................................................... 30

7.2 DATA GAPS AND DATA FAILURES................................................................................ 31

7.3 SIGNIFICANT DEVIATIONS FROM ASTM STANDARD PRACTICE ............................. 31

8.0 CONCLUSIONS................................................................................................. 31 587
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9.0 LIMITATIONS..................................................................................................... 32

9.1 ASSUMPTIONS, LIMITATIONS, AND EXCEPTIONS OF ASSESSMENT ..................... 32

9.2 SPECIAL TERMS AND CONDITIONS............................................................................. 33

SELECTED REFERENCES

FIGURES
APPENDIX A – Environmental Data Resources, Inc., Radius Map Report APPENDIX B – Chicago Title Company, Preliminary Title Report APPENDIX C – Environmental Site Assessment Questionnaires (2) APPENDIX D – Environmental Data Resources, Inc., Historical Topographic Map Report APPENDIX E – Environmental Data Resources, Inc., Aerial Photo Decade Package APPENDIX F – Environmental Data Resources, Inc., Sanborn Map Report APPENDIX G – Environmental Data Resources, Inc., City Directory APPENDIX H – Qualifications of Environmental Professional 588
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EXECUTIVE SUMMARY
We conducted a phase I environmental site assessment (phase I ESA) for the subject property located at 19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive in Cupertino, California (the Property). The Property is approximately 2.7 acres in area and is identified by Assessor’s Parcel Numbers (APNs) 369-06-002, 369-06-003, and 369-06-004.

The Property consists of an approximately 41,000-square-foot commercial building and associated parking and landscaped areas. Most of the former tenant spaces are vacant, while a furniture store, restaurant, and salon remain on site. Review of historical records indicates that one to three structures were located along the eastern edge of the Property as early as 1897.

Orchards are visible across the Property and surrounding sites in the earliest aerial photograph of the Property from 1939. Between 1956 and 1960, the orchards were felled, and the Property was redeveloped with the present-day commercial building and parking areas. The Property has remained in similar condition since. One-Hour Dry Cleaners operated a dry-cleaning business at 10045 East Estates Drive using tetrachloroethylene (PCE) as a dry-cleaning solvent between the 1960s and 2010, when the dry-cleaning operation converted to using a hydrocarbon-based solvent. We understand that the proposed development for the Property includes 55 high-density residential units (row townhouses).

This assessment included a review of local, state, tribal, and federal environmental record sources, standard historical sources, aerial photographs, fire insurance maps, and physical setting sources. A Property reconnaissance was conducted to observe site use and current conditions, and to check for the storage, use, production, or disposal of hazardous or potentially hazardous materials. Written/oral interviews were conducted with persons knowledgeable about current and past site use.

A review of regulatory databases maintained by county, state, tribal, and federal agencies found no documentation of hazardous materials violations or discharge on the Property and in general, did not identify contaminated facilities within the appropriate ASTM search distances that would reasonably be expected to impact the Property. However, the site reconnaissance and records review found documentation and physical evidence of soil and soil gas impairments associated with the past use of the Property.

Several previous environmental investigations have been conducted to evaluate whether the subsurface has been impacted by the historical use of the Property for agriculture and dry cleaning operations. Soil samples were collected at the Property in 2021 and analyzed for agrichemicals (organochlorine pesticides [OCPs], arsenic, and lead), in addition to other constituents. Soil gas samples were collected and analyzed for volatile organic compounds (VOCs). Soil sampling results suggested that shallow soil had not been impacted by historical agricultural activities.

However, soil and soil gas have been impacted with chlorinated solvents associated with historical dry cleaning operations.

One-Hour Dry Cleaners is listed as an open cleanup program site (Case ID 2023-17s) under the oversight of Santa Clara County Department of Environmental Health (SCCDEH) and is listed on GeoTracker under global ID T10000021095. Several soil, groundwater, soil gas, indoor air, and sub-slab soil gas investigations have been conducted to evaluate the lateral and vertical extents of the PCE plume and human health risks to building occupants. The majority of PCE impacts are within the back alley behind (west of) the former One-Hour Cleaners tenant space, which is 589
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presently vacant. PCE was likely released from dumping mop water out the back door, or leaked from the sanitary sewer. The PCE released at the Property impacts soil and soil gas; there is no indication of free product in the subsurface, and groundwater has not been encountered to the total depth explored (80 feet) during previous investigations. The soil gas plume extends west to the off-site property located at 19620 Stevens Creek Boulevard. The Property owner, Idlewild Tenants in Common (TIC), entered into a voluntary remedial action agreement (RAA) with SCCDEH on July 31, 2023.

Terraphase Engineering Inc. (Terraphase) prepared a Remedial Action Plan (RAP) for the Property dated September 18, 2023. The RAP proposed implementing soil vapor extraction (SVE) to remedy PCE impacts in the vadose zone beneath the Property and neighboring property to the west. The objective of SVE is to reduce the concentrations of PCE and its breakdown products in the subsurface to a level where a vapor barrier equipped with a passive venting system can mitigate indoor air intrusion of PCE at concentrations above residential indoor air environmental screening levels (ESLs)1. The SVE system began operating in June 2024. By December 2024, Terraphase and SCCDEH concluded that SVE had been successful, and that at the current soil gas concentrations, it was appropriate to discontinue active remediation.

The SVE system was shut down in January 2025 to monitor for rebound; however, SCCDEH opined that the soil gas concentrations had not reached equilibrium. An additional extraction well was installed near the northwestern corner of the on-site commercial building and has been operating since April 2025. SVE system operation and rebound testing will continue in accordance with SCCDEH requirements.

In addition to the documented on-site PCE release, several nearby historical gasoline service stations, dry cleaners, and the former Vallco Shopping Mall have been evaluated as potential sources of soil gas impacts at the Property. We have not identified nearby releases likely to pose a current or future vapor intrusion risk to the Property. Furthermore, any soil gas impacts that remain at the Property following SVE operation will be mitigated by the installation of vapor intrusion mitigation systems (VIMS) beneath the planned buildings.

Based on the findings of this assessment, no Historical Recognized Environmental Conditions (Historical RECs) were identified for the Property. The following REC and (future) Controlled REC were identified.
• REC: Former One-Hour Cleaners PCE Releases
 Discharges of PCE from former dry cleaning operations have impacted the Property and off-site property to the west. PCE is present in soil gas and, to a lesser degree, soil, at concentrations exceeding residential and/or commercial ESLs2,3. We understand that Idlewild TIC is responsible for site cleanup prior to transfer of the Property. We recommend continued remediation-related activities of the PCE plume at the Property as appropriate with regulatory oversight.
1 San Francisco Bay Regional Water Quality Control Board (SFBRWQCB); Indoor Air Direct Exposure Human Health Risk Levels (Table IA-1); Residential; January 2019 (Rev. 1). 2 SFBRWQCB; Subslab/Soil Gas Vapor Intrusion: Human Health Risk Levels (Table SG-1); Residential; January 2019 (Rev. 1).
3 SFBRWQCB; Subslab/Soil Gas Vapor Intrusion: Human Health Risk Levels (Table SG-1); Commercial/Industrial; January 2019 (Rev. 1)
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• Future Controlled REC: Institutional Controls/Deed Restriction  Institutional Controls (ICs) will be required following successful completion of SVE. ICs will likely include an access agreement to allow SCCDEH personnel on Site at any time; funding for SCCDEH oversight; restriction of uses of the Property, restriction of modifications to the Property development without SCCDEH approval, and operation maintenance and monitoring (OM&M) and reporting for the VIMS that is expected to be installed under the planned residential units. A corresponding deed restriction would be recorded for the Property to ensure the systems remain operational. When approved, the ICs/deed restriction will represent a controlled REC for the Property.

Based on our review of regulatory databases and observations during the site reconnaissance, we identified the following business environmental risks (BERs), potential environmental concerns (PECs), and/or de minimis conditions. While not considered to be RECs, these features may pose an environmental concern to the Property. We briefly discuss each feature below. • A hazardous building materials survey performed in 2023 identified asbestos-containing materials in the on-site commercial building. The cost of asbestos abatement and disposal is considered a BER.

The following data gap and/or data failure were identified during this assessment. • At the time of report publication, we had not received a response from the Santa Clara County Fire Department (SCCFD).

The data gap and/or data failure identified during this assessment does not affect our conclusions as to the presence of RECs at the Property. We believe that sufficient information has been obtained during our contracted scope of services to evaluate the presence of RECs at the Property. This assessment has revealed evidence of one REC, no Historical RECs, one (future) Controlled REC, and no evidence of significant data gaps, in connection with the Property. We recommend the following.
• The remedial program should be continued under the oversight of SCCDEH. • SVE wells should be destroyed under SCCDEH oversight prior to Property redevelopment. • We recommend engaging a licensed asbestos abatement contractor to develop an asbestos abatement plan and remove asbestos-containing materials prior to building demolition.

We have performed a phase I environmental site assessment of the Property in general conformance with the scope and limitations of ASTM E1527-21 and the standards and practices of the AAI Final Rule (40 CFR Part 312). Any exceptions to, or deletions from this practice are described in Sections 7.0 and 9.0 of the report.

Please note, the findings from this report are valid until May 9, 2026, one year from the earliest dates of the following components: interviews, review of government records, visual inspections, and declaration of environmental professional. Updates of portions of the assessment may be necessary after a period of 180 days from the earliest date of the above components (November 5, 2025).
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1.0 INTRODUCTION

1.1 PURPOSE OF PHASE I ENVIRONMENTAL SITE ASSESSMENT
This phase I ESA was performed at the request of Toll Brothers, Inc., the User, for the purpose of environmental due diligence during property acquisition. The objective of this phase I ESA is to identify RECs associated with the Property. As defined in the ASTM Standard Practice E1527-21, a REC is:
(1) the presence of hazardous substances or petroleum products in, on, or at the subject property due to a release to the environment; (2) the likely presence of hazardous substances or petroleum products in, on, or at the subject property due to a release or likely release to the environment; or (3) the presence of hazardous substances or petroleum products in, on, or at the subject property under conditions that pose a material threat of a future release to the environment.

ASTM Standard Practice E1527-21 provides that identified RECs can be evaluated and classified into Controlled RECs or Historical RECs based on the following definitions.

A Controlled REC is defined as:
…a REC affecting the subject property that has been addressed to the satisfaction of the applicable regulatory authority or authorities with hazardous substances or petroleum products allowed to remain in place, subject to implementation of required controls (for example, activity and use limitations, institutional controls, or engineering controls).

A Historical REC is defined as:
…a previous release of hazardous substances or petroleum products affecting the subject property that has been addressed to the satisfaction of the applicable regulatory authority or authorities and meeting unrestricted use criteria established by the applicable regulatory authority or authorities, without subjecting the property to any controls (for example, activity and use limitations or other property use limitations).

In addition, while not necessarily related to those environmental issues required to be investigated in this practice, a BER is defined as:

A risk which can have a material environmental or environmentally-driven impact on the business associated with the current or planned use of commercial real estate.

A de minimis condition is defined as:

A condition related to a release that generally does not present a threat to human health or the environment and that generally would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies. 592
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1.2 USER-PROVIDED INFORMATION
ASTM Standard Practice E1527-21 describes responsibilities of the User, Toll Brothers, Inc., to complete certain tasks in connection with the performance of AAI into the Property. We requested that the User provide the following documents and information:
• Previous environmental reports (Section 3.0)
• Preliminary Title Report (Section 4.1.1)
• User questionnaire and/or interview (Section 6.0)

1.3 DETAILED SCOPE OF SERVICES
The scope of services performed included the following. • A review of previous environmental reports prepared for the Property provided to us and/or readily available.
• A review of publicly available and practicably reviewable standard local, state, tribal, and federal environmental record sources.
• A review of publicly available and practicably reviewable standard historical sources, aerial photographs, fire insurance maps, and physical setting sources. • A Property reconnaissance to observe site use and current conditions, and storage, use, production, or disposal of hazardous or potentially hazardous materials. • Written/oral interviews with owners/occupants and public sector officials, as needed. • Preparation of this report with our findings, opinions, and conclusions.

1.4 NON-SCOPE SERVICES
No non-scope services were performed in conjunction with this assessment.

1.5 SITE LOCATION AND DESCRIPTION
The Property is located at 19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive, Cupertino, California (Figures 1 and 2). The approximately

2.7-acre Property is identified as APNs 369-06-002, 369-06-003, and 369-06-004 (Figure 3) and is currently occupied by the following tenants.

TABLE 1.5-1: Current Site Occupants

ADDRESS OCCUPANT
19590 Stevens Creek Boulevard House of Falafel
19610 Stevens Creek Boulevard Soon’s Beauty Salon
10025 East Estates Drive Vacant (former watch repair shop) 10045 East Estates Drive Vacant (former One-Hour Dry Cleaners) 10051 East Estates Drive Vacant (former Joyheart Cupertino Chinese grocery store) 10055 East Estates Drive Vacant (former Le Caprice, Boutique and fine tailoring) 10065 East Estates Drive Vacant (former Computer 4 Kids Green Apple Education) 10071 East Estates Drive Vacant (former Mongkol and Sons Collision) 10075 East Estates Drive United Furniture Club
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1.6 CURRENT USE OF PROPERTY AND ADJOINING PROPERTIES
The Property is currently a commercial shopping center with some active businesses. The majority of the tenant spaces are vacant. However, the Property is zoned as a general commercial, planned residential development (P[CG, R4]), which permits high, very high, and highest density multiple-family residential uses. We understand that the proposed development for the Property will include 55 high-density residential units (row townhouses).

Based on a review of current records and observations during our site reconnaissance, the adjoining site uses are summarized below.

TABLE 1.6-1: Adjoining Site Uses

DIRECTION SITE USE
North Stevens Creek Boulevard and former Vallco shopping center South Single-family residential neighborhood
East East Estates Drive, gasoline service station/tire repair shop, restaurant, and medical offices
West Commercial shopping center

2.0 PHYSICAL SETTING

2.1 TOPOGRAPHY, GEOLOGY, AND HYDROGEOLOGY
According to published topographic maps, the Property is relatively level and is situated at approximately Elevation 200 feet (NAVD88). Review of the Geologic Map of the Cupertino and San Jose West Quadrangles, Santa Clara and Santa Cruz Counties (Dibblee and Minch, 2007) found that the Property is underlain by Holocene-aged surficial sediments (Qa.1) consisting of alluvial fan deposits (fine-grained sand, silt, and gravel).

Groundwater has not been encountered on site during previous environmental explorations.

Groundwater is likely present at the Property at depths greater than 100 feet below the ground surface (bgs) (Path Forward Environmental Engineering and Geology, 2021b). Therefore, we reviewed the following sources for groundwater depth and flow direction records for the Property and nearby facilities.
• The Geocheck – Physical Setting Source Summary of the Environmental Data Resources, Inc. (EDR) Radius Map Report (Appendix A)
• The Department of Water Resources (DWR) Online Water Data Library website (California DWR, n.d.)
• EnviroStor, a website maintained by the State of California Department of Toxic Substances Control (DTSC, n.d.)
• GeoTracker, a website maintained by the State of California Water Resources Control Board (SWRCB, n.d.)
The Geocheck – Physical Setting Source Summary indicated that one Federal United States Geological Survey (USGS) well and 56 state wells are located within 1 mile of the Property. The DWR website did not identify any wells within 1 mile of the Property. The following information was obtained regarding local groundwater conditions.
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TABLE 2.1-1: Local Groundwater Conditions

FACILITY/WELL NAME

DISTANCE AND

DIRECTION FROM

PROPERTY

REPORTED

GROUNDWATER
DEPTH

REPORTED

GROUNDWATER FLOW

DIRECTION
Tosco #11220 150 feet east 70.86 to 93.06 feet Northeast 19720 Stevens
Creek Boulevard 460 feet west 80 feet Northeast
The site-specific groundwater depth and flow direction were not determined as part of this assessment. Fluctuations in groundwater levels may occur seasonally and over a period of years due to variations in precipitation, temperature, irrigation, and other factors.

2.2 OIL AND GAS
We reviewed the Department of Conservation (DOC), Geologic Energy Management (CalGEM) website and map database to determine if any historical oil and/or gas wells were located within or near the Property (CalGEM, n.d.). No oil or gas wells were mapped on or within 1 mile of the Property.

We reviewed the United States Department of Transportation, Pipeline and Hazardous Materials Safety Administration (USDOT-PHMSA) National Pipeline Mapping System (NPMS) public viewer website for information about petroleum, natural gas, or hazardous liquid storage, processing, or transmission facilities in the vicinity of the Property (USDOT-PHMSA, n.d.). No facilities were mapped on or within ¼ mile of the Property. An active natural gas pipeline maintained by PG&E is located along Stevens Creek Boulevard, along the northern Property boundary. This pipeline would not be expected to pose an environmental concern to the Property.

2.3 INDOOR AIR QUALITY
An evaluation of indoor air quality, mold, or radon was not included as part of the contracted scope of services. The California Department of Public Health (DPH) has conducted studies of radon risks throughout the state, sorted by zip code (California DPH, 2016). Results of the studies indicate that 93 tests have been conducted within the Property zip code, with four tests exceeding the current USEPA action level of 4 picocuries per liter (pCi/L).

As part of this assessment, we conducted a Tier 1 Vapor Encroachment Screen (VES) for the Property in general accordance with ASTM E2600-22 Standard Guide for Vapor Encroachment Screening on Property Involved in Real Estate Transactions (ASTM International, 2022). The purpose of the VES is to evaluate whether a vapor encroachment condition (VEC) exists at the Property. A VEC represents the presence of likely presence of vapor-forming compounds (VFCs) in the vadose zone of the Property caused by the release of vapors from contaminated soil and/or groundwater either on or near the Property. We did not identify any on-site releases of petroleum hydrocarbons, but we note that the fuel constituent benzene has been detected in soil gas at the Property (refer to Section 3.0). Additionally, the former on-site dry cleaner is a source of chlorinated VOC impacts in soil and soil gas which creates a VEC for the Property. We also identified several potential petroleum hydrocarbon sources of vapor intrusion within 1/10 mile of the Property and VOC sources within 1/3 mile of the Property: Former Vallco Shopping Center (petroleum hydrocarbon and VOC source; 10123 North Wolfe Road); two gasoline service stations (petroleum hydrocarbon sources; 19550 and 19480 Stevens Creek Boulevard); and two dry cleaners (VOC sources; 19720 and 19705 Stevens Creek Boulevard). These sites are further 595
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discussed in Section 4.3.2 and after further review, are not believed to pose a current vapor intrusion risk to the Property.

3.0 PREVIOUS ENVIRONMENTAL REPORTS
The Property was used for agriculture between 1939 and 1956. The existing commercial building was constructed at the Property in 1960. One-Hour Dry Cleaners operated at the Property using PCE as a dry-cleaning solvent between the 1960s and 2010, when the dry-cleaning operation converted to using a hydrocarbon-based solvent. The dry cleaner was identified as an environmental concern during a phase I ESA conducted by Path Forward Environmental Engineering and Geology (Path Forward, not available for ENGEO’s review). The phase I ESA also identified potential environmental contamination from OCPs and metals associated with the former agricultural use of the Property.

This facility is listed as an open cleanup program site (case ID 2023-17s) under the oversight of SCCDEH, and is listed on GeoTracker under global ID T10000021095. Previous environmental investigations are summarized below.

Path Forward Environmental Engineering and Geology. 2021a. DRAFT Subsurface Investigation Report, Cupertino Retail Center, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. August 6, 2021.

Path Forward conducted a phase II environmental site assessment (phase II ESA) for the Property in June 2021, to evaluate shallow soil and soil gas conditions for environmental due diligence purposes in support of the planned redevelopment of the Property. The objective was to evaluate shallow soil impacts associated with the former agricultural operations at the Property and evaluate soil gas impacts from the former dry cleaner.

The scope of the investigation included the advancement of seven soil borings (B1 through B7) to a maximum depth of 15.5 feet below the ground surface (bgs). Soil samples were collected at

1.0 and 2.5 feet. Temporary soil gas probes were installed at depths of 5 and 15 feet bgs in the back alley and around the property boundary, and soil gas samples were collected. A total of 14 soil samples were analyzed for total petroleum hydrocarbons (TPH) as gasoline, diesel, and motor oil (TPH-g, TPH-d, and TPH-mo), VOCs, semi-volatile organic compounds (SVOCs), California Assessment Manual (CAM) 17 Metals, OCPs, polychlorinated biphenyls (PCBs), and asbestos. A total of 14 soil gas samples were analyzed for VOCs and fixed gases.

Soil results were compared to the San Francisco Bay Regional Water Quality Control Board’s (SFBRWQCB’s) residential ESLs4. Arsenic results were compared to the naturally occurring background concentration of 11 milligrams per kilogram (mg/kg)5. The soil results indicated that PCE and 4,4’-DDT were detected in several samples above laboratory reporting limits but below residential ESLs. None of the arsenic concentrations in the samples exceeded 11 mg/kg. The OCP and arsenic results suggested that the Property had not been adversely impacted by historical agricultural activities. TPH, SVOCs, metals, PCBs, and asbestos were either not detected above laboratory reporting limits or were detected below the ESLs. 4 SFBRWQCB; Environmental Screening Levels (ESLs); Direct Exposure Human Health Risk Levels: Residential Shallow Soil Exposure (Table S-1); 2019 (Rev. 2).
5 Duverge, D.J., Establishing Background Arsenic in Soil of the Urbanized San Francisco Bay Region, December 2011. 596
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Soil gas results were compared to the SFBRWQCB’s residential subslab/soil gas vapor intrusion human health risk levels6 with an attenuation factor of 0.03. The results indicated that PCE was detected above the ESL of 15 micrograms per cubic meter (µg/m3) in six samples, at concentrations ranging between 17 µg/m3 and 20,000 µg/m3. The maximum concentration was detected in B3 at 15 feet bgs. Chloroform was also detected above the residential ESL of

4.0 µg/m3in Sample B7 at 5 feet (5.7 µg/m3). Several samples also exceeded the commercial ESL7 of 67 µg/m3for PCE. Path Forward calculated the cumulative vapor intrusion cancer risks and noncancer hazard indices for each soil gas sample. The highest estimated cancer risk was estimated to be 1.3x10-3in Sample B3 at 15 feet, above the 1 to 100 per million (1×10-6to 1×10-4) risk management range. The highest estimated non-cancer index was estimated to be 14, above the threshold value of 1.

Path Forward concluded that the extent of PCE in soil gas is mostly limited to the northwestern portion of the Property, and noted that based on the cancer risk, a response action (vapor mitigation and/or source remediation) was warranted. Path Forward recommended that groundwater samples should be collected near the locations of elevated soil gas concentrations to assess if PCE has impacted groundwater; and that the risk to current occupants from PCE vapor intrusion should be evaluated. Path Forward recommended that the Property owner submit the report to the local regulatory agency for review.

Path Forward Environmental Engineering and Geology. 2021b. DRAFT Additional Investigation Report, Cupertino Retail Center, 10025-10075 E Estates Drive and 19610 Stevens Creek Boulevard, Cupertino, California. October 1, 2021.

Path Forward conducted an additional investigation in September 2021 to characterize subsurface conditions and determine if PCE had impacted groundwater. The scope of the investigation included the advancement of three borings (B8, B9, B9A) along the northern portion of the Property (B9A was a step-out boring advanced due to refusal at B9). Path Forward additionally reviewed off-site (downgradient) soil gas data. During drilling, borings were screened for VOCs using a photoionization detector (PID).

During the investigation, the highest PID readings were detected in Boring B8 at 15 feet bgs and decreased with depth. Path Forward opined that a secondary PCE source in groundwater was unlikely to be present based on this trend. All borings encountered refusal between 72 and 97 feet bgs, and did not encounter groundwater.

During their evaluation of off-site properties, Path Forward reviewed available data for the Vallco Shopping Mall. Details regarding this site are discussed in Section 4.3.2.

Path Forward concluded the following.
• Shallow groundwater is not present within the upper 100 feet of the Property. • Based on PID results and off-site deep soil gas samples, a secondary source of PCE is unlikely to be present at depth.
6 SFBRWQCB; Subslab/Soil Gas Vapor Intrusion: Human Health Risk Levels (Table SG-1); Residential; January 2019 (Rev. 1).
7 SFBRWQCB Subslab/Soil Gas Vapor Intrusion: Human Health Risk Levels (Table SG-1); Commercial/Industrial; January 2019 (Rev. 1)
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• The presumed downgradient extent of PCE at the Property is generally defined by off-site data collected during investigations of the former Vallco Mall.

Path Forward Environmental Engineering and Geology. 2022. DRAFT Regulatory Path for Remediation, Cupertino Retail Center, 10025-10075 E Estates Drive and 19610 Stevens Creek Boulevard Cupertino, California. Memorandum from David A Grunat, P.G., C.H.G. (Path Forward) to Deke Hunter (Hunter Storm, LLC). February 25, 2022.

Path Forward provided a memorandum dated February 25, 2022, to summarize previous environmental investigations conducted at the Property and to provide a summary of the anticipated regulatory path for remediation present at the Property.

Path Forward recommended that results of previous investigations be presented to an appropriate regulatory agency for review and development of next steps. Path Forward recommended SCCDEH as the most appropriate regulatory agency, as SCCDEH was currently overseeing two adjacent PCE release sites (Vallco Town Center and 19720 Stevens Creek Boulevard). Path Forward noted that additional site characterization would likely be required.

Path Forward indicated that as the Property was anticipated to undergo redevelopment, it is likely that the most appropriate and financially efficient remedial action would be the excavation of approximately 1,200 cubic yards of contaminated soil following building demolition. Excavated soil would be loaded directly into haul trucks and transported to an appropriate disposal facility.

Soil samples would be collected to confirm that the remedial excavation successfully removed the PCE-impacted soil.

Path Forward also indicated that residual PCE in soil gas would likely remain present for some time until it could naturally attenuate below regulatory action levels. During that period, the SCCDEH could require ongoing monitoring of soil gas to demonstrate that concentrations are decreasing following the excavation. Additionally, buildings constructed in this area would require VIMS incorporated into the building slabs, which would require ongoing OM&M. Finally, a deed restriction for the Property that includes ongoing OM&M would likely be required to ensure the systems remained operational.

Terraphase Engineering. 2022a. Indoor Air and Soil-Gas Sampling Results, 10025, 10045, and 10051 East Estates Drive, Cupertino, California. May 11, 2022.

Terraphase Engineering (Terraphase) conducted an investigation of the Property in April 2022 to evaluate the vapor intrusion risk in the former dry cleaner, watch repair shop, and current Chinese grocery store. The scope of the investigation included the collection of indoor air and sub-slab soil gas samples from three units: the dry cleaner (10045 East Estates Drive), watch repair shop (10025 East Estates Drive), and Chinese grocery store (10051 East Estates Drive).

Results of the indoor air samples were compared to the SFBRWQCB commercial/industrial indoor air ESLs8. The results indicated that PCE was not detected above the ESL of 2 µg/m3. However, benzene was detected above the indoor air ESL of 0.42 µg/m3in the sample collected from the former watch repair shop (1.4 µg/m3). Terraphase concluded that the detection of benzene was not likely due to vapor intrusion; rather, more likely due to in-house chemicals. 8 SFBRWQCB; Indoor Air Direct Exposure Human Health Risk Levels (Table IA-1); Commercial/Industrial; January 2019 (Rev. 1).
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The sub-slab soil gas results were compared to the sub-slab/soil gas commercial ESLs. The PCE concentrations reported in the samples collected from the former watch repair shop, dry cleaner, and just outside the Chinese grocery store were 120 µg/m3, 79 µg/m3, and 99 µg/m3,respectively.

All concentrations exceeded the commercial/industrial soil gas ESL of 67 µg/m3.

Terraphase provided the following conclusions.
• The PCE release only impacts soil and soil gas. The bulk of PCE is present within the back alley. PCE was likely released from dumping mop water out the back door or leaked from the sanitary sewer.
• The PCE detections in the soil samples collected at 1 foot and 2.5 feet bgs from Boring B4 (Path Forward, 2021a), located in the far northern end of the site adjacent to Stevens Creek Boulevard, likely represent a sewer leak or migration through utility trench bedding sand. • Terraphase agreed with Path Forward that it is unlikely for PCE to impact groundwater due to the depth to groundwater and clay layers encountered during Path Forward’s previous investigation between 25 to 80 feet in B8 and 45 to 65 feet in B9 (Path Forward, 2021a).

At the time of publication of Terraphase’s report, the former dry cleaner and watch repair shop had been vacated; hence, there was no risk at the time. Terraphase provided the following recommendations.
• Terraphase recommended that epoxy coating should be installed on the concrete slabs in the former dry cleaner and watch repair shop if the dry cleaner and watch repair shop units were to be occupied in the future. The PCE detection in the grocery store (0.13 µg/m3) represented a risk of 7×10-8 under a commercial/industrial scenario. • Terraphase disagreed with Path Forward’s conclusion that PCE could be remediated by excavation of 1,222 cubic yards of soil. Terraphase noted that the vertical extent of contamination was not sufficiently delineated; the 15-foot samples collected during Path Forward’s 2021 investigation reported higher PCE concentrations than the shallow samples.

If remedial action was warranted, Terraphase recommended SVE, which was more cost effective.
• Terraphase noted that the need for remediation was questionable, as the threat to groundwater was minimal, and the pathway between future residential receptors and impacted soil could be eliminated (based on site development plans included on the figures in Path Forward’s (2021b) report, which showed the bulk of the impacted soil would be beneath parking lots). Terraphase noted that based on the extent of the plume, vapor barriers may need to be installed beneath Buildings 1 and 3 of the proposed development; however, extensive remedial actions did not appear to be warranted. • The highest concentration of PCE detected in soil gas at the Vallco site was 5,890 µg/m3in sample SV-14N. Terraphase noted that it is highly unlikely that the PCE release at the Property crossed Stevens Creek Boulevard and impacted the Vallco site. As groundwater was not a potential pathway, the PCE would have to reach the Vallco site through either soil gas migration or a preferential pathway. Based on the demonstrated attenuation of PCE in soil gas between the release area (behind the dry cleaner) and samples collected at the north of the Property, it was unlikely that PCE could migrate in soil gas across Stevens Creek Boulevard at the concentrations observed. Additionally, Terraphase concluded that transport through the sanitary sewer was unlikely, as the Property sanitary sewer drains to a 12-inch sewer main in Stevens Creek Boulevard that drains to the east, away from the Vallco site. 599
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Terraphase. 2022b. Soil-Gas Investigation Report, 10025-10075 East Estates Drive, Cupertino, California; August 16, 2022.

Terraphase conducted an additional investigation in July 2022 to evaluate the current concentrations at the former dry cleaner unit and the extent of PCE migration in soil gas. The scope of the investigation included installation and sampling of three permanent and one temporary nested soil vapor probes in the former dry cleaner unit, near the western site boundary, and on the adjacent property to the west. Two triple-depth nested borings (B-11 and B-12) were installed with probe depths of 5, 15, and 25 feet bgs in the alley behind the dry cleaner. One dual-depth nested boring (B-10) was installed within the dry cleaner with probe depths of 5 and 10 feet bgs. One temporary dual-depth nested boring (B-13) was installed on the neighboring site to the west of the Property with probe depths of 7 and 10 feet.

The sample results indicated that the highest concentration of PCE detected was 30,000 µg/m3 in the 10-foot sample collected from inside the former dry cleaner (B-10). The PCE concentrations from samples collected in the back alley were consistent with Path Forward’s previous results.

PCE was non-detect in the 25-foot sample collected from Boring B-12; however, the 25-foot sample collected from Boring B-11 contained a PCE concentration of 5,700 µg/m3.

Terraphase concluded that PCE had migrated through the sand in most of the borings between 15 and 25 feet bgs to the adjacent property to the west. PCE was detected in the 15-foot sample collected from B-13 at a concentration of 7,100 µg/m3. However, the shallow PCE concentration within sample B-13 was below commercial screening levels.

Terraphase concluded that the PCE released at the Property impacts only soil and soil gas; there is no indication of free product in the subsurface. PCE had migrated westward beneath the adjacent commercial property at concentrations above the commercial ESLs; however, Terraphase noted that ESLs are intended to be conservative. Terraphase recommended that SVE be implemented to remediate soil vapor concentrations on site and off site. Terraphase recommended a 300-cubic-feet-per-minute SVE system. Terraphase also opined that removal of impacted soil is not economically feasible, as the impacts extend to 25 feet bgs.

Terraphase. 2022c. Soil-Vapor Investigation and Soil-Vapor Extraction Pilot Test Report, 10025-10075 East Estates Drive, Cupertino, California; September 6, 2022.

Terraphase prepared an additional investigation report dated September 6, 2022, to summarize the previous investigations conducted by Path Forward and Terraphase, and to provide recommendations for additional sampling. The report also includes a work plan for additional soil gas investigations at the neighboring property and a pilot scale test of SVE at the Property.

Terraphase noted that although the levels of contamination may not, under a risk-based analysis, require remediation, the Property owner has decided to conduct remediation because the Property is for sale and because the soil gas plume extends beneath the neighboring property to the west. The following scopes of work were recommended as part of the work plan.

Additional Air Sampling
Terraphase recommended that three indoor air samples and one outdoor ambient air sample be collected from the neighboring building to the west of the Property (19620 Stevens Creek Boulevard). Prior to sampling, the building would be screened for indoor air sources and a building survey form would be completed.
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Additional Nested Soil Gas Monitoring Point Installation and Sampling Terraphase recommended that three permanent, triple-nested soil vapor monitoring wells (B-14 through B-16) be installed at the neighboring property to the west of the Property, to facilitate the collection of soil gas samples and for monitoring of vacuum responses during SVE pilot testing to evaluate the effective vacuum radius of influence.

SVE Pilot Test Program
Terraphase proposed a SVE pilot test to evaluate the effectiveness of SVE as a remedy to reduce concentrations of PCE in soil gas at the Property and neighboring site to the west, to below the commercial/industrial ESLs, and to evaluate SVE design parameters useful for full-scale design and technical feasibility under site-specific conditions. The proposed scope of the SVE pilot test included installing one, 6-inch-diameter PVC SVE extraction well near the back door of the dry cleaner. The well would be screened in a layer of gravel from 13 to 23 feet bgs, and soil vapor would be extracted to evaluate several SVE parameters.

Terraphase. 2023a. Soil-Vapor Extraction Pilot-Scale Test Work Plan, 10025, 10045, and 10051 East Estates Drive, Cupertino, California. June 20, 2023.

Terraphase prepared a work plan for an SVE pilot-scale study dated June 20, 2023. The work plan expanded upon the recommendations provided in the pilot test report (Terraphase, 2022c).

The scope of work completed is discussed below.

Terraphase. 2023b. Preliminary Results of the Soil Vapor Extraction Pilot Test Conducted at the Idlewild Shopping Center, 10025-10075 East Estates Drive, Cupertino, California. August 4, 2023.

Terraphase prepared a technical memorandum to summarize the preliminary results of the pilot-scale SVE test. Terraphase conducted a 120-hour pilot-scale test of SVE in the alleyway behind the former dry cleaner between July 18 and July 23, 2023.

Terraphase installed the extraction well, SVE-01, in the alleyway. The well contained a 4-inch-diameter pipe screened between 7 and 23 feet bgs. A trailer-mounted SVE system was installed across the alley from SVE-01. The system is equipped with a variable frequency drive (VFD) controlling a blower capable of producing an air maximum flow rate of 190 standard cubic feet per minute at 190.5 inches of water column (in H2O)/14 inches of mercury (in Hg) vacuum.

The off-gases from the SVE well are scrubbed in two 300-pound canisters of granular activated carbon (GAC) arranged in series.

The soil gas concentrations generally indicated that PCE concentrations decreased in each well.

As part of the off-site investigation, Terraphase installed two Vapor Pins (SV-7 and SV-8) in the sidewalk adjacent to the building of the Property, approximately 70 feet from SVE-01. The PCE results were non-detect for SV-7 and 11 µg/m3for SV-8.

Terraphase. 2023c. Remedial Action Plan, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. September 18, 2023.

Terraphase prepared a RAP for the Property. The purpose of the RAP was to remedy PCE impacts in the vadose zone beneath the Property and neighboring property to the west. The objective was to reduce the concentrations of PCE and its breakdown products in the subsurface 601
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to a level where a vapor barrier equipped with a passive venting system can mitigate indoor air intrusion of PCE at concentrations above residential indoor air ESLs, when combining the total risk from each detected compound in shallow soil gas. The initial remedial goal was to reduce PCE concentrations to below 460 µg/m3in shallow soil gas, based on an attenuation factor of 1,000 for a vapor barrier and passive venting system.

Terraphase noted that the radius of influence (ROI) determined in the SVE pilot study was 80 feet.

Given this effective radius, the pilot-scale SVE system would be able to reach the known extents of the VOC plume under the Property and neighboring property to the west.

The preliminary remedial design included the following: permitting requirements, an OM&M plan, summary of design details, performance monitoring metrics, system shutdown conditions, and contingency actions. Terraphase also noted that ICs would be required following completion of SVE. ICs will likely include the following.
• An access agreement to allow SCCDEH personnel on site at any time. • Funding for SCCDEH oversight.
• OM&M and reporting for the vapor barrier that is expected to be installed under the planned residential units.

ENGEO. 2023a. Phase I Environmental Site Assessment, Idlewild Shopping Center, 19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive, Cupertino, California. October 25, 2023. Project No. 22934.000.001.

We prepared a phase I ESA for the Property dated October 25, 2023. At the time of the assessment, the Property consisted of an approximately 41,000-square-foot commercial building and associated parking and landscaped areas.

Based on the findings of the assessment, no Historical RECs were identified for the Property. The following REC and (future) Controlled REC were identified:
• REC: Former One-Hour Cleaners PCE Releases
 Discharges of PCE from former dry cleaning operations have impacted the Property and off-site property to the west. PCE is present in soil gas and, to a lesser degree, soil, at concentrations exceeding residential and/or commercial ESLs. We understand that Idlewild TIC is responsible for site cleanup prior to transfer of the Property. We recommended continued remediation-related activities of the PCE plume at the Property as appropriate with regulatory oversight.
• Future Controlled REC: Institutional Controls/Deed Restriction  ICs will be required following successful completion of SVE. ICs will likely include an access agreement to allow SCCDEH personnel on Site at any time; funding for SCCDEH oversight; and OM&M and reporting for the vapor barrier that is expected to be installed under the planned residential units. A corresponding deed restriction would be recorded for the Property to ensure the systems remain operational. When approved, the ICs/deed restriction will represent a Controlled REC for the Property.

Based on our observations during the site reconnaissance, we also identified the following PEC, not considered to be a REC.
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• During the site reconnaissance, several wells observed were missing bolts or gaskets. The Property owner should be alerted, and these features should be repaired to maintain the integrity of the wells and ensure that they do not act as a pathway for stormwater to enter the subsurface.

We recommended the following.
• The proposed remedial program should be continued under the oversight of SCCDEH. • Wells with missing bolts and gaskets should be repaired to maintain the integrity of the wells and ensure that they do not act as a pathway for stormwater to enter the subsurface.

ENGEO. 2023b. Environmental Peer Review, Idlewild Shopping Center, 19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive, Cupertino, California. November 30, 2023. Project No. 22934.000.001.

We prepared an environmental peer review of previous environmental reports for the Property dated November 30, 2023, and provided review comments. We generally agreed with the findings stated in Path Forward’s and Terraphase’s reports, including the characterization of PCE impacts and the conclusion that former dry cleaning activities likely had not affected the former Vallco site.

We disagreed with excavation as a sole remedy but supported Terraphase’s recommendation for SVE and targeted soil excavation(s).

We noted that benzene had been detected in soil gas above the residential ESLs and noted that SCCDEH may consider benzene a contaminant of concern. We also noted that indoor air sampling had not been completed at the neighboring property as recommended, and requested clarification.

The SVE pilot test lacked key data, and we recommended including boring logs, operational metrics, and updated plume maps. We also advised further soil sampling to define the depth of PCE impacts to soil and assess sewer line contributions.

We also questioned the proposed remediation timelines and suggested clarifying the SVE operational schedule and regulatory review periods. Lastly, we noted that SCCDEH may require site-specific attenuation factors and active VIMS, and we agreed that institutional controls and a deed restriction will likely be needed post-remediation.

Terraphase. 2024a. Technical Memorandum, Idlewild Soil Vapor Extraction (SVE) System Status Update. August 12, 2024.

Terraphase prepared a status update of the SVE system that began operating in June 2024.

Terraphase reported that concentrations of PCE in the SVE well influent had decreased by more than a factor of 10 since operation began. PCE concentrations in the monitoring wells had similarly decreased. Terraphase concluded that the system was operating effectively. 603
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Terraphase. 2024b. Soil Vapor Extraction Operations, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. December 4, 2024.

Terraphase prepared a report on SVE system progress which included the following. • A gridded soil sampling program in the former dry cleaner in September 2023. • The installation of one new soil gas monitoring point (B-14). • Six rounds of soil gas/SVE system monitoring.

Terraphase concluded the following:
• No significant “hot spot” of PCE was identified in soil beneath the former dry cleaning tenant space. The source of PCE in soil vapor at the Property was likely incidental releases of mop water containing PCE released to the environment through leaks in the sanitary sewer. • The extent of PCE in soil vapor has been adequately characterized in all directions from the likely release location. The depth of PCE impacts has been adequately characterized. • The SVE remediation has been successful. Concentrations of PCE in soil gas have fallen by almost two orders of magnitude at location B-10 inside the former dry cleaner unit. Other monitored locations throughout the radius of influence have also seen significant reductions.

Terraphase concluded that at the current soil gas concentrations, it was appropriate to discontinue active remediation. Residual PCE concentrations would be managed through the mitigation measures planned for the future Property development. • Terraphase recommended discontinuing the SVE system and initiating rebound testing to assess if the effect of SVE on the PCE concentrations in the subsurface was permanent.

SCCDEH. 2025a. Letter, One-Hour Dry Cleaners, 10045 East Estates Dr., Cupertino, CA 95014, APN: 369-06-22. Site Cleanup Program Case No. 2023-17s, GeoTracker ID No. T10000021095.

January 17, 2025.

SCCDEH issued a letter to the Property owner summarizing their review of Terraphase’s (2024b) report. SCCDEH agreed it was acceptable to discontinue the SVE system operation and initiate rebound testing but required changes to the scope of testing.

Terraphase. 2025. One-Month Soil-Vapor Extraction (SVE) Rebound Testing Report, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. March 12, 2025.

The SVE system was shut down on January 23, 2025, to monitor for rebound. Terraphase prepared a report to summarize the rebound testing results. Terraphase noted that in general, PCE concentrations had stabilized in the wells sampled. Terraphases noted that Idlewild TIC was not requesting site closure at the time. The future housing developer would be installing VIMS under the future structures and would continue to monitor the subsurface under SCCDEH oversight. Terraphase opined that PCE concentrations in the subsurface were well below levels where a properly installed VIMS would protect future site occupants. Terraphase also recommended abandonment of the sanitary sewer behind the former dry cleaner and opined that this would remove residual PCE source material.
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Terraphase opined that the SVE system had removed as much PCE mass from the subsurface as was practical, and recommended decommissioning the SVE system, as continued operation was unlikely to result in significant further removal from the subsurface.

SCCDEH. 2025b. Letter, One-Hour Dry Cleaners, 10045 East Estates Dr., Cupertino, CA 95014, APN: 369-06-22. Site Cleanup Program Case No. 2023-17s, GeoTracker ID No. T10000021095.

April 3, 2025.

SCCDEH issued a letter summarizing their review of Terraphase’s (2025) report. SCCDEH did not agree with Terraphase’s recommendation that the SVE system could be shut down because they did not believe that the soil gas concentrations had reached equilibrium. SCCDEH opined that in order to demonstrate that the soil gas concentrations had reached equilibrium, the rebound monitoring period should be at least 6 months.

On March 31, 2025, SCCDEH received an email from Terraphase stating that the SVE system would be restarted and an additional SVE well would be installed and connected to the existing system. SCCDEH noted that this decision was counter to Terraphase’s previous conclusions and recommendations. SCCDEH required quarterly remediation progress reports documenting the operational parameters of the system.

We note that the SVE system was restarted on April 4, 2025. During our reconnaissance of the Property on June 3, 2025, we observed the second SVE well and operation of the SVE system.

As of the publication of this report, no additional reports documenting the SVE progress or sampling results have been uploaded to GeoTracker.

4.0 RECORDS REVIEW

4.1 PROPERTY RECORDS

4.1.1 Title Report/Ownership
ASTM Standard Practice E1527-21 requires a review of title records dating back to 1980. A Preliminary Title Report (PTR) lists recorded land title details, ownership fees, leases, land contracts, easements, liens, deficiencies, and other encumbrances attached to or recorded against a property. Laws and regulations pertaining to land trusts vary from state to state and the detail of information presented in a PTR can vary greatly by jurisdiction. As a result, we utilize a PTR, when provided to us, as a supplement to other historical record sources. We assume that any environmental liens, activity and use limitations (AULs), deed restrictions, and/or institutional controls for the Property are noted in the PTR.

A PTR for the Property, prepared by Chicago Title Company and dated May 29, 2025, was provided for our review. The Property title is vested in the following entities: Joseph Nacy Castello; Rosalie Castello Flores; Tamara M. Foglesong; Jennifer Castello; Rick Costello II; Victor M.

Castello; Gina C. Wagner; Geno I. Castello and Victoria M. Castello; Rosalyn J. Castello; Ryan Andersen; Cara Clover Borromei; Danica Cavigliano; and Nicolas Cavigliano.

No references to environmental liens, AULs, deed restrictions, and/or institutional controls were noted. However, the PTR states that there are three monitoring wells located on the Property with no recorded agreements. Several soil gas extraction and monitoring wells associated with SVE 605
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are located on the Property. These wells should be destroyed prior to Property redevelopment.

This report is included in Appendix B.

4.1.2 Environmental Liens and Activity and Use Limitations The PTR did not identify environmental liens or AULs associated with the Property. In addition, a questionnaire completed by the User (Appendix C) indicated that they are not aware of any environmental cleanup liens recorded against the Property.

We reviewed two engineering control (EC) and IC registries for environmental liens or AULs associated with the Property: EnviroStor, a website maintained by DTSC, and GeoTracker, a website maintained by SWRCB. No records of environmental liens or AULs were noted. However, we anticipate that a deed restriction will be recorded on the Property following completion of SVE and installation of VIMS.

4.2 HISTORICAL RECORD SOURCES
The purpose of the historical record review is to identify uses or occupancies of the Property and surrounding areas that are likely to have led to RECs on the Property.

4.2.1 Historical Topographic Maps, Aerial Photographs, and Sanborn Maps We reviewed historical USGS topographic maps and aerial photographs for discernible changes to the Property. EDR provided the following maps and photographs, presented in Appendices D and E. No Sanborn fire insurance maps were available for the Property; the search report is presented in Appendix F.

TABLE 4.2.1-1: Historical Review Summary

HISTORICAL MAP/PHOTOGRAPH YEARS
Topographic Maps 1897, 1899, 1902, 1943, 1947, 1948, 1953, 1961, 1968, 1973, 1980, 1995, 2012, 2015, 2018, 2021
Aerial Photographs 1939, 1948, 1950, 1956, 1963, 1968, 1974, 1982, 1991, 1998, 2006, 2009, 2012, 2016, 2020
Sanborn Maps N/A
In the 1897 topographic map, the Property is depicted as undeveloped. Stevens Creek Boulevard is located in its present-day alignment north of the Property. A dirt road and structure extend south from Stevens Creek Boulevard, adjacent to the eastern side of the Property. Calabazas Creek is depicted approximately 1/8 mile southeast of the Property. In the 1939 aerial photograph, orchards are located across the Property and surrounding sites. The dirt road and three structures (homesteads) appear to be either adjacent to the current Property boundary or within the eastern side of the Property. The Property and surrounding areas appeared in similar condition until the late 1950s. Between 1956 and 1961, the orchards were felled and the Property was redeveloped with the present-day commercial building and parking areas. The Property has appeared in similar condition since.

The remaining agricultural areas around the Property were redeveloped into commercial uses between the early 1960s and early 1980s. The gasoline service station adjacent to the east of the Property across East Estates Drive was constructed between 1956 and 1961. Residential developments were constructed south of the Property. The former Vallco shopping center was 606
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constructed between 1968 and 1974. Between 1974 and 1982, the commercial shopping center to the west of the Property was constructed. The Vallco shopping center was demolished between mid-2019 and early 2020. Recent aerial imagery shows that grading has begun on the Vallco redevelopment.

4.2.2 City Directory
City Directories, published since the 18th century for major towns and cities, list the name of the resident or business associated with each address. A city directory search conducted by EDR is included in Appendix G. Listings for the Property are tabulated below.

TABLE 4.2.2-1: City Directory Listings

YEAR LISTING(S)
1968
19590 Stevens Creek Boulevard – Winchell’s Donut House
19610 Stevens Creek Boulevard – Ellanah’s House of Beauty 10025 East Estates Drive – Idlewild Barber Shop
10045 East Estates Drive – One-Hour Martinizing
10051 East Estates Drive – Jakob Realty Co
10055 East Estates Drive – Sparkle Clean Self Serve Laundromat 10065 East Estates Drive – Stevens Creek Rexall Drug
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Mayfair Market
1971
19590 Stevens Creek Boulevard – Winchell’s Donut House
19610 Stevens Creek Boulevard – Ellanah’s House of Beauty 10025 East Estates Drive – Idlewild Barber Shop
10045 East Estates Drive – One-Hour Martinizing
10051 East Estates Drive – Jakob Realty Co
10055 East Estates Drive – Unlisted
10065 East Estates Drive – Stevens Creek Rexall, Rexll Org Stevens Creek 10071 East Estates Drive – Unlisted
10075 East Estates Drive – Mayfair Markets
1976
19590 Stevens Creek Boulevard – Winchell’s Donut House
19610 Stevens Creek Boulevard – Advance Coiffures
10025 East Estates Drive – Unlisted
10045 East Estates Drive – Unlisted
10051 East Estates Drive – Unlisted
10055 East Estates Drive – Unlisted
10065 East Estates Drive – Unlisted
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Unlisted
1981
19590 Stevens Creek Boulevard – Winchell’s Donut House
19610 Stevens Creek Boulevard – Advance Coiffures, Soon’s Beauty House 10025 East Estates Drive – Unlisted
10045 East Estates Drive – Unlisted
10051 East Estates Drive – Unlisted
10055 East Estates Drive – Unlisted
10065 East Estates Drive – Unlisted
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Unlisted
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YEAR LISTING(S)
1985
19590 Stevens Creek Boulevard – Winchell’s Donut House
19610 Stevens Creek Boulevard – Soon’s Beauty Salon
10025 East Estates Drive – Unlisted
10045 East Estates Drive – Unlisted
10051 East Estates Drive – Unlisted
10055 East Estates Drive – Unlisted
10065 East Estates Drive – Unlisted
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Unlisted
1992
19590 Stevens Creek Boulevard – Pizza Hut
19610 Stevens Creek Boulevard – Soon’s Beauty Salon, Belbein Skin Care 10025 East Estates Drive – Unlisted
10045 East Estates Drive – Unlisted
10051 East Estates Drive – Unlisted
10055 East Estates Drive – Unlisted
10065 East Estates Drive – Unlisted
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Unlisted
1995
19590 Stevens Creek Boulevard – Pizza Hut
19610 Stevens Creek Boulevard – Soon’s Beauty Salon
10025 East Estates Drive – Idlewild Barber Shop
10045 East Estates Drive – Unlisted
10051 East Estates Drive – Peterson, Terry
10055 East Estates Drive – Pitzer Auto Parts Stores
10065 East Estates Drive – Wells Interiors
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Fabricland, Viking at Fabric Land 2000
19590 Stevens Creek Boulevard – Pizza Hut
19610 Stevens Creek Boulevard – Soon’s Beauty Salon, Nails by Lynn 10025 East Estates Drive – Idlewild Barber Shop
10045 East Estates Drive – Unlisted
10051 East Estates Drive – Peterson’s Video Transfer Services 10055 East Estates Drive – 3 Beads & A Button
10065 East Estates Drive – Wells Interiors
10071 East Estates Drive – Viking Sewing Machine Center 10075 East Estates Drive – Pham, Khanh Q; United Furniture Club 2005
19590 Stevens Creek Boulevard – House of Falafel
19610 Stevens Creek Boulevard – Unlisted
10025 East Estates Drive – Cupertino Watch & Jewelry Repair 10045 East Estates Drive – Unlisted
10051 East Estates Drive – Unlisted
10055 East Estates Drive – Cohanna Enterprises
10065 East Estates Drive – Island Moves Family Center
10071 East Estates Drive – Unlisted
10075 East Estates Drive – Ann & Charlie Corp, United Furniture Club 2010
19590 Stevens Creek Boulevard – House of Falafel
19610 Stevens Creek Boulevard – Soon’s Beauty Salon
10025 East Estates Drive – Cupertino Watch & Jewelry Repair 10045 East Estates Drive – One-Hour Dry Cleaning
10051 East Estates Drive – Peterson’s Video Transfer Services 10055 East Estates Drive – Le Caprice
10065 East Estates Drive – Sonny’s Place Hawaiian Shop
10071 East Estates Drive – Viking Sewing Center
10075 East Estates Drive – United Furniture Club
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YEAR LISTING(S)
2014
19590 Stevens Creek Boulevard – House of Falafel
19610 Stevens Creek Boulevard – Soon’s Beauty Salon
10025 East Estates Drive – Cupertino Watch & Jewelry Repair 10045 East Estates Drive – One-Hour Dry Cleaning
10051 East Estates Drive – Peterson’s Video Transfer Services 10055 East Estates Drive – Le Caprice
10065 East Estates Drive – Unlisted
10071 East Estates Drive – M & S Collision
10075 East Estates Drive – United Furniture Club
2017
19590 Stevens Creek Boulevard – House of Falafel
19610 Stevens Creek Boulevard – Soon’s Beauty Salon, JK Properties 10025 East Estates Drive – Cupertino Watch & Jewelry Repair, Prospect Barber Stylist
10045 East Estates Drive – One-Hour Dry Cleaning
10051 East Estates Drive – Heartland Society of Northern California 10055 East Estates Drive – Le Caprice
10065 East Estates Drive – Han’s Asian Antiques & Art
10071 East Estates Drive – M & S Collision, Viking Sewing Machine Center 10075 East Estates Drive – Unlisted
2020
19590 Stevens Creek Boulevard – House of Falafel, Tang Wu 19610 Stevens Creek Boulevard – Soon’s Beauty Salon, JK Properties 10025 East Estates Drive – Cupertino Watch & Jewelry Repair 10045 East Estates Drive – One-Hour Dry Cleaning
10051 East Estates Drive – Heartland Society of Northern California 10055 East Estates Drive – Le Caprice
10065 East Estates Drive – Unlisted
10071 East Estates Drive – M & S Collision, South Bay Business Services Inc. 10075 East Estates Drive – Hai Le, Michael Nguyen, United Furniture Club Other listings in the vicinity of the Property are primarily associated with various commercial establishments such as restaurants, banks, medical and dental offices, gasoline service stations, and retail stores.

4.3 ENVIRONMENTAL DATABASE RECORD SOURCES
EDR performed a search of federal, tribal, state, and local databases for records for the Property and nearby properties. Details of the databases searched by EDR are provided in Appendix A.

A list of the facilities documented by EDR within the approximate minimum search distance of the Property is provided below.

4.3.1 Property Database Records
The Property is listed on the following environmental database record sources.

TABLE 4.3.1-1: Environmental Database Listings for the Property

FACILITY STREET DATABASES
One-Hour Cleaners by Lee /
One-Hour Martinizing by Lee/
Enterprise Controls, Inc.
10045 East Estates Drive

CERS, CPS-SLIC, CUPA

LISTINGS, DRYCLEANERS,

ECHO, EDR HIST CLEANER,

EMI, FINDS, HAZNET, HWTS,

RCRA-LQG
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The listings for the Property pertain to hazardous waste generation, disposal, and release for the One-Hour Cleaners facility. The Property is listed as a dry cleaner between 1969 and 2014.

Halogenated solvents are listed as wastes between 1993 and 2000. Petroleum hydrocarbon solvent is listed as a waste in 2019. Site investigations related to releases from the former One-Hour Cleaners facility are discussed in Section 3.0.

4.3.2 Adjoining and Nearby Property Database Records
The following databases include adjoining and nearby facilities listed within the appropriate ASTM search distances of the Property on environmental database record sources.

TABLE 4.3.2-1: Environmental Database Listings for Adjoining and Nearby Properties

FACILITY DATABASES
RCRA NONGEN / NLR 54
E MANIFEST 38
CUPA LISTINGS 29
LUST 14
UST FINDER RELEASE 9
CORTESE 8
HIST LUST 8
CERS HAZ WASTE 7
ENVIROSTOR 7
HIST CORTESE 7
RCRA-SQG 6
CPS-SLIC 4
HIST UST 4
SWEEPS UST 4
UST 4
AST 3
CA FID UST 3
CERS TANKS 2
EDR HIST AUTO 2
EDR HIST CLEANER 2
BROWNFIELDS 1
DRYCLEANERS 1
FINDS 1
HIST CAL-SITES 1
HWP 1
NOTIFY 65 1
NPL 1
RESPONSE 1
ROD 1
SEMS-ARCHIVE 1
SWRCY 1
UST FINDER 1
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Adjoining and nearby properties of potential environmental concern are discussed below.

Former Vallco Shopping Center – 10123 North Wolfe Road
The former Vallco Shopping Mall, located between approximately 120 to 2400 feet north-northeast of the Property, is listed in the AST, CA FID UST, CERS, CHMIRS, CORTESE,

CPS-SLIC, CUPA LISTINGS, ECHO, E MANIFEST, FINDS, HAZNET, HIST CORTESE, HIST LUST, HIST UST, HWTS, LUST, RCRA NONGEN/NLR, RCRA-SQG, SWEEPS UST, and UST FINDER RELEASE databases searched by EDR. The Vallco Shopping Mall operated from 1979 to 2018, and is divided into the western portion (west of North Wolfe Road) and the eastern portion (northeast of North Wolfe Road and Vallco Parkway). We discuss the western and eastern sites below.

Western Vallco Site:

One closed leaking underground storage tank (LUST) case (Sears Automotive Center, GeoTracker ID T0608552828) and one open cleanup program site (CPS) case (Vallco Town Center, GeoTracker ID T10000017167) are associated with the western Vallco Site. The LUST case pertains to the removal of six underground storage tanks (USTs) in 1985 and subsequent soil sampling and removal.

The CPS case pertains to investigations of PCE release(s). The source is not known due to the many tenants of the mall. WSP conducted a soil gas investigation at the Vallco facility in 2021 which included an evaluation of whether the Idlewild site may be contributing to PCE in soil gas at Vallco by sampling along the southern Vallco site boundary (WSP, 2021). WSP concluded that it was unlikely that the PCE release at the Property contributed to elevated concentrations at Vallco. Terraphase also evaluated WSP’s findings and opined that it was unlikely that PCE could migrate in soil gas across Stevens Creek Boulevard at the concentrations observed at Vallco.

In 2023, as part of redevelopment of the western Vallco Mall site, soil was excavated to a depth of 15 feet for the construction of underground parking, and additional recent targeted excavations were conducted to remove soils impacted with PCBs, TPH, pesticides, and metals. Additionally, a PCE hot spot was excavated to a depth of 20 feet (WSP, 2023). The 2024 Updated Site Management Plan prepared by EKI provides recent soil and soil gas data showing that several VOC plumes remain in soil gas at the western Vallco Mall site after removal, though concentrations have decreased since pre-excavation. Generally, the plumes are confined to the western Vallco Mall site and contain concentrations of VOCs within the same order of magnitude or one order of magnitude higher than the residential soil gas ESLs, and below concentrations observed at the Property. No further remediation is required or planned at Vallco. We do not consider this site a potential source of petroleum hydrocarbon or VOC impacts to the Property, and vice-versa.

Eastern Vallco Site:

One closed LUST case (J.C. Penney, GeoTracker ID T0608500770) and one open CPS case (East Vallco Mall Site, GeoTracker ID T10000020648) are associated with the eastern site. The eastern Vallco site is in the early stages of redevelopment and investigation. Because this site is situated east of the western Vallco Mall site and northeast of the Property, any impacts from the eastern Vallco site would impact the western Vallco before the Property. Due to the distance and location of the eastern Vallco site, we do not consider this site a potential source of vapor impacts to the Property.
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Joe’s Union Service/Tosco #11220/Mobil Service Station/Vallco 76 Service Station #112220-30242/Apro LLC DBA United Pacific 2205/Stan Boyett & Son Inc. DBA Boyett Petroleum/Estates Mobile Service/Platinum Energy #2611220/ConocoPhillips Company #2611220 – 19550 Stevens Creek Boulevard
This former gasoline service station, located adjacent to the eastern side of the Property across East Estates Drive, is listed in the CUPA LISTINGS, EDR HIST AUTO, HIST UST, LUST, CERS

HAZ WASTE, SWEEPS UST, CA FID UST, CERS TANKS, CERS, CORTESE, HIST CORTESE, HIST LUST, SWEEPS UST, EMI, HIST RCRA NONGEN/NLR, RCRA-SQG, FINDS, ECHO, and UST databases searched by EDR. This site is associated with two closed LUST cases on GeoTracker: Tosco #11220 (global ID T0608575840) and Mobil (global ID T0608500926).

According to the case summary available on GeoTracker for the Mobil case, in 1985, a loss of 1,800 gallons of product was identified through inventory reconciliation. The USTs were removed in 1985 and soil investigations were completed in the UST area to 120 feet bgs. Very low levels of contamination were detected and groundwater was not encountered. Santa Clara Valley Water District (SCVWD) issued a case closure/no further action letter on March 15, 1996.

In April 2001, free product was encountered in a soil boring. Extensive additional investigation and remediation was subsequently conducted. In May 2012, verification groundwater monitoring commenced. The site was granted case closure by SCCDEH on September 23, 2014. Based on distance and the remedial actions implemented at this facility, this facility would not be expected to pose a concern to the Property.

Shell Automotive/Jiffy Lube #2355/Allan Domash – 19480 Stevens Creek Boulevard This gasoline service station/Jiffy Lube site, located approximately 417 feet east of the Property, is listed in the LUST, HIST LUST, CORTESE, HIST CORTESE, CERS, AST, CERS HAZ WASTE, CA FID UST, CERS TANKS, CUPA LISTINGS databases searched by EDR. This facility is also listed as a closed LUST case on GeoTracker under case ID T0608501269.

According to the case closure summary/no further action letter, one 10,000-gallon gasoline UST, two 6,000-gallon gasoline USTs, three 12,000-gallon gasoline USTs, and one 550-gallon waste oil UST were removed from the site between 1987 and 1990. Soil vapor extraction was performed at the site from February to August 1992, and four consecutive quarters of groundwater monitoring were conducted after shutdown of the SVE system. Based upon the results of source removal, remedial actions performed, and verification monitoring, the extent of soil contamination was defined, and groundwater did not appear to be impacted, and SCVWD issued case closure on September 30, 1994. Based on distance and the case closure status, this facility would not be expected to pose a concern to the Property.

One-Hour Photo Service/Holiday Cleaners of America – 19720 Stevens Creek Boulevard This former photo developing facility and former dry-cleaning facility, located approximately 466 feet west of the Property, is listed in the CERS, CPS-SLIC, CUPA LISTINGS, DRYCLEANERS, EMI, FINDS databases searched by EDR. This facility is also listed as a cleanup program site on GeoTracker under case ID T10000016970, with the status open – assessment and interim remedial action as of April 1, 2021. 612
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The site owner entered into a voluntary remedial action agreement with SCCDEH on April 1, 2021. According to the Corrective Action Work Plan (CAP) (WSP, 2022), the southwestern area of the site is impacted by PCE in soil gas associated with historical dry cleaning operations.

In September 2019 and January 2020, samples of soil gas, sub-slab vapor, and indoor air were collected to evaluate the potential for vapor intrusion from VOCs. Analytical results revealed that PCE was detected in sub-slab vapor samples (from 37 to 1,500 µg/m3) and in soil gas samples (from 1.68 to 1,050 µg/m3). Furthermore, PCE was detected in indoor air samples (from 1.15 to

2.64 µg/m3). In September 2020, WSP performed additional sub-slab vapor and indoor air sampling and analyses. The results indicate that the PCE impacts to soil gas are concentrated in the southwestern area of the site and do not appear to extend easterly beyond the site boundary (towards the Property). Therefore, this facility is not expected to pose a concern to the Property.

Wardrobe Custom Cleaners/Minuteman Press/Mel’s Cleaners – 19705 Stevens Creek Boulevard This former dry cleaning facility, located approximately 577 feet northwest of the Property, is listed in the CUPA LISTINGS, ECHO, EDR HIST CLEANER, FINDS, and RCRA-SQG databases searched by EDR. No information is available regarding chemicals handled at this property or previous investigations; however, based on distance, this facility would not be expected to pose a concern to the Property.

Orphan Properties
One property is listed on the EDR “Orphan Summary” list but appears to be located beyond the ASTM recommended radius search criteria.

Based on the distances to the identified database sites, regional topographic gradient, and the EDR findings, it is unlikely that releases from the above-stated database sites pose a current risk to the Property. Furthermore, soil gas conditions at the Property are well characterized and vapor intrusion will be mitigated through the installation of VIMS beneath future building foundations.

4.4 REGULATORY AGENCY FILES AND RECORDS
The following agencies were contacted for records pertaining to the Property.

TABLE 4.4-1: Regulatory Agency Records

NAME OF AGENCY RECORDS REVIEWED
City of Cupertino Building and
Planning Departments
We contacted the City of Cupertino Building and Planning Departments on May 9, 2025, regarding historical building permit and planning records for the Property. The Building and Planning Departments provided the following files.
• Planning documents, construction plans, and certificates of occupancy for the original businesses at the Property (circa 1960) and renovations for later Property tenants (various dates). • Applications for electrical and building permits for One-Hour Martinizing Dry Cleaners at 10045 East Estates Drive, from 1960.
• A plumbing/water system permit for 10045 East Estates Drive from 1986.
• Signage, HVAC, and other building permits for the other Property addresses.
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NAME OF AGENCY RECORDS REVIEWED
City of Cupertino Fire Department
We contacted the City of Cupertino Fire Department on
May 9, 2025, regarding hazardous material and UST records for the Property. The City of Cupertino Fire Department indicated they have no files pertaining to the Property.

City of Cupertino Code
Enforcement Department
We contacted the City of Cupertino Code Enforcement Department on May 9, 2025, regarding records of illegal dumping and other code violations for the Property. The Code Enforcement
Department indicated they have no files pertaining to the Property.

Santa Clara County Department
of Environmental Health
We contacted the SCCDEH on May 9, 2025, regarding
environmental records for the Property. The SCCDEH provided inspection forms for the former One-Hour Cleaners dated between 1999 and 2015. The inspection forms did not suggest that there were large-scale releases of hazardous materials. We also contacted Mr. Aaron Costa, the case worker for the One-Hour Dry Cleaners cleanup case, to schedule a phone interview. However, Mr. Costa declined to conduct an interview and referred us to the case’s GeoTracker page.

Santa Clara County Fire
Department (SCCFD)
We contacted the SCCFD on May 12, 2025, regarding
environmental records for the Property. As of the publication of this report, we have not received a response from SCCFD. This constitutes a data gap for the Property.

Santa Clara Valley Water District
(Valley Water)
We reviewed the online well information map provided by Valley Water regarding groundwater well records for the Property. The map depicts two soil vapor extraction wells, SVE-01 and SVE-02, on the Property.

Santa Clara County Assessor’s
Office
We reviewed online parcel maps provided by the Santa Clara County Assessor’s Office. The Property boundary and APNs provided in the EDR radius map report are consistent with the online parcel maps.

California SWRCB
We reviewed GeoTracker, the website maintained by SWRCB, for files pertaining to the Property. The Property is listed as an open CPS case under global ID T10000021095.

California DTSC We reviewed EnviroStor, the website maintained by DTSC, for files pertaining to the Property. No listings were found for the Property.

4.5 PER- AND POLYFLUOROALKYL SUBSTANCES
Per- and polyfluoroalkyl substances (PFAS) are a class of compounds used in a wide range of industrial processes and consumer products, including carpets, clothing, fabrics for furniture, packaging for food and cookware, and firefighting foam. PFAS are known as "forever chemicals" as the substances are highly recalcitrant in the environment. Common land uses associated with PFAS include sites where firefighting foam was used or stored; wastewater treatment plants utilizing biosolids spreading; chemical and electronics manufacturing facilities; landfills; and other industrial manufacturing facilities. In 2024, the USEPA announced its final rule designating two PFAS, perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS), as hazardous substances under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), 40 CFR 302 (USEPA, 2024a) and published the Final PFAS National Primary Drinking Water Regulation for six PFAS (USEPA, 2024b).

We reviewed the EDR Radius Map Report for PFAS database listings as well as the GeoTracker PFAS map (SWRCB, n.d.) for records of investigative orders, locations with PFAS data, or water system wells on the Property and within 1 mile of the Property. Neither the Property nor nearby 614
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sites were identified on PFAS database listings. Two water wells were mapped on the GeoTracker PFAS map within 1 mile (approximately 0.6 mile north-northwest of) the Property; neither of the wells reported detectable concentrations of PFAS compounds. Based on the historical use of the Property and nearby sites, we did not identify any on-site or off-site sources of PFAS that would be likely to impact soil or groundwater beneath the Property.

5.0 SITE RECONNAISSANCE

5.1 METHODOLOGY
We conducted a reconnaissance of the Property on June 3, 2025. The reconnaissance was performed by Jenna Keith, a Project Engineer of ENGEO. We looked for hazardous materials storage, superficial staining or discoloration, debris, stressed vegetation, or other conditions that may be indicative of potential sources of soil or groundwater contamination. We also checked for evidence of fill/ventilation pipes, ground subsidence, or other evidence of existing or pre-existing USTs. Finally, we viewed adjoining properties from the Property and public thoroughfares to determine features, activities, uses, and conditions at adjoining properties that may indicate RECs at the Property. Photographs taken during the site reconnaissance are presented in Figures 4A through 4C.

We did not view the interior of any of the active or vacant commercial tenant spaces.

5.2 SITE AND ADJOINING PROPERTIES SETTING
The Property can be accessed through both Stevens Creek Boulevard and East Estates Drive.

The commercial structure on the Property is situated along the western edge with an alley behind (west of) the building and parking in the northern and eastern areas. The SVE trailer and piping are located behind the former One-Hour Cleaners tenant space, near the northwestern corner of the building. The Property is bounded to the north by Stevens Creek Boulevard and the former Vallco shopping center; to the south by a single-family residential neighborhood; to the east by East Estates Drive, a gasoline service station/tire repair shop, a restaurant, and medical offices; and to the west by a commercial shopping center.

5.3 SITE CONDITIONS
The following table summarizes our observations during the reconnaissance.

TABLE 5.3-1: Site Conditions

FEATURE TYPE OBSERVATIONS
Structures or Other Improvements
An approximately 41,000-square-foot commercial building is located in the western portion of the Property. The building is a one-story wooden frame structure with concrete flooring. Some units were occupied with commercial businesses and some were vacant. The exterior of the commercial building is finished with shingles on the rooftops and stone columns.

Roads The Property is accessed via East Estates Drive and Stevens Creek Boulevard.

Potable Water Supply/ Source Drinking water is supplied to the Property by Valley Water.

Sewage Disposal, Septic Systems,
or Cesspools
Sewage disposal connections to the Property are provided by the municipal wastewater system.
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FEATURE TYPE OBSERVATIONS
Wastewater Treatment System No wastewater treatment systems were observed at the Property during the reconnaissance.

Stormwater Conveyance System Stormwater drains were observed throughout the parking lot during the reconnaissance.

Wells
No groundwater wells were observed on the Property at the time of the reconnaissance. Soil vapor extraction and
monitoring wells were observed at the Property and at the adjacent 19620 Stevens Creek Boulevard site associated with SVE operation.

Hazardous Substances and
Petroleum Products in Connection
with Identified Uses
No hazardous substances or petroleum products in connection with identified uses were observed within the Property during the site reconnaissance.

Hazardous Substance and Petroleum
Product Containers Not in Connection
With Identified Uses
No hazardous substances or petroleum products not in
connection with identified uses were observed within the Property during the site reconnaissance.

Unidentified Substance Containers No unidentified substance containers were observed on the Property.

Storage Tanks (underground and
above-ground)
No above-ground storage tanks or evidence of existing USTs were observed during the site reconnaissance.

Strong, Pungent, or Noxious Odors
and Their Sources
No odors indicative of hazardous materials or petroleum material impacts were noted at the time of the reconnaissance.

Standing Surface Water and Pools or
Sumps Containing Liquids
No pools of potentially hazardous liquid were observed within the Property at the time of our reconnaissance.

Drums, Totes, and Intermediate Bulk
Containers
Nine 55-gallon drums associated with previous environmental investigations were observed on the Property at the time of the reconnaissance.

Polychlorinated Biphenyl (PCB)-
Containing Equipment
No potential PCB-containing equipment, including
transformers, were observed within the Property during our site reconnaissance.

Pits, Ponds, and Lagoons No pits, ponds, or lagoons were observed within the Property at the time of our reconnaissance.

Stained Soil/Pavement No stained soil or pavement was observed within the Property at the time of our reconnaissance.

Stressed Vegetation No signs of stressed vegetation were observed on the Property at the time of our reconnaissance.

Solid Waste/Debris
A waste collection area was observed in the southwest corner of the Property. The debris primarily consisted of furniture and cardboard boxes.

Stockpiles/Fill Material No stockpiles or fill material were observed on the Property during the reconnaissance.

5.4 INTERIOR OBSERVATIONS
We did not enter any onsite structures during the reconnaissance. From the outside, the commercial building is a one-story, wood-frame building with concrete flooring. The frame was observed to be in good condition. The southwestern corner of the building consisted of a storage space. Most of the former tenants have vacated the building. 616
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5.5 ASBESTOS, LEAD, AND PCB-CONTAINING BUILDING MATERIALS Common asbestos-containing building materials (ACBMs) include flooring and associated adhesive; baseboard and baseboard adhesive; carpet adhesive; leveling compound; drywall, joint and/or texturing compounds; ceiling tiles; roofing felts; roof patching compounds; and mechanical/boiler system insulation. Federal regulations (40 CFR Part 61, Subpart M) require that potential ACBMs be sampled and analyzed for the presence of asbestos prior to any renovation or demolition activities that disturb such materials (USEPA, 2021b). Common leadcontaining building materials include lead-based paint; roofing and pipework; and glazing and leaded glass. Common PCB-containing building materials include caulk, grout, and joint material; hydraulic fluid in elevators; fluorescent light ballasts; mastic used in tile and carpet; oil-based paints, sealants, coatings, varnishes, and lacquers; and asphaltic roofing. Hazardous building materials are generally found in buildings constructed prior to 1980.

An asbestos, lead, and PCB-containing building material survey is considered an ASTM non-scope item and was not conducted by ENGEO as part of this assessment. However, we were provided an Asbestos Inspection report prepared by Stockton Environmental Inc., dated October 25, 2023. The report identified both non-friable and friable ACBMs. The report recommended preparation of an asbestos abatement plan and engagement of a registered asbestos abatement contractor to remove ACBMs prior to demolition.

6.0 INTERVIEWS
We requested written and/or oral interviews with the User; the present owners of the Property; and the SCCDEH case worker for the Former One-Hour Dry Cleaners case to obtain information regarding RECs in connection with the Property. The SCCDEH case worker declined our request for interview and referred us to GeoTracker. The questionnaires are presented in Appendix C.

6.1 USER INTERVIEW
Mr. Robert Connolly of Toll Brothers, Inc. completed a User-based environmental site questionnaire pertaining to applicable environmental information regarding the Property on May 12, 2025. In the questionnaire, Mr. Connolly identified the current Property owner as the Castello family. Mr. Connolly identified potential environmental issues with the Property as discussed in ENGEO’s 2023 phase I ESA. Mr. Connolly is unaware of commonly known, reasonably ascertainable, or specialized knowledge indicative of releases or threatened releases that is material to the potential presence of RECs. Mr. Connolly has indicated that the purchase price of the Property is reflective of fair market value of the Property.

6.2 KEY SITE MANAGER INTERVIEW
A Key Site Manager is defined as the current Property owner or owner representative, leasing agent, or other person having good knowledge of the uses and physical characteristics of the Property. Mr. Jeffrey Raines of Terraphase completed a Key Site Manager-related environmental site questionnaire on behalf of the Property owner on June 2, 2025. The questionnaire pertains to applicable environmental information regarding the Property and adjoining properties. In the questionnaire, Mr. Raines indicated that the Property was formerly used for agriculture; has been occupied by the current shopping center since 1960; and that the current Property owner, Idlewild TIC, assumed title of the Property in 2021. Mr. Raines indicated that the Property was formerly used for dry cleaning which released PCE into the subsurface. 617
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The questionnaire references the gasoline service station located at 19550 Stevens Creek Boulevard (APN 369-06-007) as part of the Property. We note that this site is not part of the Property.

7.0 FINDINGS AND OPINIONS
This assessment included a review of local, state, tribal, and federal environmental record sources, standard historical sources, aerial photographs, fire insurance maps, and physical setting sources. We conducted a reconnaissance of the Property to review site use and current conditions to check for the storage, use, production, or disposal of hazardous or potentially hazardous materials and conducted written/oral interviews with persons knowledgeable about current and past site use.

7.1 FINDINGS
A review of regulatory databases maintained by county, state, tribal, and federal agencies found no documentation of hazardous materials violations or discharge on the Property and in general, did not identify contaminated facilities within the appropriate ASTM search distances that would reasonably be expected to impact the Property. However, the site reconnaissance and records review found documentation and physical evidence of soil and soil gas impairments associated with the past use of the Property.

Based on the findings of this assessment, one REC, no Historical RECs, and one (future) Controlled REC were identified for the Property.
• REC: Former One-Hour Cleaners PCE Releases
 Discharges of PCE from former dry cleaning operations have impacted the Property and off-site property to the west. PCE is present in soil gas and, to a lesser degree, soil, at concentrations exceeding residential and/or commercial ESLs9,10. We understand that Idlewild TIC is responsible for site cleanup prior to transfer of the Property. We recommend continued remediation-related activities of the PCE plume at the Property as appropriate with regulatory oversight.
• Future Controlled REC: Institutional Controls/Deed Restriction  ICs will be required following successful completion of SVE. ICs will likely include an access agreement to allow SCCDEH personnel on Site at any time; funding for SCCDEH oversight; restriction of uses of the Property, restriction of modifications to the Property development without SCCDEH approval, and OM&M and reporting for the VIMS that is expected to be installed under the planned residential units. A corresponding deed restriction would be recorded for the Property to ensure the systems remain operational.

When approved, the ICs/deed restriction will represent a controlled REC for the Property.

Based on our review of regulatory databases and observations during the site reconnaissance, we identified the following BERs, PECs, and/or de minimis conditions. While not considered to be RECs, these features may pose an environmental concern to the Property. We briefly discuss each feature below.
9 SFBRWQCB; Subslab/Soil Gas Vapor Intrusion: Human Health Risk Levels (Table SG-1); Residential; January 2019 (Rev. 1).
10 SFBRWQCB; Subslab/Soil Gas Vapor Intrusion: Human Health Risk Levels (Table SG-1); Commercial/Industrial; January 2019 (Rev. 1)
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• A hazardous building materials survey performed in 2023 identified asbestos-containing materials in the onsite commercial building. The cost of asbestos abatement and disposal is considered a BER.

7.2 DATA GAPS AND DATA FAILURES
As defined in the ASTM Standard Practice E1527-21, a data gap is:

A lack or inability to obtain information required by this practice despite good faith efforts by the environmental professional to gather such information.

A significant data gap is:

A data gap that affects the ability of the environmental professional to identify a recognized environmental condition.

The following data gaps were identified during this assessment. • At the time of report publication, we had not received a response from the SCCFD.

The data gaps identified during this assessment do not affect our conclusions as to the presence of RECs at the Property.

As defined in the ASTM Standard Practice E1527-21, a data failure is:

Failure to achieve the historical research objective even after reviewing the standard historical resources that are reasonably ascertainable and likely to be useful. A data failure is one type of data gap.

Data failures are common when attempting to identify the use of the Property at 5-year intervals back to the first developed use or back to 1940, whichever is earlier. While gaps in the historical record information of greater than 5 years were identified, these data failures are not considered significant given the aggregate information available.

7.3 SIGNIFICANT DEVIATIONS FROM ASTM STANDARD PRACTICE
There were no significant deviations from ASTM Standard Practice E1527-21 in the preparation of this report.

8.0 CONCLUSIONS
We have performed a phase I environmental site assessment of the Property in general conformance with the scope and limitations of ASTM E1527-21 and the standards and practices of the AAI Final Rule (40 CFR Part 312). Any exceptions to, or deletions from this practice are described in Sections 7.0 and 9.0 of the report.

We believe that sufficient information has been obtained during our contracted scope of services to evaluate the presence of RECs at the Property. This assessment has revealed evidence of one REC, no Historical RECs, and one (future) Controlled REC, and no evidence of significant data gaps, in connection with the Property. We recommend the following. 619
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• The remedial program should be continued under the oversight of SCCDEH. • SVE wells should be destroyed under SCCDEH oversight prior to Property redevelopment. • We recommend engaging a licensed asbestos abatement contractor to develop an asbestos abatement plan and remove asbestos-containing materials prior to building demolition.

9.0 LIMITATIONS

9.1 ASSUMPTIONS, LIMITATIONS, AND EXCEPTIONS OF ASSESSMENT We strive to perform our professional services in accordance with generally accepted principles and practices currently employed in the area; there is no warranty, express or implied. The recommendations and conclusions presented in this report were based on the findings of our study, which were developed solely from the contracted services. The findings of the report are based in part on contracted database research, out-of-house reports, and personal communications. Our opinions formed are based on the assumed accuracy of the relied upon data in conjunction with our relevant professional experience related to such data interpretation.

We assume no liability for the validity of the materials relied upon in the preparation of this report.

This document must not be subject to unauthorized reuse; that is, reuse without our written authorization. Such authorization is essential because it requires us to evaluate the document's applicability given new circumstances, not the least of which is passage of time. The findings from a phase I environmental site assessment are valid for one year after from the earliest date of the following components: records review, site reconnaissance, interviews, declaration by environmental professional. Updates of portions of the assessment may be necessary after a period of 180 days of the earliest date of the four components.

This phase I environmental site assessment is not intended to represent a complete soil, soil gas, or groundwater characterization, nor define the depth or extent of soil, soil gas, or groundwater contamination. It is intended to provide an evaluation of potential environmental concerns associated with the use of the Property. Laboratory testing of soil, soil gas, or groundwater samples was not within the scope of the contracted services. The assessment did not include an asbestos survey, an evaluation of lead-based paint, an inspection of light ballasts for PCBs, or a mold survey. A radon evaluation was not performed.

This report is based upon field and other conditions discovered at the time of preparation of our assessment. Visual observations referenced in this report are intended only to represent conditions at the time of the reconnaissance. We would not be aware of site contamination, such as dumping and/or accidental spillage, which occurred subsequent to our site reconnaissance.

A more extensive assessment that would include a subsurface exploration with laboratory testing of soil, soil gas, and groundwater samples could provide more definitive information concerning site-specific conditions. If additional assessment activities are considered for the Property and if other entities are retained to provide such services, we cannot be held responsible for any and all claims arising from or resulting from the performance of such services by other persons or entities.

ENGEO can also not be held responsible from any and all claims arising or resulting from clarifications, adjustments, modifications, discrepancies, or other changes necessary to reflect changed field or other conditions.
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9.2 SPECIAL TERMS AND CONDITIONS
We have prepared this report for the exclusive use of Toll Brothers, Inc., the User. It is recognized and agreed that we have assumed responsibility only for undertaking the study for the User. The responsibility for disclosures including but not limited to this report and for remedial or mitigative action shall be solely that of the User.
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SELECTED REFERENCES
ASTM International. 2021. ASTM E1527-21: Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process. November 2021. (https://www.astm.org)
ASTM International. 2022. ASTM E2600-22: Standard Guide for Vapor Intrusion Pathway Assessment. June 2022. (https://www.astm.org)
California DOC, Geologic Energy Management Division (CalGEM). n.d. Well Finder. (https://maps.conservation.ca.gov/doggr/wellfinder/)
California DPH, Indoor Air Program Radon Program. 2016. California Indoor Radon Test Results. (https://www.cdph.ca.gov/Programs/CEH/DRSEM/CDPH%20Document%20Library/EMB/ Radon/Radon%20Test%20Results.pdf).

California DWR. n.d. Water Data Library (WDL) Station Map. (http://www.water.ca.gov/waterdatalibrary/)
Dibblee, T.W., and Minch, J.A. 2007. Geologic map of the Cupertino and San Jose West quadrangles, Santa Clara and Santa Cruz Counties, California. Map scale 1:24,000.

DTSC. n.d. EnviroStor. (https://envirostor.dtsc.ca.gov/public/) EKI Environment & Water (EKI). 2024. Updated Site Management Plan, Area West of Wolfe Road of Former Vallco Mall, 10123 North Wolfe Road, Cupertino, California. February 28, 2024.

ENGEO. 2023a. Phase I Environmental Site Assessment, Idlewild Shopping Center, 19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive, Cupertino, California. October 25, 2023. Project No. 22934.000.001.

ENGEO. 2023b. Environmental Peer Review, Idlewild Shopping Center, 19610 to 19590 Stevens Creek Boulevard and 10025, 10045, 10051, 10065, and 10075 East Estates Drive, Cupertino, California. November 30, 2023. Project No. 22934.000.001.

Path Forward Environmental Engineering and Geology (Path Forward). 2021a. DRAFT Subsurface Investigation Report, Cupertino Retail Center, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. August 6, 2021.

Path Forward. 2021b. DRAFT Additional Investigation Report, Cupertino Retail Center, 10025-10075 E Estates Drive and 19610 Stevens Creek Boulevard, Cupertino, California.

October 1, 2021.

SCCDEH. 2025a. Letter, One-Hour Dry Cleaners, 10045 East Estates Dr., Cupertino, CA 95014, APN: 369-06-22. Site Cleanup Program Case No. 2023-17s, GeoTracker ID No.

T10000021095. January 17, 2025.

SCCDEH. 2025b. Letter, One-Hour Dry Cleaners, 10045 East Estates Dr., Cupertino, CA 95014, APN: 369-06-22. Site Cleanup Program Case No. 2023-17s, GeoTracker ID No.

T10000021095. April 3, 2025.
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SELECTED REFERENCES (Continued)
June 11, 2025
Stockton Environmental Inc. 2023. Asbestos Inspection, Idlewild Shopping Center, 10025 E Estates Dr, Cupertino, CA 95014. October 24, 2023.

SWRCB. n.d. GeoTracker. (https://geotracker.waterboards.ca.gov/) SWRCB. n.d. GeoTracker PFAS Map.
(https://geotracker.waterboards.ca.gov/map/pfas_map)
Terraphase Engineering (Terraphase). 2022a. Indoor Air and Soil-Gas Sampling Results, 10025, 10045, and 10051 East Estates Drive, Cupertino, California. May 11, 2022.

Terraphase. 2022b. Soil-Gas Investigation Report, 10025-10075 East Estates Drive, Cupertino, California; August 16, 2022.

Terraphase. 2022c. Soil-Vapor Investigation and Soil-Vapor Extraction Pilot Test Report, 10025-10075 East Estates Drive, Cupertino, California; September 6, 2022.

Terraphase. 2023a. Soil-Vapor Extraction Pilot-Scale Test Work Plan, 10025, 10045, and 10051 East Estates Drive, Cupertino, California. June 20, 2023.

Terraphase. 2023b. Preliminary Results of the Soil Vapor Extraction Pilot Test Conducted at the Idlewild Shopping Center, 10025-10075 East Estates Drive, Cupertino, California.

August 4, 2023.

Terraphase. 2023c. Remedial Action Plan, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. September 18, 2023.

Terraphase. 2024a. Technical Memorandum, Idlewild Soil Vapor Extraction (SVE) System Status Update. August 12, 2024.

Terraphase. 2024b. Soil Vapor Extraction Operations, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. December 4, 2024.

Terraphase. 2025. One-Month Soil-Vapor Extraction (SVE) Rebound Testing Report, 10025-10075 East Estates Drive and 19590-19610 Stevens Creek Boulevard, Cupertino, California. March 12, 2025.

USDOT-PHMSA. n.d. NPMS Public Viewer. (https://pvnpms.phmsa.dot.gov/PublicViewer/) USEPA. 2021a. All Appropriate Inquiries (AAI) Final Rule. 40 CFR Part 312. Federal Register, vol. 86, no. 16, pp 7468. (https://www.ecfr.gov/current/title-40) USEPA. 2021b. National Emission Standards for Hazardous Air Pollutants: Asbestos. 40 CFR Part 61, Subpart M. Federal Register, vol. 86, no. 37430. (https://www.ecfr.gov/current/title40/part-61/subpart-M) USEPA. 2024a. Designation, Reportable Quantities, and Notification. 40 CFR Part 302. Federal Register, vol. 89, no. 24040. April (https://www.ecfr.gov/current/title-40/chapterI/subchapter-J/part-302) 623
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SELECTED REFERENCES (Continued)
June 11, 2025
USEPA. 2024b. Per- and Polyfluoroalkyl Substances (PFAS) Final PFAS National Primary Drinking Water Regulation. April 26, 2024. (https://www.epa.gov/sdwa/and-polyfluoroalkylsubstances-pfas) WSP USA, Inc. (WSP). 2021. Expanded Soil Gas Investigation, Former Vallco Mall, 10123 North Wolfe Road, Cupertino, CA. July 30, 2021.

WSP. 2022. Corrective Action Work Plan, Okaigon Dojo, 19720 Stevens Creek Boulevard, Cupertino, California. August 2022.

WSP. 2023. Soil Removal Action Completion Report, Area of Former Vallco Mall West of Wolfe Road, 10123 North Wolfe Road, Cupertino, California. December 4, 2023; Revised December 20, 2023.
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FIGURES
FIGURE 1: Vicinity Map
FIGURE 2: Site Plan
FIGURE 3: Assessor’s Parcel Map
FIGURES 4A through 4C: Site Photographs
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SITE PHOTOGRAPHS

IDLEWILD SHOPPING CENTER

CUPERTINO, CALIFORNIA
FIGURE NO.
4A
Path: H:\Active Projects\_22000 to 23999\22934\22934000001 Idlewild Shopping Center\006_2025 Phase I ESA\DRAFTING\Figure 4 site photographs ORIGINAL FIGURE PRINTED IN COLOR COPYRIGHT © 2025 BY ENGEO INCORPORATED. THIS DOCUMENT MAY NOT BE REPRODUCED IN WHOLE OR IN PART BY ANY MEANS WHATSOEVER, NOR MAY IT BE QUOTED WITHOUT THE EXPRESS WRITTEN CONSENT OF ENGEO INCORPORATED.

VIEW OF EASTERN SIDE OF COMMERCIAL BUILDING FACING

SOUTHWEST

VIEW OF NORTHEASTERN CORNER OF PROPERTY

VIEW OF SOUTHERN EDGE OF BUILDING VIEW OF WASTE COLLECTION AREA IN SOUTHWEST CORNER OF

PROPERTY

VIEW OF WESTERN EDGE OF BUILDING SOIL VAPOR EXTRACTION SYSTEM TRAILER AND DRUMS NEAR

NORTHWEST CORNER OF COMMERCIAL BUILDING
PHOTO 1 PHOTO 2
PHOTO 3 PHOTO 4
PHOTO 5 PHOTO 6
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SITE PHOTOGRAPHS

IDLEWILD SHOPPING CENTER

CUPERTINO, CALIFORNIA
FIGURE NO.
4B
Path: H:\Active Projects\_22000 to 23999\22934\22934000001 Idlewild Shopping Center\006_2025 Phase I ESA\DRAFTING\Figure 4 site photographs ORIGINAL FIGURE PRINTED IN COLOR COPYRIGHT © 2025 BY ENGEO INCORPORATED. THIS DOCUMENT MAY NOT BE REPRODUCED IN WHOLE OR IN PART BY ANY MEANS WHATSOEVER, NOR MAY IT BE QUOTED WITHOUT THE EXPRESS WRITTEN CONSENT OF ENGEO INCORPORATED.

SOIL VAPOR EXTRACTION WELL 1, BEHIND FORMER DRY CLEANER SOIL VAPOR EXTRACTION WELL 2, ON NORTH SIDE OF BUILDING

SOIL VAPOR MONITORING WELL VIEW OF NORTHERN SIDE OF COMMERCIAL BUILDING

VACANT INTERIOR TENANT SPACE ADJACENT COMMERCIAL PROPERTY TO WEST OF PROPERTY PHOTO 7 PHOTO 8
PHOTO 9 PHOTO 10
PHOTO 11 PHOTO 12
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SITE PHOTOGRAPHS

IDLEWILD SHOPPING CENTER

CUPERTINO, CALIFORNIA
FIGURE NO.
4C
Path: H:\Active Projects\_22000 to 23999\22934\22934000001 Idlewild Shopping Center\006_2025 Phase I ESA\DRAFTING\Figure 4 site photographs ORIGINAL FIGURE PRINTED IN COLOR COPYRIGHT © 2025 BY ENGEO INCORPORATED. THIS DOCUMENT MAY NOT BE REPRODUCED IN WHOLE OR IN PART BY ANY MEANS WHATSOEVER, NOR MAY IT BE QUOTED WITHOUT THE EXPRESS WRITTEN CONSENT OF ENGEO INCORPORATED.

TIRE REPAIR SHOP AND GASOLINE SERVICE STATION TO EAST OF

PROPERTY

FORMER VALLCO SHOPPING CENTER TO NORTH OF PROPERTY
PHOTO 13 PHOTO 14
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APPENDIX A
ENVIRONMENTAL DATA RESOURCES, INC.

Radius Map Report
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FORM-LBC-TFS
®kcehCoeG htiw tropeR ™paM suidaR RDE ehT
6 Armstrong Road, 4th floor
Shelton, CT 06484
Toll Free: 800.352.0050
www.edrnet.com
Idlewild Shopping Center
Stevens Creek Boulevard & E Estates Drive
Cupertino, CA 95014
Inquiry Number: 07984167.2r
May 09, 2025
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TABLE OF CONTENTS

SECTION PAGE
Executive Summary ES1
Overview Map 2
Detail Map 3
Map Findings Summary 4
Map Findings 9
Orphan Summary 756
Government Records Searched/Data Currency Tracking GR-1

GEOCHECK ADDENDUM
Physical Setting Source Addendum A-1
Physical Setting Source Summary A-2
Physical Setting Source Map A-8
Physical Setting Source Map Findings A-9
Physical Setting Source Records Searched PSGR-1
Thank you for your business.

Please contact EDR at 1-800-352-0050
with any questions or comments.

Disclaimer - Copyright and Trademark Notice
This Report contains certain information obtained from a variety of public and other sources reasonably available to Environmental Data Resources, LLC. It cannot be concluded from this Report that coverage information for the target and surrounding properties does not exist from other sources. This Report is provided on an "AS IS", "AS AVAILABLE" basis. NO WARRANTY EXPRESS OR IMPLIED IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA RESOURCES, LLC AND ITS SUBSIDIARIES,

AFFILIATES AND THIRD PARTY SUPPLIERS DISCLAIM ALL WARRANTIES, OF ANY KIND OR NATURE, EXPRESS OR IMPLIED,

ARISING OUT OF OR RELATED TO THIS REPORT OR ANY OF THE DATA AND INFORMATION PROVIDED IN THIS REPORT,

INCLUDING WITHOUT LIMITATION, ANY WARRANTIES REGARDING ACCURACY, QUALITY, CORRECTNESS, COMPLETENESS,

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INCIDENTAL, INDIRECT, SPECIAL, CONSEQUENTIAL OR OTHER DAMAGES OF ANY TYPE OR KIND (INCLUDING BUT NOT LIMITED TO LOSS OF PROFITS, LOSS OF USE, OR LOSS OF DATA) INFORMATION PROVIDED IN THIS REPORT. Any analyses, estimates, ratings, environmental risk levels, or risk codes provided in this Report are provided for illustrative purposes only, and are not intended to provide, nor should they be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any property.

Only an assessment performed by a qualified environmental professional can provide findings, opinions or conclusions regarding the environmental risk or conditions in, on or at any property.

Copyright 2025 by Environmental Data Resources, LLC. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, LLC, or its affiliates, is prohibited without prior written permission.

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TC07984167.2r Page 1
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EXECUTIVE SUMMARY
TC07984167.2r EXECUTIVE SUMMARY 1
A search of available environmental records was conducted by Environmental Data Resources, Inc (EDR).

The report was designed to assist parties seeking to meet the search requirements of EPA’s Standards and Practices for All Appropriate Inquiries (40 CFR Part 312), the ASTM Standard Practice for Environmental Site Assessments (E1527 - 21), the ASTM Standard Practice for Environmental Site Assessments for Forestland or Rural Property (E2247 - 16), the ASTM Standard Practice for Limited Environmental Due Diligence: Transaction Screen Process (E1528 - 22) or custom requirements developed for the evaluation of environmental risk associated with a parcel of real estate.

TARGET PROPERTY INFORMATION

ADDRESS

STEVENS CREEK BOULEVARD & E ESTATES DRIVE
CUPERTINO, CA 95014

COORDINATES
Latitude (North): 37.3226020 - 37˚ 19’ 21.36’’
Longitude (West): 122.0157770 - 122˚ 0’ 56.79’’
Universal Tranverse Mercator: Zone 10
UTM X (Meters): 587204.2
UTM Y (Meters): 4130910.8
Elevation: 199 ft. above sea level

USGS TOPOGRAPHIC MAP ASSOCIATED WITH TARGET PROPERTY
Target Property Map: 50005309 CUPERTINO, CA
Version Date: 2021
East Map: 50003395 SAN JOSE WEST, CA
Version Date: 2021

AERIAL PHOTOGRAPHY IN THIS REPORT
Portions of Photo from: 20200525
Source: USDA
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D38 JIFFY-LUBE 19480 STEVENS CREEK AST Lower 409, 0.077, East D37 SHELL AUTOMOTIVE 19480 STEVENS CK BD EDR Hist Auto Lower 409, 0.077, East D36 SHELL 19480 STEVENS CREEK LUST, HIST LUST, Cortese, HIST CORTESE, CERS Lower 409, 0.077, East B35 10142 EAST ESTATES D 10142 EAST ESTATES D RCRA NonGen / NLR, E MANIFEST Higher 212, 0.040, SSE C34 FUSION ACADEMY CUPER 19638 STEVENS CREEK RCRA NonGen / NLR Higher 200, 0.038, West C33 FAMILY & COSMETIC DE 19668 STEVENS CREEK CUPA Listings Higher 200, 0.038, West A32 STACEY A LEE A DENTA 10055 MILLER AVE #10 RCRA NonGen / NLR Lower 180, 0.034, ESE A31 ANNE E MURRAY, DDS 10055 MILLER AVE STE RCRA NonGen / NLR Lower 180, 0.034, ESE A30 ANNE E MURRAY DDS 10055 MILLER AV 104 CERS HAZ WASTE, CUPA Listings, CERS Lower 180, 0.034, ESE A29 IA 072313CUPERTINO O 10055 MILLER AV 101 CUPA Listings Lower 180, 0.034, ESE A28 DRS LIN & LO DMD INC 10055 MILLER AV 101 CUPA Listings, HWTS, HAZNET Lower 180, 0.034, ESE A27 DRS LIN & LO DMD INC 10055 MILLER AV 102 CERS HAZ WASTE Lower 180, 0.034, ESE A26 FUJIMOTO&LEE ORAL&MA 10055 MILLER AV CERS HAZ WASTE, CUPA Listings Lower 180, 0.034, ESE B25 AL ORTIZ 10140 RICH WOOD DRIV RCRA NonGen / NLR, E MANIFEST Higher 153, 0.029, SSW A24 TOSCO #11220 19550 STEVENS CREEK LUST, HIST LUST Lower 147, 0.028, East A23 TOSCO #11220 19550 STEVENS CREEK UST FINDER RELEASE Lower 147, 0.028, East A22 JOE’S UNION SERVICE 19550 STEVENS CREEK CUPA Listings Lower 147, 0.028, East A21 STAN BOYETT & SON IN 19550 STEVENS CREEK RCRA NonGen / NLR Lower 147, 0.028, East A20 BOYETT PETROLEUM BP 19550 STEVENS CREEK LUST, CERS HAZ WASTE, SWEEPS UST, CERS TANKS, CA...Lower 147, 0.028, East A19 VALLCO 76 SVC 19550 STEVENS CREEK RCRA NonGen / NLR Lower 147, 0.028, East A18 PLATINUM ENERGY #261 19550 STEVENS CREEK UST Lower 147, 0.028, East A17 ESTATES MOBILE SERVI 19550 STEVENS CREEK EDR Hist Auto Lower 147, 0.028, East A16 APRO DISTRIBUTION 22 19550 STEVENS CREEK UST FINDER Lower 147, 0.028, East A15 TOSCO NORTHWEST CO N 19550 STEVENS CREEK RCRA-SQG, FINDS, ECHO Lower 147, 0.028, East A14 MOBIL 19550 STEVENS CREEK LUST, HIST LUST, SWEEPS UST, Cortese, EMI, HIST... Lower 147, 0.028, East A13 BOYETT PETROLEUM BP 19550 STEVENS CREEK UST Lower 147, 0.028, East A12 MOBIL 19550 STEVENS CREEK UST FINDER RELEASE Lower 147, 0.028, East A11 VALLCO 76 #112220-30 19550 STEVENS CREEK UST Lower 147, 0.028, East A10 CONOCOPHILLIPS COMPA 19550 STEVENS CREEK CUPA Listings Lower 147, 0.028, East A9 MOBIL SERVICE STATIO 19550 STEVENS CREEK HIST UST Lower 147, 0.028, East A8 APRO DISTRIBUTION 22 19550 STEVENS CREEK UST Lower 147, 0.028, East A7 APRO LLC DBA UNITED 19550 STEVENS CREEK RCRA NonGen / NLR, E MANIFEST Lower 147, 0.028, East A6 ONE HOUR MARTINIZING 10045 E ESTATES DRIV FINDS Lower 1 ft.

A5 ONE HOUR CLEANERS BY 10045 E ESTATES DR RCRA-LQG, CPS-SLIC, FINDS, DRYCLEANERS, HWTS,... Lower 1 ft.

A4 ONE HOUR MARTINIZING 10045 E ESTATES DRIV EMI Lower 1 ft.

A3 ONE HOUR MARTINIZING 10045 E ESTATES DR ECHO Lower 1 ft.

A2 ENTERPRISE CONTROLS 10045 ESTATES DR EDR Hist Cleaner Lower 1 ft.

A1 ONE HOUR CLEANERS BY 10045 ESTATES DR CUPA Listings Lower 1 ft.

Reg PANASONIC 10900 N TANTAU AVENU NPL, SEMS, RCRA-SQG, US ENG CONTROLS, ENVIROSTOR,...Same 5007, 0.948, NE

MAPPED SITES SUMMARY
Target Property Address:

STEVENS CREEK BOULEVARD & E ESTATES DRIVE
CUPERTINO, CA 95014
Click on Map ID to see full detail.

MAP RELATIVE DIST (ft. & mi.)

ID DATABASE ACRONYMS ELEVATION DIRECTION SITE NAME ADDRESS 636
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I77 EDWARD & LYNN PUCCIN 10128 DENISON AVENUE RCRA NonGen / NLR, E MANIFEST Lower 838, 0.159, NNW 76 PARTHA MURALI 10277 EAST ESTATES D RCRA NonGen / NLR, E MANIFEST Higher 838, 0.159, South J75 HOPYARD PROPERTY MAN 19400 STEVENS CREEK RCRA NonGen / NLR Lower 772, 0.146, East 74 JACK MCKEOWN 10196 AVOCADO PLACE RCRA NonGen / NLR, E MANIFEST Higher 725, 0.137, SW I73 19698 WHEATON DR 19698 WHEATON DR RCRA NonGen / NLR, E MANIFEST Lower 682, 0.129, NW 72 ROSEMARIE PLACE 19472 ROSEMARIE PLAC RCRA NonGen / NLR, E MANIFEST Lower 671, 0.127, SE H71 DAISO 6986 19750 STEVENS CREEK CUPA Listings, HWTS Higher 642, 0.122, WSW H70 DAISO 6986 19750 STEVENS CREEK RCRA NonGen / NLR Higher 642, 0.122, WSW 69 10221 VICKSBURG DRIV 10221 VICKSBURG DRIV RCRA NonGen / NLR, E MANIFEST Higher 638, 0.121, South F68 THE PICTURE PEOPLE 19123 N WOLFE RD MS RCRA-SQG, FINDS, ECHO Lower 604, 0.114, NNE G67 MELS CLEANERS 19705 STEVNS CRK BD EDR Hist Cleaner Higher 586, 0.111, WNW G66 WARDROBE CUSTOM CLEA 19705 STEVENS CREEK CUPA Listings Higher 586, 0.111, WNW G65 MINUTEMAN PRESS 19701 STEVENS CREEK CUPA Listings Higher 586, 0.111, WNW G64 WARDROB CUSTOM CLEAN 19705 STEVENS CRK BL RCRA-SQG, FINDS, ECHO Higher 586, 0.111, WNW F63 I & G DIRECT REAL ES 10080 N. WOLFE ROAD RCRA NonGen / NLR, E MANIFEST Lower 544, 0.103, NE F62 I & G DIRECT REAL ES 10080 NORTH WOLF ROA E MANIFEST Lower 544, 0.103, NE F61 CUPERTINO FINANCIAL 10050 N WOLFE RD CUPA Listings, HWTS, HAZNET Lower 544, 0.103, NE F60 I & G DIRECT REAL ES 10080 N WOLFE RD RCRA NonGen / NLR Lower 544, 0.103, NE F59 KAISER OCCUPATIONAL 10050 N WOLFE RD 1-1 RCRA NonGen / NLR Lower 544, 0.103, NE F58 KAISER CUPERTINO OCC 10050 N WOLFE RD RCRA NonGen / NLR Lower 544, 0.103, NE F57 VALLCO PROPERTY OWNE 10000 N WOLFE ROAD RCRA NonGen / NLR Lower 532, 0.101, NE F56 VALLCO PROPERTYOWNER 10000 N WOLFE ROAD RCRA NonGen / NLR Lower 532, 0.101, NE C55 HOLIDAY CLEANERS 19720 STEVENS CREEK CUPA Listings Higher 474, 0.090, West C54 HOLIDAY CLEANERS OF 19720 STEVENS CREEK FINDS, DRYCLEANERS, EMI, CERS Higher 474, 0.090, West C53 19720 STEVENS CREEK 19720 STEVENS CREEK CPS-SLIC, CUPA Listings Higher 474, 0.090, West C52 HOLIDAY CLEANERS 19720 STEVENS CREEK EDR Hist Cleaner Higher 474, 0.090, West C51 ONE HOUR PHOTO SERVI 19744 STEVENS CREEK CUPA Listings Higher 474, 0.090, West E50 JIFFY LUBE #1615 10101 WOLFE RD CUPA Listings Lower 443, 0.084, North E49 BADGER DAYLIGHTING 10101 NORTH WOLFE RO RCRA NonGen / NLR, E MANIFEST Lower 443, 0.084, North E48 SEARS AUTO CENTER #6 10101 N WOLFE RD CUPA Listings Lower 443, 0.084, North E47 SEARS ROEBUCK & CO 10101 WOLFE RD RCRA-SQG, LUST, HIST LUST, SWEEPS UST, HIST UST,... Lower 443, 0.084, North E46 SEARS AUTOMOTIVE CEN 10101 N WOLFE RD UST FINDER RELEASE Lower 443, 0.084, North E45 SEARS, #1468 10101 N WOLFE RD LUST, HIST UST, FINDS, ECHO, CERS Lower 443, 0.084, North E44 SEARS AUTO CENTER 10101 WOLFE RD AST Lower 443, 0.084, North E43 VALLCO DENTAL CARE 10101 WOLFE RD CUPA Listings Lower 443, 0.084, North D42 ALLAN DOMASH 19480 STEVENS CREEK LUST, AST, HAULERS, CERS HAZ WASTE, CERS TANKS, CA...Lower 409, 0.077, East D41 JIFFY LUBE # 2355 19480 STEVENS CREEK RCRA NonGen / NLR, E MANIFEST Lower 409, 0.077, East D40 SHELL 19480 STEVENS CREEK UST FINDER RELEASE Lower 409, 0.077, East D39 ALLAN DOMASH 19480 STEVENS CREEK SWEEPS UST, HIST UST Lower 409, 0.077, East

MAPPED SITES SUMMARY
Target Property Address:

STEVENS CREEK BOULEVARD & E ESTATES DRIVE
CUPERTINO, CA 95014
Click on Map ID to see full detail.

MAP RELATIVE DIST (ft. & mi.)

ID DATABASE ACRONYMS ELEVATION DIRECTION SITE NAME ADDRESS 637
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P116 ICE CAPADES CHALET 10123 N WOLFE RD CPS-SLIC, HWTS Lower 1198, 0.227, North P115 VALLCO PROPERTY OWNE 10123 N. WOLFE ROAD RCRA NonGen / NLR, E MANIFEST Lower 1198, 0.227, North P114 VALLCO SHOPPING MALL 10123 N WOLFE RD STE RCRA NonGen / NLR, E MANIFEST Lower 1198, 0.227, North P113 KITS CAMERAS ONE HR 10123 N WOLFE RD STE RCRA-SQG, FINDS, ECHO Lower 1198, 0.227, North P112 ICE CENTER CUPERTINO 10123 N WOLFE ROAD, RCRA NonGen / NLR, E MANIFEST Lower 1198, 0.227, North P111 10123 NORTH WOLFE RD CHMIRS, HIST CORTESE Lower 1198, 0.227, North P110 THE PICTURE PEOPLE # 10123 N WOLFE RD 216 CUPA Listings Lower 1198, 0.227, North P109 RITZ CAMERA #562 10123 N WOLFE RD 210 CUPA Listings Lower 1198, 0.227, North P108 VALLCO PROPERTY OWNE 10123 NORTH WOLFE RO RCRA NonGen / NLR, E MANIFEST Lower 1198, 0.227, North P107 ICE CENTER ENTERPRIS 10123 N WOLFE RD CPS-SLIC, HWTS, HAZNET, CERS Lower 1198, 0.227, North P106 ICE CENTER CUPERTINO 10123 N WOLFE RD STE RCRA NonGen / NLR Lower 1198, 0.227, North P105 VALLCO PROPERTY OWNE 10123 N. WOLFE RD RCRA NonGen / NLR Lower 1198, 0.227, North O104 ROBERT F HARLEY DDS 10055 N PORTAL AV 13 CUPA Listings Higher 1112, 0.211, WNW O103 THEODORE A FLOOR DDS 10055 N PORTAL AV 10 CERS HAZ WASTE, CUPA Listings Higher 1112, 0.211, WNW O102 DONALD P ARALDI DDS 10055 N PORTAL AV 10 CUPA Listings Higher 1112, 0.211, WNW O101 MICHAEL SCHUCK DDS 10055 N PORTAL AV 10 CUPA Listings Higher 1112, 0.211, WNW N100 CVS (SIS) 19499 STEVENS CREEK RCRA NonGen / NLR, E MANIFEST Lower 1105, 0.209, East N99 TARGET STORE T3224 19499 STEVENS CREEK CUPA Listings, HWTS, HAZNET Lower 1105, 0.209, East N98 TARGET 3224 19499 STEVENS CREEK RCRA NonGen / NLR, FINDS, ECHO, E MANIFEST Lower 1105, 0.209, East N97 CVS PHARMACY #17687 19499 STEVENS CREEK CUPA Listings, HWTS, HAZNET Lower 1105, 0.209, East M96 ELLEN WU 10168 DENISON AVE RCRA NonGen / NLR, E MANIFEST Lower 1041, 0.197, NNW 95 CHRYSTAL SILVA DUENO 10277 COLD HARBOR AV RCRA NonGen / NLR, E MANIFEST Higher 1033, 0.196, SW M94 10153 DENISON AVE 10153 DENISON AVE RCRA NonGen / NLR Lower 1031, 0.195, NW 93 ZHEN LI 19773 WINTERGREEN DR RCRA NonGen / NLR, E MANIFEST Higher 1023, 0.194, SW M92 MASATO KAIDA 10154 DENISON AVENUE RCRA NonGen / NLR, E MANIFEST Lower 973, 0.184, NNW L91 GARDENS OF FOUNTAINB 10200 MILLER MAVE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L90 GARDENS OF FOUNTAINB 10200 MILLER AVE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L89 GARDENS 10200 MILLER AVE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L88 GARDENS 10200 MILLER AVE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L87 SONTAR APARTMENTS 10200 MILLER AVE. RCRA NonGen / NLR Higher 953, 0.180, SSE L86 GARDENS APARTMENTS 10200 MILLER AVE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L85 GARDENS OF FONTAINBL 10200 MILLER AVENUE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L84 GARDENS OF FONTAINEB 10200 MILLER AVE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE L83 GARDENS AT FONTAINEB 10200 MILLER AVENUE RCRA NonGen / NLR, E MANIFEST Higher 953, 0.180, SSE K82 BRIAN FEINBERG 19782 BIXBY DR RCRA NonGen / NLR, E MANIFEST Higher 932, 0.177, WSW K81 19782 BIXBY DRIVE 19782 BIXBY DRIVE RCRA NonGen / NLR, E MANIFEST Higher 932, 0.177, WSW J80 CA7-701-01-28 19376 STEVENS CREEK RCRA NonGen / NLR Lower 930, 0.176, East J79 BANK OF AMERICA 19376 STEVENS CREEK RCRA NonGen / NLR, E MANIFEST Lower 930, 0.176, East J78 BANK OF AMERICA 19376 STEVENS CREEK RCRA NonGen / NLR, E MANIFEST Lower 930, 0.176, East

MAPPED SITES SUMMARY
Target Property Address:

STEVENS CREEK BOULEVARD & E ESTATES DRIVE
CUPERTINO, CA 95014
Click on Map ID to see full detail.

MAP RELATIVE DIST (ft. & mi.)

ID DATABASE ACRONYMS ELEVATION DIRECTION SITE NAME ADDRESS 638
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144 CUPERTINO VILLAGE CL 10989 NORTH WOLFE RO ENVIROSTOR, VCP, CERS Lower 5040, 0.955, North 143 HEWLETT PACKARD COSA 5301 STEVENS CREEK B SEMS-ARCHIVE, RCRA-SQG, ENVIROSTOR, CPS-SLIC, HIST...Lower 4975, 0.942, East 142 SAFEWAY STORE 767 6150 BOLLINGER RD RESPONSE, ENVIROSTOR, SWRCY, DEED, CHMIRS, CUPA...Higher 4500, 0.852, SSE 141 VALLCO BUILDING 80 10432 N. TANTAU AVEN ENVIROSTOR Lower 3812, 0.722, NE 140 AMPEX CUPERTINO FACI 10435 N TANTAU AVE SEMS-ARCHIVE, ENVIROSTOR Lower 3332, 0.631, NE 139 SEDGWICK ELEMENTARY 10480 FINCH AVENUE ENVIROSTOR, LUST, HIST LUST, SCH, Cortese, HIST... Higher 2693, 0.510, SE T138 FIRST DEVELOPMENT CO 19110 STEVENS CREEK UST FINDER RELEASE Lower 2434, 0.461, East T137 FIRST DEVELOPMENT CO 19110 STEVENS CREEK LUST, HIST LUST, Cortese, HIST CORTESE, CERS Lower 2434, 0.461, East T136 FIRST DEVELOPMENT CO 19140 STEVENS CREEK LUST, HIST LUST, Cortese, HIST CORTESE, CERS Lower 2297, 0.435, East T135 FIRST DEVELOPMENT CO 19140 STEVENS CREEK UST FINDER RELEASE Lower 2297, 0.435, East 134 RECYCLETEK 10455 MILLER AVE SWRCY Higher 1928, 0.365, SSE S133 SHELL 19990 STEVENS CREEK LUST, HIST LUST, Cortese, HIST CORTESE Higher 1919, 0.363, West S132 SHELL SERVICE STATIO 19990 STEVENS CREEK RCRA-SQG, LUST, FINDS, ECHO, HWTS, HAZNET, CERS Higher 1919, 0.363, West S131 SHELL 19990 STEVENS CREEK UST FINDER RELEASE Higher 1919, 0.363, West S130 USA PETROLEUM COMPAN 19990 STEVENS CREEK LUST, HIST UST, Cortese, Notify 65, CERS Higher 1919, 0.363, West S129 SHELL 19990 STEVENS CREEK UST FINDER RELEASE Higher 1919, 0.363, West R128 JC PENNEY 10150 WOLFE HIST CORTESE Lower 1893, 0.359, NNE R127 J.C. PENNEY 10150 N WOLFE RD UST FINDER RELEASE Lower 1893, 0.359, NNE R126 J.C. PENNEY 10150 N WOLFE RD LUST, HIST UST, CERS Lower 1893, 0.359, NNE R125 J. C. PENNEY CO., IN 10150 N WOLFE RD LUST, HIST LUST, SWEEPS UST, CA FID UST, Cortese Lower 1893, 0.359, NNE Q124 FORMER TANDEM / APPL 19333 VALLCO PARKWAY CPS-SLIC, BROWNFIELDS, HIST UST, CERS Lower 1675, 0.317, NE Q123 TANDEM COMPUTERS LOC 19333 VALLCO PARKWAY SEMS-ARCHIVE, RCRA-SQG, SWEEPS UST, HIST UST, CA... Lower 1675, 0.317, NE 122 MIKE BIRDSALL 10151 DEEPROSE PLACE RCRA NonGen / NLR, E MANIFEST Higher 1314, 0.249, WSW N121 APPLE 19339 STEVENS CREEK CERS HAZ WASTE, CUPA Listings, CERS Lower 1286, 0.244, East P120 VALLCO PROPERTY OWNE 10123 N WOLFE RD RCRA NonGen / NLR, E MANIFEST Lower 1198, 0.227, North P119 VALLCO GENERATOR ROO 10123 N WOLFE RD CUPA Listings Lower 1198, 0.227, North P118 VALLCO FASHION PARK 10123 N WOLFE RD STE RCRA-SQG, FINDS, HWTS, HAZNET Lower 1198, 0.227, North P117 VALLCO PROPERTY OWNE 10123 N WOLFE RD RCRA NonGen / NLR, E MANIFEST Lower 1198, 0.227, North

MAPPED SITES SUMMARY
Target Property Address:

STEVENS CREEK BOULEVARD & E ESTATES DRIVE
CUPERTINO, CA 95014
Click on Map ID to see full detail.

MAP RELATIVE DIST (ft. & mi.)

ID DATABASE ACRONYMS ELEVATION DIRECTION SITE NAME ADDRESS 639
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TC07984167.2r EXECUTIVE SUMMARY 6

TARGET PROPERTY SEARCH RESULTS
The target property was not listed in any of the databases searched by EDR.

DATABASES WITH NO MAPPED SITES
No mapped sites were found in EDR’s search of available ("reasonably ascertainable ") government records either on the target property or within the search radius around the target property for the following databases:

STANDARD ENVIRONMENTAL RECORDS
Lists of Federal NPL (Superfund) sites
Proposed NPL Proposed National Priority List Sites
NPL LIENS Federal Superfund Liens
Lists of Federal Delisted NPL sites
Delisted NPL National Priority List Deletions
Lists of Federal sites subject to CERCLA removals and CERCLA orders FEDERAL FACILITY Federal Facility Site Information listing SEMS Superfund Enterprise Management System
Lists of Federal RCRA facilities undergoing Corrective Action CORRACTS Corrective Action Report
Lists of Federal RCRA TSD facilities
RCRA-TSDF RCRA - Treatment, Storage and Disposal
Lists of Federal RCRA generators
RCRA-VSQG RCRA - Very Small Quantity Generators (Formerly Conditionally Exempt Small Quantity Generators)
Federal institutional controls / engineering controls registries LUCIS Land Use Control Information System
US ENG CONTROLS Engineering Controls Sites List
US INST CONTROLS Institutional Controls Sites List
Federal ERNS list
ERNS Emergency Response Notification System
Lists of state and tribal landfills and solid waste disposal facilities SWF/LF Solid Waste Information System
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Lists of state and tribal leaking storage tanks
INDIAN LUST Leaking Underground Storage Tanks on Indian Land Lists of state and tribal registered storage tanks
FEMA UST Underground Storage Tank Listing
INDIAN UST Underground Storage Tanks on Indian Land
Lists of state and tribal voluntary cleanup sites
VCP Voluntary Cleanup Program Properties
INDIAN VCP Voluntary Cleanup Priority Listing

ADDITIONAL ENVIRONMENTAL RECORDS
Local Brownfield lists
US BROWNFIELDS A Listing of Brownfields Sites
Local Lists of Landfill / Solid Waste Disposal Sites
WMUDS/SWAT Waste Management Unit Database
HAULERS Registered Waste Tire Haulers Listing
INDIAN ODI Report on the Status of Open Dumps on Indian Lands ODI Open Dump Inventory
DEBRIS REGION 9 Torres Martinez Reservation Illegal Dump Site Locations IHS OPEN DUMPS Open Dumps on Indian Land
Local Lists of Hazardous waste / Contaminated Sites
US HIST CDL Delisted National Clandestine Laboratory Register SCH School Property Evaluation Program
CDL Clandestine Drug Labs
Toxic Pits Toxic Pits Cleanup Act Sites
US CDL National Clandestine Laboratory Register
Local Land Records
LIENS Environmental Liens Listing
LIENS 2 CERCLA Lien Information
DEED Deed Restriction Listing
Records of Emergency Release Reports
HMIRS Hazardous Materials Information Reporting System
CHMIRS California Hazardous Material Incident Report System LDS Land Disposal Sites Listing
MCS Military Cleanup Sites Listing
SPILLS 90 SPILLS 90 data from FirstSearch
Other Ascertainable Records
FUDS Formerly Used Defense Sites
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DOD Department of Defense Sites
SCRD DRYCLEANERS State Coalition for Remediation of Drycleaners Listing US FIN ASSUR Financial Assurance Information

EPA WATCH LIST EPA WATCH LIST
2020 COR ACTION 2020 Corrective Action Program List
TSCA Toxic Substances Control Act
TRIS Toxic Chemical Release Inventory System
SSTS Section 7 Tracking Systems
RMP Risk Management Plans
RAATS RCRA Administrative Action Tracking System
PRP Potentially Responsible Parties
PADS PCB Activity Database System
ICIS Integrated Compliance Information System
FTTS FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Control Act)
MLTS Material Licensing Tracking System
COAL ASH DOE Steam-Electric Plant Operation Data
COAL ASH EPA Coal Combustion Residues Surface Impoundments List PCB TRANSFORMER PCB Transformer Registration Database
RADINFO Radiation Information Database
HIST FTTS FIFRA/TSCA Tracking System Administrative Case Listing DOT OPS Incident and Accident Data
CONSENT Superfund (CERCLA) Consent Decrees
INDIAN RESERV Indian Reservations
FUSRAP Formerly Utilized Sites Remedial Action Program
UMTRA Uranium Mill Tailings Sites
LEAD SMELTERS Lead Smelter Sites
US AIRS Aerometric Information Retrieval System Facility Subsystem US MINES Mines Master Index File
MINES MRDS Mineral Resources Data System
ABANDONED MINES Abandoned Mines
DOCKET HWC Hazardous Waste Compliance Docket Listing
UXO Unexploded Ordnance Sites
FUELS PROGRAM EPA Fuels Program Registered Listing
PFAS NPL Superfund Sites with PFAS Detections Information PFAS FEDERAL SITES Federal Sites PFAS Information
PFAS TRIS List of PFAS Added to the TRI
PFAS TSCA PFAS Manufacture and Imports Information
PFAS RCRA MANIFEST PFAS Transfers Identified In the RCRA Database Listing PFAS ATSDR PFAS Contamination Site Location Listing
PFAS WQP Ambient Environmental Sampling for PFAS
PFAS NPDES Clean Water Act Discharge Monitoring Information

PFAS PROJECT NORTHEASTERN UNIVERSITY PFAS PROJECT
PFAS ECHO Facilities in Industries that May Be Handling PFAS Listing PFAS ECHO FIRE TRAIN Facilities in Industries that May Be Handling PFAS Listing PFAS PT 139 AIRPORT All Certified Part 139 Airports PFAS Information Listing AQUEOUS FOAM NRC Aqueous Foam Related Incidents Listing BIOSOLIDS ICIS-NPDES Biosolids Facility Data
PFAS PFAS Investigation Site Location Listing
AQUEOUS FOAM Former Fire Training Facility Assessments Listing CA BOND EXP. PLAN Bond Expenditure Plan
CHROME PLATING Chrome Plating Facilities Listing
ENF Enforcement Action Listing
Financial Assurance Financial Assurance Information Listing ICE Inspection, Compliance and Enforcement
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HWT Registered Hazardous Waste Transporter Database
MINES Mines Site Location Listing
MWMP Medical Waste Management Program Listing
NPDES NPDES Permits Listing
PEST LIC Pesticide Regulation Licenses Listing
PROC Certified Processors Database
HAZMAT Hazardous Material Facilities
UIC UIC Listing

UIC GEO UIC GEO (GEOTRACKER)
WASTEWATER PITS Oil Wastewater Pits Listing
WDS Waste Discharge System
WIP Well Investigation Program Case List

MILITARY PRIV SITES MILITARY PRIV SITES (GEOTRACKER)

PROJECT PROJECT (GEOTRACKER)
WDR Waste Discharge Requirements Listing
CIWQS California Integrated Water Quality System

NON-CASE INFO NON-CASE INFO (GEOTRACKER)

OTHER OIL GAS OTHER OIL & GAS (GEOTRACKER)

PROD WATER PONDS PROD WATER PONDS (GEOTRACKER)

SAMPLING POINT SAMPLING POINT (GEOTRACKER)
WELL STIM PROJ Well Stimulation Project (GEOTRACKER)

EDR HIGH RISK HISTORICAL RECORDS
EDR Exclusive Records
EDR MGP EDR Proprietary Manufactured Gas Plants

EDR RECOVERED GOVERNMENT ARCHIVES
Exclusive Recovered Govt. Archives
RGA LF Recovered Government Archive Solid Waste Facilities List RGA LUST Recovered Government Archive Leaking Underground Storage Tank SURROUNDING SITES: SEARCH RESULTS
Surrounding sites were identified in the following databases.

Elevations have been determined from the USGS Digital Elevation Model and should be evaluated on a relative (not an absolute) basis. Relative elevation information between sites of close proximity should be field verified. Sites with an elevation equal to or higher than the target property have been differentiated below from sites with an elevation lower than the target property.

Page numbers and map identification numbers refer to the EDR Radius Map report where detailed data on individual sites can be reviewed.

Sites listed in bold italics are in multiple databases.

Unmappable (orphan) sites are not considered in the foregoing analysis. 643
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STANDARD ENVIRONMENTAL RECORDS
Lists of Federal NPL (Superfund) sites
NPL: Also known as Superfund, the National Priority List database is a subset of CERCLIS and identifies over 1,200 sites for priority cleanup under the Superfund program. The source of this database is the U.S. EPA.

A review of the NPL list, as provided by EDR, and dated 03/27/2025 has revealed that there is 1 NPL site within approximately 1 mile of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ PANASONIC 10900 N TANTAU AVENU NE 1/2 - 1 (0.948 mi.) 0 9 Cerclis ID:: 901325
EPA Id: CAD041472341
Lists of Federal CERCLA sites with NFRAP
SEMS-ARCHIVE: SEMS-ARCHIVE (Superfund Enterprise Management System Archive) tracks sites that have no further interest under the Federal Superfund Program based on available information. The list was formerly known as the CERCLIS-NFRAP, renamed to SEMS ARCHIVE by the EPA in 2015. EPA may perform a minimal level of assessment work at a site while it is archived if site conditions change and/or new information becomes available. Archived sites have been removed and archived from the inventory of SEMS sites. Archived status indicates that, to the best of EPA’s knowledge, assessment at a site has been completed and that EPA has determined no further steps will be taken to list the site on the National Priorities List (NPL), unless information indicates this decision was not appropriate or other considerations require a recommendation for listing at a later time. The decision does not necessarily mean that there is no hazard associated with a given site; it only means that. based upon available information, the location is not judged to be potential NPL site.

A review of the SEMS-ARCHIVE list, as provided by EDR, and dated 03/27/2025 has revealed that there is 1 SEMS-ARCHIVE site within approximately 0.5 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ TANDEM COMPUTERS LOC 19333 VALLCO PARKWAY NE 1/4 - 1/2 (0.317 mi.) Q123 620 Site ID: 0901539
EPA Id: CAD069101152
Lists of Federal RCRA generators
RCRA-LQG: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Large quantity generators (LQGs) generate over 1,000 kilograms (kg) of hazardous waste, or over 1 kg of acutely hazardous waste per month.

A review of the RCRA-LQG list, as provided by EDR, and dated 02/17/2025 has revealed that there is 1 644
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RCRA-LQG site within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 EPA ID:: CAD981579311
RCRA-SQG: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Small quantity generators (SQGs) generate between 100 kg and 1,000 kg of hazardous waste per month.

A review of the RCRA-SQG list, as provided by EDR, and dated 02/17/2025 has revealed that there are 6 RCRA-SQG sites within approximately 0.25 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ WARDROB CUSTOM CLEAN 19705 STEVENS CRK BL WNW 0 - 1/8 (0.111 mi.) G64 245 EPA ID:: CAD982022998
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ TOSCO NORTHWEST CO N 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A15 112 EPA ID:: CA0001036896
SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 EPA ID:: CAD983590241
THE PICTURE PEOPLE 19123 N WOLFE RD MS NNE 0 - 1/8 (0.114 mi.) F68 249 EPA ID:: CAD983667304
KITS CAMERAS ONE HR 10123 N WOLFE RD STE N 1/8 - 1/4 (0.227 mi.) P113 576 EPA ID:: CAD983646282
VALLCO FASHION PARK 10123 N WOLFE RD STE N 1/8 - 1/4 (0.227 mi.) P118 601 EPA ID:: CAR000038307
Lists of state- and tribal (Superfund) equivalent sites RESPONSE: Identifies confirmed release sites where DTSC is involved in remediation, either in a lead or oversight capacity. These confirmed release sites are generally high-priority and high potential risk.

A review of the RESPONSE list, as provided by EDR, has revealed that there is 1 RESPONSE site within approximately 1 mile of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ SAFEWAY STORE 767 6150 BOLLINGER RD SSE 1/2 - 1 (0.852 mi.) 142 684 Database: RESPONSE, Date of Government Version: 01/21/2025 Status: Certified O&M - Land Use Restrictions Only
Facility Id: 43280131
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Lists of state- and tribal hazardous waste facilities
ENVIROSTOR: The Department of Toxic Substances Control’s (DTSC’s) Site Mitigation and Brownfields Reuse Program’s (SMBRP’s) EnviroStor database identifes sites that have known contamination or sites for which there may be reasons to investigate further. The database includes the following site types: Federal Superfund sites (National Priorities List (NPL)); State Response, including Military Facilities and State Superfund; Voluntary Cleanup; and School sites. EnviroStor provides similar information to the information that was available in CalSites, and provides additional site information, including, but not limited to, identification of formerly-contaminated properties that have been released for reuse, properties where environmental deed restrictions have been recorded to prevent inappropriate land uses, and risk characterization information that is used to assess potential impacts to public health and the environment at contaminated sites.

A review of the ENVIROSTOR list, as provided by EDR, and dated 01/21/2025 has revealed that there are 7 ENVIROSTOR sites within approximately 1 mile of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ PANASONIC 10900 N TANTAU AVENU NE 1/2 - 1 (0.948 mi.) 0 9 Facility Id: 43360032
Status: Refer: RWQCB
SEDGWICK ELEMENTARY 10480 FINCH AVENUE SE 1/2 - 1 (0.510 mi.) 139 668 Facility Id: 60002143
Status: Certified
SAFEWAY STORE 767 6150 BOLLINGER RD SSE 1/2 - 1 (0.852 mi.) 142 684 Facility Id: 43280131
Status: Certified O&M - Land Use Restrictions Only
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ AMPEX CUPERTINO FACI 10435 N TANTAU AVE NE 1/2 - 1 (0.631 mi.) 140 679 Facility Id: 43380012
Status: Refer: RWQCB
VALLCO BUILDING 80 10432 N. TANTAU AVEN NE 1/2 - 1 (0.722 mi.) 141 682 Facility Id: 43360116
Status: Refer: RWQCB
HEWLETT PACKARD COSA 5301 STEVENS CREEK B E 1/2 - 1 (0.942 mi.) 143 698 Facility Id: 43380016
Facility Id: 80001401
Facility Id: 71002428
Status: Refer: Other Agency
Status: Inactive - Needs Evaluation
CUPERTINO VILLAGE CL 10989 NORTH WOLFE RO N 1/2 - 1 (0.955 mi.) 144 731 Facility Id: 60000385
Status: Active
Lists of state and tribal leaking storage tanks
LUST: Leaking Underground Storage Tank (LUST) Sites included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater.

A review of the LUST list, as provided by EDR, has revealed that there are 14 LUST sites within 646
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approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ USA PETROLEUM COMPAN 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S130 636 Database: LUST, Date of Government Version: 02/24/2025
Status: Completed - Case Closed
Global Id: T0608501271
Global Id: T0608514737
SHELL SERVICE STATIO 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S132 644 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Date Closed: 11/21/1995
Date Closed: 07/19/2005
SCVWD ID: 07S1W18E01F
SCVWD ID: 07S1W18M01F
SHELL 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S133 653 Database: LUST REG 2, Date of Government Version: 09/30/2004 Facility Status: Case Closed
Facility Status: Preliminary site assessment underway
date9: 11/21/1995
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A14 95
Database: LUST REG 2, Date of Government Version: 09/30/2004 Database: LUST, Date of Government Version: 02/24/2025
Status: Completed - Case Closed
Facility Status: Case Closed
Global Id: T0608575840
Global Id: T0608500926
date9: 3/15/1996
BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A20 120 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Date Closed: 03/15/1996
SCVWD ID: 07S1W18L01F
SCVWD ID: 07S1W18F01F
TOSCO #11220 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A24 139 Database: LUST REG 2, Date of Government Version: 09/30/2004 Facility Status: Remedial action (cleanup) Underway
SHELL 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D36 163 Database: LUST REG 2, Date of Government Version: 09/30/2004 Database: LUST, Date of Government Version: 02/24/2025
Status: Completed - Case Closed
Facility Status: Case Closed
Global Id: T0608501269
date9: 9/30/1994
ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D42 182 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Date Closed: 09/30/1994
SCVWD ID: 07S1W18F02F
SEARS, #1468 10101 N WOLFE RD N 0 - 1/8 (0.084 mi.) E45 194 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Date Closed: 12/06/1999
SCVWD ID: 07S1W18G01F
SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 Database: LUST REG 2, Date of Government Version: 09/30/2004 Database: LUST, Date of Government Version: 02/24/2025
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Status: Completed - Case Closed
Facility Status: Case Closed
Global Id: T0608552828
date9: 12/6/1999
J. C. PENNEY CO., IN 10150 N WOLFE RD NNE 1/4 - 1/2 (0.359 mi.) R125 629 Database: LUST REG 2, Date of Government Version: 09/30/2004 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Facility Status: Case Closed
Date Closed: 09/01/1994
SCVWD ID: 07S1W18B01F
date9: 9/1/1994
J.C. PENNEY 10150 N WOLFE RD NNE 1/4 - 1/2 (0.359 mi.) R126 631 Database: LUST, Date of Government Version: 02/24/2025
Status: Completed - Case Closed
Global Id: T0608500770
FIRST DEVELOPMENT CO 19140 STEVENS CREEK E 1/4 - 1/2 (0.435 mi.) T136 656 Database: LUST REG 2, Date of Government Version: 09/30/2004 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Database: LUST, Date of Government Version: 02/24/2025
Status: Completed - Case Closed
Facility Status: Case Closed
Date Closed: 11/04/1991
Global Id: T0608500624
SCVWD ID: 07S1W18J01F
date9: 11/4/1991
FIRST DEVELOPMENT CO 19110 STEVENS CREEK E 1/4 - 1/2 (0.461 mi.) T137 660 Database: LUST REG 2, Date of Government Version: 09/30/2004 Database: LUST SANTA CLARA, Date of Government Version: 03/03/2014 Database: LUST, Date of Government Version: 02/24/2025
Status: Completed - Case Closed
Facility Status: Case Closed
Date Closed: 11/02/1993
Date Closed: 06/27/1995
Global Id: T0608502296
Global Id: T0608500623
SCVWD ID: 07S1W18H01F
SCVWD ID: 07S1W18H02F
date9: 6/27/1995
date9: 11/2/1993
CPS-SLIC: Cleanup Program Sites (CPS; also known as Site Cleanups [SC] and formerly known as Spills, Leaks, Investigations, and Cleanups [SLIC] sites) included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater.

A review of the CPS-SLIC list, as provided by EDR, has revealed that there are 5 CPS-SLIC sites within approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ 19720 STEVENS CREEK 19720 STEVENS CREEK W 0 - 1/8 (0.090 mi.) C53 216 Database: CPS-SLIC, Date of Government Version: 02/24/2025 Global Id: T10000016970
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Facility Status: Open - Assessment & Interim Remedial Action Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 Database: CPS-SLIC, Date of Government Version: 02/24/2025 Global Id: T10000021095
Facility Status: Open - Remediation
ICE CENTER ENTERPRIS 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P107 553 Database: CPS-SLIC, Date of Government Version: 02/24/2025 Global Id: T10000020648
Facility Status: Open - Site Assessment
ICE CAPADES CHALET 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P116 594 Database: CPS-SLIC, Date of Government Version: 02/24/2025 Global Id: T10000017167
Facility Status: Open - Remediation
FORMER TANDEM / APPL 19333 VALLCO PARKWAY NE 1/4 - 1/2 (0.317 mi.) Q124 626 Database: CPS-SLIC, Date of Government Version: 02/24/2025 Database: SLIC REG 2, Date of Government Version: 09/30/2004 Global Id: T10000000740
Facility Id: SL18235653
Facility Status: Completed - Case Closed
HIST LUST: A listing of open and closed leaking underground storage tanks. This listing is no longer updated by the county. Leaking underground storage tanks are now handled by the Department of Environmental Health.

A review of the HIST LUST list, as provided by EDR, and dated 03/29/2005 has revealed that there are 8 HIST LUST sites within approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ SHELL 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S133 653 SCVWD ID: 07S1W18E01
SCVWD ID: 07S1W18M01
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A14 95
SCVWD ID: 07S1W18F01
TOSCO #11220 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A24 139 SCVWD ID: 07S1W18L01
SHELL 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D36 163 SCVWD ID: 07S1W18F02
SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 SCVWD ID: 07S1W18G01
J. C. PENNEY CO., IN 10150 N WOLFE RD NNE 1/4 - 1/2 (0.359 mi.) R125 629 SCVWD ID: 07S1W18B01
FIRST DEVELOPMENT CO 19140 STEVENS CREEK E 1/4 - 1/2 (0.435 mi.) T136 656 SCVWD ID: 07S1W18J01
FIRST DEVELOPMENT CO 19110 STEVENS CREEK E 1/4 - 1/2 (0.461 mi.) T137 660 649
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SCVWD ID: 07S1W18H01
SCVWD ID: 07S1W18H02
Lists of state and tribal registered storage tanks
UST: The Underground Storage Tank database contains registered USTs. USTs are regulated under Subtitle I of the Resource Conservation and Recovery Act (RCRA). The data come from the State Water Resources Control Board’s Hazardous Substance Storage Container Database.

A review of the UST list, as provided by EDR, has revealed that there are 4 UST sites within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ APRO DISTRIBUTION 22 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A8 87 Database: UST, Date of Government Version: 11/26/2024
VALLCO 76 #112220-30 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A11 90 Database: UST, Date of Government Version: 11/26/2024
Facility Id: 39
BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A13 92 Database: UST, Date of Government Version: 11/26/2024
PLATINUM ENERGY #261 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A18 117 Database: UST, Date of Government Version: 11/26/2024
AST: A listing of aboveground storage tank petroleum storage tank locations.

A review of the AST list, as provided by EDR, has revealed that there are 3 AST sites within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ JIFFY-LUBE 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D38 167 Database: AST, Date of Government Version: 07/06/2016
ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D42 182 Database: AST, Date of Government Version: 07/06/2016
SEARS AUTO CENTER 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E44 194 Database: AST, Date of Government Version: 07/06/2016
Lists of state and tribal brownfield sites
BROWNFIELDS: A listing of sites the SWRCB considers to be Brownfields since these are sites have come to them through the MOA Process.

A review of the BROWNFIELDS list, as provided by EDR, and dated 12/11/2024 has revealed that there is 1 BROWNFIELDS site within approximately 0.5 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ FORMER TANDEM / APPL 19333 VALLCO PARKWAY NE 1/4 - 1/2 (0.317 mi.) Q124 626 650
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ADDITIONAL ENVIRONMENTAL RECORDS
Local Lists of Landfill / Solid Waste Disposal Sites
SWRCY: A listing of recycling facilities in California.

A review of the SWRCY list, as provided by EDR, and dated 12/02/2024 has revealed that there is 1 SWRCY site within approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ RECYCLETEK 10455 MILLER AVE SSE 1/4 - 1/2 (0.365 mi.) 134 655 Cert Id: RC317024.001
Local Lists of Hazardous waste / Contaminated Sites
HIST Cal-Sites: Formerly known as ASPIS, this database contains both known and potential hazardous substance sites. The source is the California Department of Toxic Substance Control. No longer updated by the state agency. It has been replaced by ENVIROSTOR.

A review of the HIST Cal-Sites list, as provided by EDR, and dated 08/08/2005 has revealed that there is 1 HIST Cal-Sites site within approximately 1 mile of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ PANASONIC 10900 N TANTAU AVENU NE 1/2 - 1 (0.948 mi.) 0 9 CERS HAZ WASTE: List of sites in the California Environmental Protection Agency (CalEPA) Regulated Site Portal which fall under the Hazardous Chemical Management, Hazardous Waste Onsite Treatment, Household Hazardous Waste Collection, Hazardous Waste Generator, and RCRA LQ HW Generator programs.

A review of the CERS HAZ WASTE list, as provided by EDR, and dated 01/12/2025 has revealed that there are 7 CERS HAZ WASTE sites within approximately 0.25 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ THEODORE A FLOOR DDS 10055 N PORTAL AV 10 WNW 1/8 - 1/4 (0.211 mi.) O103 546 Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A20 120 FUJIMOTO&LEE ORAL&MA 10055 MILLER AV ESE 0 - 1/8 (0.034 mi.) A26 144 DRS LIN & LO DMD INC 10055 MILLER AV 102 ESE 0 - 1/8 (0.034 mi.) A27 145 ANNE E MURRAY DDS 10055 MILLER AV 104 ESE 0 - 1/8 (0.034 mi.) A30 149 ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D42 182 APPLE 19339 STEVENS CREEK E 1/8 - 1/4 (0.244 mi.) N121 613 651
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Local Lists of Registered Storage Tanks
SWEEPS UST: Statewide Environmental Evaluation and Planning System. This underground storage tank listing was updated and maintained by a company contacted by the SWRCB in the early 1990’s. The listing is no longer updated or maintained. The local agency is the contact for more information on a site on the SWEEPS list.

A review of the SWEEPS UST list, as provided by EDR, and dated 06/01/1994 has revealed that there are 4 SWEEPS UST sites within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A14 95
Status: A
Tank Status: A
Comp Number: 39669
BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A20 120 Status: A
Tank Status: A
Comp Number: 501
ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D39 168 Comp Number: 9161
SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 Comp Number: 7020
HIST UST: Historical UST Registered Database.

A review of the HIST UST list, as provided by EDR, and dated 10/15/1990 has revealed that there are 4 HIST UST sites within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL SERVICE STATIO 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A9 89 Facility Id: 00000039669
ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D39 168 Facility Id: 00000009161
SEARS, #1468 10101 N WOLFE RD N 0 - 1/8 (0.084 mi.) E45 194 SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 Facility Id: 00000007020
CERS TANKS: List of sites in the California Environmental Protection Agency (CalEPA) Regulated Site Portal which fall under the Aboveground Petroleum Storage and Underground Storage Tank regulatory programs.

A review of the CERS TANKS list, as provided by EDR, and dated 01/12/2025 has revealed that there are 2 CERS TANKS sites within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A20 120 ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D42 182 652
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CA FID UST: The Facility Inventory Database contains active and inactive underground storage tank locations. The source is the State Water Resource Control Board.

A review of the CA FID UST list, as provided by EDR, and dated 10/31/1994 has revealed that there are 3 CA FID UST sites within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A20 120 Facility Id: 43001002
Status: A
ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D42 182 Facility Id: 43001308
Status: I
SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 Facility Id: 43007398
Status: I
Other Ascertainable Records
RCRA NonGen / NLR: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Non-Generators do not presently generate hazardous waste.

A review of the RCRA NonGen / NLR list, as provided by EDR, and dated 02/17/2025 has revealed that there are 54 RCRA NonGen / NLR sites within approximately 0.25 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ AL ORTIZ 10140 RICH WOOD DRIV SSW 0 - 1/8 (0.029 mi.) B25 140 EPA ID:: CAC003262198
FUSION ACADEMY CUPER 19638 STEVENS CREEK W 0 - 1/8 (0.038 mi.) C34 157 EPA ID:: CAL000480892
10142 EAST ESTATES D 10142 EAST ESTATES D SSE 0 - 1/8 (0.040 mi.) B35 159 EPA ID:: CAC003207317
10221 VICKSBURG DRIV 10221 VICKSBURG DRIV S 0 - 1/8 (0.121 mi.) 69 252 EPA ID:: CAC002985289
DAISO 6986 19750 STEVENS CREEK WSW 0 - 1/8 (0.122 mi.) H70 256 EPA ID:: CAL000482526
JACK MCKEOWN 10196 AVOCADO PLACE SW 1/8 - 1/4 (0.137 mi.) 74 267 EPA ID:: CAC003175468
PARTHA MURALI 10277 EAST ESTATES D S 1/8 - 1/4 (0.159 mi.) 76 274 EPA ID:: CAC003184879
19782 BIXBY DRIVE 19782 BIXBY DRIVE WSW 1/8 - 1/4 (0.177 mi.) K81 300 EPA ID:: CAC003194464
BRIAN FEINBERG 19782 BIXBY DR WSW 1/8 - 1/4 (0.177 mi.) K82 304 EPA ID:: CAC003262957
GARDENS AT FONTAINEB 10200 MILLER AVENUE SSE 1/8 - 1/4 (0.180 mi.) L83 308 653
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EPA ID:: CAC003242566
GARDENS OF FONTAINEB 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L84 313 EPA ID:: CAC003223618
EPA ID:: CAC003187447
EPA ID:: CAC003206985
EPA ID:: CAC003241022
GARDENS OF FONTAINBL 10200 MILLER AVENUE SSE 1/8 - 1/4 (0.180 mi.) L85 324 EPA ID:: CAC003312444
GARDENS APARTMENTS 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L86 328 EPA ID:: CAC003128766
EPA ID:: CAC003113376
EPA ID:: CAC003095190
SONTAR APARTMENTS 10200 MILLER AVE. SSE 1/8 - 1/4 (0.180 mi.) L87 339 EPA ID:: CAC003319977
GARDENS 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L88 342 EPA ID:: CAC003144194
GARDENS 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L89 353 EPA ID:: CAC003173292
EPA ID:: CAC003157856
EPA ID:: CAC003237700
GARDENS OF FOUNTAINB 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L90 364 EPA ID:: CAC003290066
EPA ID:: CAC003261424
GARDENS OF FOUNTAINB 10200 MILLER MAVE SSE 1/8 - 1/4 (0.180 mi.) L91 375 EPA ID:: CAC003274393
ZHEN LI 19773 WINTERGREEN DR SW 1/8 - 1/4 (0.194 mi.) 93 384 EPA ID:: CAC003150175
CHRYSTAL SILVA DUENO 10277 COLD HARBOR AV SW 1/8 - 1/4 (0.196 mi.) 95 390 EPA ID:: CAC003185617
MIKE BIRDSALL 10151 DEEPROSE PLACE WSW 1/8 - 1/4 (0.249 mi.) 122 616 EPA ID:: CAC003307225
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ APRO LLC DBA UNITED 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A7 82 EPA ID:: CAL000443757
VALLCO 76 SVC 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A19 118 EPA ID:: CAL000191947
STAN BOYETT & SON IN 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A21 136 EPA ID:: CAL000478912
ANNE E MURRAY, DDS 10055 MILLER AVE STE ESE 0 - 1/8 (0.034 mi.) A31 152 EPA ID:: CAL000258150
STACEY A LEE A DENTA 10055 MILLER AVE #10 ESE 0 - 1/8 (0.034 mi.) A32 154 EPA ID:: CAL000489828
JIFFY LUBE # 2355 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D41 171 EPA ID:: CAL000336645
BADGER DAYLIGHTING 10101 NORTH WOLFE RO N 0 - 1/8 (0.084 mi.) E49 209 EPA ID:: CAC003135042
VALLCO PROPERTYOWNER 10000 N WOLFE ROAD NE 0 - 1/8 (0.101 mi.) F56 225 654
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EPA ID:: CAP000364448
VALLCO PROPERTY OWNE 10000 N WOLFE ROAD NE 0 - 1/8 (0.101 mi.) F57 227 EPA ID:: CAC003261990
KAISER CUPERTINO OCC 10050 N WOLFE RD NE 0 - 1/8 (0.103 mi.) F58 230 EPA ID:: CAR000284257
KAISER OCCUPATIONAL 10050 N WOLFE RD 1-1 NE 0 - 1/8 (0.103 mi.) F59 233 EPA ID:: CAL000420146
I & G DIRECT REAL ES 10080 N WOLFE RD NE 0 - 1/8 (0.103 mi.) F60 235 EPA ID:: CAC003323742
I & G DIRECT REAL ES 10080 N. WOLFE ROAD NE 0 - 1/8 (0.103 mi.) F63 241 EPA ID:: CAC003023750
ROSEMARIE PLACE 19472 ROSEMARIE PLAC SE 1/8 - 1/4 (0.127 mi.) 72 259 EPA ID:: CAC002984767
19698 WHEATON DR 19698 WHEATON DR NW 1/8 - 1/4 (0.129 mi.) I73 263 EPA ID:: CAC003022302
HOPYARD PROPERTY MAN 19400 STEVENS CREEK E 1/8 - 1/4 (0.146 mi.) J75 271 EPA ID:: CAL000461481
EDWARD & LYNN PUCCIN 10128 DENISON AVENUE NNW 1/8 - 1/4 (0.159 mi.) I77 278 EPA ID:: CAC003016706
BANK OF AMERICA 19376 STEVENS CREEK E 1/8 - 1/4 (0.176 mi.) J78 282 EPA ID:: CAC002996164
BANK OF AMERICA 19376 STEVENS CREEK E 1/8 - 1/4 (0.176 mi.) J79 290 EPA ID:: CAC002983657
CA7-701-01-28 19376 STEVENS CREEK E 1/8 - 1/4 (0.176 mi.) J80 298 EPA ID:: CAC002997592
MASATO KAIDA 10154 DENISON AVENUE NNW 1/8 - 1/4 (0.184 mi.) M92 380 EPA ID:: CAC003254947
10153 DENISON AVE 10153 DENISON AVE NW 1/8 - 1/4 (0.195 mi.) M94 388 EPA ID:: CAC003043422
ELLEN WU 10168 DENISON AVE NNW 1/8 - 1/4 (0.197 mi.) M96 394 EPA ID:: CAC003081430
TARGET 3224 19499 STEVENS CREEK E 1/8 - 1/4 (0.209 mi.) N98 435 EPA ID:: CAR000266254
CVS (SIS) 19499 STEVENS CREEK E 1/8 - 1/4 (0.209 mi.) N100 532 EPA ID:: CAR000269852
VALLCO PROPERTY OWNE 10123 N. WOLFE RD N 1/8 - 1/4 (0.227 mi.) P105 548 EPA ID:: CAC003247639
ICE CENTER CUPERTINO 10123 N WOLFE RD STE N 1/8 - 1/4 (0.227 mi.) P106 551 EPA ID:: CAL000431845
VALLCO PROPERTY OWNE 10123 NORTH WOLFE RO N 1/8 - 1/4 (0.227 mi.) P108 558 EPA ID:: CAC003194790
ICE CENTER CUPERTINO 10123 N WOLFE ROAD, N 1/8 - 1/4 (0.227 mi.) P112 572 EPA ID:: CAC003300539
VALLCO SHOPPING MALL 10123 N WOLFE RD STE N 1/8 - 1/4 (0.227 mi.) P114 579 EPA ID:: CAL000405154
VALLCO PROPERTY OWNE 10123 N. WOLFE ROAD N 1/8 - 1/4 (0.227 mi.) P115 589 655
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EPA ID:: CAC003232625
EPA ID:: CAC002997606
VALLCO PROPERTY OWNE 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P117 596 EPA ID:: CAC003057272
VALLCO PROPERTY OWNE 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P120 607 EPA ID:: CAP000355214
EPA ID:: CAC003034443
ROD: Record of Decision. ROD documents mandate a permanent remedy at an NPL (Superfund) site containing technical and health information to aid the cleanup.

A review of the ROD list, as provided by EDR, and dated 01/29/2025 has revealed that there is 1 ROD site within approximately 1 mile of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ PANASONIC 10900 N TANTAU AVENU NE 1/2 - 1 (0.948 mi.) 0 9 EPA ID:: CAD041472341
FINDS: The Facility Index System contains both facility information and "pointers" to other sources of information that contain more detail. These include: RCRIS; Permit Compliance System (PCS); Aerometric Information Retrieval System (AIRS); FATES (FIFRA [Federal Insecticide Fungicide Rodenticide Act] and TSCA Enforcement System, FTTS [FIFRA/TSCA Tracking System]; CERCLIS; DOCKET (Enforcement Docket used to manage and track information on civil judicial enforcement cases for all environmental statutes); Federal Underground Injection Control (FURS); Federal Reporting Data System (FRDS); Surface Impoundments (SIA); TSCA Chemicals in Commerce Information System (CICS); PADS; RCRA-J (medical waste transporters/disposers); TRIS; and TSCA. The source of this database is the U.S. EPA/NTIS.

A review of the FINDS list, as provided by EDR, and dated 11/11/2024 has revealed that there are 2 FINDS sites within approximately 0.001 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 Registry ID:: 110009537698
ONE HOUR MARTINIZING 10045 E ESTATES DRIV 0 - 1/8 (0.000 mi.) A6 82 Registry ID:: 110071743262
ECHO: ECHO provides integrated compliance and enforcement information for about 800,000 regulated facilities nationwide.

A review of the ECHO list, as provided by EDR, and dated 12/21/2024 has revealed that there is 1 ECHO site within approximately 0.001 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR MARTINIZING 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A3 41 Registry ID: 110009537698
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UST FINDER RELEASE: US EPA’s UST Finder data is a national composite of leaking underground storage tanks.

This data contains information about, and locations of, leaking underground storage tanks. Data was collected from state sources and standardized into a national profile by EPA’s Office of Underground Storage Tanks, Office of Research and Development, and the Association of State and Territorial Solid Waste Management Officials.

A review of the UST FINDER RELEASE list, as provided by EDR, and dated 06/08/2023 has revealed that there are 9 UST FINDER RELEASE sites within approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ SHELL 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S129 635 SHELL 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S131 643 Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A12 91
TOSCO #11220 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A23 138 SHELL 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D40 170 SEARS AUTOMOTIVE CEN 10101 N WOLFE RD N 0 - 1/8 (0.084 mi.) E46 197 J.C. PENNEY 10150 N WOLFE RD NNE 1/4 - 1/2 (0.359 mi.) R127 634 FIRST DEVELOPMENT CO 19140 STEVENS CREEK E 1/4 - 1/2 (0.435 mi.) T135 655 FIRST DEVELOPMENT CO 19110 STEVENS CREEK E 1/4 - 1/2 (0.461 mi.) T138 667 UST FINDER: EPA developed UST Finder, a web map application containing a comprehensive, state-sourced national map of underground storage tank (UST) and leaking UST (LUST) data. It provides the attributes and locations of active and closed USTs, UST facilities, and LUST sites from states and from Tribal lands and US territories . UST Finder contains information about proximity of UST facilities and LUST sites to: surface and groundwater public drinking water protection areas; estimated number of private domestic wells and number of people living nearby; and flooding and wildfires.

A review of the UST FINDER list, as provided by EDR, and dated 06/08/2023 has revealed that there is 1 UST FINDER site within approximately 0.25 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ APRO DISTRIBUTION 22 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A16 115 E MANIFEST: EPA established a national system for tracking hazardous waste shipments electronically.

This system, known as ?e-Manifest,? will modernize the nation?s cradle-to-grave hazardous waste tracking process while saving valuable time, resources, and dollars for industry and states.

A review of the E MANIFEST list, as provided by EDR, and dated 02/17/2025 has revealed that there are 38 E MANIFEST sites within approximately 0.25 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ AL ORTIZ 10140 RICH WOOD DRIV SSW 0 - 1/8 (0.029 mi.) B25 140 10142 EAST ESTATES D 10142 EAST ESTATES D SSE 0 - 1/8 (0.040 mi.) B35 159 10221 VICKSBURG DRIV 10221 VICKSBURG DRIV S 0 - 1/8 (0.121 mi.) 69 252 JACK MCKEOWN 10196 AVOCADO PLACE SW 1/8 - 1/4 (0.137 mi.) 74 267 PARTHA MURALI 10277 EAST ESTATES D S 1/8 - 1/4 (0.159 mi.) 76 274 19782 BIXBY DRIVE 19782 BIXBY DRIVE WSW 1/8 - 1/4 (0.177 mi.) K81 300 BRIAN FEINBERG 19782 BIXBY DR WSW 1/8 - 1/4 (0.177 mi.) K82 304 GARDENS AT FONTAINEB 10200 MILLER AVENUE SSE 1/8 - 1/4 (0.180 mi.) L83 308 GARDENS OF FONTAINEB 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L84 313 GARDENS OF FONTAINBL 10200 MILLER AVENUE SSE 1/8 - 1/4 (0.180 mi.) L85 324 657
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Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ GARDENS APARTMENTS 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L86 328 GARDENS 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L88 342 GARDENS 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L89 353 GARDENS OF FOUNTAINB 10200 MILLER AVE SSE 1/8 - 1/4 (0.180 mi.) L90 364 GARDENS OF FOUNTAINB 10200 MILLER MAVE SSE 1/8 - 1/4 (0.180 mi.) L91 375 ZHEN LI 19773 WINTERGREEN DR SW 1/8 - 1/4 (0.194 mi.) 93 384 CHRYSTAL SILVA DUENO 10277 COLD HARBOR AV SW 1/8 - 1/4 (0.196 mi.) 95 390 MIKE BIRDSALL 10151 DEEPROSE PLACE WSW 1/8 - 1/4 (0.249 mi.) 122 616 Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ APRO LLC DBA UNITED 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A7 82 JIFFY LUBE # 2355 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D41 171 BADGER DAYLIGHTING 10101 NORTH WOLFE RO N 0 - 1/8 (0.084 mi.) E49 209 I & G DIRECT REAL ES 10080 NORTH WOLF ROA NE 0 - 1/8 (0.103 mi.) F62 239 I & G DIRECT REAL ES 10080 N. WOLFE ROAD NE 0 - 1/8 (0.103 mi.) F63 241 ROSEMARIE PLACE 19472 ROSEMARIE PLAC SE 1/8 - 1/4 (0.127 mi.) 72 259 19698 WHEATON DR 19698 WHEATON DR NW 1/8 - 1/4 (0.129 mi.) I73 263 EDWARD & LYNN PUCCIN 10128 DENISON AVENUE NNW 1/8 - 1/4 (0.159 mi.) I77 278 BANK OF AMERICA 19376 STEVENS CREEK E 1/8 - 1/4 (0.176 mi.) J78 282 BANK OF AMERICA 19376 STEVENS CREEK E 1/8 - 1/4 (0.176 mi.) J79 290 MASATO KAIDA 10154 DENISON AVENUE NNW 1/8 - 1/4 (0.184 mi.) M92 380 ELLEN WU 10168 DENISON AVE NNW 1/8 - 1/4 (0.197 mi.) M96 394 TARGET 3224 19499 STEVENS CREEK E 1/8 - 1/4 (0.209 mi.) N98 435 CVS (SIS) 19499 STEVENS CREEK E 1/8 - 1/4 (0.209 mi.) N100 532 VALLCO PROPERTY OWNE 10123 NORTH WOLFE RO N 1/8 - 1/4 (0.227 mi.) P108 558 ICE CENTER CUPERTINO 10123 N WOLFE ROAD, N 1/8 - 1/4 (0.227 mi.) P112 572 VALLCO SHOPPING MALL 10123 N WOLFE RD STE N 1/8 - 1/4 (0.227 mi.) P114 579 VALLCO PROPERTY OWNE 10123 N. WOLFE ROAD N 1/8 - 1/4 (0.227 mi.) P115 589 VALLCO PROPERTY OWNE 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P117 596 VALLCO PROPERTY OWNE 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P120 607 Cortese: The sites for the list are designated by the State Water Resource Control Board (LUST), the Integrated Waste Board (SWF/LS), and the Department of Toxic Substances Control (Cal-Sites).

A review of the Cortese list, as provided by EDR, and dated 12/11/2024 has revealed that there are 8 Cortese sites within approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ USA PETROLEUM COMPAN 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S130 636 Cleanup Status: COMPLETED - CASE CLOSED
SHELL 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S133 653 Cleanup Status: COMPLETED - CASE CLOSED
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A14 95
Cleanup Status: COMPLETED - CASE CLOSED
SHELL 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D36 163 Cleanup Status: COMPLETED - CASE CLOSED
SEARS ROEBUCK & CO 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E47 198 658
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Cleanup Status: COMPLETED - CASE CLOSED
J. C. PENNEY CO., IN 10150 N WOLFE RD NNE 1/4 - 1/2 (0.359 mi.) R125 629 Cleanup Status: COMPLETED - CASE CLOSED
FIRST DEVELOPMENT CO 19140 STEVENS CREEK E 1/4 - 1/2 (0.435 mi.) T136 656 Cleanup Status: COMPLETED - CASE CLOSED
FIRST DEVELOPMENT CO 19110 STEVENS CREEK E 1/4 - 1/2 (0.461 mi.) T137 660 Cleanup Status: COMPLETED - CASE CLOSED
CUPA Listings: A listing of sites included in the county’s Certified Unified Program Agency database.

California’s Secretary for Environmental Protection established the unified hazardous materials and hazardous waste regulatory program as required by chapter 6.11 of the California Health and Safety Code. The Unified Program consolidates the administration, permits, inspections, and enforcement activities.

A review of the CUPA Listings list, as provided by EDR, has revealed that there are 30 CUPA Listings sites within approximately 0.25 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ FAMILY & COSMETIC DE 19668 STEVENS CREEK W 0 - 1/8 (0.038 mi.) C33 156 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 ONE HOUR PHOTO SERVI 19744 STEVENS CREEK W 0 - 1/8 (0.090 mi.) C51 215 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 19720 STEVENS CREEK 19720 STEVENS CREEK W 0 - 1/8 (0.090 mi.) C53 216 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 HOLIDAY CLEANERS 19720 STEVENS CREEK W 0 - 1/8 (0.090 mi.) C55 224 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 MINUTEMAN PRESS 19701 STEVENS CREEK WNW 0 - 1/8 (0.111 mi.) G65 247 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 WARDROBE CUSTOM CLEA 19705 STEVENS CREEK WNW 0 - 1/8 (0.111 mi.) G66 247 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 DAISO 6986 19750 STEVENS CREEK WSW 0 - 1/8 (0.122 mi.) H71 258 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 MICHAEL SCHUCK DDS 10055 N PORTAL AV 10 WNW 1/8 - 1/4 (0.211 mi.) O101 545 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 DONALD P ARALDI DDS 10055 N PORTAL AV 10 WNW 1/8 - 1/4 (0.211 mi.) O102 546 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 THEODORE A FLOOR DDS 10055 N PORTAL AV 10 WNW 1/8 - 1/4 (0.211 mi.) O103 546 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 ROBERT F HARLEY DDS 10055 N PORTAL AV 13 WNW 1/8 - 1/4 (0.211 mi.) O104 548 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 ESTATES DR 0 - 1/8 (0.000 mi.) A1 40 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 CONOCOPHILLIPS COMPA 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A10 90 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 BOYETT PETROLEUM BP 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A20 120 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 JOE’S UNION SERVICE 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A22 138 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 659
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Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ FUJIMOTO&LEE ORAL&MA 10055 MILLER AV ESE 0 - 1/8 (0.034 mi.) A26 144 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 DRS LIN & LO DMD INC 10055 MILLER AV 101 ESE 0 - 1/8 (0.034 mi.) A28 147 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 IA 072313CUPERTINO O 10055 MILLER AV 101 ESE 0 - 1/8 (0.034 mi.) A29 148 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 ANNE E MURRAY DDS 10055 MILLER AV 104 ESE 0 - 1/8 (0.034 mi.) A30 149 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 ALLAN DOMASH 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D42 182 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 VALLCO DENTAL CARE 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E43 193 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 SEARS AUTO CENTER #6 10101 N WOLFE RD N 0 - 1/8 (0.084 mi.) E48 208 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 JIFFY LUBE #1615 10101 WOLFE RD N 0 - 1/8 (0.084 mi.) E50 214 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 CUPERTINO FINANCIAL 10050 N WOLFE RD NE 0 - 1/8 (0.103 mi.) F61 237 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 CVS PHARMACY #17687 19499 STEVENS CREEK E 1/8 - 1/4 (0.209 mi.) N97 398 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 TARGET STORE T3224 19499 STEVENS CREEK E 1/8 - 1/4 (0.209 mi.) N99 454 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 RITZ CAMERA #562 10123 N WOLFE RD 210 N 1/8 - 1/4 (0.227 mi.) P109 569 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 THE PICTURE PEOPLE # 10123 N WOLFE RD 216 N 1/8 - 1/4 (0.227 mi.) P110 569 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 VALLCO GENERATOR ROO 10123 N WOLFE RD N 1/8 - 1/4 (0.227 mi.) P119 607 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 APPLE 19339 STEVENS CREEK E 1/8 - 1/4 (0.244 mi.) N121 613 Database: CUPA SANTA CLARA, Date of Government Version: 02/14/2025 DRYCLEANERS: A list of drycleaner related facilities that have EPA ID numbers. These are facilities with certain SIC codes: power laundries, family and commercial; garment pressing and cleaners’ agents; linen supply; coin-operated laundries and cleaning; drycleaning plants except rugs; carpet and upholster cleaning; industrial launderers; laundry and garment services.

A review of the DRYCLEANERS list, as provided by EDR, has revealed that there are 2 DRYCLEANERS sites within approximately 0.25 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ HOLIDAY CLEANERS OF 19720 STEVENS CREEK W 0 - 1/8 (0.090 mi.) C54 217 Database: DRYCLEANERS, Date of Government Version: 02/20/2025 EPA Id: CAL000337795
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 Database: DRYCLEANERS, Date of Government Version: 02/20/2025 Database: DRYCLEAN BAY AREA, Date of Government Version: 02/20/2019 660
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EPA Id: CAD981579311
EMI: Toxics and criteria pollutant emissions data collected by the ARB and local air pollution agencies
A review of the EMI list, as provided by EDR, and dated 12/31/2022 has revealed that there is 1 EMI site within approximately 0.001 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR MARTINIZING 10045 E ESTATES DRIV 0 - 1/8 (0.000 mi.) A4 41 Facility Id: 1010
HIST CORTESE: The sites for the list are designated by the State Water Resource Control Board [LUST], the Integrated Waste Board [SWF/LS], and the Department of Toxic Substances Control [CALSITES]. This listing is no longer updated by the state agency.

A review of the HIST CORTESE list, as provided by EDR, and dated 04/01/2001 has revealed that there are 7 HIST CORTESE sites within approximately 0.5 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ SHELL 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S133 653 Reg Id: 43-1293
Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ MOBIL 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A14 95
Reg Id: 43-0921
SHELL 19480 STEVENS CREEK E 0 - 1/8 (0.077 mi.) D36 163 Reg Id: 43-1291
Not reported 10123 NORTH WOLFE RD N 1/8 - 1/4 (0.227 mi.) P111 570 Reg Id: 43-1252
JC PENNEY 10150 WOLFE NNE 1/4 - 1/2 (0.359 mi.) R128 635 Reg Id: 43-0743
FIRST DEVELOPMENT CO 19140 STEVENS CREEK E 1/4 - 1/2 (0.435 mi.) T136 656 Reg Id: 43-0587
FIRST DEVELOPMENT CO 19110 STEVENS CREEK E 1/4 - 1/2 (0.461 mi.) T137 660 Reg Id: 43-0586
HWP: Detailed information on permitted hazardous waste facilities and corrective action ("cleanups") tracked in EnviroStor.

A review of the HWP list, as provided by EDR, and dated 02/10/2025 has revealed that there is 1 HWP site within approximately 1 mile of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ HEWLETT PACKARD COSA 5301 STEVENS CREEK B E 1/2 - 1 (0.942 mi.) 143 698 EPA ID: CAD049231319
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Cleanup Status: PROTECTIVE FILER
HWTS: DTSC maintains the Hazardous Waste Tracking System that stores ID number information since the early 1980s and manifest data since 1993. The system collects both manifest copies from the generator and destination facility.

A review of the HWTS list, as provided by EDR, and dated 07/19/2024 has revealed that there is 1 HWTS site within approximately 0.001 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 HAZNET: The data is extracted from the copies of hazardous waste manifests received each year by the DTSC. The annual volume of manifests is typically 700,000-1,000,000 annually, representing approximately 350,000-500,000 shipments. Data from non-California manifests & continuation sheets are not included at the present time. Data are from the manifests submitted without correction, and therefore many contain some invalid values for data elements such as generator ID, TSD ID, waste category, & disposal method. The source is the Department of Toxic Substance Control is the agency. This database begins with calendar year 1993.

A review of the HAZNET list, as provided by EDR, and dated 12/31/2024 has revealed that there is 1 HAZNET site within approximately 0.001 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 GEPAID: CAD981579311
Notify 65: Listings of all Proposition 65 incidents reported to counties by the State Water Resources Control Board and the Regional Water Quality Control Board. This database is no longer updated by the reporting agency.

A review of the Notify 65 list, as provided by EDR, and dated 09/05/2024 has revealed that there is 1 Notify 65 site within approximately 1 mile of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ USA PETROLEUM COMPAN 19990 STEVENS CREEK W 1/4 - 1/2 (0.363 mi.) S130 636 CERS: The CalEPA Regulated Site Portal database combines data about environmentally regulated sites and facilities in California into a single database. It combines data from a variety of state and federal databases, and provides an overview of regulated activities across the spectrum of environmental programs for any given location in California. These activities include hazardous materials and waste, state and federal cleanups, impacted ground and surface waters, and toxic materials A review of the CERS list, as provided by EDR, and dated 01/12/2025 has revealed that there is 1 CERS site within approximately 0.001 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ONE HOUR CLEANERS BY 10045 E ESTATES DR 0 - 1/8 (0.000 mi.) A5 47 662
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EDR HIGH RISK HISTORICAL RECORDS
EDR Exclusive Records
EDR Hist Auto: EDR has searched selected national collections of business directories and has collected listings of potential gas station/filling station/service station sites that were available to EDR researchers. EDR’s review was limited to those categories of sources that might, in EDR’s opinion, include gas station/filling station/service station establishments. The categories reviewed included, but were not limited to gas, gas station, gasoline station, filling station, auto, automobile repair, auto service station, service station, etc. This database falls within a category of information EDR classifies as "High Risk Historical Records", or HRHR. EDR’s HRHR effort presents unique and sometimes proprietary data about past sites and operations that typically create environmental concerns, but may not show up in current government records searches.

A review of the EDR Hist Auto list, as provided by EDR, has revealed that there are 2 EDR Hist Auto sites within approximately 0.125 miles of the target property.

Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ESTATES MOBILE SERVI 19550 STEVENS CREEK E 0 - 1/8 (0.028 mi.) A17 116 SHELL AUTOMOTIVE 19480 STEVENS CK BD E 0 - 1/8 (0.077 mi.) D37 167 EDR Hist Cleaner: EDR has searched selected national collections of business directories and has collected listings of potential dry cleaner sites that were available to EDR researchers. EDR’s review was limited to those categories of sources that might, in EDR’s opinion, include dry cleaning establishments. The categories reviewed included, but were not limited to dry cleaners, cleaners, laundry, laundromat, cleaning/laundry, wash & dry etc. This database falls within a category of information EDR classifies as "High Risk Historical Records", or HRHR. EDR’s HRHR effort presents unique and sometimes proprietary data about past sites and operations that typically create environmental concerns, but may not show up in current government records searches.

A review of the EDR Hist Cleaner list, as provided by EDR, has revealed that there are 3 EDR Hist Cleaner sites within approximately 0.125 miles of the target property.

Equal/Higher Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ HOLIDAY CLEANERS 19720 STEVENS CREEK W 0 - 1/8 (0.090 mi.) C52 215 MELS CLEANERS 19705 STEVNS CRK BD WNW 0 - 1/8 (0.111 mi.) G67 248 Lower Elevation Address Direction / Distance Map ID Page ____________________ ________ ___________________ _____ _____ ENTERPRISE CONTROLS 10045 ESTATES DR 0 - 1/8 (0.000 mi.) A2 40 663
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Due to poor or inadequate address information, the following sites were not mapped. Count: 1 records.

Site Name Database(s)
____________ ____________
CDL
664
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EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.

Natural Gas
1 6 0
2 0 0
2 0 0
2 0 0
2 0 0
2 4 0
240
2 4 0
1 6 0
2 0 0
665
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EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.

Natural Gas
200
666
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MAP FINDINGS SUMMARY
Search
Distance Target Total
Database Property (Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted

STANDARD ENVIRONMENTAL RECORDS
Lists of Federal NPL (Superfund) sites
NPL 1.000 0 0 0 1 NR 1
Proposed NPL 1.000 0 0 0 0 NR 0
NPL LIENS 1.000 0 0 0 0 NR 0
Lists of Federal Delisted NPL sites
Delisted NPL 1.000 0 0 0 0 NR 0
Lists of Federal sites subject to
CERCLA removals and CERCLA orders
FEDERAL FACILITY 0.500 0 0 0 NR NR 0
SEMS 0.500 0 0 0 NR NR 0
Lists of Federal CERCLA sites with NFRAP
SEMS-ARCHIVE 0.500 0 0 1 NR NR 1
Lists of Federal RCRA facilities
undergoing Corrective Action
CORRACTS 1.000 0 0 0 0 NR 0
Lists of Federal RCRA TSD facilities
RCRA-TSDF 0.500 0 0 0 NR NR 0
Lists of Federal RCRA generators
RCRA-LQG 0.250 1 0 NR NR NR 1
RCRA-SQG 0.250 4 2 NR NR NR 6
RCRA-VSQG 0.250 0 0 NR NR NR 0
Federal institutional controls /
engineering controls registries
LUCIS 0.500 0 0 0 NR NR 0
US ENG CONTROLS 0.500 0 0 0 NR NR 0
US INST CONTROLS 0.500 0 0 0 NR NR 0
Federal ERNS list
ERNS 0.001 0 NR NR NR NR 0
Lists of state- and tribal
(Superfund) equivalent sites
RESPONSE 1.000 0 0 0 1 NR 1
Lists of state- and tribal
hazardous waste facilities
ENVIROSTOR 1.000 0 0 0 7 NR 7
Lists of state and tribal landfills
and solid waste disposal facilities
SWF/LF 0.500 0 0 0 NR NR 0
TC07984167.2r Page 4
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MAP FINDINGS SUMMARY
Search
Distance Target Total
Database Property (Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted Lists of state and tribal leaking storage tanks
LUST 0.500 7 0 7 NR NR 14
INDIAN LUST 0.500 0 0 0 NR NR 0
CPS-SLIC 0.500 2 2 1 NR NR 5
HIST LUST 0.500 4 0 4 NR NR 8
Lists of state and tribal registered storage tanks
FEMA UST 0.250 0 0 NR NR NR 0
UST 0.250 4 0 NR NR NR 4
AST 0.250 3 0 NR NR NR 3
INDIAN UST 0.250 0 0 NR NR NR 0
Lists of state and tribal voluntary cleanup sites
VCP 0.500 0 0 0 NR NR 0
INDIAN VCP 0.500 0 0 0 NR NR 0
Lists of state and tribal brownfield sites
BROWNFIELDS 0.500 0 0 1 NR NR 1

ADDITIONAL ENVIRONMENTAL RECORDS
Local Brownfield lists
US BROWNFIELDS 0.500 0 0 0 NR NR 0
Local Lists of Landfill / Solid
Waste Disposal Sites
WMUDS/SWAT 0.500 0 0 0 NR NR 0
SWRCY 0.500 0 0 1 NR NR 1
HAULERS 0.001 0 NR NR NR NR 0
INDIAN ODI 0.500 0 0 0 NR NR 0
ODI 0.500 0 0 0 NR NR 0
DEBRIS REGION 9 0.500 0 0 0 NR NR 0
IHS OPEN DUMPS 0.500 0 0 0 NR NR 0
Local Lists of Hazardous waste /
Contaminated Sites
US HIST CDL 0.001 0 NR NR NR NR 0
HIST Cal-Sites 1.000 0 0 0 1 NR 1
SCH 0.250 0 0 NR NR NR 0
CDL 0.001 0 NR NR NR NR 0
Toxic Pits 1.000 0 0 0 0 NR 0
CERS HAZ WASTE 0.250 5 2 NR NR NR 7
US CDL 0.001 0 NR NR NR NR 0
Local Lists of Registered Storage Tanks
SWEEPS UST 0.250 4 0 NR NR NR 4
HIST UST 0.250 4 0 NR NR NR 4
CERS TANKS 0.250 2 0 NR NR NR 2
CA FID UST 0.250 3 0 NR NR NR 3
TC07984167.2r Page 5
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MAP FINDINGS SUMMARY
Search
Distance Target Total
Database Property (Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted Local Land Records
LIENS 0.001 0 NR NR NR NR 0
LIENS 2 0.001 0 NR NR NR NR 0
DEED 0.500 0 0 0 NR NR 0
Records of Emergency Release Reports
HMIRS 0.001 0 NR NR NR NR 0
CHMIRS 0.001 0 NR NR NR NR 0
LDS 0.001 0 NR NR NR NR 0
MCS 0.001 0 NR NR NR NR 0
SPILLS 90 0.001 0 NR NR NR NR 0
Other Ascertainable Records
RCRA NonGen / NLR 0.250 18 36 NR NR NR 54
FUDS 1.000 0 0 0 0 NR 0
DOD 1.000 0 0 0 0 NR 0
SCRD DRYCLEANERS 0.500 0 0 0 NR NR 0
US FIN ASSUR 0.001 0 NR NR NR NR 0
EPA WATCH LIST 0.001 0 NR NR NR NR 0
2020 COR ACTION 0.250 0 0 NR NR NR 0
TSCA 0.001 0 NR NR NR NR 0
TRIS 0.001 0 NR NR NR NR 0
SSTS 0.001 0 NR NR NR NR 0
ROD 1.000 0 0 0 1 NR 1
RMP 0.001 0 NR NR NR NR 0
RAATS 0.001 0 NR NR NR NR 0
PRP 0.001 0 NR NR NR NR 0
PADS 0.001 0 NR NR NR NR 0
ICIS 0.001 0 NR NR NR NR 0
FTTS 0.001 0 NR NR NR NR 0
MLTS 0.001 0 NR NR NR NR 0
COAL ASH DOE 0.001 0 NR NR NR NR 0
COAL ASH EPA 0.500 0 0 0 NR NR 0
PCB TRANSFORMER 0.001 0 NR NR NR NR 0
RADINFO 0.001 0 NR NR NR NR 0
HIST FTTS 0.001 0 NR NR NR NR 0
DOT OPS 0.001 0 NR NR NR NR 0
CONSENT 1.000 0 0 0 0 NR 0
INDIAN RESERV 1.000 0 0 0 0 NR 0
FUSRAP 1.000 0 0 0 0 NR 0
UMTRA 0.500 0 0 0 NR NR 0
LEAD SMELTERS 0.001 0 NR NR NR NR 0
US AIRS 0.001 0 NR NR NR NR 0
US MINES 0.250 0 0 NR NR NR 0
MINES MRDS 0.250 0 0 NR NR NR 0
ABANDONED MINES 0.250 0 0 NR NR NR 0
FINDS 0.001 2 NR NR NR NR 2
DOCKET HWC 0.001 0 NR NR NR NR 0
ECHO 0.001 1 NR NR NR NR 1
UXO 1.000 0 0 0 0 NR 0
TC07984167.2r Page 6
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MAP FINDINGS SUMMARY
Search
Distance Target Total
Database Property (Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted FUELS PROGRAM 0.250 0 0 NR NR NR 0
PFAS NPL 0.250 0 0 NR NR NR 0
PFAS FEDERAL SITES 0.250 0 0 NR NR NR 0
PFAS TRIS 0.250 0 0 NR NR NR 0
PFAS TSCA 0.250 0 0 NR NR NR 0
PFAS RCRA MANIFEST 0.250 0 0 NR NR NR 0
PFAS ATSDR 0.250 0 0 NR NR NR 0
PFAS WQP 0.250 0 0 NR NR NR 0
PFAS NPDES 0.250 0 0 NR NR NR 0
PFAS PROJECT 0.250 0 0 NR NR NR 0
PFAS ECHO 0.250 0 0 NR NR NR 0
PFAS ECHO FIRE TRAIN 0.250 0 0 NR NR NR 0
PFAS PT 139 AIRPORT 0.250 0 0 NR NR NR 0
AQUEOUS FOAM NRC 0.250 0 0 NR NR NR 0
BIOSOLIDS 0.001 0 NR NR NR NR 0
UST FINDER RELEASE 0.500 4 0 5 NR NR 9
UST FINDER 0.250 1 0 NR NR NR 1
E MANIFEST 0.250 8 30 NR NR NR 38
PFAS 0.250 0 0 NR NR NR 0
AQUEOUS FOAM 0.250 0 0 NR NR NR 0
CA BOND EXP. PLAN 1.000 0 0 0 0 NR 0
CHROME PLATING 0.500 0 0 0 NR NR 0
Cortese 0.500 3 0 5 NR NR 8
CUPA Listings 0.250 20 10 NR NR NR 30
DRYCLEANERS 0.250 2 0 NR NR NR 2
EMI 0.001 1 NR NR NR NR 1
ENF 0.001 0 NR NR NR NR 0
Financial Assurance 0.001 0 NR NR NR NR 0
ICE 0.001 0 NR NR NR NR 0
HIST CORTESE 0.500 2 1 4 NR NR 7
HWP 1.000 0 0 0 1 NR 1
HWT 0.250 0 0 NR NR NR 0
HWTS 0.001 1 NR NR NR NR 1
HAZNET 0.001 1 NR NR NR NR 1
MINES 0.250 0 0 NR NR NR 0
MWMP 0.250 0 0 NR NR NR 0
NPDES 0.001 0 NR NR NR NR 0
PEST LIC 0.001 0 NR NR NR NR 0
PROC 0.500 0 0 0 NR NR 0
Notify 65 1.000 0 0 1 0 NR 1
HAZMAT 0.250 0 0 NR NR NR 0
UIC 0.001 0 NR NR NR NR 0
UIC GEO 0.001 0 NR NR NR NR 0
WASTEWATER PITS 0.500 0 0 0 NR NR 0
WDS 0.001 0 NR NR NR NR 0
WIP 0.250 0 0 NR NR NR 0
MILITARY PRIV SITES 0.001 0 NR NR NR NR 0
PROJECT 0.001 0 NR NR NR NR 0
WDR 0.001 0 NR NR NR NR 0
CIWQS 0.001 0 NR NR NR NR 0
CERS 0.001 1 NR NR NR NR 1
TC07984167.2r Page 7
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MAP FINDINGS SUMMARY
Search
Distance Target Total
Database Property (Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted NON-CASE INFO 0.001 0 NR NR NR NR 0
OTHER OIL GAS 0.001 0 NR NR NR NR 0
PROD WATER PONDS 0.001 0 NR NR NR NR 0
SAMPLING POINT 0.001 0 NR NR NR NR 0
WELL STIM PROJ 0.001 0 NR NR NR NR 0

EDR HIGH RISK HISTORICAL RECORDS
EDR Exclusive Records
EDR MGP 1.000 0 0 0 0 NR 0
EDR Hist Auto 0.125 2 NR NR NR NR 2
EDR Hist Cleaner 0.125 3 NR NR NR NR 3

EDR RECOVERED GOVERNMENT ARCHIVES
Exclusive Recovered Govt. Archives
RGA LF 0.001 0 NR NR NR NR 0
RGA LUST 0.001 0 NR NR NR NR 0
- Totals -- 0 113 83 30 12 0 238
NOTES:

TP = Target Property
NR = Not Requested at this Search Distance
Sites may be listed in more than one database
TC07984167.2r Page 8
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Pathway: NO PATHWAY INDICATED
Substance: TRICHLOROBENZENE
CAS Number: 12002-48-1
Substance ID: C401
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: BUTYL ACETATE
CAS Number: 123-86-4
Substance ID: C290
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: ISOPROPANOL
CAS Number: 67-63-0
Substance ID: C069
NPL Status: Currently on the Final NPL
Scoring: Not reported
Pathway: Not reported
Substance: Not reported
CAS Number: Not reported
Substance ID: Not reported
NPL Status: Currently on the Final NPL
Substance as of 08/2019:

Native American Entity: Not reported
NAI: Not reported
Site Score: 28.899999999999999
Longitude: -122.0015
Latitude: 37.3361
Final Date: 1990-08-30 00:00:00
Federal: N
City,State,Zip: CUPERTINO, CA 95014
Address: 10900 N Tantau Ave/19000 Homestead Rd
Name: INTERSIL INC./SIEMENS COMPONENTS
Site ID: 901325
EPA ID: CAD041472341
EPA Region: 9
NPL:

CERS
CIWQS
WDS
HAZNET
HWTS
ENF
ECHO
FINDS
PRP
ROD
HIST Cal-Sites

CPS-SLIC
5007 ft. ENVIROSTOR
1/2-1 US ENG CONTROLS
NE CUPERTINO, CA 95014 RCRA-SQG
Region 10900 N TANTAU AVENUE SEMS CAD041472341
NPL PANASONIC NPL 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: XYLENE
CAS Number: 1330-20-7
Substance ID: U239
NPL Status: Currently on the Final NPL
Scoring: 2
Pathway: GROUND WATER PATHWAY
Substance: TRICHLOROETHYLENE (TCE)
CAS Number: 79-01-6
Substance ID: U228
NPL Status: Currently on the Final NPL
Scoring: 3
Pathway: GROUND WATER PATHWAY
Substance: TRICHLOROETHANE, 1,1,1-
CAS Number: 71-55-6
Substance ID: U226
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: TOLUENE
CAS Number: 108-88-3
Substance ID: U220
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: TETRACHLOROETHENE
CAS Number: 127-18-4
Substance ID: U210
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: METHANOL
CAS Number: 67-56-1
Substance ID: U154
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: TRICHLOROFLUOROMETHANE
CAS Number: 75-69-4
Substance ID: U121
NPL Status: Currently on the Final NPL
Scoring: 1
Pathway: NO PATHWAY INDICATED
Substance: DICHLOROETHENE, 1,1-
CAS Number: 75-35-4
Substance ID: U078
NPL Status: Currently on the Final NPL
Scoring: 1
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Final Date: 08/30/1990
Proposed Date: 06/24/1988
Site Status as of 08/2019:

Date Proposed: 06/24/88
Date Finalized: 08/30/90
Date Deleted: Not reported
Federal Site: N
Site Status: F
Site ID: 0901325
EPA Region: 09
Site as of 08/2019:

NPL Name: INTERSIL INC./SIEMENS COMPONENTS
Narratives as of 08/2019:

Category Value: 1300
Category Description: Distance To Nearest Population-> 0 And <= 1/4 Mile NPL Status: Currently on the Final NPL
Category Value: 130 FTBGS
Category Description: Depth To Aquifer-> 100 Feet
NPL Status: Currently on the Final NPL
Category as of 08/2019:
comments on the proposed remedial action plan.
the State plans to issue tentative site cleanup requirements and hear public remedial activities are scheduled to begin in June 1990. Also in June 1990, studies for the site and off-site downgradient areas. Interim off-site two companies released draft reports of remedial investigations/feasibility equipment was removed. Status August 30, 1990): In February 1990, the operation. Intersil stopped operations in 1988, and all remaining underground a pump and treat system for the two uppermost aquifers has been in full-scale water in the uppermost aquifer to the surface and treat it. Since April 1988, soils. In July 1986, a system was installedto pump contaminated ground both companies to determine the extent of contamination in ground water and issued Waste Discharge Requirements under the California Water Code requiring 1985. In June 1986, the California Regional Water Quality Control Board system was installed to extract gases from soil; the system was expanded in State supervision. The underground storage tanks were removed, and in 1983 a remedial investigations at the site in 1982 and 1983, respectively, under public wells within 3 miles of the site. Siemens and Intersil began the two companies. More than 300,000 people obtain drinking water from from leaking underground storage tanks, piping, and other equipment involving site. Contamination is believed to have resulted from locali ed spills and 1,1-dichloroethylene, in soils on the site and in ground water on and off the 1,1,1-trichloroethane, tetrachloroethylene, trichlorofluoroethane, and detection program found organic solvents, including trichloroethylene, California Regional Water Quality Control Board s underground tank leak business areas. Investigations conducted in 1982 as part of the California. The facilities are surrounded by residential, industrial, and near one another covering 15 acres in Cupertino, Santa Clara County, Components have manufactured semiconductors for several years on two locations Conditions at proposal June 24, 1988): Intersil, Inc., and Siemens Summary Details:

PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: E
Finish Date: Not reported
Start Date: 1990-11-26 05:00:00
SEQ: 1
Action Name: ADMIN REC
Action Code: AR
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
SEMS Detail:

Non NPL Status: Not reported
NPL: Currently on the Final NPL
FF: N
Longitude: -122.001500
Latitude: +37.336100
FIPS Code: 06085
Cong District: 14,17
City,State,Zip: CUPERTINO, CA 95014
Address 2: Not reported
Address: 10900 N TANTAU AVE/19000 HOMESTEAD RD
Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
SEMS:

Site Location URL:

Federal Register URL:

Site Progress URL:

Site List URL:

Federal Facility Indicator: No
Site Score: 28.9
Listing Date: 8/30/1990
Site EPA ID: CAD041472341
Site Name: Intersil Inc./Siemens Components
Narr:

NPL Status: Final
Deleted Date: Not reported
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 2005-09-29 04:00:00
Start Date: 2004-12-31 05:00:00
SEQ: 3
Action Name: 5 YEAR
Action Code: FE
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 2000-09-28 04:00:00
Start Date: 2000-08-01 04:00:00
SEQ: 2
Action Name: 5 YEAR
Action Code: FE
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1995-09-28 04:00:00
Start Date: 1995-09-28 04:00:00
SEQ: 1
Action Name: 5 YEAR
Action Code: FE
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: Not reported
Start Date: 2020-03-02 06:00:00
SEQ: 1
Action Name: CI
Action Code: CR
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1992-09-08 04:00:00
Start Date: 1992-09-08 04:00:00
SEQ: 1
Action Name: PCOR
Action Code: CM
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 2020-09-28 05:00:00
Start Date: 2019-11-07 06:00:00
SEQ: 6
Action Name: 5 YEAR
Action Code: FE
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 2015-09-22 05:00:00
Start Date: 2014-11-05 05:00:00
SEQ: 5
Action Name: 5 YEAR
Action Code: FE
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 2010-09-30 04:00:00
Start Date: 2010-09-30 04:00:00
SEQ: 4
Action Name: 5 YEAR
Action Code: FE
OU: 00
FF: N
NPL: F
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Qual: Not reported
Finish Date: 1987-06-01 04:00:00
Start Date: 1987-06-01 04:00:00
SEQ: 1
Action Name: HAZRANK
Action Code: HR
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1990-08-14 04:00:00
Start Date: 1990-08-14 04:00:00
SEQ: 3
Action Name: RV ASSESS
Action Code: RS
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1989-08-07 04:00:00
Start Date: 1989-08-07 04:00:00
SEQ: 2
Action Name: RV ASSESS
Action Code: RS
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1992-12-29 05:00:00
Start Date: 1992-12-29 05:00:00
SEQ: 1
Action Name: RV ASSESS
Action Code: RS
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
SEQ: 1
Action Name: DISCVRY
Action Code: DS
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: H
Finish Date: 1987-03-01 05:00:00
Start Date: 1987-03-01 05:00:00
SEQ: 1
Action Name: PA
Action Code: PA
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1988-06-24 04:00:00
Start Date: 1988-06-24 04:00:00
SEQ: 1
Action Name: PROPOSED
Action Code: NP
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1990-08-30 04:00:00
Start Date: 1990-08-30 04:00:00
SEQ: 1
Action Name: NPL FINL
Action Code: NF
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
OU: 01
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: St Ovrsght
Qual: Not reported
Finish Date: Not reported
Start Date: 1990-09-27 04:00:00
SEQ: 1
Action Name: OM
Action Code: OM
OU: 01
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: St Ovrsght
Qual: Not reported
Finish Date: Not reported
Start Date: 1989-09-15 04:00:00
SEQ: 1
Action Name: ST COOP
Action Code: MA
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: H
Finish Date: 1987-06-01 04:00:00
Start Date: 1987-06-01 04:00:00
SEQ: 1
Action Name: SI
Action Code: SI
OU: 00
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Perf
Qual: Not reported
Finish Date: 1986-05-01 04:00:00
Start Date: 1986-05-01 04:00:00
PANASONIC (Continued) 1000218337
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: St Ovrsght
Qual: Not reported
Finish Date: 1990-09-27 04:00:00
Start Date: 1989-03-16 05:00:00
SEQ: 1
Action Name: PRP RI/FS
Action Code: BD
OU: 01
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: St Ovrsght
Qual: Not reported
Finish Date: 1990-09-27 04:00:00
Start Date: 1990-09-27 04:00:00
SEQ: 1
Action Name: PRP RD
Action Code: BE
OU: 01
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: St Ovrsght
Qual: Not reported
Finish Date: 1992-09-08 04:00:00
Start Date: 1990-09-27 04:00:00
SEQ: 1
Action Name: PRP RA
Action Code: BF
OU: 01
FF: N
NPL: F
Site Name: INTERSIL INC./SIEMENS COMPONENTS
EPA ID: CAD041472341
Site ID: 0901325
Region: 09
Current Action Lead: EPA Ovrsght
Qual: Not reported
Finish Date: Not reported
Start Date: 2024-10-08 05:00:00
SEQ: 1
Action Name: PRP LR
Action Code: ME
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Sub-Part K Indicator: Not reported
Hazardous Secondary Material Indicator: N
Federal Facility Indicator: Not reported
Active Site State-Reg Handler: ---
Federal Universal Waste: No
Universal Waste Destination Facility: No
Universal Waste Indicator: No
Off-Site Waste Receipt: No
Underground Injection Control: No
Smelting Melting and Refining Furnace Exemption: No
Small Quantity On-Site Burner Exemption: No
Recycler Activity with Storage: No
Transfer Facility Activity: No
Transporter Activity: No
Mixed Waste Generator: No
Importer Activity: No
Short-Term Generator Activity: No
Operator Type: Private
Operator Name: Not Required
Owner Type: Not reported
Owner Name: Not reported
Mailing City,State,Zip: CUPERTINO, CA 95014
Mailing Address: 10710 NORTH TANTAU AVENUE
State District: 2
State District Owner: Ca
Active Site Indicator: Handler Activities
Accessibility: Not reported
Biennial Report Cycle: Not reported
Non-Notifier: Not reported
Federal Waste Generator Description: Small Quantity Generator Land Type: Not reported
EPA Region: 09
Contact Title: Not reported
Contact Email: Not reported
Contact Fax: Not reported
Contact Telephone: Not reported
Contact City,State,Zip: Not reported
Contact Address: Not reported
Contact Name: Not reported
EPA ID: CAD041472341
Handler City,State,Zip: CUPERTINO, CA 95014
Handler Address: 10900 N Tantau Ave
Handler Name: Intersil Inc
Date Form Received by Agency: 19960901
RCRA Listings:

Current Action Lead: EPA Perf
Qual: R
Finish Date: 1990-09-27 04:00:00
Start Date: 1990-09-27 04:00:00
SEQ: 1
Action Name: ROD
Action Code: RO
OU: 01
FF: N
NPL: F
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Large Quantity Handler of Universal Waste: No
State District Owner: Ca
Federal Waste Generator Description: Small Quantity Generator Handler Name: INTERSIL INC
Receive Date: 19960901
Historic Generators:

Owner/Operator Email: Not reported
Owner/Operator Fax: Not reported
Owner/Operator Telephone Ext: Not reported
Owner/Operator Telephone: 415-555-1212
Owner/Operator City,State,Zip: NOT REQUIRED, ME 99999
Owner/Operator Address: NOT REQUIRED
Date Ended Current: Not reported
Date Became Current: Not reported
Legal Status: Private
Owner/Operator Name: INTERSIL INCORPORATED
Owner/Operator Indicator: Owner
Owner/Operator Email: Not reported
Owner/Operator Fax: Not reported
Owner/Operator Telephone Ext: Not reported
Owner/Operator Telephone: 415-555-1212
Owner/Operator City,State,Zip: NOT REQUIRED, ME 99999
Owner/Operator Address: NOT REQUIRED
Date Ended Current: Not reported
Date Became Current: Not reported
Legal Status: Private
Owner/Operator Name: NOT REQUIRED
Owner/Operator Indicator: Operator
Handler - Owner Operator:

Sub-Part P Indicator: No
Manifest Broker: No
Recycler Activity Without Storage: No
Exporter of Spent Lead Acid Batteries: No
Importer of Spent Lead Acid Batteries: No
Recognized Trader-Exporter: No
Recognized Trader-Importer: No
Handler Date of Last Change: 20020627
Financial Assurance Required: Not reported
Significant Non-Complier With a Compliance Schedule Universe: No Addressed Significant Non-Complier Universe: No
Unaddressed Significant Non-Complier Universe: No
Significant Non-Complier Universe: No
Groundwater Controls Indicator: N/A
Human Exposure Controls Indicator: N/A
Institutional Control Indicator: No
Environmental Control Indicator: No
Corrective Action Priority Ranking: No NCAPS ranking
Non-TSDFs Where RCRA CA has Been Imposed Universe: No
Subject to Corrective Action Universe: No
202 GPRA Corrective Action Baseline: No
2018 GPRA Renewals Baseline: Not on the Baseline
2018 GPRA Permit Baseline: Not on the Baseline
PANASONIC (Continued) 1000218337
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Action ID: 1
Action Name: Record of Decision
EPA ID: CAD041472341
Action Taken Date: 09/27/1990
Event Code: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address 2: Not reported
Address: 10900 N TANTAU AVE/19000 HOMESTEAD RD
Name: INTERSIL INC./SIEMENS COMPONENTS
SIte:

Evaluations: No Evaluations Found
Evaluation Action Summary:

Violations: No Violations Found
Facility Has Received Notices of Violations:

NAICS Description: Semiconductor And Related Device Manufacturing NAICS Code: 334413
List of NAICS Codes and Descriptions:

Electronic Manifest Broker: Not reported
Non Storage Recycler Activity: Not reported
Current Record: No
Spent Lead Acid Battery Exporter: No
Spent Lead Acid Battery Importer: No
Recognized Trader Exporter: No
Recognized Trader Importer: No
Large Quantity Handler of Universal Waste: No
State District Owner: Not reported
Federal Waste Generator Description: Large Quantity Generator Handler Name: INTERSIL, INC.

Receive Date: 19920229
Electronic Manifest Broker: Not reported
Non Storage Recycler Activity: Not reported
Current Record: No
Spent Lead Acid Battery Exporter: No
Spent Lead Acid Battery Importer: No
Recognized Trader Exporter: No
Recognized Trader Importer: No
Large Quantity Handler of Universal Waste: No
State District Owner: Ca
Federal Waste Generator Description: Large Quantity Generator Handler Name: INTERSIL INC
Receive Date: 19800818
Electronic Manifest Broker: Not reported
Non Storage Recycler Activity: Not reported
Current Record: Yes
Spent Lead Acid Battery Exporter: No
Spent Lead Acid Battery Importer: No
Recognized Trader Exporter: No
Recognized Trader Importer: No
PANASONIC (Continued) 1000218337
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Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Groundwater
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Soil
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Groundwater
EPA ID: CAD041472341
Media:

Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Contaminated Media: Groundwater
Operable Unit: 01
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Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Groundwater
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Soil
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Soil
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
PANASONIC (Continued) 1000218337
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Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Groundwater
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Groundwater
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Soil
EPA ID: CAD041472341
Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
Action Taken Date: 09/27/1990
Action Name: Record of Decision
Operable Unit: 01
Action ID: 1
Contaminated Media: Soil
EPA ID: CAD041472341
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Alias Type: Envirostor ID Number
Alias Name: 43360032
Alias Type: PCode
Alias Name: P23080
Alias Type: EPA (FRS #)
Alias Name: 110033615185
Alias Type: EPA (FRS #)
Alias Name: 110001168245
Alias Type: EPA Identification Number
Alias Name: CAD041472341
Alias Type: Alternate Name
Alias Name: INTERSIL/SIEMENS
Alias Type: Alternate Name
Alias Name: INTERSIL INC / SIEMENS COMPONENTS
Potential Description: NONE SPECIFIED
Confirmed COC: NONE SPECIFIED
Potential COC: NONE SPECIFIED
Past Use: NONE SPECIFIED
APN: NONE SPECIFIED
Longitude: -122.0082
Latitude: 37.33097
Funding: Responsible Party
Site Mgmt Req: NONE SPECIFIED
Restricted Use: NO
Special Program: Not reported
Senate: 13
Assembly: 26
Division Branch: Cleanup Berkeley
Supervisor: Referred - Not Assigned
Program Manager: Not reported
Lead Agency: US EPA
Regulatory Agencies: US EPA
NPL: YES
Acres: Not reported
Site Type Detailed: State Response or NPL
Site Type: Federal Superfund
Site Code: Not reported
Status Date: 01/30/1989
Status: Refer: RWQCB
Facility ID: 43360032
City,State,Zip: CUPERTINO, CA 95014
Address: 10910 N TANTAU AVE
Name: INTERSIL
ENVIROSTOR:

Longitude: -122.001500
Latitude: +37.336100
Superfund Alternative Agreement: N
NPL Status: Currently on the Final NPL
Fiscal Year: 1990
Federal Facility: N
Event: Not reported
Contact Telephone: Not reported
Contact Name: Not reported
Event Code: Not reported
PANASONIC (Continued) 1000218337
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Hazardous Ranking Score: Not reported
Cortese: Not reported
Access: Not reported
SIC Name: MANU - ELECTRONIC & OTHER ELECTRIC EQUIP
SIC Code: 36
NPL: Listed
Lead Agency: ENVIRONMENTAL PROTECTION AGENCY
Status Name: PROPERTY/SITE REFERRED TO RWQCB

CONTROL BOARD (RWQCB) LEAD
Status: DOES NOT REQUIRE DTSC ACTION. REFERRED TO REGIONAL WATER QUALITY State Senate District: 01301989
File Name: Not reported
Branch Name: NORTH COAST
Branch: NC
Type: NPL SITE, RP-FUNDED
Facility Type: NPRP
Facility ID: 43360032
Region: BERKELEY
City: CUPERTINO
Address: 10910 N TANTAU AVE
Name: INTERSIL
Calsite:

Date Post Remedial Action Monitoring Began: Not reported Date Remedial Action Underway: Not reported
Date Remediation Plan Submitted: Not reported
Date Pollution Characterization Began: Not reported
Date Preliminary Site Assessment Began: Not reported
Date Prelim Site Assmnt Workplan Submitted: Not reported Date Confirmed: Not reported
Leak Source: Not reported
Leak Cause: Not reported
How Discovered: Not reported
Local Case #: Not reported
Date Closed: Not reported
Facility Status: Remedial action (cleanup) Underway
Facility ID: 43S0064
Region: 2
SLIC REG 2:

Schedule Revised Date: Not reported
Schedule Due Date: Not reported
Schedule Document Type: Not reported
Schedule Sub Area Name: Not reported
Schedule Area Name: Not reported
Future Due Date: Not reported
Future Document Type: Not reported
Future Sub Area Name: Not reported
Future Area Name: Not reported
Comments: Facility Identified: Hazardous Waste/Border Zone Property List.

Completed Date: 08/11/1981
Completed Document Type: * Discovery
Completed Sub Area Name: Not reported
Completed Area Name: PROJECT WIDE
Completed Info:

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the site. There are two backup municipal supply wells within There are seven private wells and a creek downgradient of and Freon at 63 ppb.
per billion (ppb), 1,1-DCE at 92 ppb, chloroform at 100 ppb, benzenes. Groundwater contaminants include TCE at 910 parts dichloroethene (DCE), trichloroethane (TCA), and chloro- Detected soil contaminants include trichloroethene (TCE), located within the Hillview-Porter region.
tion sump and a chemical storage shed. The facility is
site appears to be primarily associated with a neutraliza- include the use of acids and solvents. Contamination at the operation at the site since 1963. Manufacturing processes Background Info: A manufacturer of microwave electronic equipment has been in Alternate City,St,Zip: CUPERTINO, CA 95014
Alternate Address: 10910 N TANTAU AVE
Alternate City,St,Zip: CUPERTINO, CA 95014
Alternate Address: 10600 RIDGEVIEW CT
Alternate City,St,Zip: CUPERTINO, CA 95014
Alternate Address: 10900 TANTAU AVENUE (INTERSIL)
Alternate City,St,Zip: CUPERTINO, CA 95014
Alternate Address: 19000 HOMESTEAD (SIEMENS)
Unknown Type: 0
For Residential Reuse: 0
For Industrial Reuse: 0
For Commercial Reuse: 0
Activity Comments: Not reported
Removal Action Certification: Not reported
Action Included Fencing: Not reported
Well Decommissioned: Not reported
Action Included Capping: Not reported
Liquids Treated (Gals): 0
Liquids Removed (Gals): 0
Definition of Status: PROPERTY/SITE REFERRED TO RWQCB
Activity Status: REFRW
Request to Delete Activity: Not reported
Estimated Size: Not reported
Est Person-Yrs to complete: 0
Comments Date: 08111981
Revised Due Date: Not reported
AWP Completion Date: Not reported
Proposed Budget: 0
AWP Code: Not reported
Activity Name: DISCOVERY
Activity: DISC
Facility ID: 43360032
State Senate District Code: 11
State Assembly District Code: 22
Lat/Long Description: Not reported
Lat/long Method: Not reported
Lat/Long (dms): 0 0 0 / 0 0 0
Lat/Long Direction: Not reported
Region Water Control Board Name: SAN FRANCISCO BAY
Region Water Control Board: SF
Supervisor Responsible for Site: Not reported
Staff Member Responsible for Site: Not reported
Groundwater Contamination: Confirmed
Date Site Hazard Ranked: Not reported
PANASONIC (Continued) 1000218337
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Registry ID: 110064129269
FINDS:

SIEMENS COMPONENTS, INC.

MENLO EQUITIES ASSOCIATES LLC
PRP Name: INTERSIL, INC.

PRP:

Non NPL Status: Not reported
NPL Status: Final
Action Completion: 1990-09-27 00:00:00
SEQ ID: 1
Operable Unit Number: OVERALL SITE
Action: GOVT ROD for PRP Remedy
Site ID: 901325
RG: 9
EPA ID: CAD041472341
City,State,Zip: CUPERTINO, CA 95014
Address: 10900 N Tantau Ave/19000 Homestead Rd
Name: INTERSIL INC./SIEMENS COMPONENTS
ROD:

Special Programs Name: Not reported
Special Programs Code: Not reported
Alternate Name: Not reported
Alternate Name: INTERSIL
Alternate Name: INTERSIL/SIEMENS
Alternate Name: INTERSIL INC / SIEMENS COMPONENTS
ID Value: CAD041472341
ID Name: EPA IDENTIFICATION NUMBER
ID Value: P23080
ID Name: BEP DATABASE PCODE
Comments: Facility Drive-By: No evidence of waste.

Comments Date: 08311981
Comments: List.

Comments Date: 08111981
Comments: Facility Identified: Hazardous Waste/Border Zone Property Comments Date: 08111981
Comments: Site is a RWQCB referral.

Comments Date: 01311990
Comments: water, and inhaling chemicals volatized from soil.

Comments Date: 01311990
Comments: contaminated groundwater, inhaling VOCs from use of groundComments Date: 01311990 Comments: health threats include touching contaminated soils, drinking Comments Date: 01311990
Comments: Groundwater and soil contaminated with VOCs. Potential Comments Date: 01311990
Comments: section 25356.

Comments Date: 01311989
Comments: This is the date the site was first listed pursuant to Comments Date: 01311989
groundwater and surface water contamination.
downgradient from the site are potential receptors for

1.5 miles of the site. Inhabitants of the residential area PANASONIC (Continued) 1000218337
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Registry ID: 110058327519
storers, and disposers of hazardous waste.
types of information about generators, transporters, treaters, Hazardous and Solid Waste Amendments (HSWA) of 1984. It tracks many Resource Conservation and Recovery Act (RCRA) of 1976 and the (RCRAInfo) is EPA’s comprehensive information system in support of the The Resource Conservation and Recovery Act Information System Inventory (TRI).

California Integrated Water Quality System (CIWQS), andToxic Release Environmental Reporting System (CERS),EnviroStor, GeoTracker, systems managed within CalEPA. The five systems are: California combines and merges facility and site information from five different implemented a new data warehouse system (nSite). This data warehouse The California Environmental Protection Agency (CalEPA) has recently activities.
information about waste management and pollution prevention transported, or released into the environment, and includes toxic chemicals that are being used, manufactured, treated, as federal facilities. It contains information about more than 650 database reported annually by certain covered industry groups, as well The Toxic Release Inventory System (TRIS) is a publicly available EPA Cleanup; and School sites.

Response, including Military Facilities and State Superfund; Voluntary Federal Superfund sites (National Priorities List (NPL)); State further. The EnviroStor database includes the following site types:
contamination or sites for which there may be reasons to investigate Information System (GIS) tool for identifying sites that have known (DTSC’s)-EnviroStor database is an online search and Geographic California’s Department of Toxic Substances Control’s

IDENTIFY DUPLICATE OR MISSING FACILITIES

STABLE IDENTIFIERS TO IMPROVE CONTINUITY FROM YEAR TO YEAR AND TO HELP

INVENTORY DATA ARE KEPT SEPARATE FROM THE EMISSIONS DATA AND HAVE RELEASE POINTS, CONTROL APPROACHES, AND REGULATIONS. FACILITY

AND THEIR PHYSICAL LOCATION, EMISSIONS UNITS, EMISSIONS PROCESSES, POINT POLLUTANT EMITTERS. IT CONTAINS INFORMATION ABOUT FACILITY SITES

STATIONARY SOURCES AND VOLUNTARILY-REPORTED SMALLER SOURCES OF AIR

THE EMISSION INVENTORY SYSTEM (EIS) MAINTAINS AN INVENTORY OF LARGE Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

Registry ID: 110001168245
Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

Registry ID: 110071753956
POSSIBLE INCLUSION ON THE NPL.

WELL AS SITES THAT ARE IN THE SCREENING AND ASSESSMENT PHASE FOR

EITHER PROPOSED TO BE OR ARE ON THE NATIONAL PRIORITIES LIST (NPL) AS SITES EVALUATED BY THE SUPERFUND PROGRAM. IT CONTAINS SITES THAT ARE

PROVIDING DATA ON THE INVENTORY OF ACTIVE AND ARCHIVED HAZARDOUS WASTE

LEGACY SYSTEMS INTO A COMPREHENSIVE TRACKING AND REPORTING TOOL,

THE SUPERFUND ENTERPRISE MANAGEMENT SYSTEM (SEMS) INTEGRATES MULTIPLE Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

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Source Of Facility: Enf Action
# Of Places: 1
NAICS Desc 3: Not reported
NAICS Code 3: Not reported
NAICS Desc 2: Not reported
NAICS Code 2: Not reported
NAICS Desc 1: Not reported
NAICS Code 1: Not reported
SIC Desc 3: Not reported
SIC Code 3: Not reported
SIC Desc 2: Not reported
SIC Code 2: Not reported
SIC Desc 1: Semiconductors and Related Devices
SIC Code 1: 3674
Place Longitude: -122.005359
Place Latitude: 37.335635
# Of Agencies: Not reported
Agency Type: Not reported
Facility Type: Industrial
Place Subtype: Not reported
Place Type: Facility
Agency Name: Not reported
Facility Id: 201394
Region: 2
City,State,Zip: CUPERTINO, CA 95014
Address: 10900 TANTAU
Name: 10900 N. TANTUA, CUP, INTERSIL
ENF:

City,State,Zip: CUPERTINO, CA 95014
Address: 10900 N TANTAU AVENUE
Name: INTERCIL C/O GEOMATRIX
DFR URL:

Registry ID: 110001168245
Envid: 1000218337
ECHO:
additional FINDS: detail in the EDR Site Report.

Click this hyperlink while viewing on your computer to access Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

Registry ID: 110071740379

IDENTIFY DUPLICATE OR MISSING FACILITIES

STABLE IDENTIFIERS TO IMPROVE CONTINUITY FROM YEAR TO YEAR AND TO HELP

INVENTORY DATA ARE KEPT SEPARATE FROM THE EMISSIONS DATA AND HAVE RELEASE POINTS, CONTROL APPROACHES, AND REGULATIONS. FACILITY

AND THEIR PHYSICAL LOCATION, EMISSIONS UNITS, EMISSIONS PROCESSES, POINT POLLUTANT EMITTERS. IT CONTAINS INFORMATION ABOUT FACILITY SITES

STATIONARY SOURCES AND VOLUNTARILY-REPORTED SMALLER SOURCES OF AIR

THE EMISSION INVENTORY SYSTEM (EIS) MAINTAINS AN INVENTORY OF LARGE Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

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Total Assessment Amount: 0
# Of Programs1: 1
Latest Milestone Completion Date: Not reported
Program: ENFCAO
GROUND WATER.

Description: ORDER FOR INVESTIGATION AND REMEDIATION OF POLLUTED SOIL & Title: Enforcement - 2 438181N01
Status: Active
EPL Issuance Date: Not reported
ACL Issuance Date: Not reported
Termination Date: Not reported
Achieve Date: Not reported
Adoption/Issuance Date: Not reported
Effective Date: 08/15/1990
Enforcement Action Type: Clean-up and Abatement Order
Order / Resolution Number: 90-11901
Region: 2
Enforcement Id(EID): 222753
Direction/Voice: Not reported
Fee Code: Not reported
Individual/General: Not reported
Status Enrollee: Not reported
WDR Review - Planned: Not reported
WDR Review - Pending: Not reported
WDR Review - No Action Required: Not reported
WDR Review - Rescind: Not reported
WDR Review - Revise/Renew: Not reported
WDR Review - Amend: Not reported
Termination Date: Not reported
Expiration/Review Date: Not reported
Effective Date: Not reported
Status Date: Not reported
Status: Not reported
Application Fee Amt Received: Not reported
301H: Not reported
Dredge Fill Fee: Not reported
Reclamation: Not reported
Npdes Type: Not reported
Major-Minor: Not reported
Npdes# CA#: Not reported
Order #: Not reported
Region: Not reported
Reg Measure Type: Not reported
Reg Measure Id: Not reported
WDID: Not reported
# Of Programs: Not reported
Program Category2: UNREGS
Program Category1: Not reported
Program: Not reported
Facility Waste Type 4: Not reported
Facility Waste Type 3: Not reported
Facility Waste Type 2: Not reported
Facility Waste Type: Not reported
Pretreatment: Not reported
Complexity: Not reported
Threat To Water Quality: Not reported
Design Flow: Not reported
PANASONIC (Continued) 1000218337
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301H: Not reported
Dredge Fill Fee: Not reported
Reclamation: Not reported
Npdes Type: Not reported
Major-Minor: Not reported
Npdes# CA#: Not reported
Order #: Not reported
Region: Not reported
Reg Measure Type: Not reported
Reg Measure Id: Not reported
WDID: Not reported
# Of Programs: Not reported
Program Category2: UNREGS
Program Category1: Not reported
Program: Not reported
Facility Waste Type 4: Not reported
Facility Waste Type 3: Not reported
Facility Waste Type 2: Not reported
Facility Waste Type: Not reported
Pretreatment: Not reported
Complexity: Not reported
Threat To Water Quality: Not reported
Design Flow: Not reported
Source Of Facility: Enf Action
# Of Places: 1
NAICS Desc 3: Not reported
NAICS Code 3: Not reported
NAICS Desc 2: Not reported
NAICS Code 2: Not reported
NAICS Desc 1: Not reported
NAICS Code 1: Not reported
SIC Desc 3: Not reported
SIC Code 3: Not reported
SIC Desc 2: Not reported
SIC Code 2: Not reported
SIC Desc 1: Semiconductors and Related Devices
SIC Code 1: 3674
Place Longitude: -122.005359
Place Latitude: 37.335635
# Of Agencies: Not reported
Agency Type: Not reported
Facility Type: Industrial
Place Subtype: Not reported
Place Type: Facility
Agency Name: Not reported
Facility Id: 201394
Region: 2
City,State,Zip: CUPERTINO, CA 95014
Address: 10900 TANTAU
Name: 10900 N. TANTUA, CUP, INTERSIL
Total $ Paid/Completed Amount: 0
Project $ Completed: 0
Liability $ Paid: 0
Project $ Amount: 0
Liability $ Amount: 0
Initial Assessed Amount: 0
PANASONIC (Continued) 1000218337
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Owner City,State,Zip: PALM BAY, FL 329050000
Owner Address 2: Not reported
Owner Address: 2401 PALM BAY RD NE STE M/S59-
Owner Name: HARRIS SMICONDUCTOR
Mailing City,State,Zip: PALM BEACH GARDENS, FL 334100000 Mailing Address 2: Not reported
Mailing Address: 3910 RCA BLVD STE 1011
Mailing Name: Not reported
Last Act Date: Not reported
Create Date: 07/23/1982
Inactive Date: 04/15/1994
EPA ID: CAD041472341
City,State,Zip: CUPERTINO, CA 95014
Address 2: Not reported
Address: 10900 N TANTAU AVE
Name: INTERSIL INC
HWTS:

Total $ Paid/Completed Amount: 0
Project $ Completed: 0
Liability $ Paid: 0
Project $ Amount: 0
Liability $ Amount: 0
Initial Assessed Amount: 0
Total Assessment Amount: 0
# Of Programs1: 1
Latest Milestone Completion Date: Not reported
Program: ENFCAO
Description: Not reported
Title: Enforcement - 2 438181N01
Status: Active
EPL Issuance Date: Not reported
ACL Issuance Date: Not reported
Termination Date: Not reported
Achieve Date: Not reported
Adoption/Issuance Date: Not reported
Effective Date: 08/15/1990
Enforcement Action Type: Clean-up and Abatement Order
Order / Resolution Number: 90-119
Region: 2
Enforcement Id(EID): 225142
Direction/Voice: Not reported
Fee Code: Not reported
Individual/General: Not reported
Status Enrollee: Not reported
WDR Review - Planned: Not reported
WDR Review - Pending: Not reported
WDR Review - No Action Required: Not reported
WDR Review - Rescind: Not reported
WDR Review - Revise/Renew: Not reported
WDR Review - Amend: Not reported
Termination Date: Not reported
Expiration/Review Date: Not reported
Effective Date: Not reported
Status Date: Not reported
Status: Not reported
Application Fee Amt Received: Not reported
PANASONIC (Continued) 1000218337
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Elevation Site Database(s) EPA ID Number
TSD EPA ID: KYD005009923
Gepaid: CAD041472341
Year: 1993
Tons: 3
Disposal Method: D80 - Disposal, Land Fill
CA Waste Code: -
TSD EPA ID: KYD005009923
Gepaid: CAD041472341
Year: 1993
Tons: 0.225
Disposal Method: D99 - Disposal, Other
CA Waste Code: 551 - Laboratory waste chemicals
TSD EPA ID: CAD009452657
Gepaid: CAD041472341
Year: 1994
Mailing Address: 3910 RCA BLVD STE 1011
Mailing Name: Not reported
Telephone: 4087434319
Contact: WILLIAM SANBORN SR, ENGR FRMN
City,State,Zip: CUPERTINO, CA 950140000
Address 2: Not reported
Address: 10900 N TANTAU AVE
Name: INTERSIL INC
HAZNET:

Facility Zip: 950140000
Facility State: CA
Facility County: Not reported
Facility City: CUPERTINO
Facility Address 2: Not reported
Facility Address: 10900 N TANTAU AVE
Facility Name: INTERSIL INC
Inactive Date: 1994-04-15 00:00:00
Issued EPA ID Date: 1982-07-23 00:00:00
NAICS Description: Semiconductor and Related Device Manufacturing NAICS Code: 334413
Create Date: 2002-03-14 16:36:26.000
EPA ID: CAD041472341
NAICS:

Longitude: -122.005891
Latitude: 37.336746
Category: FEDERAL
Facility Type: PERMANENT
Facility Status: Inactive
Contact Fax: Not reported
Contact Phone: Not reported
City,State,Zip: Not reported
Contact Address 2: Not reported
Contact Address: Not reported
Contact Name: WILLIAM SANBORN SR, ENGR FRMN
Owner Fax: Not reported
Owner Phone: Not reported
PANASONIC (Continued) 1000218337
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Elevation Site Database(s) EPA ID Number
101 additional CA HAZNET: record(s) in the EDR Site Report.

Click this hyperlink while viewing on your computer to access Tons: 48.8824
Disposal Method: D80 - Disposal, Land Fill
CA Waste Code: 352 - Other organic solids
TSD EPA ID: CAT000646117
Gepaid: CAD041472341
Year: 1988
Tons: 148.3328
Disposal Method: D80 - Disposal, Land Fill
CA Waste Code: 181 - Other inorganic solid waste
TSD EPA ID: CAT000646117
Gepaid: CAD041472341
Year: 1988
Tons: 0.1
Disposal Method: UNK -
CA Waste Code: 791 - Liquids with pH <= 2
TSD EPA ID: CAT080014079
Gepaid: CAD041472341
Year: 1988
Tons: 0.7923
Disposal Method: D99 - Disposal, Other
CA Waste Code: 135 - Unspecified aqueous solution
TSD EPA ID: CAD059494310
Gepaid: CAD041472341
Year: 1988
Tons: 0
Disposal Method: 03 -
CA Waste Code: 181 - Other inorganic solid waste
TSD EPA ID: CAT000646117
Gepaid: CAD041472341
Year: 1988
Tons: 1.5
Disposal Method: R01 - Recycler
CA Waste Code: 181 - Other inorganic solid waste
TSD EPA ID: CAD009452657
Gepaid: CAD041472341
Year: 1989
Tons: 6.7424
Disposal Method: D80 - Disposal, Land Fill
CA Waste Code: 151 - Asbestos containing waste
TSD EPA ID: CAD982042475
Gepaid: CAD041472341
Year: 1993
Tons: 1
Disposal Method: *** - Invalid Code
perchloroethylene, etc)
CA Waste Code: 211 - Halogenated solvents (chloroforms, methyl chloride, PANASONIC (Continued) 1000218337
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Elevation Site Database(s) EPA ID Number
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: Y
Waste Quantity: 5
Quantity Tons: 4.214
Meth Code: D80 - Disposal, Land Fill
RCRA Code: Not reported
Waste Code Description: 151 - Asbestos-containing waste TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAD982042475
Trans Name: Not reported
TSDF EPA ID: CAD982042475
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: CAD981425911
Manifest ID: 93138821
Receipt Date: 19931119
Creation Date: 9/14/1995 0:00:00
Shipment Date: 19931117
Gen EPA ID: CAD041472341
Year: 1993
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 450
Quantity Tons: 0.225
Meth Code: D99 - Disposal, Other
RCRA Code: D001
Waste Code Description: 551 - Laboratory waste chemicals 561 Detergent and soap TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAD009452657
Trans Name: Not reported
TSDF EPA ID: CAD009452657
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: CAD009452657
Manifest ID: 93163895
Receipt Date: 19940209
Creation Date: 9/15/1995 0:00:00
Shipment Date: 19940209
Gen EPA ID: CAD041472341
Year: 1994
Additional Information:

PANASONIC (Continued) 1000218337
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF EPA ID: KYD005009923
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: OHD009865825
Manifest ID: 92289981
Receipt Date: 19930129
Creation Date: 9/15/1995 0:00:00
Shipment Date: 19930122
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 6000
Quantity Tons: 3
Meth Code: D80 - Disposal, Land Fill
RCRA Code: D040
Waste Code Description: - Not reported
TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: KYD005009923
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ARD981908551
Manifest ID: 92289975
Receipt Date: 19930908
Creation Date: 9/12/1995 0:00:00
Shipment Date: 19930901
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: Y
Waste Quantity: 3
Quantity Tons: 2.5284
Meth Code: D80 - Disposal, Land Fill
RCRA Code: Not reported
Waste Code Description: 151 - Asbestos-containing waste TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAD982042475
Trans Name: Not reported
TSDF EPA ID: CAD982042475
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: CAD981425911
Manifest ID: 93138821
Receipt Date: 19931119
Creation Date: 9/14/1995 0:00:00
Shipment Date: 19931117
PANASONIC (Continued) 1000218337
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POTW: The POTW Does not have an approved pretreatment program. Some POTWs Reclamation: No reclamation requirements associated with this facility.

Baseline Flow: 0
Design Flow: 0
Secondary Waste Type: Not reported
Secondary Waste: Not reported
applicable DOHS standards.
ignitable or reactive substances and must be managed according to Primary Waste Type: Hazardous/Influent or Solid Wastes that contain toxic, corrosive, Waste2: Contaminated Ground Water
Waste Type2: Not reported
Primary Waste: CNWTRS
applicable DOHS standards.
ignitable or reactive substances and must be managed according to Primary Waste Type: Hazardous/Influent or Solid Wastes that contain toxic, corrosive, SIC Code 2: Not reported
SIC Code: 3674
Agency Type: Private
Agency Telephone: 6109927885
Agency Contact: LISA HAMILTON
Agency City,St,Zip: KING OF PRUSSIA 19406
Agency Address: 640 FREEDON BUSINESS CTR
Agency Name: GENERAL ELECTRIC COMPANY
Facility Contact: LISA HAMILTON
Facility Telephone: 6109927885
Subregion: 2
are assigned by the Regional Board
NPDES Number: CAG912003 The 1st 2 characters designate the state. The remaining 7 under Waste Discharge Requirements.

Facility Status: Active - Any facility with a continuous or seasonal discharge that is pumping.
repairing, oil production, storage and disposal operations, water washing, geothermal operations, air conditioning, ship building and processing operation of whatever nature, including mining, gravel semisolid wastes from any servicing, producing, manufacturing or Facility Type: Industrial - Facility that treats and/or disposes of liquid or Facility ID: San Francisco Bay 438181002
City: CUPERTINO
Address: 10900 N TANTAU AVE
Name: 10900 N TANTAU INTERSIL
WDS:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 2000
Quantity Tons: 1
Meth Code: *** - Invalid Code
RCRA Code: D040
perchloroethylene, etc.

Waste Code Description: 211 - Halogenated solvents (chloroform, methyl chloride, TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
PANASONIC (Continued) 1000218337
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Enf Action Type: Clean-up and Abatement Order
Enf Action Date: 08-15-1990
Site Zip: 95014
Site City: CUPERTINO
Site Address: 10900 TANTAU
Site Name: 10900 N. Tantua, Cup, Intersil
Site ID: 348178
Enforcement Action:

CERS Description: Unregulated
CERS ID: 201394
Site ID: 348178
City,State,Zip: CUPERTINO, CA 95014
Address: 10900 TANTAU
Name: 10900 N. TANTUA, CUP, INTERSIL
CERS:

Longitude: -122.005359
Latitude: 37.335635
Violations within 5 years: 0
Enforcement Actions within 5 years: 0
TTWQ: 1
Complexity: A
Major/Minor: Not reported
Design Flow: 0.0001
Expiration/Review Date: 06/18/1989
Termination Date: Not reported
Effective Date: 06/18/1986
Adoption Date: 06/18/1986
NPDES Number: Not reported
WDID: 2 438181N01
Order Number: 86-049
Regulatory Measure Type: WDR
Regulatory Measure Status: Historical
Program: UNREGS
Region: 2
SIC/NAICS: 3674
Place/Project Type: Other
Agency Address: 412 Creamery Way, Exton, PA 19341
Agency: General Electric Company
City,State,Zip: CUPERTINO, CA 95014
Address: 10900 TANTAU
Name: 10900 N. Tantua, Cup, Intersil
CIWQS:
products, solid wastes, and sewage pump out facilities. treatment systems that are complex, such as marinas with petroleum disposal), or any Class II or III disposal site, or facilities without waste treatment system (except for septic systems with subsurface Complexity: Category B - Any facility having a physical, chemical, or biological from a waste treatment facility.
or municipal water supply. Awsthetic impairment would include nuisance significant human population, or render unusable a potential domestic adverse impact on receiving biota, can cause aesthetic impairment to a Treat To Water: Moderate Threat to Water Quality. A violation could have a major the regional board and/or EPA.
may have local pretreatment programs that have not been approved by PANASONIC (Continued) 1000218337
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Enf Action Source: CIWQS,
Enf Action Program: UNSPEC
Enf Action Division: Water Boards
Enf Action Notes: Not reported
Enf Action Description: Clean-up and Abatement Order
PANASONIC (Continued) 1000218337
Facility ID: FA0200567
Record ID: PR0313940
Longitude: -122.015268
Latitude: 37.322342
Program Identifier: DEH PERMIT-HAZ WASTE GENERATOR PROGRAM Program Description: GENERATES 100 KG TO < 5 TONS/YEAR
PE#: 2205
UDF Email: Not reported
Telephone: 4082523454
Region: SANTA CLARA
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 ESTATES DR
Name: ONE HOUR CLEANERS BY LEE
CUPA SANTA CLARA:

Site 1 of 31 in cluster A
1 ft.

Relative:

Lower
Actual:
198 ft.
< 1/8 CUPERTINO, CA 95014
10045 ESTATES DR N/A
A1 ONE HOUR CLEANERS BY LEE CUPA Listings S112346389
1989 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1988 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1987 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1986 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1985 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1983 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1982 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1980 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1979 ONE HOUR MARTINIZING Drycleaning Plants, Except Rugs 1978 1 HOUR MARTINIZING Drycleaning Plants, Except Rugs 1977 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1976 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1975 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1974 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1973 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1972 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1971 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1970 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs 1969 ENTERPRISE CONTROLS INC Drycleaning Plants, Except Rugs Year: Name: Type:

EDR Hist Cleaner
Site 2 of 31 in cluster A
1 ft.

Relative:

Lower
Actual:
198 ft.
< 1/8 CUPERTINO, CA 95014
10045 ESTATES DR N/A
A2 ENTERPRISE CONTROLS INC EDR Hist Cleaner 1018709493
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2014 MJ CHOYS INC Drycleaning Plants, Except Rugs
2013 MJ CHOYS INC Drycleaning Plants, Except Rugs
2012 MJ CHOYS INC Drycleaning Plants, Except Rugs
2011 MJ CHOYS INC Drycleaning Plants, Except Rugs
2010 MJ CHOYS INC Drycleaning Plants, Except Rugs
2009 MJ CHOYS INC Drycleaning Plants, Except Rugs
2008 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1999 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1998 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1997 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1996 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1995 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1994 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1993 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1992 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1991 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
1990 ONE HOUR CLEANERS Drycleaning Plants, Except Rugs
ENTERPRISE CONTROLS INC (Continued) 1018709493
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DR
Name: ONE HOUR MARTINIZING BY LEE
DFR URL:

Registry ID: 110009537698
Envid: 1025892815
ECHO:

Site 3 of 31 in cluster A
1 ft.

Relative:

Lower
Actual:
198 ft.
< 1/8 CUPERTINO, CA 95014
10045 E ESTATES DR N/A
A3 ONE HOUR MARTINIZING BY LEE ECHO 1025892815
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 2
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 1987
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
EMI:

Site 4 of 31 in cluster A
1 ft.

Relative:

Lower
Actual:
198 ft.
< 1/8 CUPERTINO, CA 95014
10045 E ESTATES DRIVE N/A
A4 ONE HOUR MARTINIZING BY LEE EMI S105938894
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Elevation Site Database(s) EPA ID Number
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 1997
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 1996
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 2
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 1990
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
ONE HOUR MARTINIZING BY LEE (Continued) S105938894
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Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2000
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 1999
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 1998
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
ONE HOUR MARTINIZING BY LEE (Continued) S105938894
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Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2003
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2002
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2001
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported ONE HOUR MARTINIZING BY LEE (Continued) S105938894
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Year: 2006
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2005
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0.143
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2004
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
ONE HOUR MARTINIZING BY LEE (Continued) S105938894
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Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: .128
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2008
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: .1732528
Total Organic Hydrocarbon Gases Tons/Yr: .248
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2007
City,State,Zip: CUPERTINO, CA 952100000
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: .262
Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
ONE HOUR MARTINIZING BY LEE (Continued) S105938894
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Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0.225804
Total Organic Hydrocarbon Gases Tons/Yr: 0.46000000000000002 Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2010
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
Name: ONE HOUR MARTINIZING BY LEE
Part. Matter 10 Micrometers and Smllr Tons/Yr: 0
Particulate Matter Tons/Yr: 0
SOX - Oxides of Sulphur Tons/Yr: 0
NOX - Oxides of Nitrogen Tons/Yr: 0
Carbon Monoxide Emissions Tons/Yr: 0
Reactive Organic Gases Tons/Yr: 0
Total Organic Hydrocarbon Gases Tons/Yr: 0.14000000000000001 Consolidated Emission Reporting Rule: Not reported
Community Health Air Pollution Info System: Not reported Air District Name: BAY AREA AQMD
SIC Code: 7216
Air District Name: BA
Facility ID: 1010
Air Basin: SF
County Code: 43
Year: 2009
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DRIVE
ONE HOUR MARTINIZING BY LEE (Continued) S105938894
Contact Fax: Not reported
Contact Telephone: 408-252-3454
Contact City,State,Zip: CUPERTINO, CA 95014
Contact Address: 10045 E ESTATES DR
Contact Name: ENVIRONMENTAL MANAGER
EPA ID: CAD981579311
Handler City,State,Zip: CUPERTINO, CA 95014
Handler Address: 10045 E Estates Dr
Handler Name: One Hour Cleaners By Lee
Date Form Received by Agency: 19861118
RCRA Listings:

CERS
HAZNET
Site 5 of 31 in cluster A HWTS
1 ft. DRYCLEANERS
Relative:

Lower
Actual:
198 ft.
< 1/8 CUPERTINO, CA 95014 FINDS
10045 E ESTATES DR CPS-SLIC CAD981579311
A5 ONE HOUR CLEANERS BY LEE RCRA-LQG 1000118162
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Sub-Part P Indicator: No
Manifest Broker: No
Recycler Activity Without Storage: No
Exporter of Spent Lead Acid Batteries: No
Importer of Spent Lead Acid Batteries: No
Recognized Trader-Exporter: No
Recognized Trader-Importer: No
Handler Date of Last Change: 20020627
Financial Assurance Required: Not reported
Significant Non-Complier With a Compliance Schedule Universe: No Addressed Significant Non-Complier Universe: No
Unaddressed Significant Non-Complier Universe: No
Significant Non-Complier Universe: No
Groundwater Controls Indicator: N/A
Human Exposure Controls Indicator: N/A
Institutional Control Indicator: No
Environmental Control Indicator: No
Corrective Action Priority Ranking: No NCAPS ranking
Non-TSDFs Where RCRA CA has Been Imposed Universe: No
Subject to Corrective Action Universe: No
202 GPRA Corrective Action Baseline: No
2018 GPRA Renewals Baseline: Not on the Baseline
2018 GPRA Permit Baseline: Not on the Baseline
Sub-Part K Indicator: Not reported
Hazardous Secondary Material Indicator: N
Federal Facility Indicator: Not reported
Active Site State-Reg Handler: ---
Federal Universal Waste: No
Universal Waste Destination Facility: No
Universal Waste Indicator: No
Off-Site Waste Receipt: No
Underground Injection Control: No
Smelting Melting and Refining Furnace Exemption: No
Small Quantity On-Site Burner Exemption: No
Recycler Activity with Storage: No
Transfer Facility Activity: No
Transporter Activity: No
Mixed Waste Generator: No
Importer Activity: No
Short-Term Generator Activity: No
Operator Type: Not reported
Operator Name: Not reported
Owner Type: Private
Owner Name: Mac Lee
Mailing City,State,Zip: CUPERTINO, CA 95014
Mailing Address: 10045 E ESTATES DR
State District: 2
State District Owner: Ca
Active Site Indicator: Handler Activities
Accessibility: Not reported
Biennial Report Cycle: Not reported
Non-Notifier: Not reported
Federal Waste Generator Description: Large Quantity Generator Land Type: Other
EPA Region: 09
Contact Title: Not reported
Contact Email: Not reported
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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File Location: All Files are on GeoTracker or in the Local Agency Database RB Case Number: Not reported
Local Agency: SANTA CLARA COUNTY LOP
Case Worker: AC
Case Type: Cleanup Program Site
Longitude: -122.01591
Latitude: 37.3226
Lead Agency Case Number: 2023-17s
Lead Agency: SANTA CLARA COUNTY LOP
Global Id: T10000021095
Status Date: 06/01/2024
Facility Status: Open - Remediation
Region: STATE
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 EAST ESTATES DRIVE
Name: ONE-HOUR DRY CLEANERS
CPS-SLIC:

Evaluations: No Evaluations Found
Evaluation Action Summary:

Violations: No Violations Found
Facility Has Received Notices of Violations:

NAICS Codes: No NAICS Codes Found
List of NAICS Codes and Descriptions:

Electronic Manifest Broker: Not reported
Non Storage Recycler Activity: Not reported
Current Record: Yes
Spent Lead Acid Battery Exporter: No
Spent Lead Acid Battery Importer: No
Recognized Trader Exporter: No
Recognized Trader Importer: No
Large Quantity Handler of Universal Waste: No
State District Owner: Ca
Federal Waste Generator Description: Large Quantity Generator Handler Name: ONE HOUR CLEANERS BY LEE
Receive Date: 19861118
Historic Generators:

Owner/Operator Email: Not reported
Owner/Operator Fax: Not reported
Owner/Operator Telephone Ext: Not reported
Owner/Operator Telephone: 415-555-1212
Owner/Operator City,State,Zip: NOT REQUIRED, ME 99999
Owner/Operator Address: NOT REQUIRED
Date Ended Current: Not reported
Date Became Current: Not reported
Legal Status: Private
Owner/Operator Name: MAC LEE
Owner/Operator Indicator: Owner
Handler - Owner Operator:

ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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THE EMISSION INVENTORY SYSTEM (EIS) MAINTAINS AN INVENTORY OF LARGE Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

Registry ID: 110009537698
FINDS:

Click here to access the California GeoTracker records for this facility:
operated at the Site since June 2024 to remediate subsurface PCE. and adjacent properties. A Soil Vapor Extraction (SVE) System has concentrations of PCE in soil gas have been reported beneath the Site operations converted to a hydrocarbon-based solvent. Elevated tetrachloroethylene (PCE) from the 1960s until 2010 when the least the early 1960s. Dry cleaning operations included the use of environmental conditions: A dry cleaner operated on the Site since at Environmental Site Assessment report, which noted the following retail use in 1960. Additional details are presented in the Phase I farmstead and orchards. The Site was redeveloped for commercial 1950s, the Site was used for agricultural purposes, including a when a residential structure was noted. From at least 1939 until the Site. The Site appears to have been developed since at least 1897 station was generally found to be to the northeast, away from the Creek Boulevard to the north. Groundwater flow at the gasoline retail center to the west, Richwood Drive to the south, and Stevens Site is bounded by East Estates Drive to the east, the Market Place developer to redevelop the properties for residential purposes. The Site, along with several other adjacent properties, to a housing Idlewild TIC (tenants in common). Idlewild TIC intends to sell the DEH considers to be "the Site". The Site is currently owned by Santa Clara County Department of Environmental Health (DEH), and what Site History: The property with the APN 369-06-002 is currently being regulated by Claim Status: Not reported
Claim No: Not reported
RWQCB Region: SAN FRANCISCO BAY RWQCB (REGION 2)
Facility Project Subtype: Not reported
Military DOD Site: No
CA Enviroscreen 4 Score: 15-20%
CA Enviroscreen 3 Score: 16-20%
Disadvantaged Community: Not reported
Dwr Groundwater Subbasin Name: Santa Clara Valley - Santa Clara (2-009.02) CA Water Watershed Name: Santa Clara - Palo Alto (205.50) No Further Action Date: Not reported
Stop Description: Not reported
Stop Method: Not reported
Discharge Cause: Not reported
Discharge Source: Not reported
How Discovered Description: Not reported
How Discovered: Not reported
Leak Reported Date: Not reported
Begin Date: 05/19/2023
Quantity Released Gallons: Not reported
Coordinate Source: Not reported
EPA Region: 9
Potential Contaminants of Concern: Tetrachloroethylene (PCE) Potential Media Affected: Soil Vapor, Under Investigation ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Latitude: 37.322362
Region Code: 2
Owner Fax: 0
Mailing Zip: 950143340
Mailing State: CA
Mailing City: CUPERTINO
Mailing Address 2: Not reported
Mailing Address 1: 10045 E ESTATES DR
Mailing Name: Not reported
Contact Fax: 0
Contact Telephone: 4082523454
Contact Address 2: Not reported
Contact Address: 10045 E ESTATES DR
Contact Name: MOON K CHOI/OWNER
Owner Telephone: 4082523454
Owner Address 2: Not reported
Owner Address: 10045 E ESTATES DR
Owner Name: MOON K CHOI
Facility Addr2: Not reported
Inactive Date: Not reported
Facility Active: Yes
Create Date: 04/10/1987
SIC Description: Power Laundries, Family and Commercial SIC Code: 7211
NAICS Description: Drycleaning and Laundry Services (except Coin-Operated) NAICS Code: 81232
EPA Id: CAD981579311
City,State,Zip: CUPERTINO, CA 950140000
Address: 10045 E ESTATES DR
Name: ONE HOUR CLEANERS BY LEE
DRYCLEANERS:
additional FINDS: detail in the EDR Site Report.

Click this hyperlink while viewing on your computer to access transporters, and treatment, storage, and disposal facilities. provides information on hazardous waste shipments for generators, California’s Hazardous Waste Tracking System Data Mart (HWTS-DATAMART) storers, and disposers of hazardous waste.
types of information about generators, transporters, treaters, Hazardous and Solid Waste Amendments (HSWA) of 1984. It tracks many Resource Conservation and Recovery Act (RCRA) of 1976 and the (RCRAInfo) is EPA’s comprehensive information system in support of the The Resource Conservation and Recovery Act Information System Inventory (TRI).

California Integrated Water Quality System (CIWQS), andToxic Release Environmental Reporting System (CERS),EnviroStor, GeoTracker, systems managed within CalEPA. The five systems are: California combines and merges facility and site information from five different implemented a new data warehouse system (nSite). This data warehouse The California Environmental Protection Agency (CalEPA) has recently

IDENTIFY DUPLICATE OR MISSING FACILITIES

STABLE IDENTIFIERS TO IMPROVE CONTINUITY FROM YEAR TO YEAR AND TO HELP

INVENTORY DATA ARE KEPT SEPARATE FROM THE EMISSIONS DATA AND HAVE RELEASE POINTS, CONTROL APPROACHES, AND REGULATIONS. FACILITY

AND THEIR PHYSICAL LOCATION, EMISSIONS UNITS, EMISSIONS PROCESSES, POINT POLLUTANT EMITTERS. IT CONTAINS INFORMATION ABOUT FACILITY SITES

STATIONARY SOURCES AND VOLUNTARILY-REPORTED SMALLER SOURCES OF AIR ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Facility Address 2: Not reported
Facility Address: 10045 E ESTATES DR
Facility Name: ONE HOUR CLEANERS BY LEE
Inactive Date: Not reported
Issued EPA ID Date: 1987-04-10 00:00:00
NAICS Description: Drycleaning and Laundry Services (except Coin-Operated) NAICS Code: 81232
Create Date: 2004-10-20 10:23:57.043
EPA ID: CAD981579311
NAICS:

Longitude: -122.015215
Latitude: 37.322362
Category: FEDERAL
Facility Type: PERMANENT
Facility Status: Active
Contact Fax: Not reported
Contact Phone: Not reported
City,State,Zip: CUPERTINO, CA 95014
Contact Address 2: Not reported
Contact Address: 10045 E ESTATES DR
Contact Name: MOON K CHOI/OWNER
Owner Fax: Not reported
Owner Phone: Not reported
Owner City,State,Zip: CUPERTINO, CA 950143340
Owner Address 2: Not reported
Owner Address: 10045 E ESTATES DR
Owner Name: MOON K CHOI
Mailing City,State,Zip: CUPERTINO, CA 950143340
Mailing Address 2: Not reported
Mailing Address: 10045 E ESTATES DR
Mailing Name: Not reported
Last Act Date: Not reported
Create Date: 04/10/1987
Inactive Date: Not reported
EPA ID: CAD981579311
City,State,Zip: CUPERTINO, CA 95014
Address 2: Not reported
Address: 10045 E ESTATES DR
Name: ONE HOUR CLEANERS BY LEE
HWTS:

Annual Usage: 50
Name: Petroleum or Hydrocarbon Solvent, High Flash Point Facility Permit Expiration Date: 2019-03-01 00:00:00
Device Status: Registered
Drum Capacity: 40
Device Name: Union 40lb Petroleum Dry Cleaning Machine[UNI40P] Facility Status: Registered
NAICS Code: 812320
City,State,Zip: CUPERTINO, CA 95014-3340
Address: 10045 E ESTATES DR
Name: ONE HOUR MARTINIZING BY LEE
Facility ID: 1010
DRYCLEAN BAY AREA:

Longitude: -122.015215
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CA0000084517
Gepaid: CAD981579311
Year: 1997
Tons: 1.4775
Disposal Method: H01 - Transfer Station
CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CA0000084517
Gepaid: CAD981579311
Year: 1998
Tons: 0
Disposal Method: R01 - Recycler
CA Waste Code: -
TSD EPA ID: CAD981397417
Gepaid: CAD981579311
Year: 1999
Tons: 0.0667
Disposal Method: R01 - Recycler
perchloroethylene, etc)
CA Waste Code: 211 - Halogenated solvents (chloroforms, methyl chloride, TSD EPA ID: CAD981397417
Gepaid: CAD981579311
Year: 1999
Tons: 0.0975
Disposal Method: H01 - Transfer Station
CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CA0000084517
Gepaid: CAD981579311
Year: 1999
Tons: 0.0667
Disposal Method: -
perchloroethylene, etc)
CA Waste Code: 211 - Halogenated solvents (chloroforms, methyl chloride, TSD EPA ID: CAD981397417
Gepaid: CAD981579311
Year: 1999
Mailing Address: 10045 E ESTATES DR
Mailing Name: Not reported
Telephone: 4082523454
Contact: MOON K CHOI/OWNER
City,State,Zip: CUPERTINO, CA 950140000
Address 2: Not reported
Address: 10045 E ESTATES DR
Name: ONE HOUR CLEANERS BY LEE
HAZNET:

Facility Zip: 950140000
Facility State: CA
Facility County: Not reported
Facility City: CUPERTINO
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Waste Quantity: 16
Quantity Tons: 0.0667
Meth Code: - Not reported
RCRA Code: F002
perchloroethylene, etc.

Waste Code Description: 211 - Halogenated solvents (chloroform, methyl chloride, TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAD981397417
Trans 2 Name: Not reported
Trans 2 EPA ID: CAD063547996
Trans Name: Not reported
Trans EPA ID: CAR000030841
Manifest ID: 99717456
Receipt Date: Not reported
Creation Date: 8/2/2000 0:00:00
Shipment Date: 19991130
Gen EPA ID: CAD981579311
Year: 1999
Additional Information:
6 additional CA HAZNET: record(s) in the EDR Site Report.

Click this hyperlink while viewing on your computer to access Tons: 0.0975
Disposal Method: H01 - Transfer Station
CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CAD983652330
Gepaid: CAD981579311
Year: 1994
Tons: 1.455
Disposal Method: H01 - Transfer Station
CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CAT000613950
Gepaid: CAD981579311
Year: 1995
Tons: 0.03
Disposal Method: H01 - Transfer Station
CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CAT000613950
Gepaid: CAD981579311
Year: 1996
Tons: 1.32
Disposal Method: H01 - Transfer Station
CA Waste Code: 741 - Liquids with halogenated organic compounds >= 1,000 Mg./L TSD EPA ID: CA0000084517
Gepaid: CAD981579311
Year: 1996
Tons: 1.4175
Disposal Method: H01 - Transfer Station
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Shipment Date: 19990212
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: Not reported
Waste Quantity: 0
Quantity Tons: 0
Meth Code: R01 - Recycler
RCRA Code: Not reported
Waste Code Description: - Not reported
TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAD981397417
Trans 2 Name: Not reported
Trans 2 EPA ID: CAD076548635
Trans Name: Not reported
Trans EPA ID: CAR000030841
Manifest ID: 99297437
Receipt Date: 19990510
Creation Date: 9/1/1999 0:00:00
Shipment Date: 19990430
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: G
Waste Quantity: 16
Quantity Tons: 0.0667
Meth Code: R01 - Recycler
RCRA Code: F002
perchloroethylene, etc.

Waste Code Description: 211 - Halogenated solvents (chloroform, methyl chloride, TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAD981397417
Trans 2 Name: Not reported
Trans 2 EPA ID: CAD076548635
Trans Name: Not reported
Trans EPA ID: CAR000030841
Manifest ID: 99297437
Receipt Date: 19990510
Creation Date: 9/1/1999 0:00:00
Shipment Date: 19990430
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: G
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98617696
Receipt Date: 19981222
Creation Date: 2/26/1999 0:00:00
Shipment Date: 19981218
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 180
Quantity Tons: 0.09
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: SCD987574647
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98617696
Receipt Date: 19981222
Creation Date: 2/26/1999 0:00:00
Shipment Date: 19981218
Gen EPA ID: CAD981579311
Year: 1998
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: SCD987574647
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98860914
Receipt Date: 19990217
Creation Date: 4/20/1999 0:00:00
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Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: SCD987574647
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98213073
Receipt Date: 19980917
Creation Date: 12/7/1998 0:00:00
Shipment Date: 19980914
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: SCD987574647
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98289108
Receipt Date: 19981008
Creation Date: 12/8/1998 0:00:00
Shipment Date: 19981002
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: SCD987574647
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98275082
Receipt Date: 19980811
Creation Date: 10/20/1998 0:00:00
Shipment Date: 19980806
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: SCD987574647
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98213073
Receipt Date: 19980917
Creation Date: 12/7/1998 0:00:00
Shipment Date: 19980914
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98173892
Receipt Date: 19980618
Creation Date: 9/3/1998 0:00:00
Shipment Date: 19980612
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98169534
Receipt Date: 19980716
Creation Date: 9/15/1998 0:00:00
Shipment Date: 19980708
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 98169534
Receipt Date: 19980716
Creation Date: 9/15/1998 0:00:00
Shipment Date: 19980708
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 97351672
Receipt Date: 19971230
Creation Date: 7/23/1998 0:00:00
Shipment Date: 19971223
Gen EPA ID: CAD981579311
Year: 1997
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 97371289
Receipt Date: 19980521
Creation Date: 7/15/1998 0:00:00
Shipment Date: 19980515
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 390
Quantity Tons: 0.195
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96788171
Receipt Date: 19971104
Creation Date: 7/23/1998 0:00:00
Shipment Date: 19971031
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96788171
Receipt Date: 19971104
Creation Date: 7/23/1998 0:00:00
Shipment Date: 19971031
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 390
Quantity Tons: 0.195
Meth Code: H01 - Transfer Station
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96848349
Receipt Date: 19970910
Creation Date: 7/23/1998 0:00:00
Shipment Date: 19970905
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96851844
Receipt Date: 19971007
Creation Date: 7/23/1998 0:00:00
Shipment Date: 19971003
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96851844
Receipt Date: 19971007
Creation Date: 7/23/1998 0:00:00
Shipment Date: 19971003
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96859428
Receipt Date: 19970714
Creation Date: 12/4/1997 0:00:00
Shipment Date: 19970709
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96849166
Receipt Date: 19970812
Creation Date: 12/4/1997 0:00:00
Shipment Date: 19970807
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Gen EPA ID: CAD981579311
Year: 1996
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96621362
Receipt Date: 19970617
Creation Date: 12/4/1997 0:00:00
Shipment Date: 19970612
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96621362
Receipt Date: 19970617
Creation Date: 12/4/1997 0:00:00
Shipment Date: 19970612
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96487902
Receipt Date: 19961105
Creation Date: 5/21/1997 0:00:00
Shipment Date: 19961031
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96463046
Receipt Date: 19961206
Creation Date: 6/26/1997 0:00:00
Shipment Date: 19961127
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 390
Quantity Tons: 0.195
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96471531
Receipt Date: 19961230
Creation Date: 5/30/1997 0:00:00
Shipment Date: 19961227
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CA0000084517
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96477674
Receipt Date: 19961010
Creation Date: 6/26/1997 0:00:00
Shipment Date: 19961003
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96487902
Receipt Date: 19961105
Creation Date: 5/21/1997 0:00:00
Shipment Date: 19961031
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Receipt Date: 19960715
Creation Date: 5/20/1997 0:00:00
Shipment Date: 19960711
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96497281
Receipt Date: 19960816
Creation Date: 5/30/1997 0:00:00
Shipment Date: 19960809
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96497281
Receipt Date: 19960816
Creation Date: 5/30/1997 0:00:00
Shipment Date: 19960809
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96141870
Receipt Date: 19960620
Creation Date: 5/30/1997 0:00:00
Shipment Date: 19960614
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96101765
Receipt Date: 19960715
Creation Date: 5/20/1997 0:00:00
Shipment Date: 19960711
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CA0000084517
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 96101765
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95827775
Receipt Date: 19951227
Creation Date: 7/26/1996 0:00:00
Shipment Date: 19951221
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95827775
Receipt Date: 19951227
Creation Date: 7/26/1996 0:00:00
Shipment Date: 19951221
Gen EPA ID: CAD981579311
Year: 1995
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Creation Date: 7/26/1996 0:00:00
Shipment Date: 19951006
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95766658
Receipt Date: 19951108
Creation Date: 7/26/1996 0:00:00
Shipment Date: 19951103
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95814975
Receipt Date: 19951205
Creation Date: 7/26/1996 0:00:00
Shipment Date: 19951130
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95641954
Receipt Date: 19950814
Creation Date: 4/3/1996 0:00:00
Shipment Date: 19950809
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95641954
Receipt Date: 19950814
Creation Date: 4/3/1996 0:00:00
Shipment Date: 19950809
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95481517
Receipt Date: 19951012
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95424948
Receipt Date: 19950616
Creation Date: 4/2/1996 0:00:00
Shipment Date: 19950613
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95625961
Receipt Date: 19950714
Creation Date: 4/2/1996 0:00:00
Shipment Date: 19950711
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Shipment Date: 19941128
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95032915
Receipt Date: 19941229
Creation Date: 3/28/1996 0:00:00
Shipment Date: 19941228
Gen EPA ID: CAD981579311
Year: 1994
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95424948
Receipt Date: 19950616
Creation Date: 4/2/1996 0:00:00
Shipment Date: 19950613
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93763741
Receipt Date: 19941107
Creation Date: 3/28/1996 0:00:00
Shipment Date: 19941101
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93763741
Receipt Date: 19941107
Creation Date: 3/28/1996 0:00:00
Shipment Date: 19941101
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95079995
Receipt Date: 19941202
Creation Date: 3/28/1996 0:00:00
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 60
Quantity Tons: 0.03
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95063448
Receipt Date: 19941005
Creation Date: 3/26/1996 0:00:00
Shipment Date: 19941003
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
Trans Name: Not reported
TSDF EPA ID: CAT000613950
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 95063448
Receipt Date: 19941005
Creation Date: 3/26/1996 0:00:00
Shipment Date: 19941003
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 120
Quantity Tons: 0.06
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613950
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Manifest ID: 93668331
Receipt Date: 19940621
Creation Date: 3/26/1996 0:00:00
Shipment Date: 19940614
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93665788
Receipt Date: 19940719
Creation Date: 3/26/1996 0:00:00
Shipment Date: 19940713
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93467225
Receipt Date: 19940816
Creation Date: 3/26/1996 0:00:00
Shipment Date: 19940809
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93021777
Receipt Date: 19931230
Creation Date: 9/14/1995 0:00:00
Shipment Date: 19931227
Gen EPA ID: CAD981579311
Year: 1993
Additional Information:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93421710
Receipt Date: 19940422
Creation Date: 3/25/1996 0:00:00
Shipment Date: 19940418
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 390
Quantity Tons: 0.195
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Quantity Unit: P
Waste Quantity: 375
Quantity Tons: 0.1875
Meth Code: - Not reported
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: Not reported
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93027819
Receipt Date: Not reported
Creation Date: 9/12/1995 0:00:00
Shipment Date: 19931101
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93030567
Receipt Date: 19931202
Creation Date: 9/14/1995 0:00:00
Shipment Date: 19931129
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Receipt Date: 19930812
Creation Date: 9/12/1995 0:00:00
Shipment Date: 19930810
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93036330
Receipt Date: 19930910
Creation Date: 9/12/1995 0:00:00
Shipment Date: 19930907
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: Not reported
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93093692
Receipt Date: 19931008
Creation Date: 9/12/1995 0:00:00
Shipment Date: 19931004
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Map ID MAP FINDINGS
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 92623091
Receipt Date: 19930618
Creation Date: 9/8/1995 0:00:00
Shipment Date: 19930615
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 92565654
Receipt Date: 19930715
Creation Date: 9/11/1995 0:00:00
Shipment Date: 19930712
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD984908202
Trans Name: Not reported
Trans EPA ID: ILD984908202
Manifest ID: 93216513
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Elevation Site Database(s) EPA ID Number
Name: ONE HOUR MARTINIZING BY LEE
Affiliation Phone: 4089181954,
Affiliation Zip: Not reported
Affiliation Country: Not reported
Affiliation State: CA
Affiliation City: SAN JOSE
Affiliation Address: 1555 Berger Drive, Suite 300
Entity Title: Not reported
Entity Name: AARON COSTA - SANTA CLARA COUNTY LOP
Affiliation Type Desc: Local Agency Caseworker
Affiliation:

CERS Description: Cleanup Program Site
CERS ID: T10000021095
Site ID: 855174
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 EAST ESTATES DRIVE
Name: ONE-HOUR DRY CLEANERS
CERS:

Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 255
Quantity Tons: 0.1275
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l TSDF Alt Name: Not reported
TSDF Alt EPA ID: CAT000613893
Trans Name: Not reported
TSDF EPA ID: CAT000613893
Trans 2 Name: Not reported
Trans 2 EPA ID: ILD051060408
Trans Name: Not reported
Trans EPA ID: ILD051060408
Manifest ID: 92158016
Receipt Date: 19930521
Creation Date: 9/9/1995 0:00:00
Shipment Date: 19930518
Additional Code 5: Not reported
Additional Code 4: Not reported
Additional Code 3: Not reported
Additional Code 2: Not reported
Additional Code 1: Not reported
Quantity Unit: P
Waste Quantity: 195
Quantity Tons: 0.0975
Meth Code: H01 - Transfer Station
RCRA Code: F002
Waste Code Description: 741 - Liquids with halogenated organic compounds > 1000 mg/l ONE HOUR CLEANERS BY LEE (Continued) 1000118162
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Elevation Site Database(s) EPA ID Number
CERS Description: US EPA Air Emission Inventory System (EIS) CERS ID: 110009537698
Site ID: 484396
City,State,Zip: CUPERTINO, CA 95014
Address: 10045 E ESTATES DR
ONE HOUR CLEANERS BY LEE (Continued) 1000118162
additional FINDS: detail in the EDR Site Report.

Click this hyperlink while viewing on your computer to access Environmental Interest/Information System:

Click Here for FRS Facility Detail Report:

Registry ID: 110071743262
FINDS:

Site 6 of 31 in cluster A
1 ft.

Relative:

Lower
Actual:
198 ft.
< 1/8 CUPERTINO, CA 95014
10045 E ESTATES DRIVE N/A
A6 ONE HOUR MARTINIZING BY LEE FINDS 1031231931
Importer Activity: No
Short-Term Generator Activity: No
Operator Type: Other
Operator Name: Tom Robins
Owner Type: Other
Owner Name: Apro Llc
Mailing City,State,Zip: LONG BEACH, CA 90808
Mailing Address: 4130 COVER ST
State District: Not reported
State District Owner: Not reported
Active Site Indicator: Handler Activities
Accessibility: Not reported
Biennial Report Cycle: Not reported
Non-Notifier: Not reported
Federal Waste Generator Description: Not a generator, verified Land Type: Not reported
EPA Region: 09
Contact Title: Not reported
Contact Email: [email protected]
Contact Fax: Not reported
Contact Telephone: 310-323-3992
Contact City,State,Zip: LONG BEACH, CA 90808
Contact Address: 4130 COVER ST
Contact Name: TOM ROBINS
EPA ID: CAL000443757
Handler City,State,Zip: CUPERTINO, CA 95014
Handler Address: 19550 Stevens Creek Blvd
Handler Name: Apro Llc Dba United Pacific 2205
Date Form Received by Agency: 20190219
RCRA Listings:
147 ft. Site 7 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BLVD E MANIFEST CAL000443757
A7 APRO LLC DBA UNITED PACIFIC 2205 1024875099 RCRA NonGen / NLR TC07984167.2r Page 82
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Date Became Current: Not reported
Legal Status: Other
Owner/Operator Name: TOM ROBINS
Owner/Operator Indicator: Operator
Owner/Operator Email: Not reported
Owner/Operator Fax: Not reported
Owner/Operator Telephone Ext: Not reported
Owner/Operator Telephone: 310-323-3992
Owner/Operator City,State,Zip: LONG BEACH, CA 90808
Owner/Operator Address: 4130 COVER ST
Date Ended Current: Not reported
Date Became Current: Not reported
Legal Status: Other
Owner/Operator Name: APRO LLC
Owner/Operator Indicator: Owner
Handler - Owner Operator:

Sub-Part P Indicator: No
Manifest Broker: No
Recycler Activity Without Storage: No
Exporter of Spent Lead Acid Batteries: No
Importer of Spent Lead Acid Batteries: No
Recognized Trader-Exporter: No
Recognized Trader-Importer: No
Handler Date of Last Change: 20190222
Financial Assurance Required: Not reported
Significant Non-Complier With a Compliance Schedule Universe: No Addressed Significant Non-Complier Universe: No
Unaddressed Significant Non-Complier Universe: No
Significant Non-Complier Universe: No
Groundwater Controls Indicator: N/A
Human Exposure Controls Indicator: N/A
Institutional Control Indicator: No
Environmental Control Indicator: No
Corrective Action Priority Ranking: No NCAPS ranking
Non-TSDFs Where RCRA CA has Been Imposed Universe: No
Subject to Corrective Action Universe: No
202 GPRA Corrective Action Baseline: No
2018 GPRA Renewals Baseline: Not on the Baseline
2018 GPRA Permit Baseline: Not on the Baseline
Sub-Part K Indicator: Not reported
Hazardous Secondary Material Indicator: N
Federal Facility Indicator: Not reported
Active Site State-Reg Handler: ---
Federal Universal Waste: No
Universal Waste Destination Facility: Yes
Universal Waste Indicator: Yes
Off-Site Waste Receipt: No
Underground Injection Control: No
Smelting Melting and Refining Furnace Exemption: No
Small Quantity On-Site Burner Exemption: No
Recycler Activity with Storage: No
Transfer Facility Activity: No
Transporter Activity: No
Mixed Waste Generator: No
APRO LLC DBA UNITED PACIFIC 2205 (Continued) 1024875099 TC07984167.2r Page 83
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Generator Mail State: CA
Generator Mail Zip: 95014
Generator Mail City: CUPERTINO
Generator Mail Street 2: Not reported
Generator Mail Street 1: 19550 STEVENS CREEK BLVD
Generator Mail Street Number: Not reported
Generator Location Zip: 95014
Generator Location State: CA
Generator Location City: CUPERTINO
Generator Location Street 2: Not reported
Generator Location Street 1: 19550 STEVENS CREEK BLVD
Generator Location Street Number: Not reported
Generator Name: Apro Llc Dba United Pacific 2205
Generator EPA ID: CAL000443757
Origin Type: Service
Submission Type: DataImage5Copy
Manifest Status: Signed
Received Date: 20190815
Shipped Date: 20190808
Last Updated Date: 20190905
Manifest Tracking Number: 020812440JJK
E MANIFEST:

Evaluations: No Evaluations Found
Evaluation Action Summary:

Violations: No Violations Found
Facility Has Received Notices of Violations:

NAICS Description: Other Gasoline Stations
NAICS Code: 447190
List of NAICS Codes and Descriptions:

Electronic Manifest Broker: Not reported
Non Storage Recycler Activity: Not reported
Current Record: Yes
Spent Lead Acid Battery Exporter: No
Spent Lead Acid Battery Importer: No
Recognized Trader Exporter: No
Recognized Trader Importer: No
Large Quantity Handler of Universal Waste: No
State District Owner: Not reported
Federal Waste Generator Description: Not a generator, verified Handler Name: APRO LLC DBA UNITED PACIFIC 2205
Receive Date: 20190219
Historic Generators:

Owner/Operator Email: Not reported
Owner/Operator Fax: Not reported
Owner/Operator Telephone Ext: Not reported
Owner/Operator Telephone: 310-323-3992
Owner/Operator City,State,Zip: LONG BEACH, CA 90808
Owner/Operator Address: 4130 COVER ST
Date Ended Current: Not reported
APRO LLC DBA UNITED PACIFIC 2205 (Continued) 1024875099 TC07984167.2r Page 84
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Manifest Residue Indicator: N
Designated Facility Contact Company Name: Not reported
Designated Facility Location State: CA
Designated Facility Location Zip: 90222-0000
Designated Facility Location City: COMPTON
Designated Facility Location Street 2: Not reported
Designated Facility Location Street 1: N. ALAMEDA STREET Designated Facility Location Street Number: 2000
Designated Facility Mail State: CA
Designated Facility Mail Zip: 90222
Designated Facility Mail City: COMPTON
Designated Facility Mail Street 2: N. ALAMEDA STREET
Designated Facility Mail Street 1: CA90222 CA037US 2000 Designated Facility Mail Street Number: 2000
Designated Facility Name: World Oil Recycling
Designated Facility EPA ID: CAT080013352
Generator Contact Company Name: Not reported
Generator Mail State: CA
Generator Mail Zip: 90808
Generator Mail City: LONG BEACH
Generator Mail Street 2: Not reported
Generator Mail Street 1: 4130 COVER ST
Generator Mail Street Number: Not reported
Generator Location Zip: 95014
Generator Location State: CA
Generator Location City: SANTA CLARA
Generator Location Street 2: Not reported
Generator Location Street 1: 19550 STEVENS CREEK BLVD
Generator Location Street Number: Not reported
Generator Name: Apro Llc Dba United Pacific 2205
Generator EPA ID: CAL000443757
Origin Type: Service
Submission Type: DataImage5Copy
Manifest Status: Signed
Received Date: 20230530
Shipped Date: 20230519
Last Updated Date: 20230608
Manifest Tracking Number: 024548589JJK
Rejection Indicator: N
Manifest Residue Indicator: N
Designated Facility Contact Company Name: Not reported
Designated Facility Location State: AZ
Designated Facility Location Zip: 85365
Designated Facility Location City: YUMA
Designated Facility Location Street 2: Not reported
Designated Facility Location Street 1: 6500 S US HIGHWAY 95 Designated Facility Location Street Number: Not reported Designated Facility Mail State: CA
Designated Facility Mail Zip: 92882
Designated Facility Mail City: CORONA
Designated Facility Mail Street 2: 2621 GREEN RIVER RD
Designated Facility Mail Street 1: STE 105
Designated Facility Mail Street Number: Not reported
Designated Facility Name: Yuma Yes 2 Waste Transfer Station Designated Facility EPA ID: AZR000521146
Generator Contact Company Name: Not reported
APRO LLC DBA UNITED PACIFIC 2205 (Continued) 1024875099 TC07984167.2r Page 85
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Waste Line Number: 1
Manifest Tracking Number: 024548590JJK
Waste Line:

Transporter Name: All Clean Hazardous Waste Removal Inc Transporter EPA ID: CAD982492399
Transporter Line Number: 2
Manifest Tracking Number: 024548590JJK
Transporter Name: Bayview Industrial Services Inc
Transporter EPA ID: CAR000347492
Transporter Line Number: 1
Manifest Tracking Number: 024548590JJK
Transporter:

Rejection Indicator: N
Manifest Residue Indicator: N
Designated Facility Contact Company Name: Not reported
Designated Facility Location State: NV
Designated Facility Location Zip: 89003
Designated Facility Location City: BEATTY
Designated Facility Location Street 2: Not reported
Designated Facility Location Street 1: HWY 95 11 MILES S. OF BEATTY Designated Facility Location Street Number: Not reported Designated Facility Mail State: NV
Designated Facility Mail Zip: 89003
Designated Facility Mail City: BEATTY
Designated Facility Mail Street 2: HWY 95 11 MILES S. OF BEATTY Designated Facility Mail Street 1: Not reported
Designated Facility Mail Street Number: Not reported
Designated Facility Name: Us Ecology Nevada, Inc.

Designated Facility EPA ID: NVT330010000
Generator Contact Company Name: Not reported
Generator Mail State: CA
Generator Mail Zip: 90808
Generator Mail City: LONG BEACH
Generator Mail Street 2: Not reported
Generator Mail Street 1: 4130 COVER ST
Generator Mail Street Number: Not reported
Generator Location Zip: 95014
Generator Location State: CA
Generator Location City: SANTA CLARA
Generator Location Street 2: Not reported
Generator Location Street 1: 19550 STEVENS CREEK BLVD
Generator Location Street Number: Not reported
Generator Name: Apro Llc Dba United Pacific 2205
Generator EPA ID: CAL000443757
Origin Type: Service
Submission Type: DataImage5Copy
Manifest Status: Signed
Received Date: 20230606
Shipped Date: 20230519
Last Updated Date: 20230713
Manifest Tracking Number: 024548590JJK
Rejection Indicator: N
APRO LLC DBA UNITED PACIFIC 2205 (Continued) 1024875099 TC07984167.2r Page 86
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Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
State Waste Codes: CA-352
Quantity Non Haz Tons: Not reported
Quantity Non Haz Kg: Not reported
Quantity Haz Tons: 0.05
Quantity Haz Kg: 45.3515
Federal Waste Codes: D001, D018
EPA Waste Indicator: Y
Consent Number: Not reported
Waste Minimization Code Description: Not reported
Waste Minimization Code: Not reported
Source Code Description: Not reported
Source Code: Not reported
Form Code Description: Not reported
Form Code: Not reported
Waste Density Unit of Measure Description: Not reported Waste Density Unit of Measure Code: Not reported
Waste Density: Not reported
Waste Type Discrepancy Indicator: N
Quantity Discrepancy Indicator: N
Waste Residue Indicator: N
Management Method Description: STORAGE, BULKING AND/OR TRANSFER OFF SITE Management Method Code: H141
Non-Acute Waste Quantity, in Kilorgrams: 45.3515
Acute Waste Quantity, in Kilograms: 0
Waste Quantity, in Kilograms: 45.3515
Non-Acute Waste Quantity, in Tons: 0.05
Acute Waste Quantity, in Tons: 0
Waste Quantity, in Tons: 0.05
Quantity Unit of Measure Description: Pounds
Quantity Unit of Measure Code: P
Waste Quantity: 100
Container Type Description: Metal drums, barrels, kegs
Container Type Code: DM
Number of Containers: 1
Non-Hazardous Waste Description: Not reported
Ii
U.S. DOT Description: Un1325, Waste Flammable Solids, Organic, N.O.S., (Gasoline), 4.1, Pg U.S. DOT ID Number: UN1325
U.S. DOT Hazardous Indicator: Y
APRO LLC DBA UNITED PACIFIC 2205 (Continued) 1024875099 Num of inuse ust: Not reported
Facility type: Not reported
Owner type: Not reported
Longitude: -122.01469
Latitude: 37.32259
CERSID: Not reported
Permitting Agency: Santa Clara County Environmental Health Facility ID: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: APRO DISTRIBUTION 2205
UST:
147 ft. Site 8 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BL N/A
A8 APRO DISTRIBUTION 2205 UST U004350945
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Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Tank operator mailing city: Not reported
Tank operator mailing address: Not reported
Tank operator name: Not reported
Tank owner mailing state: Not reported
Tank owner mailing zip: Not reported
Tank owner mailing city: Not reported
Tank owner mailing address: Not reported
Tank owner name: Not reported
Tribal lands: Not reported
Epa region: Not reported
Num of oos ust: Not reported
Num of closed ust: Not reported
Num of inuse ust: Not reported
Facility type: Not reported
Owner type: Not reported
Longitude: -122.014690
Latitude: 37.3225900
CERSID: Not reported
Permitting Agency: Santa Clara County Environmental Health Facility ID: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: APRO DISTRIBUTION 2205
Tank spill bucket: Not reported
Tank ball float: Not reported
Tank alarms: Not reported
Tank cp shutoff: Not reported
Tank cp impressed current: Not reported
Tank sacrificial anode: Not reported
Tank piping construction: Not reported
Tank piping type: Not reported
Tank pwpiping construction: Not reported
Tank pc construction: Not reported
Tank type: Not reported
Tank capacity gallons: Not reported
Tank contents: Not reported
Tank num of compartments: Not reported
Tank installation date: Not reported
Tank closure date: Not reported
Tank configuration: Not reported
Tank status: Not reported
Tankidnumber: Not reported
Tank operator mailing state: Not reported
Tank operator mailing zip: Not reported
Tank operator mailing city: Not reported
Tank operator mailing address: Not reported
Tank operator name: Not reported
Tank owner mailing state: Not reported
Tank owner mailing zip: Not reported
Tank owner mailing city: Not reported
Tank owner mailing address: Not reported
Tank owner name: Not reported
Tribal lands: Not reported
Epa region: Not reported
Num of oos ust: Not reported
Num of closed ust: Not reported
APRO DISTRIBUTION 2205 (Continued) U004350945
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Tank spill bucket: Not reported
Tank ball float: Not reported
Tank alarms: Not reported
Tank cp shutoff: Not reported
Tank cp impressed current: Not reported
Tank sacrificial anode: Not reported
Tank piping construction: Not reported
Tank piping type: Not reported
Tank pwpiping construction: Not reported
Tank pc construction: Not reported
Tank type: Not reported
Tank capacity gallons: Not reported
Tank contents: Not reported
Tank num of compartments: Not reported
Tank installation date: Not reported
Tank closure date: Not reported
Tank configuration: Not reported
Tank status: Not reported
Tankidnumber: Not reported
Tank operator mailing state: Not reported
Tank operator mailing zip: Not reported
APRO DISTRIBUTION 2205 (Continued) U004350945
Tank Capacity: 00006000
Year Installed: 1962
Container Num: 2
Tank Num: 002
Leak Detection: Visual, Stock Inventor, Pressure Test
Container Construction Thickness: Not reported
Type of Fuel: UNLEADED
Tank Used for: PRODUCT
Tank Capacity: 00006000
Year Installed: 1962
Container Num: 1
Tank Num: 001
Total Tanks: 0004
Owner City,St,Zip: LOS ANGELES, CA 90017
Owner Address: 612 SO. FLOWER STREET
Owner Name: MOBIL OIL CORPORATION
Telephone: 4082572200
Contact Name: W.J. STEFFEN
Other Type: Not reported
Facility Type: Gas Station
Facility ID: 00000039669
Region: STATE
URL: Not reported
File Number: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BLVD
Name: MOBIL SERVICE STATION
HIST UST:
147 ft. Site 9 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BLVD N/A
A9 MOBIL SERVICE STATION HIST UST U001601007
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Leak Detection: Visual
Container Construction Thickness: Not reported
Type of Fuel: WASTE OIL
Tank Used for: WASTE
Tank Capacity: 00000280
Year Installed: 1962
Container Num: 4
Tank Num: 004
Leak Detection: Visual, Stock Inventor, Pressure Test
Container Construction Thickness: Not reported
Type of Fuel: 06
Tank Used for: PRODUCT
Tank Capacity: 00004000
Year Installed: 1962
Container Num: 3
Tank Num: 003
Leak Detection: Visual, Stock Inventor, Pressure Test
Container Construction Thickness: Not reported
Type of Fuel: REGULAR
Tank Used for: PRODUCT
MOBIL SERVICE STATION (Continued) U001601007
Facility ID: FA0259609
Record ID: PR0380387
Longitude: -122.014982
Latitude: 37.322792
Program Identifier: DEH PERMIT-HAZ WASTE GENERATOR PROGRAM Program Description: GENERATES 100 KG TO < 5 TONS/YEAR
PE#: 2205
UDF Email: Not reported
Telephone: 5102455218
Region: SANTA CLARA
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: CONOCOPHILLIPS COMPANY #2611220
CUPA SANTA CLARA:
147 ft. Site 10 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BL N/A
A10 CONOCOPHILLIPS COMPANY #2611220 S121473615 CUPA Listings Permitting Agency: CAMPBELL,CUPERTINO,LOS GATOS,MORGAN HILL Facility ID: 39
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: VALLCO 76 #112220-30242
UST:
147 ft. Site 11 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BL N/A
A11 VALLCO 76 #112220-30242 UST U004347927
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Tank spill bucket: Not reported
Tank ball float: Not reported
Tank alarms: Not reported
Tank cp shutoff: Not reported
Tank cp impressed current: Not reported
Tank sacrificial anode: Not reported
Tank piping construction: Not reported
Tank piping type: Not reported
Tank pwpiping construction: Not reported
Tank pc construction: Not reported
Tank type: Not reported
Tank capacity gallons: Not reported
Tank contents: Not reported
Tank num of compartments: Not reported
Tank installation date: Not reported
Tank closure date: Not reported
Tank configuration: Not reported
Tank status: Not reported
Tankidnumber: Not reported
Tank operator mailing state: Not reported
Tank operator mailing zip: Not reported
Tank operator mailing city: Not reported
Tank operator mailing address: Not reported
Tank operator name: Not reported
Tank owner mailing state: Not reported
Tank owner mailing zip: Not reported
Tank owner mailing city: Not reported
Tank owner mailing address: Not reported
Tank owner name: Not reported
Tribal lands: Not reported
Epa region: Not reported
Num of oos ust: Not reported
Num of closed ust: Not reported
Num of inuse ust: Not reported
Facility type: Not reported
Owner type: Not reported
Longitude: -122.01334
Latitude: 37.323935
CERSID: Not reported
VALLCO 76 #112220-30242 (Continued) U004347927
Population within 1500ft: 1670
Substance: Not reported
Status: No Further Action
Reported Date: Not reported
Address Match Type: PointAddress
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BLVD
Name: MOBIL
Lust ID: CAT0608500926
Facility ID: Not reported
Object ID: 44898
UST FINDER RELEASE:
147 ft. Site 12 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BLVD N/A
A12 MOBIL UST FINDER RELEASE 1029044609
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Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Longitude: -122.0147
Latitude: 37.3228399999999
Y Coord: 37.32284
X Coord: -122.0147
Coordinate Source: Geocode
Closed With Residual Contaminate: Not reported
NFA Letter 4: Not reported
NFA Letter 3: Not reported
NFA Letter 2: Not reported
NFA Letter 1: Not reported
EPA Region: 9
Tribe: Not reported
Within 100yr Floodplain: No
WHPA HUC12: Not reported
WHPA Facility Type: Not reported
WHPA Water Type: Not reported
WHPA PWS Facility ID: Not reported
Within WHPA: No
SPA HUC12: Not reported
SPA Facility Type: Not reported
SPA Water Type: Not reported
SPA PWS Facility ID: Not reported
Within SPA: No
Land Use: Developed, High Intensity
Domestic Wells within 1500ft: 0
MOBIL (Continued) 1029044609
Tank operator mailing state: Ca
Tank operator mailing zip: 95350
Tank operator mailing city: Modesto
Tank operator mailing address: 6010 McHenry Ave
Tank operator name: Boyett Petroleum
Tank owner mailing state: CA
Tank owner mailing zip: 95350
Tank owner mailing city: Modesto
Tank owner mailing address: 601 McHenry Ave
Tank owner name: Boyett Petroleum
Tribal lands: No
Epa region: 9
Num of oos ust: 0
Num of closed ust: 0
Num of inuse ust: Not reported
Facility type: Motor Vehicle Fueling
Owner type: Non-Government
Longitude: -122.014690
Latitude: 37.3225900
CERSID: 10348510
Permitting Agency: Santa Clara County Environmental Health Facility ID: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: BOYETT PETROLEUM BP 18
UST:
147 ft. Site 13 of 31 in cluster A

0.028 mi.

Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014
East 19550 STEVENS CREEK BL N/A
A13 BOYETT PETROLEUM BP 18 UST U004438356
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Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Tank piping type: Pressure
Tank pwpiping construction: Fiberglass
Tank pc construction: Fiberglass
Tank type: Double Wall
Tank capacity gallons: 10000
Tank contents: Midgraded Unleaded
Tank num of compartments: 1
Tank installation date: 1/1/1988 12:00:00 AM
Tank closure date: Not reported
Tank configuration: Stand Alone Tank
Tank status: Confirmed/Updated Information
Tankidnumber: 2
Tank operator mailing state: Ca
Tank operator mailing zip: 95350
Tank operator mailing city: Modesto
Tank operator mailing address: 6010 McHenry Ave
Tank operator name: Boyett Petroleum
Tank owner mailing state: CA
Tank owner mailing zip: 95350
Tank owner mailing city: Modesto
Tank owner mailing address: 601 McHenry Ave
Tank owner name: Boyett Petroleum
Tribal lands: No
Epa region: 9
Num of oos ust: 0
Num of closed ust: 0
Num of inuse ust: Not reported
Facility type: Motor Vehicle Fueling
Owner type: Non-Government
Longitude: -122.014690
Latitude: 37.3225900
CERSID: 10348510
Permitting Agency: Santa Clara County Environmental Health Facility ID: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: BOYETT PETROLEUM BP 18
Tank spill bucket: Yes
Tank ball float: Yes
Tank alarms: No
Tank cp shutoff: Yes
Tank cp impressed current: No
Tank sacrificial anode: No
Tank piping construction: Double Walled
Tank piping type: Pressure
Tank pwpiping construction: Fiberglass
Tank pc construction: Fiberglass
Tank type: Double Wall
Tank capacity gallons: 10000
Tank contents: Regular Unleaded
Tank num of compartments: 1
Tank installation date: 1/1/1988 12:00:00 AM
Tank closure date: Not reported
Tank configuration: Stand Alone Tank
Tank status: Confirmed/Updated Information
Tankidnumber: 1
BOYETT PETROLEUM BP 18 (Continued) U004438356
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Facility ID: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: BOYETT PETROLEUM BP 18
Tank spill bucket: Yes
Tank ball float: Yes
Tank alarms: No
Tank cp shutoff: No
Tank cp impressed current: No
Tank sacrificial anode: No
Tank piping construction: Other
Tank piping type: Gravity
Tank pwpiping construction: None
Tank pc construction: Fiberglass
Tank type: Double Wall
Tank capacity gallons: 1000
Tank contents: Used Oil
Tank num of compartments: 1
Tank installation date: 1/1/1988 12:00:00 AM
Tank closure date: Not reported
Tank configuration: Stand Alone Tank
Tank status: Confirmed/Updated Information
Tankidnumber: 4
Tank operator mailing state: Ca
Tank operator mailing zip: 95350
Tank operator mailing city: Modesto
Tank operator mailing address: 6010 McHenry Ave
Tank operator name: Boyett Petroleum
Tank owner mailing state: CA
Tank owner mailing zip: 95350
Tank owner mailing city: Modesto
Tank owner mailing address: 601 McHenry Ave
Tank owner name: Boyett Petroleum
Tribal lands: No
Epa region: 9
Num of oos ust: 0
Num of closed ust: 0
Num of inuse ust: Not reported
Facility type: Motor Vehicle Fueling
Owner type: Non-Government
Longitude: -122.014690
Latitude: 37.3225900
CERSID: 10348510
Permitting Agency: Santa Clara County Environmental Health Facility ID: Not reported
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BL
Name: BOYETT PETROLEUM BP 18
Tank spill bucket: Yes
Tank ball float: Yes
Tank alarms: No
Tank cp shutoff: Yes
Tank cp impressed current: No
Tank sacrificial anode: No
Tank piping construction: Double Walled
BOYETT PETROLEUM BP 18 (Continued) U004438356
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Map ID MAP FINDINGS
Direction
Distance EDR ID Number
Elevation Site Database(s) EPA ID Number
Tank spill bucket: Yes
Tank ball float: Yes
Tank alarms: No
Tank cp shutoff: Yes
Tank cp impressed current: No
Tank sacrificial anode: No
Tank piping construction: Double Walled
Tank piping type: Pressure
Tank pwpiping construction: Fiberglass
Tank pc construction: Fiberglass
Tank type: Double Wall
Tank capacity gallons: 10000
Tank contents: Premium Unleaded
Tank num of compartments: 1
Tank installation date: 1/1/1988 12:00:00 AM
Tank closure date: Not reported
Tank configuration: Stand Alone Tank
Tank status: Confirmed/Updated Information
Tankidnumber: 3
Tank operator mailing state: Ca
Tank operator mailing zip: 95350
Tank operator mailing city: Modesto
Tank operator mailing address: 6010 McHenry Ave
Tank operator name: Boyett Petroleum
Tank owner mailing state: CA
Tank owner mailing zip: 95350
Tank owner mailing city: Modesto
Tank owner mailing address: 601 McHenry Ave
Tank owner name: Boyett Petroleum
Tribal lands: No
Epa region: 9
Num of oos ust: 0
Num of closed ust: 0
Num of inuse ust: Not reported
Facility type: Motor Vehicle Fueling
Owner type: Non-Government
Longitude: -122.014690
Latitude: 37.3225900
CERSID: 10348510
Permitting Agency: Santa Clara County Environmental Health BOYETT PETROLEUM BP 18 (Continued) U004438356
Global Id: T0608575840
Geo Track:

Case Type: LUST Cleanup Site
Lead Agency: SANTA CLARA COUNTY LOP
City,State,Zip: CUPERTINO, CA 95014
Address: 19550 STEVENS CREEK BOULEVARD
Name: TOSCO #11220
LUST:

CERS

HIST CORTESE
147 ft. Site 14 of 31 in cluster A EMI

0.028 mi. Cortese
Relative:

Lower
Actual:
197 ft.
< 1/8 CUPERTINO, CA 95014 SWEEPS UST
East 19550 STEVENS CREEK BLVD HIST LUST N/A
A14 MOBIL LUST S103992302
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groundwater sample was collected from boring SB1 and was reported to ppm Ethylbenzene, 816 ppm Xylenes and 0.468 ppm MtBE. A grab parts per million (ppm) TPHg, 99.3 ppm Benzene, 459 ppm Toluene, 157 collected and were reported to have maximum concentrations of 8,940 traffic location and lack of well supplies. 14 soil samples were measured in SB1; which was not completed as a well due to its high completed as well MW1. Approximately +-inch of free product (FP) was 75 ft bgs onsite. Groundwater was encountered and boring SB2 was limit. 2001 In April, 2 soil borings (SB1 and SB2) were advanced to to be present in any of the samples above the laboratory reporting Xylenes and Methyl tert-Butyl Ether (MtBE). Benzene was not reported Petroleum Hydrocarbons as Gasoline (TPHg), Toluene, Ethylbenzene, reported to have low to non-detectable concentrations of Total 1-1.5 feet below the ground surface (ft bgs). The samples were soil samples were collected along the product lines at depths of replaced. 4 soil samples were collected beneath the dispensers and 6 is included as Attachment 5. 2000 In September, product piping was encountered. The case was closed on March 15, 1996. This case closure levels of contamination were detected and groundwater was not the UST area to 120 feet below the ground surface (ft bgs). Very low (USTs) were removed in 1985 and soil investigations were completed in through inventory reconciliation. The underground storage tanks this site. In 1985 a loss of 1,800 gallons of product was identified Site History: A previous Fuel Leak Investigation Case (07S1W18L01f) was open at Claim Status: Not reported
Claim Number: Not reported
RWQCB Region: SAN FRANCISCO BAY RWQCB (REGION 2)
Facility Project Subtype: Not reported
Military DOD Site: No
CA Enviroscreen 4 Score: 15-20%
CA Enviroscreen 3 Score: 16-20%
Disadvantaged Community: Not reported
Dwr Groundwater Subbasin Name: Santa Clara Valley - Santa Clara (2-009.02) CA Water Watershed Name: Santa Clara - Palo Alto (205.50) No Further Action Date: 09/23/2014
Stop Description: Not reported
Stop Method: Replace product piping
Discharge Cause: Unknown
Discharge Source: Other
How Discovered Description: Piping replacement
How Discovered: Other Means
Leak Reported Date: 11/03/2000
Begin Date: 09/11/2000
Quantity Released Gallons: 0
Coordinate Source: Manual Entry on Screens
EPA Region: 9
Potential Contaminants of Concern: MTBE / TBA / Other Fuel Oxygenates, Gasoline Potential Media Affect: Aquifer used for drinking water supply Local Case Number: 07S1W18L01f
File Location: All Files are on GeoTracker or in the Local Agency Database Local Agency: Not reported
RB Case Number: 14-064
Case Worker: Not reported
Status Date: 09/23/2014
Status: Completed - Case Closed
Longitude: -122.014662333333
Latitude: 37.3226033333333
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limits.
of constituents tested for present above the laboratory reporting samples were collected and were not reported to have concentrations B15) were advanced onsite to depths of 7-9 ft bgs. 11 shallow soil TBA, and 0.84 ppb 1,2-DCA. In September, 5 soil borings (B11 through ppb Toluene, 10 ppb Ethylbenzene, 52 ppb Xylenes, 12 ppb MtBE, 27 ppb reported maximum concentrations of 680 ppb TPHg, 36 ppb Benzene, 5.2 February, the final groundwater monitoring event was conducted and In May, verification groundwater monitoring commenced. 2013 In sparge system was re-started onsite and ran through April 2012. 2012 bgs and groundwater was encountered. 2011 In October, the ozone Borings B5, B6 and B8 were advanced an additional 4 feet past 100 ft and left open for an hour and groundwater did not enter the boring. encountered in these borings. Boring B7 was advanced to 100 ft bgs confirmation soil samples and groundwater was not anticipated to be B9 and B10. Borings B9 and B10 were advanced for the collection of advanced to 30 ft bgs. Groundwater was not encountered in borings B7, depths of 80-105 ft bgs, except for boring B10, which was only In July and August, 6 soil borings (B5 through B10) were advanced to injection systems were shut down and rebound monitoring began. 2009 concentrations of COCs. 2008 In September, the SVE and ozone collected and reported to have very low to non-detectable MW13) were completed to 94 ft bgs offsite. 18 soil samples were started at the site. 2006 In April, 2 monitoring wells (MW12 and the soil vapor extraction (SVE) and ozone injection systems were 140 ppm Ethylbenzene, 820 ppm Xylenes and 2.1 ppm MtBE. 2005 In June, concentrations of 8,700 ppm TPHg, 90 ppm Benzene, 510 ppm Toluene, ft bgs. 15 soil samples were collected and reported to have maximum (OS1/SVE1 through OS/SVE5) were installed onsite between 70 and 108 (OS6 through OS11) and 5 ozone sparge/soil vapor extraction wells FP was removed by this method. 2004 In July, 6 ozone sparge wells remove the FP from these wells. It is estimated that 0.66 gallons of MW2 and MW5. Bailing commenced and continued through March 2005 to

8.5 ft bgs. In November, FP was reported to be present again in wells limits, except for one detection of 0.015 ppm Xylenes in well MW10 at of the Constituents of Concern (COCs) above the laboratory reporting samples were collected and were not reported to have concentrations MW11) were installed offsite to depths of 90-100 ft bgs. 44 soil good remedial method. 2003 In July and August, 4 wells (MW8 through vapor phase. Based on the results of the test, DPE was found to be a

21.62 pounds of Benzene, and 31.37 pounds of MtBE were removed in the disposed of offsite. It is estimated that 746.08 pounds of TPHg, site. Approximately 2,300 gallons of groundwater were extracted and at this time, a dual phase extraction (DPE) test was conducted at the completion, approximately 0.01 ft FP was measured in well MW5. Also ppm MtBE, and 2.5 ppm Tert Butyl Alcohol (TBA). Following well Benzene, 220 ppm Toluene, 170 ppm Ethylbenzene, 920 ppm Xylenes, 12 reported to have maximum concentrations of 33,000 ppm TPHg, 12 ppm MW7) were installed to 90 ft bgs. 48 soil samples were collected and indicative of an older fuel leak. 2002 In April, 6 wells (MW2 through reported that the presence of TPHjf and TPHd in the sample was ppb Jet Fuel A, and 1,470,000 ppb TPH as Diesel (TPHd). It was ppb Toluene, 5,210 ppb Ethylbenzene, 27,000 ppb Xylenes, 1,400,000 and reported to contain 273,000 ppb TPHg, 16,700 ppb Benzene, 27,700 Additionally, a sample of the product (SB1-W PRODUCT) was analyzed 22,700 ppb Toluene, 4,860 ppb Ethylbenzene, and 25,600 ppb Xylenes. contain 248,000 parts per billion (ppb) TPHg, 14,700 ppb Benzene, MOBIL (Continued) S103992302
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Action: Staff Letter - #42267
Date: 10/03/2003
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter - #38507
Date: 08/20/2002
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter - #21890
Date: 01/09/2001
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Notice of Responsibility - #10921
Date: 01/29/2001
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter - #70211
Date: 11/02/2007
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: In Situ Physical/Chemical Treatment (other than SVE) Date: 10/11/2011
Action Type: REMEDIATION
Global Id: T0608575840
Action: Well Installation Report
Date: 01/24/2011
Action Type: RESPONSE
Global Id: T0608575840
Action: Well Installation Workplan
Date: 10/29/2010
Action Type: RESPONSE
Global Id: T0608575840
Action: Staff Letter
Date: 09/16/2010
Action Type: ENFORCEMENT
Global Id: T0608575840
LUST:

Phone Number: Not reported
Email: Not reported
City: OAKLAND
Address: 1515 CLAY ST SUITE 1400
Organization Name: SAN FRANCISCO BAY RWQCB (REGION 2)
Contact Name: Regional Water Board
Contact Type: Regional Board Caseworker
Global Id: T0608575840
LUST:

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Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 04/20/2010
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Soil Vapor Extraction (SVE)
Date: 06/01/2005
Action Type: REMEDIATION
Global Id: T0608575840
Action: Request for Closure - Regulator Responded
Date: 12/06/2013
Action Type: RESPONSE
Global Id: T0608575840
Action: Preliminary Site Assessment Workplan - Regulator Responded Date: 07/30/2013
Action Type: RESPONSE
Global Id: T0608575840
Action: Soil and Water Investigation Report
Date: 04/26/2010
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report
Date: 04/13/2011
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 09/10/2010
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 07/08/2008
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 11/17/2008
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter - #507221
Date: 12/27/2005
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter - #46113
Date: 12/10/2004
Action Type: ENFORCEMENT
Global Id: T0608575840
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Action: Monitoring Report - Quarterly
Date: 10/29/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Unauthorized Release Form
Date: 11/03/2000
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 10/29/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 11/28/2001
Action Type: RESPONSE
Global Id: T0608575840
Action: Correspondence
Date: 01/01/1996
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 01/31/2011
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 10/30/2010
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 07/30/2010
Action Type: RESPONSE
Global Id: T0608575840
Action: Corrective Action Plan / Remedial Action Plan
Date: 11/14/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Well Installation Workplan
Date: 12/07/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Staff Letter
Date: 10/28/2011
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 05/04/2011
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Action Type: RESPONSE
Global Id: T0608575840
Action: Remedial Progress Report
Date: 04/30/2008
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 06/01/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Well Installation Report
Date: 08/01/2002
Action Type: RESPONSE
Global Id: T0608575840
Action: Request for Closure
Date: 12/05/2013
Action Type: RESPONSE
Global Id: T0608575840
Action: CAP/RAP - Other Report
Date: 11/14/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 07/30/2008
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 03/31/2005
Action Type: RESPONSE
Global Id: T0608575840
Action: Soil and Water Investigation Report
Date: 10/19/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Staff Letter
Date: 03/05/2014
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 12/08/2009
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Remedial Progress Report
Date: 08/05/2005
Action Type: RESPONSE
Global Id: T0608575840
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Action: Soil and Water Investigation Workplan
Date: 05/15/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 04/30/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 01/30/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Closure/No Further Action Letter
Date: 09/23/2014
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Notice of Responsibility
Date: 10/28/2009
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 10/14/2009
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 08/29/2002
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 01/30/2008
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 02/20/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 04/13/2011
Action Type: RESPONSE
Global Id: T0608575840
Action: Soil and Water Investigation Report
Date: 06/19/2001
Action Type: RESPONSE
Global Id: T0608575840
Action: Other Report / Document
Date: 04/13/2011
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Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Other Workplan
Date: 12/14/2000
Action Type: RESPONSE
Global Id: T0608575840
Action: Well Destruction Report
Date: 08/08/2014
Action Type: RESPONSE
Global Id: T0608575840
Action: Soil and Water Investigation Report
Date: 07/07/2006
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 10/30/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Soil and Water Investigation Report
Date: 09/18/2003
Action Type: RESPONSE
Global Id: T0608575840
Action: Soil and Water Investigation Workplan
Date: 09/20/2002
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 10/30/2008
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 04/30/2008
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 01/30/2008
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 10/30/2009
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 07/30/2009
Action Type: RESPONSE
Global Id: T0608575840
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Action: Monitoring Report - Quarterly
Date: 04/30/2013
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 01/30/2013
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 10/30/2012
Action Type: RESPONSE
Global Id: T0608575840
Action: Monitoring Report - Quarterly
Date: 07/30/2012
Action Type: RESPONSE
Global Id: T0608575840
Action: Leak Stopped
Date: 09/11/2000
Action Type: Other
Global Id: T0608575840
Action: Staff Letter
Date: 08/05/2013
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 06/04/2009
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 05/27/2009
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Staff Letter
Date: 05/14/2012
Action Type: ENFORCEMENT
Global Id: T0608575840
Action: Preliminary Site Assessment Report
Date: 06/20/2001
Action Type: RESPONSE
Global Id: T0608575840
Action: Leak Reported
Date: 11/03/2000
Action Type: Other
Global Id: T0608575840
Action: Notification - Public Notice of Case Closure
Date: 01/02/2014
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Status Date: 11/14/2003
Status: Open - Remediation
Global Id: T0608575840
Status Date: 09/20/2002
Status: Open - Site Assessment
Global Id: T0608575840
Status Date: 09/11/2000
Status: Open - Site Assessment
Global Id: T0608575840
Status Date: 09/11/2000
Status: Open - Case Begin Date
Global Id: T0608575840
LUST: