series, to accommodate a maximum flow of 1,000 cfm prior to discharge to the atmosphere in accordance with Air District permit requirements.
3.5 Air Emissions Controls
Extracted vapors will be treated through VGAC filters to reduce the COCs and meet the requirements of the Air District permit. Sampling will be conducted on a regular basis from influent and effluent sampling ports to determine mass removal and emissions quantities in accordance with applicable permit requirements. If the SVE system vapor treatment does not meet permit requirements, vapor extraction will be temporarily stopped, and the treatment system will be adjusted to meet the permit requirements, as necessary.
Air District permit application forms are included in Appendix D. Preliminary estimated VOC emissions are provided in Table 4.
3.6 Contingencies
3.6.1 Groundwater
Moisture extracted as part of SVE system operation will be separated from the vapor prior to treatment and stored in a holding tank, as needed. The design is predicated on the perched groundwater zone not being temporally continuous based on well gauging information from 2021. Perched groundwater levels may fluctuate significantly with precipitation with increases in the rainy season (approximately October — March) and decreases in the dry season (approximately April — September) and therefore extraction is not intended to occur continuously during SVE implementation. The wellhead connections for the SVE system will also allow for the installation of a submersible pump for groundwater extraction, if needed during periods of groundwater infiltration in the area (e.g., during and following the rainy season). If submersible pumps are used, the extracted groundwater will be treated using bag filters to remove fines, as needed, and liquid phase GAC vessels of adequate capacity placed in series. The existing water treatment system will be visually assessed prior to groundwater treatment and might be retrofitted, if possible and, as needed, to adequately treat the groundwater prior to discharge in accordance with applicable permits. If the existing water treatment system is no longer viable, a new system will be installed.
Treated water will be discharged to the sewer system under an industrial wastewater discharge permit through the City of Santa Maria. Sampling will be conducted from influent and effluent sampling ports per discharge permit requirements. If effluent does not meet permit requirements, discharge will be temporarily stopped and the treatment system will be adjusted to meet permit requirements, as necessary. SVE system operation may continue while the groundwater treatment system is paused pending adequate space in the LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
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groundwater storage tanks. A permit application for sewer discharge from an industrial facility is included in Appendix D.
3.6.1.1 Baseline Groundwater Sampling
In accordance with the Settlement Agreement and the Offsite and Onsite Groundwater Characterization Work Plan, September 2025, baseline groundwater samples and depth to groundwater measurements will be collected from shallow/perched groundwater monitoring wells (MW -1 through MW -16). The depth to water measurements will be used to verify groundwater presence and quantity and anticipated VOC concentrations requiring treatment. Additionally, as required, a groundwater sample will be analyzed for the constituents outlined in the City of Santa Maria industrial wastewater discharge permit.
3.6.1.2 Extracted Groundwater Influent and Effluent
As needed, groundwater influent (untreated) and effluent (treated) will be analyzed for constituents outlined by the discharge permit requirements and COCs and evaluated to estimate mass removal of the groundwater treatment system. If quantities are low enough, groundwater may be containerized, sampled for waste characterization, and appropriately disposed of instead of treating and discharging to the sewer.
3.6.2 Potential Short Circuiting
Cracked pavement and existing groundwater extraction wells might provide preferential pathways for ambient air to travel into the subsurface and allow short-circuiting, reducing the vacuum for nearby soil vapor extraction wells. While the extraction wells are designed to prevent flow from ambient air from the immediate surrounding area, the radius of capture will extend past the well box and is therefore influenced by existing wells and the surrounding pavement. Startup testing results will be reviewed, and the conditions within the target treatment capture area assessed. If preferential pathways are identified that could allow the extraction wells to pull ambient air and reduce the vacuum in the subsurface, the pavement will be sealed. Existing extraction wells will be fitted with new, locking expansion caps, as needed, based on existing conditions.
3.6.3 Location and Elevation Survey
If groundwater accumulates and must be extracted and treated prior to discharge, the affected wells will be surveyed by a California -licensed Professional Land Surveyor. Vertical and horizontal locations, including sampling ports, outlets, and ground surface elevation, will be measured in accordance with the State of California's GeoTracker (GeoTracker) requirements. Following completion of installation and surveying, the survey data will be uploaded to the GeoTracker Electronic Submittal of Information (ESI) system.
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Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
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3.6.4 Site Power Suooly Evaluation
SVE systems are generally considered energy -intensive and require industrial -level Site power supply. Prior to implementation, the Site power supply will be evaluated to ensure access to an energy system with the capacity to run the system continuously. The Pacific Gas & Electric Company (PG&E) supplies the energy service to Santa Maria and will be contacted, as needed, to confirm the capacity of the current energy system.
Due to the Site location within a heavily industrial area, it is likely that the energy service is within the required range. In the event the power draw is greater than the system's current capacity, alternative lower -energy systems may need to be considered as a new power supply drop or transformer from PG&E generally has a lead time of over a year.
3.7 System Telemetry Requirements
Wireless telemetry will be used to provide real-time alarms, including blower status, groundwater storage tank level, vacuum levels, and/or pressure sensors on the groundwater treatment system. The use of the remote telemetry will allow for reduced system downtime.
3.8 Waste Management
Spent GAC media will be transported for offsite recycling or disposal at an approved facility. Documentation for the recycling or disposal of the spent GAC media will be provided in the Semi -Annual SVE Progress Report and/or SVE Completion Report, depending on timing.
4.0 SVE OPERATION, MAINTENANCE AND MONITORING
4.1 SVE Startup Testing
The objective of the SVE startup testing is to refine system parameters and optimize effectiveness of the system. The startup testing will be focused to address the area of highest observed soil vapor concentrations.
Testing for the SVE system will be performed for up to two weeks to refine the system operation as needed.
The SVE system will operate for up to 24 hours a day and be monitored by field technicians from the SVE system manufacturer with oversight from Langan personnel. Startup testing may include field monitoring, performing stepped rate and constant rate vacuum tests, and sampling.
System operating parameters including temperature, vacuum, influent flow (cfm), applied well -head vacuum, and vacuum at observation wells will be recorded at least three times per day during system startup operation. Total VOC concentrations will be measured in the field using a PI D.
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Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
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4.1.1 Startuo Phase Groundwater Levels
Prior to startup testing water levels will be gauged at monitoring wells (Figure 2) to verify the lack of or depth of perched groundwater on the Site and in the SVE implementation area. If present, potential groundwater removal will be managed as indicated in Section 3.6.1.
4.1.2 Sam
oling
During startup testing, soil vapor sampling will be conducted to document initial COC concentrations as a baseline from which to evaluate SVE effectiveness and to optimize mass removal and achieve treatment requirements in accordance with Air District permits.
4.1.2.1 Baseline Soil Vapor Sampling
Baseline soil vapor samples will be collected from the six soil vapor probes and five SVE wells intended for SVE performance monitoring within the SVE target treatment zone:
• SV8
• SV11
• SV12
• SV15
• SV16
• SV17
• SVE-1
• SVE-3
• SVE-5
• SVE-6
• SVE-8
Samples from soil vapor probes will be collected using 1 -liter laboratory -supplied summa canisters and flow controllers while using a sealed shroud to facilitate leak testing. Soil vapor probes will be purged of three times their volume prior to sampling in accordance with the California Department of Toxic Substances Control's (DTSC) Active Soil Gas Advisory. A leak tracer gas, such as helium, will be used to confirm leakage does not occur during sampling. A known concentration of the tracer gas (about 20% to 30% helium by volume) will be added inside the shroud and maintained at this concentration during sampling. Tracer gas concentrations within the soil vapor samples will be tested at the laboratory to verify the quality of the field sampling. In addition to laboratory testing, a tracer gas monitoring device will be used to evaluate leakage occurring in real time by testing the sample train following purging and sample collection. Soil vapor samples from SVE wells will be collected in tedlar bags using a soil vapor pump or in 1 -liter laboratory supplied summa canisters with flow controllers. SVE wells will be fitted with a temporary sampling port to facilitate sample collection.
Samples will be submitted under chain of custody protocol to a State of California Environmental Laboratory Accreditation Program (ELAP)-certified laboratory and analyzed for VOCs by USEPA Method TO -15. Soil vapor samples from soil vapor probes will additionally be analyzed for helium by ASTM Method D1946 if helium was used as the tracer gas, as applicable.
LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
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4.1.2.2 SVE Vapor Influent and Effluent
Soil vapor samples from the SVE system will be collected from the wellhead or blower inlet for the five SVE wells intended for SVE performance monitoring (SVE-1, SVE-3, SVE-5, SVE-6, SVE-8) during the initial field monitoring, periodically during operation, and just before system rebound testing and shutdown. Samples will also be collected from the blower inlet, at a sampling port between GAC vessels, and from an effluent sampling port from the soil vapor treatment system at a minimum at initial startup and just before system rebound testing and shutdown. These samples will also be collected periodically based on PID monitoring results and in accordance with the Air District Permit to better understand the SVE treatment system operation.
Soil vapor samples will be collected into tedlar bags or 1 -liter summa canisters, submitted under chain of custody protocol to a State of California ELAP-certified laboratory, and analyzed for VOCs by USEPA Method TO -15.
4.1.3 Construction Com
uletion Re
wort
Following installation of the SVE, the Agencies will prepare a SVE Construction Completion Report. The SVE Construction Completion Report will include a summary of the soil vapor monitoring locations, well box installation, final design plans, boring logs, SVE well construction logs, SVE startup activities, treatment system specifications, and describe construction activities. The report will be signed and certified by a Professional Geologist and/or Professional Engineer registered in the State of California.
4.2 Performance Monitoring
Per Table 1 of the Settlement Agreement the Agencies will complete monthly maintenance and four semi-annual monitoring events to assess the performance of the SVE system during operation. Quality control samples will be collected using a PID from various sampling ports on the SVE system, such as the blower inlet and VGAC outlet, and soil vapor monitoring samples will be collected from existing vapor probes or SVE wellheads.
The results of performance monitoring and quality control sampling for the SVE system will be included in the Semi -Annual progress reports. Reports will be completed for as long as the system is in operation and submitted by April 30th for the operating period of October to March and by October 31St for the operating period of April to September, per Exhibit A of the Settlement Agreement.
LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
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4.3 Remedial Goals, SVE Discontinuation, and Contingency VMS Per the Settlement Agreement, the agencies shall operate the SVE system until one of the following remedial goals is reached:
• TCE concentrations in soil vapor have reduced to a concentration of 3,000 pg/m3 and corresponding human health vapor intrusion risk level of 1 x 10' I LCR (based on an attenuation factor of 0.01); or • If the first remedial goal (1) is not met, the SVE system has operated for two (2) years (and accounting for any SVE System Interruptions as set forth in the Settlement Agreement), and TCE concentrations have reduced to a concentration of 30,000 µg/m3or less and based on a risk level of 1 x 104 ILCR; then the remedial goal shall be achieved by installation of a VMS at the former SEMCO building. After installation, the SVE system, including VMS, shall be owned and the responsibility of the current owner of the SEMCO Property.
Following the completion of SVE system operation, soil vapor monitoring will be conducted following a suitable rebound period based on the site -specific conditions and findings from post -shutdown vapor sampling at weekly intervals until concentrations are stabilized or can be used to estimate rebound time constants (DTSC, 2011). Remedial goals will be compared to the 95% UCL of the mean soil vapor concentrations, calculated using data from existing soil vapor probes SV8, SV11, SV12, SV15, SV16, and SV17 and five of the SVE wells that will be installed/utilized for SVE remediation SVE-1, SVE-3, SVE-5, SVE-6, and SVE-8 (Figure 6), per the Settlement Agreement.
If determined necessary based on the risk evaluation, a VMS may be required for the SEMCO building. If required, the perforated pipe installed beneath the SEMCO building will be connected to a riser, the installed inlet vent will be uncapped, and a radon fan will be installed on the riser and operated by the building owner as outlined in Appendix E. A VMS basis of design schematic is attached as Appendix E.
Once the SVE meets the remedial goals described above, the system will be discontinued, and the Agencies will submit a SVE Completion Report to the CCRWQCB. The SVE Completion Report will include final monitoring data, removal of SVE media onsite, and abandonment of the SVE wells.
LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
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5.0 QUALITY ASSURANCE/ QUALITY CONTROL
The Quality Assurance / Quality Control (QA / QC) procedures will be utilized in both sample collection and chemical analyses. The purpose of the QA/QC procedures is to ensure the reliability and validity of data generated during the monitoring events described in this work plan. QC samples will be collected during field activities, including field duplicate(s), an equipment blank, and a trip blank sample.
5.1 Field QA / QC Procedures
Field QA/QC procedures will be performed during sampling activities and will consist of the following measures:
• Chain of custody records will be used to document sample collection and will be submitted to the laboratory performing the chemical analyses. A chain of custody record will accompany all samples submitted for chemical analyses; and
• Daily information regarding sample collection will be recorded in field logs, including sample type(s), description, sample identification number(s), and sample time(s).
Field QA/QC samples will be collected and submitted for chemical analyses along with the samples, and will including the following:
• Field Duplicate Sample: One duplicate sample will be collected at a rate of once per sampling event or 10%, whichever is greater, and analyzed to evaluate the analytical procedures and methods employed by the laboratory. The duplicate sample will be collected concurrently with its parent sample and will be submitted for VOCs analysis.
• Equipment Blank Sample: One equipment blank sample will be collected per sampling day during the baseline groundwater sampling event to determine the efficacy of decontamination procedures for sampling equipment and will be collected when disposable or dedicated sampling equipment is not used. The equipment blank sample will consist of deionized water poured over or pumped through the decontaminated sampling equipment, and collection of the rinsate into the appropriate sample containers. The equipment blank sample will be submitted for VOCs analysis. • Trip Blank Sample: One trip blank sample will be submitted and analyzed per sampling event that includes water VOC analysis. The trip blank water sample will consist of a sample of deionized water provided by the laboratory and stored with the water VOC samples collected during each day of field activities. The purpose of the trip blank sample is to evaluate the potential for cross -contamination of LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
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aqueous VOC samples during handling. The trip blank sample(s) will be handled in the same manner as all other samples and submitted for VOCs analysis.
5.2 Laboratory QA / QC Procedures
Laboratory QA / QC procedures include the following:
• Chemical analyses will be performed within the required holding time for all samples chemically analyzed, and
• A State of California ELAP-certified laboratory will conduct the required analyses.
The laboratory will provide the following information for each sample:
• Method blank data;
• Surrogate recovery, instrument tuning, and calibration data; and • Signed laboratory reports including the sample designation, date of sample collection, date of sample analysis, laboratory analytical method employed, sample volume, and the reporting limit (RL).
LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
22 September 2025
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6.0 REFERENCES
Analytical Consulting Group, Inc. (ACG), 2021 a. Site Assessment Workplan. Monitoring Well Evaluation. Soil Vapor Sampling. Indoor Air Sampling. Former Semco Twist Drill & Tool Company. 2936 Industrial Parkway.
Santa Maria, California. Site I.D. No. SLT3S2411351 (October 20, 2015, California Water Code [Water Code] section 13267 Investigative Order [2015 Orderl. February 12.
ACG, 2021 b. Results of Indoor Air Sampling, Former Semco Twist Drill & Tool Company. 2936 Industrial Parkway. Santa Maria, California. April 7.
ACG, 2021c. Monitoring Well Investigation Report, Former Semco Twist Drill & Tool Company. 2936 Industrial Parkway. Santa Maria, California. Site I.D. No. SLT3S2411351. July 16.
ACG, 2021d. Soil Vapor Sampling Report, Former Semco Twist Drill & Tool Company. 2936 Industrial Parkway. Santa Maria, California. Site I.D. No. SLT3S2411351. July 16.
ACG, 2022a. Results of Second Round Indoor Air Sampling, Former Semco Twist Drill & Tool Company. 2936 Industrial Parkway. Santa Maria, California. February 11.
ACG, 2022b. Site Assessment Report, Former Semco Twist Drill & Tool Company. 2936 Industrial Parkway.
Santa Maria, California. Site I.D. No. SLT3S2411351. May 25.
California Environmental Protection Agency Department of Toxic Substances Control (DTSC). 2011.
Guidance for the Evaluation and Mitigation of Subsurface Vapor Intrusion to Indoor Air (Vapor Intrusion Guidance). October.
California Department of Water Resources (DWR). 1991. Monitoring Well Standards Bulletin 74-90. June 1991.
DWR, 2003, California's Groundwater, Bulletin 118 — Update 2003, dated 2003.
DWR. 2004. California Department of Water Resources Santa Maria River Valley Groundwater Basin.
California's Groundwater Bulletin No. 118. Last updated February 27, 2004.
California Environmental Protection Agency (CaIEPA) Department of Toxic Substances Control (DTSC), 2010. Proven Technologies and Remedies Guidance Remediation of Chlorinated Volatile Organic Compounds in Vadose Zone Soil. April. Retrieved from:
https://dtsc.ca.gov/wp-content/uploads/sites/31/2018/11/cVOC_040110.pdf CaIEPA DTSC, Los Angeles Regional Water Quality Control Board, and San Francisco Regional Water Quality Control Board, 2015. Advisory -Active Soil Gas Investigations. July.
Central Coast Regional Water Quality Control Board (CCRWQCB). 2023. Cleanup and Abatement Order No.
R3-2023-0070. Former Semco Twist Drill and Tool Company, Inc. ET AL. Industrial Parkway, Santa Maria Santa Barbara County. September 25.
LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
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CCRWQCB, State Water Resources Control Board (SWRCB), and CaIEPA, 2019. Water Quality Plan for the Central Coast Basin. June.
Dixson, K.L. and Nichols, R., 2006. Soil vapor extraction system design: A case study comparing vacuum and pore -gas velocity cutoff criteria. Remediation Journal 17(1). December. DOI: 10.1002/rem.20112 ERC Environmental and Energy Services Co., 1988. Subsurface Investigation Letter Report, SEMCO Twist Drill and Tool Company, Santa Maria, California. 1 April.
ERC Environmental and Energy Services Co., 1989. Subsurface Investigation: Phase 2, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California, California. March.
ERC Environmental and Energy Services Co., 1990a. Supplemental Subsurface Investigation, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California. March.
ERC Environmental and Energy Services Co., 1990b. Shallow and Deep Ground -water Investigation SEMCO Twist Drill and Tool Company Facility, Santa Maria, California. July.
ERC Environmental and Energy Services Co., 1990c. Remedial Action Plan for Shallow Aquifer System, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California. August.
ERC Environmental and Energy Services Co., 1991. Results of Soil Sampling Beneath the Concrete Pond Structure Located at the SEMCO Facility, Santa Maria, California. 3 December.
Everest Services, Inc., 2004. 2003 Third Quarter Report for Groundwater Monitoring Activities at 2936 Industrial Parkway, APNs 111-291-027 & 028, Santa Maria, California. February 24.
Fetter, 2014. Applied Hydrogeology, Fourth Edition.
Langan, 2024. Groundwater Monitoring Network and Extraction and Treatment System Evaluation Workplan, 2926, 2936, 2946, 2956, 2976, and 2986 Industrial Parkway, Santa Maria, California. 25 March.
Langan, 2025. Draft Revised Offsite Deep Groundwater Monitoring Investigation Work Plan, 2926, 2936, 2946, 2956, 2976, and 2986 Industrial Parkway, Santa Maria, California. June.
National Drought Mitigation Center, 2025. United States Drought Monitor Time Series: Santa Barbara County, 2000-2025. https://droughtmonitor.unl.edu/DmData/TimeSeries.aspx .
Occupational Safety and Health Administration. Hazardous Waste Operations and Emergency Response.
Code of Federal Regulations. Title 29, Part 1910, Section 120(b)(4).
Padre, 2023. Interim Remedial Action Plan, High -Vacuum Dual Phase Extraction Pilot Test, 3037 Industrial Parkway, Santa Maria, Santa Barbara County, California, (GLOBAL ID NO. SLT3S0301290). Prepared for: EFT Enterprises, L.P. July.
LANGAN
Work Plan For Onsite Soil Vapor Extraction
2936 Industrial Parkway, Santa Maria
Santa Barbara County, California
(Global ID No. SLT3S0301290)
Attachment B
22 September 2025
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Padre, 2024. Interim Remedial Action Report, High -Vacuum Dual Phase Extraction Pilot Test, 3037 Industrial Parkway, Santa Maria, Santa Barbara County, California, (GLOBAL ID NO. SLT3S0301290). Prepared for: EFT Enterprises, L.P. July.
San Francisco Bay Regional Water Quality Control Board (SFRWQCB), 2019. Environmental Screening Levels (ESLs): Groundwater Direct Exposure — Maximum Contaminant Level (MCL) Priority. July.
Switzer, C. and Kozzon, D. S., 2007. Soil Vapor Extraction Performance in Layered Vadose Zone Materials.
May. https://doi.org/10.2136/vzj2005.0131
Tetra Tech, Inc. (Tetra Tech), 1994. SEMCO Groundwater Remediation System Repair and Maintenance - Status Report, 2936 Industrial Parkway, Santa Maria, California, Contract No. 91 T0087, Task Order No. 3- 087-1.0-300478. 19 August.
Tetra Tech, 1998a. Water Treatment System, SEMCO Twist Drill and Tool Company, Santa Maria, California, Monitoring and Reporting Program (MRP) No. 92-16.30 March.
Tetra Tech, 1998b. Semi -Annual Report of Groundwater Monitoring, SEMCO Twist Drill and Tool Company, Santa Maria, California. December.
Tetra Tech, 2000. Letter Report on the Status of the SEMCO Groundwater Treatment System and Present Specific Actions for Groundwater Cleanup Optimization. 1 November.
Truex, M. J., Becker, D. J., Simon, M. A., Oostrom, M., Rice, A. K., &Johnson, C. D., 2013. Soil Vapor Extraction System Optimization, Transition, and Closure Guidance (PNNL-21843, RPT-DVZ-AFRI-006).
Pacific Northwest National Laboratory. Prepared for the U.S. Department of Energy under Contract DE- AC05-76RL01830. February. Retrieved from: https://www.clu-in.org/download/techfocus/sve/pnnl- 21843.pdf
United States Army Corps of Engineers (USACE), 2002. Soil Vapor Extraction and Bioventing. 3 June.
United States Environmental Protection Agency (USEPA) Solid Waste and Emergency Response, 1999.
Multi -Phase Extraction: State -of -the -Practice. June.
USEPA Office of Research and Development, 2001. Development of Recommendations and Methods to Support Assessment of Soil Venting Performance and Closure. September.
USEPA, 2017. How to Evaluate Alternative Cleanup Technologies For Underground Storage Tank Sties, A Guide For Corrective Action Plan Reviewers, Chapter II Soil Vapor Extraction. October.
WESTEC Services, 1989. Subsurface Investigation SEMCO Twist Drill and Tool Company, Santa Maria, California. January.
Worts, G.F. 1951. Geology and Ground -Water Resources of the Santa Maria Valley Area, California.
Geologic Survey Water -Supply Paper 1000. 1951. Available online:
https://pubs.usgs.gov/wsp/1000/report.pdf
LANGAN
Attachment B
TABLES
LANGAN
Table 1
Onsite Well Construction Summary
SEMCO, Santa Maria, California
Atfacnentrect: 781016901
eptember 2025
Well Name
Boring
Name
Well Status
Well Depth (feet bgs)
Water Depth (feet bgs)
Screen
Interval (feet
bgs)
Well
diameter
Well Head
Elevation2 at
installation
(feet above
msl)
Ground
Surface
Elevation at
installation
(feet above
msl)
Surface cover
Notes
2003
2021
Well
Completion Log
(1988 - 1991)
Extraction Well
Permit
Application
(1992)
2003
2021
2003
2021
Shallow Groundwater Monitoring Wells
MW-1/SMW-1
-
Sampled
Located, sampled, recharged
after purging 22 gallons
20 --
24.7 24.9
11.15 10.9
5.21 - 20
2 inches
236.44/ 236.49
236.62/ 236.63
Flush mount
with traffic box
Labeled as MW 12 on one map;
"could not grout surface casing"
noted on well construction log
MW-2/SMW-2
-
Sampled
Located, well cover not able to
be removed
26 --
20.31 —
19.99 —
5.2 - 25.2
2 inches
236.17/ 236.18
236.51/ 236.53
Flush mount
with traffic box
0.31 feet of free product on top
of water in 2003; "surface casing
not grouted" noted on well
construction log
MW-3/SMW-3
--
Dry
Located, well plug intact, dry
but moist at the bottom
24.5 --
22.21 22.44
—
—
9.5 - 24.5
2 inches
237.55/ 237.56
237.84/ 237.86
Flush mount
with traffic box
—
MW -4
NB -6
Dry
Located, well plug intact, dry
but moist at the bottom
30 --
30.4 29.52
—
—
9.5 - 29.4
4 inches
236.09
236.42
Flush mount
with traffic box
"dry well" noted on construction
log
MW -5
NB -7
Sampled
Located, well plug intact but
casing and well box damaged,
dry but moist at the bottom
29.5 --
29 29.02
9 --
8.8 - 28.9
4 inches
237.80
238.07
Flush mount
with traffic box
"dry well" noted on construction
log
MW -6
NB -12
Sampled
Not located
20.5 —
18.91 -
15.2 —
5.1 -19.9
4 inches
237.30
237.91
Flush mount
with traffic box
"low well yield" noted on
construction log
MW -7
NB -14
--
Located, well plug intact but
well box damaged and top
plugged with soil
24.8 —
45.6 21.14
--
--
3.9 - 24.0
4 inches
237.56
238.11
Flush mount
with traffic box
"dry well" noted on construction
log
MW -8
NB -15
Sampled
Located, sampled with grab
sample
25.5 —
24.7 13.46
8.91 9.9
4.7 - 24.8
4 inches
236.01
236.62
Flush mount
with traffic box
"dry well" noted on construction
log
MW -9
NB -13
Dry
Located, well plug intact, dry
but moist at the bottom
25.6 —
24.55 24.77
—
—
4.7 - 24.8
4 inches
236.32
236.79
Flush mount
with traffic box
"dry well" noted on construction
log
MW -10
-
Sampled
Located, well plug and cap
intact, sampled, recharged
after purging 6.5 gallons
39.0 --
37.6 37.74
34.2 34.17
33.0 - 37.5
4 inches
236.80
237.00
Flush mount
with traffic box
—
MW -11
NB -22
Dry
Located, well plug intact and
cap intact, dry but moist at the
bottom
20.0 --
40.05 40.27
-
--
9.7 - 19.2
4 inches
237.58
238.00
Flush mount
with traffic box
Labeled as MW -16 on one map
MW -12
NB -27
Not located
Not located
25.5 --
—
—
9.1 - 24.6
4 inches
236.24
236.58
Flush mount
with traffic box
—
MW -13
NB -39
Not located
Not located
41.0 --
--
--
--
--
20.50-39.40
2 inches
238.04
238.34
Flush mount
with traffic box
—
MW -14
NB -38
Dry
Located, well plug and cap
intact, dry but moist at the
bottom
47.25 -
21 85
45.74 --
--
25.65 - 45.65
2 inches
237.57
237.89
Flush mount
with traffic box
MW -15
NB -40
Not located
Not located
45.05 --
--
--
--
--
26.30 - 45.05
2 inches
236.24
236.45
Flush mount
with traffic box
MW -16
NB -44
Dry
Located , dry
45.57 --
45.18 45.36
--
--
25.47 - 45.09
2 inches
236.49
236.72
Flush mount
with traffic box
LANGAN
Table 1
Onsite Well Construction Summary
SEMCO, Santa Maria, California
Ati_Aanentr ect:781016901
eptember 2025
Well Name
Boring
Name
Well Status
Well Depth (feet bgs)
Water Depth (feet bgs)
Screen
Interval (feet
bgs)
Well
diameter
Well Head
Elevation2 at
installation
(feet above
msl)
Ground
Surface
Elevation at
installation
(feet above
msl)
Surface cover
Notes
2003
2021
Well
Completion Log
(1988 - 1991)
Extraction Well
Permit
Application
(1992)
2003
2021
2003
2021
Deep Groundwater Monitoring Wells
DMW-1
DMW-1
Abandoned
NA
210
--
--
—
—
--
188 - 208
4 inches
237.74
237.9
Flush mount
with traffic box
DMW-2
DMW-2
Sampled
Located, well plug intact, dry
but moist at the bottom
208
—
199
191.87
139.22
--
179 - 199
4 inches
236.43
236.4
Flush mount
with traffic box
DMW-3
DMW-3
Sampled
Not located
201.0
--
200
--
139
--
180 - 200
4 inches
236.19
236.38
Flush mount
with traffic box
DMW-4
DMW-4
Sampled
Located, dry
209.4
--
207
204.33
141
--
187 - 207
4 inches
238.21
238.44
Flush mount
with traffic box
DMW-51
--
Dry
Located, dry but moist at the
bottom
200.63
--
--
—
4 inches
--
--
—
--
Extraction Wells
EX -1
—
--
—
—
40 —
—
--
--
10 - 40
4 inches
--
--
--
EX-2
--
--
—
--
40 --
—
--
--
10 - 40
4 inches
--
--
--
EX-3
--
--
—
—
40 --
--
--
--
10 - 40
4 inches
--
--
--
EX-4
--
--
—
—
40 --
--
--
—
10 - 40
4 inches
--
--
--
--
EX-5
--
--
—
—
40 --
--
-
--
10 - 40
4 inches
--
--
--
--
Notes:
'Well location found during 2021 investigation and not previously 2 Well Head Elevation is presumed to be Top of Casing Elevation Information gathered from the 2003 Everest Services, Inc. report, Appendix A.
bgs - below ground surface
msl - mean sea level
noted on other maps or reports. Noted as "DMW5?" for the purpose of the 2021 investigation 2003 Third Quarter Report For Groundwater Monitoring Activities, the 2021 Analytical Consulting Group, Inc. report, Monitoring Well Investigation Report, Former Semco Twist Drill & Tool Company, and Well Completion Logs provided in
LANGAN
Table 2
Historical Groundwater Elevation Data (Shallow/Perched Zone) SEMCO, Santa Maria, California
La nRttachrno4ntt 8781016901
September 2025
Well Name
Casing Elevation
(feet amsl)
Well depth
(feet bwc)
Date measured
Depth to Water (feet
bwc)
Groundwater Elevation
(feet amsl)
MW -1
236.44
24.7 Nov -88
9.37 227.07
Nov -89
10.33 226.11
Feb -90
9.64 226.80
Feb -90
8.57 227.87
Jun -90
10.24 226.20
Dec -98
—
—
Sep -03
11.15 227.34
Jun -21
10.90 227.59
MW -2
236.17
20.3 Nov -88
9.84 226.33
Nov -89
11.56 224.61
Feb -90
8.55 227.62
Feb -90
6.71 229.46
Jun -90
9.56 226.61
Jul -94
18.16 218.01
Jul -95
7.00 229.17
Jun -96
9.71 226.46
Jan -97
7.70 228.47
Jun -97
10.70 225.47
Dec -97
10.77 225.40
Jul -98
6.78 229.39
Nov -98
—
—
Dec -98
6.78 229.39
Jul -99
9.97 226.20
Jan -00
10.30 225.87
Jul -00
10.94 225.23
Dec -00
13.55 222.62
Sep -03
19.99 218.44
Jun -21
Unable to open well
—
MW -3
237.56
22.2 Nov -88
11.56 226.00
Nov -89
12.56 225.00
Feb -90
11.52 226.04
Feb 90
10.62 226.94
Jun -90
11.94 225.62
Dec -98
14.07 223.49
Sep -03
-
-
Jun -21
Dry
—
MW -4
236.09
30.4 Nov -89
—
—
Feb -90
—
—
Feb -90
-
-
Jun -90
—
—
Dec -98
-
-
Sep -03
_ -
-
Jun -21
Dry
—
MW -5
237.80
29.0 Nov -89
—
—
Feb -90
—
—
Feb -90
-
-
Jun -90
—
—
Dec -98
12.88 224.92
Sep -03
9.00 231.03
Jun -21
Dry
—
LANGAiti
Table 2
Historical Groundwater Elevation Data (Shallow/Perched Zone) SEMCO, Santa Maria, California
La nRttachrnsj.entt 8781016901
September 2025
Well Name
Casing Elevation
(feet amsl)
Well depth
(feet bwc)
Date measured
Depth to Water (feet
bwc)
Groundwater Elevation
(feet amsl)
MW -6
237.30
18.9 Nov -89
15.20 222.10
Feb -90
12.60 224.70
Feb -90
10.52 226.78
Jun -90
9.11 228.19
Aug -94
11.23 226.07
Jun -95
11.32 225.98
Jun -96
13.02 224.28
Jan -97
7.69 229.61
Jun -97
13.30 224.00
Dec -97
9.21 228.09
Jul -98
7.89 229.41
Nov -98
13.96 223.34
Dec -98
10.90 226.40
Jul -99
12.51 224.79
Jan -00
12.38 224.92
Jul -00
13.01 224.29
Dec -00
14.29 223.01
Sep -03
15.20 224.34
Jun -21
Unable to locate
—
MW -7
237.56
24.01 Nov -89
—
—
Feb -90
—
—
Feb -90
-
-
Jun -90
—
—
Dec -98
-
-
Sep -03
-
-
Jun -21
Dry
—
MW -8
236.01
24.72 Nov -89
—
-
Feb -90
—
-
Feb -90
-
-
Jun -90
20.45 215.56
Aug -94
10.60 225.41
Jun -95
6.23 229.78
Jun -96
7.81 228.20
Jan -97
3.77 232.24
Jun -97
8.30 227.71
Dec -97
5.19 230.82
Jul -98
5.84 230.17
Nov -98
8.55 227.46
Dec -98
6.36 229.65
Jul -99
6.35 229.66
Jan -00
5.44 230.57
Jul -00
6.25 229.76
Dec -00
6.78 229.23
Sep -03
8.91 229.37
Jun -21
9.90 228.38
MW -9
236.32
24.6 Nov -89
—
—
Feb -90
—
—
Feb -90
-
-
Jun -90
-
-
Dec -98
-
--
Sep-03
—
--
Jun-21
Dry
--
LANGAiti
Table 2
Historical Groundwater Elevation Data (Shallow/Perched Zone) SEMCO, Santa Maria, California
La nRttachrror4ntt 8781016901
September 2025
Well Name
Casing Elevation
(feet amsl)
Well depth
(feet bwc)
Date measured
Depth to Water (feet
bwc)
Groundwater Elevation
(feet amsl)
MW 10
236.80
37.6 Feb -90
34.46 202.34
Feb -90
34.31 202.49
Jun -90
34.28 202.52
Aug -94
33.96 202.84
Jun -95
33.47 203.33
Jun -96
33.95 202.85
Jan -97
34.19 202.61
Jun -97
34.03 202.77
Dec -97
34.41 202.39
Jul -98
33.30 203.50
Nov -98
34.10 202.70
Dec -98
34.18 202.62
Jul -99
33.97 202.83
Jan -00
34.25 202.55
Jul -00
33.87 202.93
Dec -00
34.21 202.59
Sep -03
34.20 204.89
Jun -21
34.17 204.92
MW -11
237.58
40.0 Feb -90
16.45 221.13
Feb -90
9.71 227.87
Jun -90
11.66 225.92
Feb -90
16.45 221.13
Aug -94
12.39 225.19
Jun -95
9.75 227.83
Jun -96
11.26 226.32
Jan -97
7.71 229.87
Jun -97
12.00 225.58
Dec -97
9.35 228.23
Jul -98
8.68 228.90
Nov -98
13.48 224.10
Dec -98
9.80 227.78
Jul -99
11.02 226.56
Jan -00
11.99 225.59
Jul -00
11.74 225.84
Dec -00
13.73 223.85
Sep -03
-
-
Jun -21
Dry
-
MW -14
239.84
21.85 Sep 03
-
-
45.74 Jun -21
Dry
-
MW -16
238.76
45.2 Sep -03
-
-
Jun -21
Dry
—
Notes:
Historical data from 2003 Third Quarter Report For Groundwater Monitoring Activities at 2936 Industrial Parkway, APNs 111-291-027 & 028, Santa Maria, California, dated 24 February 2004 by Everest Services, Inc. and Monitoring WeII Investigation Report, Former Semco Twist Drill & Tool Company, 2936 Industrial Parkway, Santa Maria, California, dated 16 July 2021 by Analytical Consulting Group, Inc. 'Well depth reported at 45.6 feet in bws in 2003.
2 Well depth reported at 13.46 feet in bwc in 2021.
amsl - above mean sea level
bwc - below well casing
— - Information not available
LANGAiti
Table 3
Proposed SVE Well Construction Details
SEMCO, Santa Maria, California
LangRialige,mti 781016901
September 2025
Well ID
Maximum Total
Depth of Well
(feet bgs)
Casing Diameter
(inches)
Approximate
Bentonite Seal
Interval
(feet bgs)
Approximate
Sand Pack
Interval
(feet bgs)
Screen Slot Size
(inch)
Approximate Screened Interval
(feet bgs)
Well Screen
(Top)
Well Screen
(Bottom)
SVE-1
50 4
2 - 4
4 - 50
0.01 5
50 SVE-2
50 4
2 - 4
4 - 50
0.01 5
50 SVE-3
50 4
2 - 4
4 - 50
0.01 5
50 SVE-4
50 4
2 - 4
4 - 50
0.01 5
50 SVE-5
50 4
2 - 4
4 - 50
0.01 5
50 SVE-6
50 4
2 - 4
4 - 50
0.01 5
50 SVE-7
50 4
2 - 4
4 - 50
0.01 5
50 SVE-8
50 4
2 - 4
4 - 50
0.01 5
50 Notes:
SVE wells will be installed up to a maximum total depth of 50 feet bgs and actual depths will be recorded during installation. bgs - below ground surface
ID - identification
SVE - soil vapor extraction
LANGAN
Table 4
Preliminary Estimated VOC Emissions
SEMCO, Santa Maria, California
LangwrritaEsRmgntt 1016901
September 2025
COCs
Other VOCs detected above ESLs
Compound
TCE
cis-1,2-DCE
trans-1,2-DCE
Vinyl Chloride
PCE
1,1-DCE
Chloroform
Benzene
Maximum VOC Concentrations in Soil Gas (pg/m3)
11,000,000
4,000,000
5,600
5.7 13,000
18,000
45 38
Maximum Volumetric Air Flow (ft3/min)'
1,000
1,000
1,000
1,000
1,000
1,000
1,000
1,000
Maximum Daily VOC Emissions (Ibs/Day)2
989
360
0.50 0.0005
1.17 1.62
0.0040
0.0034
Maximum Daily VOC Emissions (Ibs/Year)2
360,932
131,248
184
0.187
427
591
1.48 1.25
Maximum Daily VOC Emissions Total2
721,900
262,500
370
0.37 850
1,180
3.0 2.5
Notes:
11,000 ft3/min was selected as the maximum flow rate for the purposes of this preliminary estimate but the SVE system operation will be refined based on initial testing results. 2 Maximum VOC emissions calculation is based the operation of eight wells at a time running for 24 hours/day for a total of two years and does not account for reductions in contaminant concentrations during operation.
Calculations herein are preliminary based on historical sampling data and may not reflect actual SVE operating conditions.
COCs - contaminants of concern
DCE - dichloroethene
ESLs - environmental screening levels
TCE - trichloroethene
PCE - tetrachloroethene
ROI - radius of influence
VOC - volatile organic compound
ft3/min - cubic feet per minute
Ibs - pounds
pg/m3 - micrograms per cubic meter
Example Calculations:
Maximum Daily Total VOC Emissions (Ibs/Day) =
11,000,000 µg 1,000 ft' 0.0283 m3 2.205e-9[bs 60 min 24 hour x x x x x = 989 lbs/day
m3 min 1 ft3 1µg 1 hour 1 day
Maximum Daily Total VOC Emissions (Ibs/Year) =
989 ibs 365 days
x = 360,932 lbs/year
day year
LANGAN
Attachment B
FIGURES
LANGAN
Attachment B
1st St
a,
ti
a,
W Carmen Ln
Via R
osa
W Betteravla Rd
Sunset Ridge
Golf Center
0 ro
3 Farrway D,
Mafi Trench Location
W Betteravia Rd
W McCoy Ln
Santa Maria
Country Club
SITE\
I J
a
-4
251 ft
Waller Park
O
In
135
Dickson Dr
r
s
\,(\se D r
5`
Valley Christian
Academy
Miles Ave
Shirley Ln
tY
c.)
'a) c
d� u
Hillview Rd
Oa�lia I
Legend
c::1 Approximate Site Boundary
Notes:
1. Site located in the Santa Marla USGS Quadrera)a.
2. Topographic baseman is provided through Langan's Earl AroGIS software licensing and A.rcG IS amine, National Geographic Sodety, leased.
3. All 'matures shown are approximata.
2,000
0 2,000
SCALE IN FEET
LANGAN
Langan CA, Inc,
104 W Anapamu Street, Suite 204B
Santa Barbara, CA93101
Project
SEYl W
SANTA MARIA
Figure Title
SITE
LOCATION MAP
Project No.
781016901
Data
6/16/2025
Scale
1" = 2,000'
Drawn By
AC
Figure
1 T: 805.957.6000 R 805.957.5001
www.langan,com
SANTA BARBARA
COUNTY CALIFORNIA
Path 'P.Ia ngan cnmidala,,,SEAldata9'.781016901lProject Data''.ArcGISlAPRX',781016901 aprx
Attachment B
Legend
▪ Monitoring Well Location • Former Water Supply Well 2AS ▪ Deep Monitoring Well Location Former Semeo Building
{ Extraction Well Location C::1 Approximate Site Boundary Notes;
t. Aerial imagery provided 6y Near Map, 07O3/2024.
2. All features shown are approximate,
3. Well location data digitized from the 2003 Everest Seances, Inc. report, 2003 Third Quarter Report For Groundwater
Monitoring Aclwrltles and the 2021 Analytical' Consulting Group, Inc. report, Monttaring Weil Investgatlon Report.
Former Semco TNlsl Drill $ Tool Company.
150 0 150
SCALE IN FEET
LANGAN
Langan CA, Inc.
104 W Anapamu Street, Suite 204B
Santa Barbera, CA93101
T: 80 5.957.6000 F: 805.957.6001
www.langan.com
Project
SEIvICO
SANTA MARIA
SANTA BARBARA
COUNTY CALIFORNIA
Figure Title
SITE PLAN
Protect No.
781016901
Date
6/17/2025
Scale
1"=150'
Drawn By
AC
Figure
2 ® 2025 Langan
Path Mangan.cowldalalSBAldata9i7S1016g011Project OataJArcGISWPRx1781016901.aprx
ttarhmPnt R
11 ji '-‘47 }
Location
MW -6
. -'
r`
Sample Name
MW -6_110589
MW -6_020190
MW -6_060690
MW -6_080494
MW -6_121598
MW -6_092203
-F
, W
VOCs
11/05/1989
02/01/1990
06106/1990
08/04/1994
1211511998
09/2212003
-
Location
t
MW -11
Cis-1,2-Dichloroethene
3,000
19 20
,-
Sample Name
MW -11_020390
MW -11_060790
MW -11_080494
MW -11_121598
Trichloroethene (TCE)
18,000
18,000
15,000
1,000
86 23
;zx
VOCs (Mg(L)
02/0311990
06/07/1990
08/04/1994
12/15/1998
T
__
,
Cis-1,2-Dichloroethene
8.9 1-3 ill
Trichloroethene (TCE)
290
54 20
38 .,
I
,
1 k
.. -
,• • • . • Golden
%' ��
-
West Packaging
2986 Industrial Pkwy
- • - -
- - - -_
2966 Industrial Pkwy Hans Duus Blacksmith
Raflr;oac!
Location) MW -3
2976 Industrial
Pkwy a{ 1 6�
Sample Name
SMW-3 111088
SMNW-3 110589
SMW-3.020190
MW -3.060790
SMW-3 121498
- W
VOCE (pg/L)
11110/1988
11105/1989
02/01/1990
06/07/1990
12/14/1998
15,000
3,000
a
������������`.�w����i���•�Cis-1,2-Dlohloraethene
Tetraohloroethene (PCE)
1,500
IT
I
Trans-1,2-Dichloroethene
220
`
Trichloraethene TCE)
5,500
42,000
57000
110,000
35,000
Il
111-291-040
111 2Jt N
1-041
111-291-042
CURRY
�}
J _ 41-4
I lF.
I
CURRY
Location
MW -2
PARKWAY, LP
.�
CURRY
PARKWAY, LP
MW -13
o
I PARKWAY, L'P
2986 INDUSTRIAL-
111 293 043 7
f
Sample Name
SMW-2_111088
SMW-2_110589
SMW2-2-90
w29G6 INDUSTRIAL
f
PKWY
2976 INDUSTRIAL
--
PKWY
Gt1RRY 'ift
PARKWAY, LP
VOCs 1L
(pg/L)
11/11/1988
11/05/1989
02103/1990
I
PKWY
MW -11
2996 INDUSTRIAL
Trans-1,2-Dichloroethene
7,700
l
PKWY -
Trichloroethene (TCE)
200
220
Location
M4Y•10
MW -6 MW -7 MW -14
t1,
Sample Name
MW -10_022090
MW -10 060890
MW -10 080494
MW -10 121498
MW -10 062921
I
Location
MW -5
V0Cs (pg/L)
02120/1990
06/08/1'990
08/0411994
12/14/1998
06/29/2021
?
y 111 X91-037'
Sample Name
MW -5_121598
GWlfiWB-092203
�I
RHINE, LP 2936
2AS
1,1,2-Trichloroethane
64 t
VOCs (Y9IL)
12/15/1998
09/2212003
Cis-1,2-Dichloroethene
43,000
15,000
Z000
INDUSTRIAL
Trichloroethene (TCE
30 Trichloraethene (TCE
130,000
270,000 270,000
530,000
83,000
PKWY
MW -3
■
'i� l
I
N
I
I
I
MW -10
MW
2 MW -5
I
a
I
.
MW -12 •�
i'
L calio
MW 8
1 I - - I; '4'
d
MW -6
Sample Nani
W-8 022O90 MW -A 060€190 MW -8_080494
MW -8_121698 MW -8_092203
MWB-grab
:ill) 4 I rr -.
MW-16-14 MW-1
. �� -
_
V0CWW1)
tp
02;20+1994 00.14811990 88/0471994
12/15/1998 I 09/22/2003
06,'26,'2021
- .. ;` - 1 6
111-291-038
I
C,s1.2Dlehlaroethene
r.3ott
2.4 9
`. 111-291-039
4 SALAS, FERNANDO MW-9�
MW -15
Trlchlomethene(ICE)
3,70 88
7.8 57
• 1 CURRir
I FIIGUEROA
- 'tl u. '
i29 T AL
a
.N
PARKWAY, LP
•
j
PKWYgirl
A [
_ p i-
V 1-n
I
I
2956 INDUSTRIAL PKWY I
I
'
ea
,
.e.
Location
Mw -190
• 1
.•
I
�l
1_ T J -t
Sample Name
N7W18U_060890
•
i or
it
i
3i
{..
..
IQ [' iVOCe
algal
06/08/7990
I
_ f
Ci -1.2
Dichloroethene
1,300
•'T.
.
I"
r
MW -4-
111-291-036
Trichloroethene(ICE)
80 I
I y
j
1 •,
i
1 •r.
,
f 1 .�.
rt
'.s
1 I
CURRY PARKWAY, LP
2946 INDUSTRIAL PKWY
I
_may- r-
ti
• .. rff, ..� gift eb .. .... r. ,mutt.. in ri alt -_ r truer p,r trr on rlrsmi mm r Ir wr..r�.rrrear r,
_
Location
..
51W-12
- -_
- t
Sample Name
M1W-12_080890 ,
MW 12 080494
MW -12_12149$
M
minent w.
r Santa Maria BBQ aLltflttf'rs
V0Cs
tpgii
06/08/1990
46/04/1994
72/74/1998
2936 Industrial Pkwy Industrial Parkway
Cis-1,2-Dichloroethene
8,500
4200
Atfr'/f .
• - 4,
Trichloraethene
fTCEj
4,800
3„200
-- -
.3,800
-
..�
�..
la - - I,m a r t. !
'
-
Location
MW -1
_. ti
, ,� r m,
Sample Name
SMW1_111088
SMW-1_110589
SHAW -1_020390
MW -1_060690
MW -1_121498
MW -1_092203.
MW -1_062921
_
S ill * -
it
V.
VOCs (mot)
11/10/1988
11/05/1989
02./03/1990
48/48/1990
12/14/1998
09/22/2003
06/29/2021
-
Cis-1,2-Dlchtamethene
-
0.6 490
47 •.
Trans-1,2-Dichloroethene
2,800
0.7 1170 0 100
TrIchloroethene (TCE)
280,000
320,000
430,000
250,000
24 300
280
8 00 to
r
''
1,4-Dioxans (P-Dioxane)
-
89 2
SCALE IN FEET —_._
1 r
— 4 _te
Nate.
Legend 1:nerxan gsrymouldedbyNearmap,arinao24
g 4.All shown are
3- samples are 'measured in feet below ground surface (feet bga).
VOCs Volatile Com ound.
LANGAN
Project
Figure Title
Project No.
781016901
Figure
Canada
4 = is
organic Compounds
'MonitoringWell Location ', SNA•Not Analyzed
B. ND U • Net detected above laboratory ,waling b»Ms
2996 Industrial Parkway, Santa Maria, Caldana, dated 16 July 2021 by Analytical Consulting Group, Inc.; ej7'- Groundwater analytical data and well located digitized ham Monitoring Well Imvestigation Raison, Pomar Samoa Twist Drill SERSICO Former Water Supply Well 2AS a Tool Comps
/� `,
SHALLOW/PERCHED
! 1 I % A 1
Date
6/17!20255
,
2003 Third Charter Report For Groundwater Monitoring kM n Advirres a12938 useral Parkway, APNs 111.291.027& 028, Langan CA, Inc.
{,j RO u NDVYATER VOCS
Scale
A
Approximate Location of Well 2AS Same Mad., California dated 24 February 2004 by Everest Semmes, Inc; Sow.•Annual Report of Groundwater Monlcong, pp ma oca SEMCO Twist Drill and Tod Company, Santa Maria California dared Deaambar 1098 by Terra Tech. Inc.; SEMCO Groundwater Remediation System Repair and Ma,ntenanoeStatus Report, 2936 fM strdal P rkway, SariM Maria, Caliromia AND 1 4 - D I OXA N E
1" = 100,
Former Semco Building Contract No. 91-1100B7, T00B7. k Order No. 3-087-1-0-300478 dated 19 August 1994 by Tetra Tech Inc.; Shallow and Deep Groundwater Irrvesligallon SEMCO Twist Drill Tad Company Faulk', Santa Maria, CaAfronl dated Arty 1990 by ERG 104 W Ana arnu `Street, Suite 2040
P Drawn
/
By
and
Environmental and Energy &memo Co.; Supplemental Subsurface Investigatr+ SEMCO Twist Doll and Tool Company L ] Approximate Site Boundary Faciity, Santa Mane, California dated Maroh t990 by ERC Envrionrnental and Energy Sere Co.; Subaru -foe Investigation:
Santa Barbara, CA 93141
SANTA MARIA
CONCENTRATIONS MAP
AC
r r Phase 2 SEMCO Twist Drill and Tod Conpnay Tank. Santa Maria, California dated December 1989 by ERC
Emmonmental and Energy Services Co.; and, St bsurfaoe Mrrestigatrm SEMCO Twist Drill and Tool Company, Santa Maria, Parcel California datedJanuar/1989byWESTEcservices. SANTA T: 805.957.6000 F: 805.957-6001 www.langan.com
BARBARA COUNTY CALIFORNIA
Path: Wangan.earnldalalSBAldata917810169011PrMeot DatalArceIS)APRx1781016901.aprx
Attarhmant R
Legend
o Soil Sample
• Former Water Supply Well 2AS
Approximate Location of Well 2AS
IJFormer Sernco Building
l.. Approximate Site Boundary
A!.
Notes:
1 Aerial imagery provided by Nearmap, 07/03/2024.
2. All features shown are approximate.
3. Soli sampling location data digitized from the Site Assessment Report. Vadose Zone Soil Sampling, Former SEMCO Twist Drill & Tool Company, 2936 Industrial Parkway. Santa Marls.
California dated 25 May 2022 by Analytical Consulting Group, Inc.; Results of Solt Sampling Beneath the Concrete Pond Structure Located at the SEMCO Faciity, Santa Maria. California dated 3 December 1991 lay ERC Environmental and Energy Services Co. Inc.; Supplementary Subsurface Investigation, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California dated March 1990 by ERC Environmental and Energy Services Co.; and, Subsurface Investigaton Letter Report, SEMCO Twist Drill and Tool Company, Santa Marla, California dated 1 April 1988 by WESTEC Services, Inc.
100 o 100
SP -1 SP -2
P-3
B7-4-)
Railroad
8227
NB42
NB32
.1O
88 iJ B4 B33 1J er
—B224
Industrial
LANGAN
Langan CA, Inc.
104 W Anaparnu Street, Suite 2040
Santa Barbara, CA 93101
Parkway
Project
SEM co
SANTA MARIA
Figure Title
SOIL SAMPLING
LOCATIONS MAP
Project No.
781016901
Date
6/17/2025
Scale
1" = 100'
Drawn By
AC
Figure
4 SCALE IN FEET
T: 805.957.6000 F: 805.957.6001 www.langan.com
SANTA BARBARA COUNTY CALIFORNIA
Path: Mangan.carnldatalSBAldata917810169011Prolect DataLArceISLAPPJ0781016901.aprx
•
Former Water Supply Well 2AS
Previous Soil Vapor Sampling
Locations
3,000 pgfm3 TCE
30,000 pglm3 TCE
300,000 pg/m' TCE
3,000,000 pgfm3 TCE
Former Semco Building
L 1:1 Approximate Site Boundary
Parcel
Notes:
1. Aerial Imagery provided by Nearmap. 07/012024.
2. All features shown are approximate.
3. Samples are measured in feet below ground
surface (feet bgs),
4. VOCs = Volatile Organic Compounds
5. Sail vapor (SV) and sub -slab (SS) sampling well
location and concentration data digitized from the Sot
Vapor Sampling (deport, Farmer SEMCD Twist Drill & Tool Company, 2936 Industrial Parkway, Santa Maria, California.
Site I.D. No. St.T3S2411351 dated 16 July 2021 by Analytical Consulting Group, Inc.
60 0 60
SCALE IN FEET
L14IVt514IV
Langan CA, Inc.
104 W Anapamu Street, Suite 2040
Santa Barbara, CA 93101
T: 805.957.6000 F: 805.957.6001 www.langan.com
Project
WA CO
SANTA MARIA
SANTA BARBARA COUNTY CALIFORNIA
Figure Title
SOIL VAPOR TCE
CONCENTRATIONS
CONTOUR MAP
Project No.
781016901
Date
7/30/2025
Scale
1"=60'
Drawn By
AC
Figure
5 Path: Mangan.carn'idatal8BAldata417blolea01tProlect DatalAncelalAPRk17a1016901.aprx
Attachment R
Project
Figure Title
Project No.
781016901
Figure
Legend
i Previous Soil Vapor Sampling
Locations
Previous Extraction Well Location
Proposed Extraction Well Location
Approximate SVE System Piping
Configuration
r
Former Samoa Building
Approximate location of SVE
Treatment System Enclosure
-- Approximate Extraction Well
--• Radius of Capture (28 feet)
Parcel
• SV32
5V2,1 SV19
SV29 110
1 L{ 1 " . EX -2 lig
I
• SS4
-0-SVE-4
Notes:
1. Aerial imagery provided by Nearmap, 0710312024.
2. NI features shown are approximate.
3. SVE = Soil Vapor Extraction
4. Soil vapor (SV) and sub -slab (SS) sampling well lacatlon data digitized from the Soil Vapor Sampling Report, Former SEMCO Twist Drill & Tool Company, 2936 Industrial
Parkway, Santa Maria, California, Site I.D. No. 5L7352411351 dated 16 July 2[121 by Analytical Consulting Group, Inc. 40 0 40
SCALE IN FEET
SVE-2
SV16
i
1'
I
1 rf EX -3
C
SV150—
,SV-1i- -_
SVE-7
LANGAN
Langan CA, Inc.
104 W Anapamu Street, Suite 204B
Santa Barbara. CA 93101
T: 805.957.6000 F: 805.957.6001 www.langan.com
MA CO
SANTA MARIA
SANTA BARBARA COUNTY CALIFORNIA
SVE SCHEMATIC
LAYOUT
Date
7/30/2025
Scale
1" = 40'
Drawn By
AC
6 SV36
© 2025 Langan
Path: Ulangan.comydatalSBAldala.91781016991 Project DalamArcGISIAPRx1781016901.apra
Attachment B
Interval
1-2 feet
1 foot
Up to
45 feet
Depth
Ground surface
Cover
Up to
2 feet bgs 8 -inch borehole
Up to
4 feet bgs
Up to
5 feet bgs
Up to
50 feet bgs
Bottom of boring _
4 inch Sch 40 PVC well casing
Concrete (for well box)
Cement-bentonite grout (less than
2% bentonite)
1-2 feet Bentonite chip or pellets
seal, hydrated
1 foot
//2/12 filter sand pack
4 inch diameter well screen: Sch 40
PVC flush threaded, 0.010 -inch slots
Bottom of screen up to 50 feet bgs
SVE WELL CONSTRUCTION DIAGRAM (typicafl
NOT TO SCALE
As Needed
o U_ C75
a CD
TD
O O
0 I-
4 -Inch Diameter
Rubber
Well Seal
4 -Inch Diameter Sch. 40
PVC or HDPE
Wellhead Fittinb; Typical
l
As Needed
Access for Tubing and Associated Power
Cords For Submersible Pump; Outlet/Tubing
Diameter 1-1/4"
Access for water level meter
Adjustable Vacuum
Relief Valve (0-20" Hg)
Vacuum Gage (0-20" Hg)
Sample Port
1/4" Inner Diameter
Flow Measurement
Port - Min. 1/2" Diameter
Gate Valve To Fit
Diameter Of Vapor
Extraction Pipe
Vapor Flow
Sch. 40 PVC Or HDPE To Match
Diameter Of Vapor Extraction Hose
As Needed
Vapor Tight Reducer
Typical 4 -inch Sch. 40 PVC
Extraction Well;
Above -Ground Completion
As Needed
To Submersible Pump
SVE WELLHEAD DIAGRAM (typicaO
NOT TO SCALE
WORKPLAN FOR
ONSITE SOIL VAPOR
EXTRACTION
LANGAN
135 MAIN STREET, SUITE 1500, SAN FRANCISCO, CA 94105
T:415 955 5200 F:415 955 5201 www.langan.com
NEW JERSEY NEW YORK CONNECTICUT PENNSYLVANIA WASHINGTON, DC VIRGINIA
WEST VIRGINIA OHIO FLORIDA TEXAS ARIZONA CALIFORNIA
ABU DHABI ATHENS DOHA DUBAI LONDON PANAMA
1.14:021ellin=a9Prialalif 1126 ifs"W=Ift6 NSA"
ta r.. in
Issuances
Description
Date
WORKPLAN FOR
ONSITE SOIL VAPOR
EXTRACTION
Description
7/30/2025
Revisions
Date
Set Title
SOIL VAPOR
EXTRACTION SYSTEM
Drawing Title
SOIL VAPOR
EXTRACTION WELL
CONSTRUCTION AND
WELLHEAD DIAGRAM
Figure No.
Figure 7
Date
Project No.
7/30/2025
781016901
Attachment B
APPENDIX A
AVAILABLE WELL COMPLETION LOGS AND BORING LOGS
LANGAN
SANTA MARIA-LOMPOC AIR BASE
DRILLING 9F WATER WELLS
4. From To
18 ' Yellow Sand
18 LOG
Well 'No. 2,q -$
39 ..Brown Sand 21
48 .•Hard Brown Clay 9
59 i . Clay 'and ;Gravel i 11
79 . 'Yellow ' Clay 20
84 ' . Clay Gravel and Boulder 15
107 Sand Gravel Sandy Clay . 23
145 Sand, Clay, Small Gravel 38
180 Sand, Clay, and Boulders
• 35
Depth
of Strata;
247 ' .Good Gravel <-„'_,/. i,"
Sample No. 9.10-11 taken
between 147 and 182
251 ''Solid Clay and Gravel
Tote], depth of drilling - 2S1 feet
' " " " casing .. 250 "
1Depth after cementing - 247 "
Perforated from 138' up to 182• = 56 feet
t7' holes every 14" 308 holes.
All perforations are k"x3"
Water static) before pumping May 29, 1942 - 125 feet
Drilling and perforating completed May 29, 1942.
Well tested as follows:' All heads below based on measurements from top of casing, (pymP base)
Sample No.
1. 2
3 4
5 7
9 10) Perforated'`
11)
12 ,;
1000 G.P.M. - 135 feet.
?50 " - 133 "
500 " - 131 "
'250 " - 128 "
Attachment B
WESTEC Services, Inc. WELL COMPLETION RECORD
JOB NO. 2805 (.0 00 I WELL NO. �fr1w I HYDROGEOLOGIST SC W /CED/ EA A.
CLIENT _5 Yy)C O DRILLER ✓4 .SE(L VICE•
WELL LOCATION DATE/TIME l 1 1O ✓ 88 c^ 7 4 5
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed 1110/38 9:51
Borehole Diameter (in.) 8/1
Type and Size of Casing (in.) PVC 2i/ 6ct-l40
Type and Size of Screen (in.) WG 24
.5C.1-1 40
Screen Perforation Diameter (in.) . G2O in./.
Screen Length (ft.) ) 4 . 791
Centralizer Depths (ft.) ,
Completion Technique:
1) Type of Filter Pack and Placement
Method
i,uTE2EY 3.541uD/-TEtanriliE
2) Type of Bentonite and Placement ethod
A-61�EfJTD,J lTE CH
3) Type of Grout Mixture and Placement
Method
Description of Potential Problems With Well:
C ou Ll) ftJ T ✓� 2ou T
L5oZFacc C43/ki�
Development Technique
//A ,Li D Vu rn P
GROUT
BENTONITE
FILTER PACK
= To IN
To F
4 Well Head Elevation
Ground Surface Elev.
Well Head Completion Method
7R4 FF" c 7e
Drilling Method/Rig Type
Surface Casing: Type PVC.
Diameter f O
Length 8
o
MATERIALS
Cement (sks.)
Filter Pack Material (ft3)
Casing Material (ft.)
8 Bentonite (ft3
. )
Top of Bentonite Seal • 2 5 ft.
boy
gQH = Top of Filter Pack .3.25 ft.
Top of Screen 5, z 1 ft.
Bottom of Screen 2O ft.
Bottom of Hole 20 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
Attachment B
WWESTEC Services, Inc. WELL COMPLETION RECORD
WELL NO..711W oG HYDROGEOLOGIST SCI / 26.1) / EA A
DRILLER VdLLEY . lA ELLL. 6EJLV/CL_._
JOB NO. 38OS CO
CLIENT 5E/YIC0
WELL LOCATION DATE/TIME 1 Vi u/ 8 5 I D: U 9
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed 1 I/ O /3 b
Borehole Diameter (in.) 8
Type and Size of Casing (in.) RI/C.. 2"
604 40
Type and Size of Screen (in.) PV'C. 2 " SC -I40
Screen Perforation Diameter (in.) . 02
Screen Length (ft.) 20
Centralizer Depths (ft.) ,
Completion Technique:
1) Type of Filter Pack and Placement
Method
t�lo%ITCMX 3 � pry 721=m m /E
12) Type of Bentonite and Placement Method
l�uo\ CJ0,3,Tau ITE. //-HA D
3) Type of Grout Mixture and Placement
Method
Description of Potential Problems With WeII:
6L2l?FACE CAS/ILK, /llor
G iCoc,r r -2)v E "Ft)
No I € Cb Il AP.s
Development Technique
//,atiiQ 2 v -n2
Z 7.1b6
To
4 To5
—/2
la
— 1
— 2z
= z4
I 5
2(4, earl
WeII Head Elevation
Ground Surface Elev.
WeII Head Completion Method
Drilling Method/Rig Type
GEo RFX
Surface Casing: Type PVC
Diameter /0
Length 8'
MATERIALS
Cement (sks.)
Filter Pack Material (ft3)
Casing Material (ft.)
Bentonite (ft3)
Top of Bentonite Seal a. O ft.
Top of Filter Pack 3 .2 ft.
Top of Screen .52
ft.
Bottom of Screen JJ. a ft.
Bottom of Hole ,- (,, ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
Attachment B
NWESrEC Services, Inc.
WELL COMPLETION RECORD
JOB NO -3 80 Sla Co I WELL NO..5/Thit)3 HYDROGEOLOGIST a-C1i/CED/ A CLIENT JEil'1C.0 DRILLER VLLLEY jJ 7J- , E1LV 10E
WELL LOCATION DATE/TIME 1)/I 0/ 88 14 : I /.
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed //l/ 0/83
Borehole Diameter (in.) j
Type and Size of Casing (in.) R/c 2 6 .H 4O
Type and Size of Screen (in.) R'C .2" sc H QD
Screen Perforation Diameter (in.)
Screen Length (ft.) JS df
Centralizer Depths (ft.)
Completion Technique:
1) Type of Filter Pack and Placement
Method
Mokirdc.eX ‘3/72CC2-4172/E
2) Type of Bentonite and Placement Method
��. ozrou //-/Q &t o
3) Type of Grout Mixture and Placement
Method
Description of Potential Problems With WeII:
Development Technique
k
=4
WeII Head Elevation
Ground Surface Elev.
Well Head Completion Method
7'7AFF/C dc/
Drilling Method/Rig Type
ro
Surface Casing: Type PVC.
Diameter / O
Length 8'
T,F
= 8
7c's
—Jo
MATERIALS
Cement (sks.)
= t Filter Pack Material (ft3) 4
14 — 20
Casing Material (ft.) 2 Q.5
Bentonite (ft3) /
Top of Bentonite Seal 3 ft.
Top of Filter Pack 5 ft.
Top of Screen 9,S 5 ft.
Bottom of Screen a 4.s ft.
Bottom of Hole X29. 5 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
NWESTEC Services, Inc.
FIELD LOG OF BORING
BORING NUMBER X31 0 m w 3)
LAnggianNote:
Sheet 2 missing
in 1989 Westec
Report
SHEET OF Z —
PROJECT NAME
.5 iC o
PROJECT NUMBER
3$o5(o OO/
ELEVATION AND DATUM
LOCATION
DRILUNG COMPANY
VALLEY G)Ec_c_ SgICVICz.
DRLLER
DATE�D TIME STARTED
// 4/64s 1A:18
DATEAP9 TIME COMPLETED
1l10%36
DRILLING EQUIPMENT
C'F7)
DRILLING METHOD
/-kb flow TCwl
COMPLETION DEPTH
TOTAL NO. OF SAMPLES
WE AND TYPE OF BIT
8 A U �7�
HOLE DIANE/TER
8 SAMPLES
NO OF
BULK
SS
DRIVE
PITCHER
DRILLNG F/L�D
/- O ice)
DRLLPIG
WATER
LEVEL
FIRST
AFTER HOURS
SAMPLE HAMMER ,
TYPE DRIVING WT. 140 lb DROP 30j
HYDROGEOLOGIST/ DATE
ZaiL/a
CHECKED BY/ DATE
d
DEPTH
E
3 DESCRIPTION
N m
ESTIMATED
PERCENT OF
COMMENTS
1 J:7:03
'
GR
SA
Fl
AO
FinJE - ,n c S,w D . 7 -Am -LT.
.S1J
95 5
/a.'a 5 6 Jo - /
5 P t)W/jJ, DkY, mop- 17r�.t;}
/-7411) .3pprn
Z
X
.3O
PpoI -/ metJoR .SILT
/2
14 DETA
ERC
Environment3.
and Energy
Services Co.
JOBNO. 39 3c{ jcC°(
CLIENT 5CIWO
WELL LOCATION 5 E1'y`JC'.0
WELL COMPLETION RECORD
WELL NO. hi `f
GROUND SURFACE
LS OF .CONSTRUCTION
Date Completed /I - I `/
Borehole Diameter (in.) /0 -1ti
Type and Size of Casing (in.) 4i -t;4 Rl C
Type and Size of Screen (in.) et-ii4
Screen Perforation Diameter (in.) CJ, C')._O
Screen Length (ft.) 1 9. `3
Centralizer Depths (ft.)
Completion Technique:
1) Type of Filter Pack and Placement
Method %
2) Type of Bentonite and Placement Method
3) Type of Grout Mixture and Placement
Method 11
iti^711<sx t Lcls'elpA0. 1zuilc 12u d4
Description of Potential Problems ith Weil:
Development Technique
Attachment B
HYDROGEOLOGIST ,41 /Crt / D: of c 4
DRILLER VCt/fey �I.)e I b, -c (!rrt,
DATE/TIME Jl — tr � `i C� /06'0
Well Head Elevation 23 6, 1
Ground Surface Elev. 23t,. =1 Z
Well �t-Head��CC�ompletion Method
`Trot t `c be
Drillin g Method/Rig Type
/-em / 4 ee) Rex
Surface Casing: Type 4!/9
Diameter '"
Length
MATERIALS
Cement (sks.) Z Sk s
Filter Pack Material (ft?) /2...5k
Casing Material (ft.) 3O C)
Bentonite (ft.3) .. 5A 5
Top of Bentonite Seal 5. 3 ft.
Top of Filter Pack 7. S ft.
Top of Screen CI5 ft.
Bottom of Screen 2. ct , ( ft.
Bottom of Hole '�(t,v ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
ERC
Environrner .
and Energy
Services Co.
JOB NO. 3`i 3 -(f . OO t
CLIENT E Y11C0
WELL LOCATION 5 E hl CO
GROUND SURFACE
DETAILS O.= CQNSTRL..0
lON
Date Completed l/
Borehole Diameter (in.) _le, -1(t
Type and Size of Casing (in.) H _r n 'PO C
Type and Size of Screen (in.) 'I-r� 'U[_
Screen Perforation Diameter (in.) O. 0 Z..&
Screen Length (ft.) '.2_ 0 .
Centralizer Depths (ft.) VA, -- ,
Completion Technique:
1) Type of Filter Pack and Placement
Method
3L.571 C3kt S<.,,[f
Attachment B
WELL COMPLETION RECORD
WELL NO. rn Lk) S HYDROGEOLOGIST /� ! I Ci't / b i ric- its
DRILLER J
1alic i LL)Ct(rrl�4-t lik:1,1
DATE/TIME II I - e `7 (2.s / 3 ( 0
�c w c:; I {,
Tr -em rx ► e
2) Type of Bentonite and Placement Method
L'-5 rcott.i. l (114 / I rermot'-e
3) Type of Grout Mixture and Placement
Method
/7-fr /Lei 7-r c. y1� 20 b cu'int.:4-e/itiutj
Description of Potential Problems With Well:
Loci(
Development Technique
Well Head Elevation 2-'37, H v
Ground Surface Elev. 2 C '7
Well Head Completion Method
T1�a E6c 3c.
Drilling ethod/Rig Type
HC 1 L' S i't' m. /c:c 7t?X
Surface Casing: Type /V#
Diameter
Length
MATERIALS
Cement (sks.) .Z 54_5
Filter Pack Material (ft?) ) 'z 5/T.__.5
Casing Material (ft.) Z'2.5 t't
Bentonite (ft3) /..5 54
Top of Bentonite Seal I. 5 ft,
Top of Filter Pack E,. 5 ft.
Top of Screen ft.
Bottom of Screen Z8 : '? ft,
Bottom of Hole 241. 5 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
DE
A
ERC
Environmenta.
and Energy
Services Co.
JOB NO.
CLIENT
WELL COMPLETION RECORD
5'1'3 LI I roc ( WELL NO. ! W
WELL LOCATION 5 E Ill CO
GROUND SURFACE
LS OF CONSTRUCTON
Date Completed I!' 7 -
Borehole Diameter (in.) 1 Q
Type and Size of Casing (in.) II -IA pv
Type and Size of Screen (in.) q -1 h PJ c.
Screen Perforation Diameter (in.) 0,01.-0
Screen Length (ft.) / ,
Centralizer Depths (ft.) /VA
Completion Technique:
1) Type of Filter Pack and Placement
Method
5 Leo rSl L kr
7-2,er77rhrr
2) Type of Bentonite and Placement Method
L?5��rz:reicc(ct (A&)/Tr-cmw�
3) Type of Grout Mixture and Placement
Method '
I3-y--IItdzc'T tA.,J/-5'% eo.:truj-c/ilart41'
Description of Potential Problems With WeII:
L60. I(j`ell. I
Development }Technique
zt t - 1 r. •�,
GROUT
BENTONITE
FILTER PACK
HYDROGEO� rLOGIIST
DRILLER (ja. J e9
DATETTIME )/ - . -
Attachment B
41( rt �bICYCk,
WC.
07/5
Well Head Elevation 2 3 7, 30
Ground Surface Elev. 2:3 7, '1f
WeII Head Completion Method
77--A41 gc,e5S
Drilling Method/Rig Type
, �1 • �i-rat ec Rex
Surface Casing: Type NA
Diameter
Length
MATERIALS
Cement (sks.) Z S X-5
Filter Pack Material (ft3) .
Casing Material (ft) 2C 5
Bentonite (ft3 ) /4, 5 > k 5
Top of Bentonite Seal Z. ft.
Top of Filter Pack `i • ft.
Top of Screen . I ft.
Bottom of Screen f `3. '1 ft.
Bottom of Hole ..ZO. 5 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
DETAI
ERC
Environmental
and Energy
Services Co.
JOB NO, 39`.34f/ • Go i
CLIENT 5 E C
Attachment B
WELL COMPLETION RECORD
HYDROGEOLOGIST Ad-4k.
�r�rG2S
(la 17 i:•W4/ htI��Yty�
WELL NO, MU) 7
WELL LOCATION S 1✓ ill CO •CCx-G+
GROUND SURFACE
S OF CONSTRUCTION
DRILLER
DATE/TIME Il`5-`d`t 1/3C•
Date Completed II - 3 -- `t
Borehole Diameter (in.) 16.1t:t
Type and Size of Casing (in.) .`f -1v1 PPtr'L
Type and Size of Screen (in.) 4- f r% PVC
Screen Perforation Diameter (in.) • 02 O
Screen Length (ft.) _:9
Centralizer Depths (ft) NAT, , —
Completion Technique:
1) Type of Filter Pack and Placement
Method
40) c.5 ictir 5414j
Tr -c. mptt
2) Type of Bentonite and Placement Method
CS G vt.1n rl lte.t lJ4 /7-TriArki f•
3) Type of Grout Mixture and Placement
Method
7q1 '/s4?L �,� ' I/G► <ss+� 4
Description of Potential Problems With Well:
•
4•,
Development Technique
GROUT
BENTONITE
FILTER PACK
Well Head Elevation Z 3 7.5 (o
Ground Surface Elev. 2 3 1
Well Head Completion Method
PL -1.
Drilling Method/Rig Type/ / c I 414* .`7 t' C��� � ec, lZCx Surface Casing: Type N4
Diameter
Length
MATERIALS
Cement (sks.) 'Z S k S
Filter Pack Materiai (ft 3) 115k s
Casing Material (ft.) 'Z 19 •k f
Bentonite (ft3 ) .514..s
Top of Bentonite Seal. 1,--C ft.
Top of Filter Pack 9 U ft.
Top of Screen S H ft.
Bottom of Screen ;LM ( ft.
Bottom of Hole ? . t.)) ft,
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
Atoi ERC
Environmental
and Energy
Services Co.
JOB NO. 393 _1 :(,>o
CLIENT 5E atC C�
WELL COMPLETION RECORD
WELL NO. FYI U.123
WELL LOCATION SC1)1CO f czcr 11YTf
GROUND SURFACE
DETAILS OF CONSTRLCTIOry
Date Completed
Borehole Diameter (in.) (
Type and Size of Casing (in.) q-f&k PVC
Type and Size of Screen (in.) `{-fnc k -NC
Screen Perforation Diameter (in.) c' 0 '-O
Screen Length (ft.) 2-O . I
Centralizer Depths (ft) Nf3 , ,` ,
Completion Technique:
1) Type of Filter Pack and Placement
Method
3 e54-4„+- / Ti-etri nt t -(
2) Type of Bentonite (/and Placement Method
L`S 6v'ciKcLleit.01,Ac.)/ % rer►tnf E +
3) Type of Grout Mixture and Placement
Method
Rfit-'4444,-.1 Try.e7r I.4,7 59 ke/
Description of Potential Problems With Well:
r• i 2-e 6
11 Development Technique
Attachment B
HYDROGEOLOGIST / (e n t b i C rc k
r I
DRILLER Ucc_ l CO rt i lire
DATEJTIME II " 3 V G.I / `1 S
•
Well Head Elevation Z 3 G -0
Ground Surface Elev. 2'3(. (a ?
Well Head Completion Method
(41'(2
Drilling Method/Rig Type
Surface Casing: Type Nei)
Diameter
Length —
MATERIALS
Cement (sks.) 2 . k 5
Filter Pack Material (ft 3) 11'5 >�
Casing Material (ft.) 25. 5
Bentonite (ft3) 2 5 k
Top of Bentonite Seal- 2 . it,
Top of Filter Pack `- • S ft.
Top of Screen Li • 7 ft.
Bottom of Screen 2- `'j. S ft.
Bottom of Hole ,L 5,S' ft,
NOTE,: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
ERC
" Environment,
and Energy
Services Co.
JOB NO.
CLIENT
E;A\co
Attachment B
WELL COMPLETION RECORD
WELL NO. q HYDROGEOLOGIST iJ 1 I eh / 1b ir'rc k
DRILLER 1{C2 t' l ( \D A 1
DATE/TIME // -S-89 C 1 i, .3 c
WELL LOCATION .5 E YIN
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed // - 3 — e `)
Borehole Diameter (in,) 1 O
Type and Size of Casing (in.) q ?1../L
Type and Size of Screen (in.) 4-(v&G1n PvC
Screen Perforation Diameter (in.) 0,01_ D
Screen Length (ft.) 2 4 ,
Centralizer Depths (ft.) NA , '
Completion Technique:
1) Type of Filter Pack and Placement
Method
# e5-11ec r 7-r evilotr -e
2) Type of Bentonite and Placement Method
5,±1 it 44 LA /1/eL 7I`Cisl�v� {
3) Type of Grout Mixture and Placement
Method (tir,uci1
w/5 '2c bey c` : Le
Description of Potential Problems With Well:
Development Technique
d(17,1
�¢ll
r --
Well Head Elevation 2 3 G:. 32,
Ground Surface Elev. z 3 (,, 7 `t
Well Head Completion Method
7 r72 b�;x
Drilling Method/Rig Type
iolLco ke,K
Surface Casing: Type Ali
Diameter
Length
MATERIALS
Cement (sks.) 5 % 5
Filter Pack Material (ft3) 1/ 5/r s
Casing Material (ft.) ;ZS_ c >t}
Bentonite (ft: ) 2. k
Top of Bentonite Seal /..7 ft.
Top of Filter Pack `).. CI ft.
Top of Screen 'iii 7 ft,
Bottom of Screen 2 `1 ft.
Bottom of Hole Z S. y_ ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
ERC
Environmental
and Energy
Services Co.
WELL COMPLETION RECORD
JOB NO. S 005 7.00' � WELL NO. ) u) iO
CLIENT ,3 6-01 LLB ((
WELL LOCATION ��tw Lt. rV I1 Ct Y -t ,
•
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed _2') 0
Borehole Diameter (in.) l (f.) -I Vt
Type and Size of Casing (in.) 'l1t PV
Type and Size of Screen (in.) y - Out ?1/4/ C..
Screen Perforation Diameter (in.) O
Screen Length (ft.) Li5 --V t
-Centralizer Depths (ft.) N!
Completion Technique:
1) Type of Filter Pack and Placement
Method
/,'z. Leta C s 4-a / Tr{ rn -c
2) Type of Bentonite and Placement Method
I/y -ill vvpht, Lic-1-sl 'ren4n4t-€
3) Type of Grout Mixture and Placement
Method
Voicla46-fvrk wi 5 1.16 por4letu,V1-
Description of Potential Problems With Well:
Development Technique
.12
Attachment B
HYDROGEOLOGIST _� J �►� V' . k 5
DRILLERAc¢. [ l eJ 1,0 C,..(
DATE/TIME - 4 3 C
Well Head Elevation
Ground Surface Elev.
Well Head Completion Method
Drilling Method/Rig Type
L ect-c�c / 1`/ 4 ,
Surface Casing: Type /VI4
Diameter .
Length —
MATERIALS L
Cement (sks.) 3� 5 .ecvLC v - e.
Filter Pack Material (ft )
Casing Material (ft.) 5 G -f f
Bentonite (ft3) Ji 5%5
Top of Bentonite Seaf 2-7. 5 ft.
Top of Filter Pack 3 i. O ft.
Top of Screen 5 3. C. ft.
Bottom of Screen 3-7- S ft.
Bottom of Hole .S` . C ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
ERC
Environmental
and Energy
Services Co.
WELL COMPLETION RECORD
Attachment B
JOB NO. Sls"C 5 7.-cC"(_ WELL NO. TU r 1 1 HYDROGEOLOGIST C V I Pvz:iC5 1f
CLIENT 5 r fr l C d DRILLER U LL 1 -Qj W JL i
WELL LOCATION .7ci 1211rla DATE/TIME 2- 2 -q0 e D 0'5
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed '2.' 2-' D
Borehole Diameter (in.) (,E /✓1 ,f
Type and Size of Casing (in.) �{-j v► f�. L
Type and Size of Screen (in.) v\ Pv .
Screen Perforation Diameter (in.)
Screen Length (ft.)
Centralizer Depths (ft.) /vt><, '- , —
Completion Technique:
1) Type of Filter Pack and Placement
Method -
l
#t2 /ice KNLe3 / fre.vt/N,L-P
2) Type off Bentonite and Placement Method
/Ii°cL 7A'1"rLv^lG 01,4;f1-4
3) Type of Grout Mixture and Placement
Me hod
qq
Description of Potential Problems With We I:
Development Technique
•
f'
\.
Well Head Elevation
Ground Surface Elev.
Well Head Completion Method
Drillin Method/Rig Type
Surface Casing: Type /V -"/Q
Diameter —
Length
MATERIALS
Cement (sks.) 3`i/t5 eci4ec,-SL-
Filter Pack Material (ft3)
Casing Material (ft.) :2 '
Bentonite (ft3 ) 2 ..5 iv, ,7
Top of Bentonite Seat 7-- l.^ ft.
Top of Filter Pack 7. 2.. ft.
Top of Screen Ct '% ft.
Bottom of Screen _i ` ft.
Bottom of Hole 2©_ C ft.
NOTE: ALL DEPTHS AREREFERENCED TO GROUND SURFACE
ERC
Environmental
and Energy
Services Co.
3RING NUMBER AVI3 2. 2 -
FIELD LOG OF BORING
Attachment B
SHEET f OF
IOJECT NAME
scm co
PROJECT NUMBER
3 ei, s7.
ELEVATION AND DATUM
LOCATION
2-934, z 4 /I) elaJ.
uralLl N ,COMPANY
V" 1 i "e! We // 7);4/ ii,e
DRILLER /
Rowe;
DATE AND TIME STARTED
11 Lc v" '2-I - Ot o
DATE AND TIME_COMPLETED
2-I -`J O & / 2
3ILLING Efl IPMENT I
� IZe_T-s o c
DRILLING METHOD
/4L o 51 -ems
COMPLETION D€PTH
'2 -0 -%/Z -f-
TOTAL NO. OF SAMPLES
SIZE AND TYPE OF BIT
8 -IN 4..0 &.
HOLE DIAMETER
t✓-(ik
NO. OF
SAMPLES
BULK
2,
SS
Z
DRIVE
PITCHER
TILLING FLUID
n Un t
ANGLE,'
DRILLING ANGLE,'
WATER
LEVEL
FIRST
AFTEA HOURS
i
"1' 2_
I SAMPLE HAMMER
fPE htin
/ //
tC-d ` 6.l DRNINGWT. Ilia DROP 30--Jk
HYDROGEOL OGST/ DATE
CLM> / z-1 -q o
CHECKED BY/ DATE ,
-( ` '''
DEPTH
W
w
DESCRIPTION
N p
ESTIMATED
PERCENT OF
COMMENTS
zO
(FEET)
D
tan
$
¢
O3
CO o
8 i
m
GR
SA
Fl
Z
•
3 B ► 1 5 I l`c la Li c.`. 4 4 ? lA:tz �'�
t�
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10 q
-
.
tU� L W a''v-li 1 K �. I S UvitZ t.." 4
b
I
�
$v" -e a4__ a, - on.
SP
q
t 0
l0
/I
•
12. 13
'Y
' • ERC
• Environmental
and Energy
Services Co.
FIELD LOG OF BORING (CONTINUED)
BORING NUMBER ^,i�p 7.7
Attachment B
SHEET _a_OF
Y
z
SAMPLES I
}cc
$
cc
BLOW
COUNT
DESCRIPTION
USCS
SYMBOL
ESTIMATED
PERCENT OF
COMMENTS
GR
SA
Fl
ffiS
Is
®
14, 3Z
,keet-o,6'-itlr�.ic joucsL r%� fLixr(r�•
LIb
of ..
I7
Ib
ty
z)
1 e3
a, --ex .. 6t,L ,u si l-1- 14,i
$4L
/
,�y
)1 4 e:
L I
JJj�
w, a i. hl I it!" e- .4/-414 6i 1 u ei f:5c%4^G
.z.2
t'Vii`!-,,T
. � c j.7scL, /'
23 ERC
Environmental
and Energy
Services Co.
JOB NO 3c -`,0S CO i
WELL COMPLETION RECORD
WELL NO. h/t1.:) HYDROGEOLOGIST
CLIENT Efl C DRILLER •Va., i1
WELL LOCATION 5ggn L Ina e-i`
z DATE/TIME 2 -2/
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed Z' z 1 —
Borehole Diameter (in.) L G -1N.r L..
Type and Size of Casing (in.) `i - i A C_
Type and Size of Screen (in.) 1 -i h Ptl C
Screen Perforation Diameter (in.) (0: C. I C
Screen Length (ft.) 15; 5
Centralizer Depths (ft.)71(# , _ , —
Completion Technique:
1) Type of Filter Pack and Placement
Method
L 1- eCe 5 i-et t; Tr -2
2) Type of Bentonite and Placement Method
t4t-+4 �l1 tr lu., C14113 J Tr C.
3) Type of Grout Mixture and Placement
Method
e (ALI t /5o
Description of)6otential Problems With Well:
Development Technique
GROUT
BE,NTONITE
FILTER PACK
Attachment B
� a si==. i f' 4 c• it. 5_
weir! 1 .1c`{l
-C C
Well Head Elevation
Ground Surface Elev.
Well Head Completion Method
Drilling. Method/Rig Type
ite r
Ad)
Surface Casing: Type Ad)
Diameter
Length
MATERIALS
Cement (sks.) 2. 5 k c c-ncve
Filter Pack Material (ft3) 6.i sfc .
Casing Material (ft.) 'Z 5. S '
Bentonite (ft3_) .3 fC 5
Top of Bentonite Seat 3.: C. ft.
Top of Filter Pack .7, L) ft.
Top of Screen qs I ft.
Bottom of Screen 2 4,. (G ft.
Bottom of Hole ';1.. S. 5 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
ERC
i Environmental
and Energy
Services Co.
MW -12)
)RING NUMBER !v /I,�B z 7 J
FIELD LOG OF BORING
Attachment B
SHEET I OF__
IOJECT NAME
ScMCO
PROJECT NUMBER
3crz 7,CieD s
ELEVATION AND DATUM
LOCATION
z.936 r>lCS €Iu
f
I DH %O MPA�NY1 Well
V lt°4 l.Ve�[ r��l�ty
DRILLER /
806,61
DATE AND TIME STARTED
2-2 I -toe Ic. 1
DATE AND TIME.COMPLETED
2- 1-5-4)02- /l3 I z- 2 / - dL 6
CHECKED BY/ DATE
_',1 , I : r.
Ig
o
PT
DEPTH
SAMPLES
RECOVERY
BLOW
COUNT
/
USCS
SYMBOL I
ESTIMATED
PERCENT OF
COMMENTS
O
� FEET)
DESCRIPTION
GR
SA
Fl
r6
-IA c AA, ere.. •
I1
1 ,14,1- 76 V b1. 3 `YW..C:' 6Az,kiztLi1—
,,>
Vie,
ICs
Z
9 Iw�cP 5.4-64..cit , well -5(/r..I— c
J
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//,
3 I
y
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5 7
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415 Z 7 -
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6 NJ
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I
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cg
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ii
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io
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/
i5
i 4
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I
1 ----_
Z
I
13 4-
•
I
Y
ERC
Environmental
and Energy
Services Co.
BORING NUMBER iy57 7 I
FIELD LOG OF BORING (CONTINUED)
Attachment B
SST _ 2. OF 2-
LRHOLOGY
DEPTH
(FEET)
SAMPLES
RECOVERY
BLOW
COUNT
DESCRIPTION
USCS
SYMBOL
ESTIMATED
PERCENT OF
COMMENTS
GR
SA
Fl
7 1 v - s1. 1 4.a_ it rL-e,
s,7
755
l!oz(
l
243
1327- 3
6 I7
I6
t'
zQ
iti5
r?
6v -h , C 44r_ 6I .!- � �ZG v�1/ -ice. -
mac.
Zcr
(-CC
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.Z 1
3 U
_z c%��. - -Iv-a r I tcr.�
)
48 VL(741 -ee,../.‘-�- l_-� s �c «, �a.,n..�J .sue
�,-I
Q
S014
l.nvirr)I!U!CI!I
and Energy
Services Co.
WELL COMPLETION RECORD
Attachment B
JOB NO
CL ENI
V'Ei_L LOCATION
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed
YDI-406i_ OLC
DRILLE_N
DATEIf IMB
Borehole Diameter (in.)
Type and Size of Casing (in ) 211 Sc., t-{_
Type and Size of Screen (ir; 't
Screen Perforation Diameter (,n.) O •02O
Screen Length (ft.) 1 g - 9 CU
Centralizer Depths (ft.)
Completion Technique:
1) Type of Filter Pack and Placement
Method
1--IQs-f , r 4-3 II Poo r roil (rl a vq t.
2) Type of Bentonite and Placement t hod U
nV�t7l lv c ps prior" -4°`z'
3) Type of Grut Mixture and Placement
Method
Description of Potential Problems With Well
A- dr1 i,,yt1/ •
Development Technique
Ai rV
GROUT
BENTONITE
FILTER PACK
-n.15
20.50 . LAO
CC
Well Head Elevation
Ground Surface Hey
Well Head Completion t,1e:hoct
Drilling Method!Rig Type
)-V5ft Obi! Z.
Surface asing: Type
Diameter
Lera;h
MATERIALS
Cement (sks.)
Filter Pack Material (ft `" )
Casing Material (ft) t -'t C
Bentonite (ft. ) 2
Top of Bentonite Seat t l • 20 ft.
Top of Filter Pack
Top of Screen 20 • 5 G ft.
Bottom of Screen 39 -Li C-) ft.
Bottom of Hole 41 • 0. ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
mib7 Environmental
and Energy
Services Co.
FIELD LOG OF BORING
Attachment B
BORING NUMBER i { z 3 q
SHEET_LOF 3
PROJECT NAME
r►i [` o
PROJECT NUMBER
:2)(3 O 5 "7 oo l
ELEVATION AND DATUM
LOCATION
DRILLING COMPANY
/Alle l�IFLL
DRILLER
i� Dbttl
DATE AND TIME STARTED
sf30:I b R II:31
DATE AND TIME COMPLETED
5-_/;,o C t;�,�o
DRILLING MU!
Bto1
DRILLING METHOD
NSA
COMPLETION DEPTH
yo'
TOTAL NO. OFSAMPLES
S"
SIZE AND TYPE OF BIT
7 I1
HOLE DIAMETER
7 it
NO.OF
SAMPLES
BULK
SS r
...
DRIVE
PITCHER
DRILLING FLUID
DRILLING ANGLE
WATER
FIRST
AFTER HOURS
/-) o ,-1 e
0 LEVEL
SAMPLE HAMMER
TYPE U. y,%,,..3
,.� , DRIVING WT. j q b lb DROP 0 J!
HYDROGEOLOGISTI DATE
G 44 it P C. y-/-10 i 90
CHECKED BY/ DATE
r
O
DEPTH
07 i
>-
8g
DESCRIPTION
ESTIMATED
PERCENT OF
COMMENTS
-+
(FEET)
$
g
y
GR
SA
Fl
1 L
3 4
5-
6 7
5 1
I
11 �+
to O 4,,4 al o. y e 1 ri e t) S» n a)
jyc
yo
i 0
, ,e s ,"
IL
2.9• -T/inI
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t4T 39-1
ZS-
J
5 Pr h
rt 0 Gt. � 00 o ,,,
13 pi
J. G e.O -C- h
14 NNW 4,v�ruumeuda�
and Energy
Services Co.
FIELD LOG OF BORING (CON l"INUED)
Attachment B
BORING NUMBER Ni B 3 9
SHEET OF 3
§
d
d
DEPTH
(FEET) DESCRIPTION
W
y
RECOVERY
BLOW
COUNT
USCS
SYMBOL
ESTIMATED
PERCENT OF
GR
SA
FI
COMMENTS
IL
`~t
10 19
20 4
511 i.-;-‘-ty Si 1#y pier) 5AnJ
ip
S
I2=ov
10 (..)/ SarvtE. Vet'y -f% fie. 5A-nc.`.fi3J
t 39— Z_
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7 ('-,e0..Net,.
Z2
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15 Zb
17 2.
29 30
8 _S11 i-v{1y 0.1.6.vey rne.)64nel .5i1'
Is
s
►Z1 17
1i.
4J/inn," (2 T►no n 2
NZ 9-3
3i
31 13:2-\\ S1I 1,-,,,41y InotsL
t7
mo17 --wCN 60 rte.() 1'n€cl4 ti@ SArlits?
'5
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6.5-
tS
13 : z t3
141
14tJU- ti an
cuvirunmeuial
and Energy
Services Co.
Attachment B
FIELD LOG OF BORING (CONTINUED
BORING NUMBER ,i Q 3,3
SHEET OF -1
iy
o
E
-+
DEPTH
(FEET)
ISAMPLES
a.
>
S
y
O
m 8
DESCRIPTION
LISCS
SYMBOL
ESTIMATED
PERCENTOF
COMMENTS
GR
SA
Fl
3i.
4 AIL lei Sas £P ahc,tP pr() meC)fjf
90 ID
13 :40
77 5iCinc), a/Ion pi GoeIASO(-VPc)
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Environment:
and Energy
Services Co,
HELL COMPLETION RECORD
Attachment B
JOB NO .300 J 00
CLIENT O'Y\C-6
WELL LOCATION
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed
-1-yo
Borehole Diameter (in.) 7
Type and Size of Casing (in.) g _ 5ch
Type and Size of Screen (in.) " SC#1
Screen Perforation Diameter (in.) O.O2,
Screen Length (ft_)
2©
Centralizer Depths (ft )
Completion Technique:
1) Type of Filter Pack and Placement
Method
Laet5; r
-141 r Ugg}l G
crS
2) Type of Bentonite and Placement Method
art \-6115 ``(� a C- 5) f o u r
3) Type of Gro
Mixture
e and Placement
Method
e>exvt"Crr t -(P G aNk.* V._00 Citai fr} ) four
Description of Potential Problems With Well:
l
t_Ft; Rbbrr1 CO rI .1
DAT[/Tl .1E_._
Well Head Elevation 3 1 .:
Ground Surface Flev • 29
well Head Compet on h"ethod
Traf(; ce0)
Drilling Method'Rig Type
Surface Casing: Type _
Diameter
t enc?h
MATERIALS
i
Cement (sks.) 2 Q2._
Filter Pack Material (f13) L/ 4"172
Casing Material (ft.) 25
Bentonite (ft3) I Vz b u g S
Top of Bentonite Seal. /5. 3 ft.
Topof Filter Pack 2 3 ft.
Top of Screen ,7 . CP5 ft.
a 5 Bottom of Screen 4 5.4' 5 ft.
:5 Bottom of Hole 41 - 25 h.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
!'�I Environmental
and Energy
Services CO.
FIELD LOG OF BORING
Attachment B
BORING NUMBER Li 3 36
SHEET ! OF 3
PROJECT NAME
-.E.rnCO
PROJECT NUMBER
.30067 co I
ELEVATION AND DATUM
LOCATION
DRILLING COMPANY
V ALL ) Et c..
DRILLER
�i o3/k1
DATE AND STARTED
5/300 7A 5
DATE AND TIME COMPLETED
.30/9 Q q'4 0
DRILLING EQUIPMENT
t3-to1
DRILLING METHOD
H 3 A
COMPLETION DEPTH
TOTAL NO. OF SAMPLES
SIZE AND TYPE OF BIT
7 HOLE DIAMETER
7'
NO. OF
SAMPLES
BULK
SS
DRIVE
PITCHER
DRILLING FLUID
DRILLING ANGLE
WATER
FIRST
AFTER HOURS
4J o kJ C
LEVEL
SAMPLE
TYPE
HAMMER l/
/v\A,u (.1 AL DRIVING wT. 140 lb DROP 30
HYDROGEOLOGIST / DATE
EAA 1 -/PC 5/_30/10
CHECKED BY /DATE
DEPTH
N
¢
8 g g
DESCRIPTION
m
ESTIMATED
PERCENT OF
N
¢
m 5
y
GR
SA
FI
COMMENTS
A3P/4ALT 3"
2 3
4 5
7 8
5 l0
5 3., Rccav&,2Y
807
10 FF,vE- mt..D _..5AAJD Y CLAY
CI -
5 %-
I /
ID
73Ro AJ , moo . Pc.A57-/C.
Hklc,l
ToPL.43r/C . (milP TO ._3O 6
,er
I a
5/LTA ,jc-, ODOR.
/3
►4
Niszir Environmental
and Energy
Services Co.
Attachment B
FIELD LOG OF BORING (CONTI
1 BORING NUMBER /`' I ` 8 3
SHEET 1R OF -3
8 d
DEPTH
SAMPLES
RECOVERY
fl 0
Ed
DESCRIPTION
8 'I'
mr
N
ESTIMATED
PERCENT OF
GR
SA
FI
COMMENTS
S
A4.,.rElz,uAr,jrt, I-0- .
/e
t i
tT
. .ie,r—/TLY CLAYE.Y W.A.J D, 6/LTY
/5c
HILIGi = 50
11 3p1.iD, 11k(f) f 5iLr FWE- -
Kit
pp,>7
/ 7
rrE.D Ge.
0 -3" 10/ CuAY .y ..*LID 1.Y5c
'8
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as
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40 m. u n L F, ti.t e s, DA m P
33 A d y�, Dan -5P X55
1 m
1/4-05
34 -34:,-
1D
Environmental
and Energy
Services Co.
FIELD LOG OF BORING (CONTINUED)
Attachment B
BORING NUMBER AJ6 38
SHEET 3 OF -3
}
E
DI
m
IRECOVERY
0 g
DESCRIPTION
ESTIMATED
PERCENT OF
��O
FEET)
'
COMMENTS
-J
N
m8
y
GR
SA
Fl
37 _Ye
39 90
Li1
42 7
37 ,3LI IaHTL:d o,L_ T Y Fi lJ s -(L.L.
RTrn
A� 4())41/E mo2L zSlL7 , Dken R
�P 95 J B.'s
3 90
/0
N Li u Tie a c_&_.
cQ7
35 i7
3(0
P5 AfetrE ``'/ . I(__.T 70 36
0 AL16r ?Di kl DQU 5c_ C 4 Y
!n 6Au 0
n2Acvc/stir C(J y
30 C)
9.08 10`1 A3 move.
1,9
Cc_
/Cr
19 61LTy iti�. -ma) .34M D
t n P moo &JaL ,RTEC
90 etc:
(;rtvironmcnt:
and Energy
Services Co.
JOB NO 30©:S CIO)
C C.O
WELL LOCATION 4(
GROUND SURFACE
DETAI,S OF CONSTRUCTION
Date Completed
WELL COMPLETION RECORD
Borehole Diameter (in.)
Type and Size of Casing (in.) 2'I $c h 140
Type and Size o1 Screen (in ) b?'t SG�tyQ
Screen Perforation Diameter (in.) 0.02.0
Screen Length (ft.) 1 'g • 4- 5
Centralizer Depths (ft.)
Completion Technique:
1) Type of Filter Pack and Placement
Method
Loner'
� t (oUG h Cr tri t
2) Type of Bentonite and Placement Method
L NO rn w I
CAI g rn
5c 3-4-1/4-:
3 3) Type of Grout Mixture and Placement
Method &Pit-\nt- , Crindt��C t lG t1r F0O( -Prowl S
Description of Potential Problems With Well:
U
GtrLA we -11 •
Development Technique
N A'
PHOC f ( PLC:!="7,IS1
Attachment B
f RC)bi,"r .Car't-f.,
70 Weil Head Elevation 3 - aLi
Ground Surface Elev ln• ray
Well Head Completion Method
go)C
Drilling MethodiRg Type
tk pr_ _l_ Qblle_ Q-4)
Surface Casing- Type
Diameter
l_endth _
MATERIALS
Cement (sks) .2 'y2.
Filter Pack Material (ft 3) 31(2- )00
Casing Material (ft.) "I 5
Bentonite (ft3) f 7z ba
Top of Bentonite Seat tq• Ld ft.
Top of Filter Pack 2 Li • C:7 ft.
Top of Screen
.260.30 ft.
Bottom of Screen '45. 05 ft.
Bottom of Hole LI5 ft.
NOTE_ ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
it Environmental
and Energy
Services Co.
FIELD LOG OF BORING
Attachment B
BORING NUMBER N J t7
PROJECT NAME
Eit'\(1,0
DRLLUNG COMPANY
(MA4. 5
SHEET % OF -
1� cA\\e,./ WP\\
DRILJNG EQUIPMENT
Z-(Ot
SIZE AND TYPE OF BIT
7 "
PROJECT NUMBER
..210C;5—'700
DRI ER
DRILLING METHOD
1-4 5
HOLE DIAMETER
7 ,,
DRILLING ANGLE
cif
ELEVATION AND DATUM
DATE AND TIME STARTED
.s/3c/j /4:��3
COMPLETION DEPTH
LOCATION 5 O -f k>,., ' l d I n "h A Q c)
54,14
NO. OF
SAMPLES
BULK
SS
DATE AND TIME COMPLETED
57/W90 C) Js.. (7
TOTAL NO. OFSAMPLES
DRIVE
PITCHER
DRILLING FLUID
NONE
SAMPLE HAMMER
TYPE p",.rnte,vra\
DEPTH
(FEET)
DRIVING WT. 14-0 1b DROP 3 o 11
DESCRIPTION
WATER
LEVEL
HYDROGEOLOGIST/ DATE
4 4 I' C s -/30h -it
m
}
ESTIMATED
PERCENT OF
GR
SA
FI
AFTER HODS
CHECKED BY / DATE
COMMENTS
3 b
7 9
100
Ii
Iz
13 14
7 I 14 rye() well .sortec)
re,/ S q -4-v r ►4 l -e rt co.), -Jed
s?
t U 34
N 4v_t
i4
7,37 Environmental
and Energy
Services Co.
FIELD LOG OF BORING (CONTINUED
Attachment B
BORING NUMBER
A/ F) 10
SHEET Z OF 3.
_
DEPTH
(FEET) 8
ISAMPLES
cc
,
w
2O
v
DESCRIPTION
N O
8 'I'
»
N
ESTIMATED
PERCENTOF
GR
SA
FI
COMMENTS
34 !%
1.7 IS
2-0
6 St14y (el A3. 6Rna
''",41
SO
sv
I4'Liz
13 ,�rawA SA-i-.JrK.'k ej
N ;3 4U ---Z.
Zi
i ci
1-+I`► l,t =
72 rte(,:-+-'
2.3 24
2.3--
Z-7
Z$
Zy
30 Piod- 0e-k\60riv' A, mej -4''Q-
5i'
"
I
N 4°--..
S4nri S"" ortrf /oo,SQ)
3,
-Pe4..)
4k...ka_ -6- A h/ S'og Orafi.se
j
3L
33 Attachment B
Environmental
and Energy
Services Co.
BORING NUMBER At it
FIELD LOG OF BORING (CONTINUED)
ii
p
DEPTH
CT)
(FEET)
co
to
1 RECOVERY
23 m S
DESCRIPTION
uses
SYMBOL
ESTIMATED
PERCENT OF
COMMENTS
GR
SA
Fl
.Sl► k+t1 ,,5I{fy f7Q/ 5(44
52.1 `--y6'5/t
/14:5-6--
w/ `r, -erteyQc 0,\ A‘, san)
N-1 4-0 —Li
.3C,
la-yer-S I rcn 5kAty /Y1br3l'
C-,e0T-e c_- wife5
37 ,
1-z. rl a t, 4 0.1e ino N-0 ., , b "
-57:75.41
1 3 `i
`T U
I.5-- f 0
C.\ c.�
Ci-
N i1 v — .
q-7
zi3
qq-
r
l;
CAe y
4,
t .i7
1'rlv irunFT1Cn`
and Energy
Services ( o_
JO[3 NO
3o05 -0o i
CLIEN1 5:_�►v C
WEI t.00ATION j cs.
GROUND SURFACE
DETAILS OF CONSTRUCTION
Dale Completed
WELL COMPLETION RECORD
WI I I_ NO rnW s Le HYD( ( ii
Gni a,41-0
CS -1 tc-+ tI L3r li TER ID; r
Borehole Diameter (in.) 7
Type and Size of Casing (in.) 2'
Type and Size of Screen On.) Z' 3c.h
Screen Perforation Diameter (in.) O• c�2
Screen Length (ft.) 1 q. Lo 2...
Centralizer Depths (ft.)
Completion Technique-
1) Type of Filter Pack and Placement
Method
1...(s n - .r
*hro try
2) Type of Bentonite and Placement Method
U V I' u
3) Type of Grout Mixture and Placement
Method
On ik Gm.fi RSr-{tundp`'r
Description of Potential Problems With Well:
cz d(j Wt,1) •
Development Technique
GROUT
BENTONITE
FILTER PACK
DATE/TIME
—t;.70
5- Lig-
Attachment B
I Veto
Well Head Elevation .2342• L4�
Ground Surface Elev (v •
Well Head Completion Method
(C4.--Cei✓ ��
Drilling Method/Rig Type
1454- al if`, _$ -La /
Surface Casing: Type __
Diameter
Length
MATERIALS
Cement (sks.) z
Filter Pack Material (f13)
Casing Material (ft.) 5
Bentonite (ft3 ) f 'rz box! S
Top of Bentonite Seat 1� • 7C) ft
Top of Filter Pack t2 Q .1 D ft.
Top of Screen
a5.ti4ft.
= 4f•CS, Bottom of Screen 45•°9 ft.
cf 5 , 5=t, Bottom of Hole 4 °-)• 5 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
Attachment B
ERC
Time Environmental
and Energy
Services Co.
BORING NUMBER fU , U
row (42
FIELD LOG OF BORING
SHEET I OF ;%-
PROJECT NAME
S 1.`I\.C,_0
PROJECT NUMBER
- 0(:) 5-7 oaf
ELEVATION AND DATUM
LOCATION
A h A r x) t1! rka : h r1P
DRILLING COMPANY .
V A\l . y We 11
DRILLER
-Rako."
DATE AND TIME STARTED
6 /7 /`1©
`� ! oop
DATE AND TIME COMPLETED
6. /71 yn (A3 nc
DRILLING EQUIPMENT
DRILLING METHOD
COMPLETION DEPTH
TOTAL NO. OF SAMPLES
SUE AND TYPE OF BIT
7 "
HOLE DIAMETER
`7 0>
NO, OF
SAMPLES
BULK
SS .
If
DRIVE
PITCHER
DRILLING FLUID
DRILLING ANGLE
WATT
FIRST
AFTER HOURS
N One '
LEVEL
SAMPLE HAMMER
TYPE co p DRIVING WT. 140 1 b DROP 3 a //
HYDROGEOLOGIST/DATE
1 A- 4 µtom._ 6 /7/q0
CHECKED BY/DATE
>.
8 0
DEPTH
ISAMPLES
RECOVERY
O
DESCRIPTION
8 2
ESTIMATED
PERGENTOF
g COMMENTS
-�
°D $
u,
GR
SA
R
•
I,
i,
/0
12-
fq
f6
1c
20 ZZ
2.4.1i
2-6
06 SO
/n 5 1 �y 5. r) 6x-r:',.0 r, E`f- 154 t�
' r
E`.
X'
i 3 ' So L . 57---3c
�
72-
f
tr.�e t\ ScrA-Ok) <_.11ic,,.. ;)rt) IiCAkr‘S
It N LL. 7r ;-eri
ink
ca�v
70 Environmental
and Energy
Services Co.
Attachment B
BORING NUMBER 1 1 q 4
FIELD LOG OF BORING (CONTINUED)
SHEET
r
�y
O
O
�
�
DEPTH
(�
w
a
RECOVERY
BLOW
cc»I T
DESCRIPTION
USCS
SYMBOL
ESTIMATED
PERCENT OF
COMMENTS
!
GR
SA
Fl
;33
3z
-34-
i6 F
- im 6i /4y 5Anc)f 4 5 Al 0.1Q
5?
10 ►b
I G -.L0
y
q4
- ,'-1- IF..4< .5i0�- e'i5 ,.)(34-
?)s. --3
l
if I, -)LL- 76-' :'+'1
St,
38 d
3 rl (1s A haae.
6P
O
!0
i L 1 ?. tv
4e
':
2-" v�- fir! S4r y 5i t I Cary
Mt.-
2c, 1
-7 a. Sj LLvi
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,+ t't-= 0pnrn
liz
if
/-13°
" sP
5P
iG : '?,4 4 3-S-`4
.o
1-0
ERCE
WELL COMPLETION RECORD
Attachment B
JOB NO. 30 2.75.001
CLIENT SEMCO
WELL NO. DM
WELL LOCATIONJah4a QriGt ) CA •
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed if- 3 0 - 90
Borehole Diameter (in.) 10 -
Type and Size of Casing (in.) CC?
Type and Size of Screen (in.) 55'11
•
-tv►
Screen Perforation Diameter (in.) b .024
Screen Length (ft.) 2..0.OO
Centralizer Depths (ft.) -- ,
Completion Technique:
1) Type of Fitter Pack and Placement
Method
3 l avi ca t--/
2) Type of Bentonite and Placement Method
"FrehItvti -E
3) Type of Grout Mixture and Placement
Method /
Description of Potential Problems With Well:
,,1 L � iuc> Ccorioavn.
"5S ri n
S ^Fq
Development Technique
4.wt 5ttv�; e
HYDROGEOLOGIST
DRILLER `-A t� r►e
C. D;ere ks
Ehtit rot\meMria+..(
DATE/TIME //-Z'-90 40 11-30-9O
2: ooh,,,
/45;004 rk
Well Head Elevation 2..b7.
Ground Surface Elev.237.g0
Well Head Completion Method
Tra-c-gg e f3 arc
Drilling Method/Rig Type
—D 14.&( 4u1e/Dri IIsy,4e+vis
Surface Casing: Type ,4t4
Diameter —
Length
MATERIALS
Cement (sks.) "4g.Sc cr-,L..�_
Filter Pack Material (ft3) S. 6
Casing Material (ft.) 2.1 0
Bentonite (ft3) 1.3&1
Top of Bentonite Seat /430.24 ft.
Top of Filter Pack 186,2$ ft.
Top of Screen 18$.00 ft.
Bottom of Screen 2OS. 0 ft.
Bottom of Hole .. t e . O ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
kgs° ERCE
Attachment B
FIELD LOG OF BORING
BORING NUMBER pM.'L
SHEET OF '
PROJECT NAME
5EMC©-beep Atoit'eAr 2 -Kw.
PROJECT NUMBER
302 r 73.00
ELEVATION AND DATUM
LOCATION Ssa #A s•f
se%11ieim 84c;41i%il
DRILLING COMPANY
r'.c�\in� Fnvironrxew> TarITC DRIVING WT. /10-i6 DROP 3O-Ih
HYDROGEOLOGIST/ DATE
Dlere.k$ /l1/.$ -4n
CHECKED BY/ DATE
DEPTH
W
>
„§
DESCRIPTION
a,
ESTIMATED
p PERCENT OF
(FEET)
(158.$)
a
0 ' cc
g
m 0
' >
an
GR
SA
Fl
COMMENTS
1 2.
4/
6 ' we..to
5P
9S
S
8 sco.a- (.4.4+1A. Y4IH.hr` si 14, liq-e
1 D
ht,,r 5,4; cso s.G. .
12 Iel
A7ri e- ,L , ht edimAyt- leapt' c.P s.x►,Q,
Sc
$s
is
!o'a e 107 g % si /01
16 I
ev;1 ` . S/ I .e 1rrWr1/ Lu.i.s4,
J
d -G► Je sato-
i8
r
sa►,d 5; 14 ct , Pl fLc, me,
GL
2575
2©
� rm j 1 v j 1+-0(5 r kutn Qe-
v�r-a .-.e 6 frcini�-- .
///
.
22 Sw4..t out_ 114 — l it?' .4ee."f-•
-
'70
10 2N
5.e
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ik CiQi1 — 4-a coetuk-1 raerKaPs?
9'S
S
sue. .J1c24' 4Zto'
2b
ssrr��
5 •e ? �'.
/€1-l ctf
ler
410 ICS
2.9 �n
BORRK1 NISraER C+M W I
7B
8o
$z
84 Sb
88 go
91-
9t/
96 78
FIELD LOG OF BORING (CONTINUED)
Attachment B
UlNUE
Attachment B
FIELD LOG OF BORING (CONTINUED
BORING NUMBER OM 1,01 I
•
SFEEr z OF 6
i ESTIMATED
DEPTH
y
DESCRIPTION
y
PERCENT OF
COMMENTS
���
y
$
IV
C
m8
N GR
SA
R
32. Sariet Jq-447{-efi
sit
le,
Ic
34 36
3a
�✓ /�'
D
,cialey 0 t 14- Yt ( Ora d•-i.c/ 'Nn.v.ta�i
AIL
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r /`
6 c 0,4/ Ck , ►�►^,i in..1r ah�c: s II
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want i a- ll- . b 1-TJ 4),,, e tt.'�
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5c
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N
yes
' ' '
1; II? C1 , bra., X44,,-
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ys SS
///:
Sy
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GS 35`
36 .p.c.Z.
Cl I10'' 4-04"5raozl (.v;44k.MiI.%
64 4s
ca is
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Se
5(.1 T�e eA s nrx-1 SOv- ,
12 50
cla,wf ."'Q
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MA = b ate,
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Z.
t
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CL I
P 25
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i
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t a.4 -6i4 4, rz-t to i 5 GC
-
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Attachment B
BORING NEA19ER bM W
FIELD LOG OF BORING (CONTINUED)
1 f!
1 -is -mot a
II/2R-qv
t(
Is /Uo Zee,' QO ii G 0. (5 tz, ( ;vs. 3u -o• a ea. P
, 7 2.
547 4-1-i sp env P` i
rA+L'``` Wd .“ 1v- S,..4,Wf/.4.r'1't1T.
le i 0
1►
-•r
1 D C \ V-4-4.4.-e,t t
( 6 cl
t; Q '� t
-. r_
5. zc -Lc' bate. i t _ G1
Attachment B
BORING NUMBER D % / j
FIELD LOG OF BORING (CONTINUED)
SHEET
SOF 6
'jGkti- I 1 4 -C%` -!h iv-r.6.4l Y".(tt.-
\
4r1 tNAI* ##v— Lt
r
$i 141 c-tt / ‘44-044,64,4-44 k
J
,
-P-t rVit \O IrtAttin Vvt./..ti .s •
/
GteVeln 5.A ar
5L
7d
50 14 Ail,
50 .5.444-e- 4,4-- /56 `
LAC 55
?ca
Z5
ERCE
Attachment B
WELL COMPLETION RECORD
JOB NO. 3©273.001
CLIENT SEIKO
WELL NO. DM W Z HYDROGEOLOGIST C • b tcrcks
WELL LOCATION $ctnIa Virrra C/7
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed /2-/-90
DRILLER Lci4M•c 6nvlrem men ha
DATE/TIME /2 - 1- 94 / 0710
Borehole Diameter (in.) /O -in
Type and Size of Casing (in.) LOG 4-/n
Type and Size of Screen (in.) SS '1-i& pr. )
Screen Perforation Diameter (in.) O. 02.0
Screen Length (ft.) 2p . C
Centralizer Depths (ft.) NA ,
Completion Technique:
1) Type of Fitter Pack and Placement
Method
3 Lay,cs�ur iri-enimt4
2) Type of Bentonite and Placement Method
'/y4" pe llt+s / TTc m -e
3) Type of Grout Mixture and Placement
Method
TrCmwti-f •
Description of Potential Problems With Well:
LOC = law Cc7.( 6p., s tee (
5 5 = 5-a0K1•tdd.. 54,e
— ceincc-, v:a a klk u u acQ
Development Technique
Purr,/ and Sure
Well Head Elevation 236.1,3
Ground Surface Elev.2.34.11
Well Head Completion Method
7'ra. �c IIGt1C
Drilling Method/Rig Type
D t..er... (41..1 e /1>/1>ra trier., s
Surface Casing: Type NA
Diameter
Length
MATERIALS
Cement (sks.) 3 sacks talcs -GL<
Filter Pack Material (ft3) 6.3
Casing Material (ft.) 200
Bentonite (ft9) 2•
Top of Bentonite Seat /6 7. 0 ft.
Top of Filter Pack ! 7q. O ft.
Top of Screen 179.0 ft.
Bottom of Screen 199.o ft.
Bottom of Hole 208.0 ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
411 ERCE
Attachment B
FIELD LOG OF BORING
BORING NUMBER D M w '
SHEET 1 OF 6
PROJECT NAME
SEMCO-beep Apsidw v.
PROJECT NUMBER
3DZ73,00 f
ELEVATION AND DATUM
LOCATION
Easf.PMar.' SaIah7
DRILLING COMPANY
Lt Ac Env/►v,1Mewl.'" Serviuv.
DRILLER
iMkrra . der
DATE AND TIME ST TED
//-30-a1 D 04 //.. 0
DATE AND TIME COMPLETED
/l -30-90 to 1545
DRILLINIG EQUIPMENT
Uri I . Sff�s AP -140 v
DRILL NG HOD
paid -'ht e f�'euersccir•c .
COMPLETION EPTH
9-04SIZE
TOTAL NO.O
AND TLY*E OF BIT / �/
/0-i i c ,� -ii 6 2 4
HOLE DIAMETER
/O .-Ih
NO.OF
SAMPLES
BULK
SS
DRIVE
PITCH ER
DRILLING FLUID
DRILLING
WATER
Fuial [as? )
AFTER 2r( HOURS
/VDylf
ILE
LEVEL
/86-7'/
-t./e6.5
SAMPLE H MER /
TYPE Au k / C DRIVING WT. 14 0 -�1 DROP 3>-1 N
HYDROGEOLOGtST/ DATE
C. 'ra, C kS//l- 3 6 -g
CHECKED BY / DATE
O
.§
DEPTH
W
w
0 j
DESCRIPTION
y
• ESTIMATED
EN g PERCENT OF
�C
J
(FEET) ¢
N
8 m 8y
GR
SA
R
COMMENTS
2. b
.we - , 1(441 6reoi.
Sit ,h41 Cite
6C
96 1 D
I
S
Lsa4C.i Gfano,1" 4a.'el6.
V
to -
sa c era-- G.h /.,-e_ (.1 sal 4,1
6 C
ao
/ v
54 ea w%
1i
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a na a as ' - /C4004-ra��
5C
13�
to
6 r *- .t
el- (al
19 .4
,L
.
z2
Sa n,. Z cv1.- a."1 -- L ©--h 0.--t' _6-e---
ste-t-fl
1q
i\U
2,6
2.. E3
5 le -'ovf 5
c
9'e
/©
3 D
a n.. e_ AA.--ct'j-
/ZOO ('n oerri-1
C I1Vr
BORING MUSES b M W 2+
ctt
Attachment B
SHEET
z c 6
FIELD LOG OF BORING (CONTINUED)
75 �'� r t7 Y an
0CRING NUMBER
I DEPTH
(FEET)
72. 711
76 78
Do
82 8g
04 eg
�o
92. 9"
"6
78 1D O
102
tog
FIELD LOG OF BORING (CONTINUED)
DESCRIPTION
VI( Y-�9't y` t v1G�- 7 t--4 i"hG 1l(ti 5
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Attachment B
9T.3_CF 6
COMMENTS
ESTIMATED
PERCENT OF
A?c Re cover,
i2
17 4
.0%
136+
S
168
!9
w
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,a Le. -- -I _.
4 95
igniZ. MMI II
WRING tNUMBER Dm w
FIELD LOG OF BORING (CONTINUED)
Attachment B
VIM r Lc6
NW. -- -w N
BORING NUMMI bpi w
FIELD LOG OF BORING (CCIUaINUED)
5p
3 Attachment B
stiszr
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Attachment B
ERCE
WELL COMPLETION RECORD
JOB NO.:3O 7.. 7 3, Co 1_ WELL NO. -1.)1911.9 3_ HYDROGEOLOGIST C' E a ,cud 5 kb CLIENT S E /M do DRILLER JJ _Lay 4 En vlE`ot2T
WELL LOCATION .1 36 1Yi its 1-r-1tz..\ PIki1 DATE/TIME -0/91 C Od 'fib
GROUND SURFACE
DETAILS OF CONSTRUCTION
Date Completed 3- 9 'q
Borehole Diameter (in.) !p -1N
Type and Size of Casing (in.) )-Itn Lc C 5
Type and Size of Screen (in.) +4, s 5
Screen Perforation Diameter (in.) 0.4710 -tin
Screen Length (ft.) 2 O.O k lL
Centralizer Depths (ft.) ,
Completion Technique:
1) Type of Filter Pack and Placement
Method
Lone 5 41 41- 3/ 71-ervl l' -e
2) Type of Bentonite and Placeme t Method
'/4-IK Vv%la ialole /�Tite1st.►.e
3) Type of Grout Mixture and Pllcement
Method JJ
‘1010.1a4 &reek 1' 7 r.e% i ie 0_0.45
P Descri tioh of Potential Problems With Well:
/
,t a'Fe5
* C s = Ln.z.> ea..- %.r. .5 i-ee
4X 55 = 544i.11-614 S'ir•e(
Development Technique
5 r
1 x�Y,%Ffw9
GROUT
BENTONITE
FILTER PACK
=I67 0
=173,6
,80
Well Head Elevation
Ground Surface Elev.
Well Head Completion Method MAC. iC. acle - me .'rL
Drilling Method/Rig Type
�u�( rud e I"be-1 i ,yi.1-en4,s
Surface Casing: Type
Diameter
Length
MATERIALS
Cement (sks.) 3 s 5
Filter Pack Material (0) 5%5
Casing Material (ft.) 200-4-F.
Bentonite (ft3) 3 Ltd=
Top of Bentonite Seal % i/7 Oft.
Top of Filter Pack 173. 6 ft.
Top of Screen
%f .O ft.
Bottom of Screen 1.40C2 -Oft.
Bottom of Hole 1-6/. O ft.
NOTE: ALL DEPTHS ARE REFERENCED TO GROUND SURFACE
ERCE
Attachment B
FIELD LOG OF BORING
BORING NUMBER M, r 3
SHEET OF 6
PROJECT NAME
5 EM e 0
PROJECT NUMBER
• O z 7 3. a o 1
ELEVATION AND DATUM
LOCATION
z.9'5 4; ='.,diu A„u,( Pith
DRILLING COMPANY .
La x. I n vl l v -o i oteH. 4-a. (
DRILLER 5 � � �
DATE AND 17MQSTARTED� t 3 �
1 I
3'� AND TIME 7- 91 COMPLETED@ 3 0
DRILLNG EIQUIPMENT
1::, V4 t1 s i4 5f-c.11i
DRILLING METHOD
t -( wz.t(
COMPLETION DEPTH
2,0 I -P- -
TOTAL NO. OF SAMPLES
Y
SSE AND TYPE TT
110 --AK 4 V'9u;4- ,;ii 5 . f
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e- ) 0
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SAMPLES
BULK
SS
1 DRIVE
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AiOiL-e
DRILLING ANGLE
WATER
LEVEL
FIRST
AFTER HOURS
SAMPLEHAMMER I
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HYDROGEOLOGIST/ DATE
C ED/ S 1.b
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ERC
Environmental
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Services Co.
BORING NUMBER D 11 1 0 3
FIELD LOG OF BORING (CONTINUED)
Attachment B
SHEET :Z OF b
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Attachment B
ERC
Environmental
and Energy
Services Co.
BORING NUMBER -Dm I
FIELD LOG OF BORING (CONTINUED)
SHEET 3 OF
g ESTIMATED
0 DEPTH
(FEET) DESCRIPTION
SAMPLES
RECOVERY
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Attachment B
ERC
Environmental
and Energy
Services Co.
BORING NUMBER b / w
FIELD LOG OF BORING (CONTINUED)
SHEET "I OF-
›-
.6
( DEPTH
[SAMPLES
RECOVERY
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COUNT
DESCRIPTION
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SYMBOL
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PERCENTOF
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ERC
Environmental
and Energy
Services Co.
Attachment B
FIELD LOG OF BORING (CONTINUED)
BORING NUMBER DPI 1 `_' 3 I
S41EEr OF
8 DEPTH
(FED
SAMPLES 1
RECOVERY
BLOW 1
COUNT
DESCRIPTION
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SYMBOL
ESTIMATED
�- CENTOF
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f • /7
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Attachment B
ERC
Environmental
and Energy
Services Co.
BORING NUMBER b l� W 3 I
FIELD LOG OF BORING (CONTINUED)
SHEEf�OF_6_
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O
0 DEPTH
(FEET)
N
RECOVERY
BLOW
COUNT
DESCRIPTION
8 ESTIMATED
PERCENT OF
COMMENTS
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GR
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SA
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Attachment B
ERCE
WELL COMPLETION RECORD
JOB NO. SO 27 3 , 00 i WELL NO. Div) in/ l HYDROGEOLOGIST C2,' i.� anti 61.6 CLIENT O DRILLER Ld4►1e Yel4171 adwall 1Dn1I •sycieus
Surface Casing: Type AM
Diameter —
Length
MATERIALS
6eff►ee4.(sks.) 5 5k5
Filter Pack Material (ft3) q 5 /E S
Casing Material (ft.) ,Z I O
Bentonite (ft3) �i LOcl C k c)--1
Top of Bentonite Seaf
Top of Filter Pack i!3$ O ft.
i97O Top of Screen / e Z O ft.
Bottom of Screen .Z.O 7. 0 ft.
xo.j, y Bottom of Hole ,D'/: " ft.
NOTE: All DEPTHS ARE REFERENCED TO GROUND SURFACE
17-
ERCE
Attachment B
FIELD LOG OF BORING
BORING NUMBER - i laj l
SHEET , OF 6
PROJECT NAME
5EMC0
PROJECT NUMBER
-3Gzi3.Co1
ELEVATION AND DATUM
LOCATION
Z.R.' IV_1 uluiif-tcz( P/t,..j
DRILLING COMPANY
Letilite 6nuiv- ittiet.1- (
DRILLER
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DATE AND TIME FAMED
3_ -r3 --H I
DATE AND TIME COMPLETED
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DRILL EUIPMENT
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bti.x-1 Watt
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COMPLETION DEPTH,
_a9,y
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LITHOLOGY
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BORING NUMBER ' > m w q
FIELD LOG OF BORING (CONTINUED)
Attachment B
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BORING NUMBER bpi(
FIELD LOG OF BORING (CONTINUED)
Attachment B
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BORING NUMBER 'oil k41 L(i
FIELD LOG OF BORING (CONTINUED)
Attachment B
SHEET OF
g ESTIMATED
p
DEPTH
(FEET)
SAMPLES
RECOVERY
BLOW
COUNT
DESCRIPTION
USCS
SYMBOL
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FIELD LOG OF BORING (CONTINUED)
BORING NUMBER I) - e
Attachment B
SHEET
o
8 0
DEPTH
(FEET)
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DESCRIPTION
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SYMBOL
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Environmental
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BORING NUMBER U sv w
FIELD LOG OF BORING (CONTINUED)
Attachment B
SHEET , E OF
8 zo
C
DEPTH
(FEET)
SAMPLES
RECOVERY
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COUNT
DESCRIPTION
USCS
SYMBOL
ESTIMATED
PERCENT OF
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2 Attachment B
APPENDIX B
HISTORICAL SUBSURFACE PROFILES (BY OTHERS)
LANGAN
Attachment B
A
MW13
BLDG
W11
MW6
Approximate
location of
sewerline
W7_
MW14
BRICK WALL
4 SUMPPIT
CONCRETE
PAD
MW10
SMW1
SMW3
B
MW16
W9
TANK
PAD
SMW2
DRIVE WAY AC GATE
MW12
BEMCO BLDG
All elevations compared to mean sea level (MSL)
MW8
A'
MW15
0 40
FEET
ERC
—: Environmental
and Energy
Services Co.
Location of Cross -sections
FIGURE
3-6
Ahac _
orient
A
240--
230 -
220
MW13
MW11 MW6
SP
SP
SP
/ SP/SC SP SC
ism,
I _ I cL
SP _
/ u CSC/SM
/
I
210 - i---i f
'SP' /
LJJsP/SM
IsPI /
200 -----ice r►�`
u
190
ERC
.07. Environmental
and Energy
Services Co.
MW10 MW1 MW12
SC --
W
SP/SC
SP
SC/SPA-�
1 _
S
MWB MW15
A'
-240
SP
SP
SP
I
n ----.
SP ��` j - . SPISC
E - -I q\ I
I
ISC1
I I
u
1 Cross -Section A -A'
SP
MLJSM
-230
220
-210
- 200
-190
LEGEND
ASPHALT COVER
GRASS SURFACE.
SAND SURFACE.
CONCRETE COVER
CINDER BLOCK WALL
3-11
FIGURE
3!7
Attachment B
B B'
240
MW16 MW9
MW1 MW10 MW3
230
220 -
SM
SP/SM
1 I
I��_SP/SC
F -I
I I
�XSP/SC
I I
LJ
ISPI
I SP/SM
I ---f
S
LP
I 1
I. ISM
I I
1-11
ISMI
! I
LJ
SP
SP
SC
ME.
SP/SC
SC
MW7 MW14
u
SP
I I
Isp
I I
I„SM/SP
-MULL
I I
ISP
I-).-SP/SM
SM
210 - I --I SM/SP I
I ---1 / \ El
F ---IS isPI
/ I \ I I
200 - P I F--XSC/SP -200
t
I I i��� i-♦ I I
i0
ICI `--. �� f� la-
190 -- -- 190
SP/SC
SM/SC
x-240
-230
-220
-210
ML
LEGEND
UNIFIED SOIL CLASS-
IFICATION SYSTEM
ASPHALT COVER
GRASS SURFACE
SAND SURFACE
CONCRETE COVER
CINDER BLOCK WALL
ERC
'Environmental
and Energy
Services Co.
Cross -Section B -B'
FIGURE
3-S
3-12
Attachment B
BRICK WALL
CONCRETE
PAD
BLDG
SUMP/PIT
A
•--
B7
B
B9
B8
•--
B 6
SMW-1
SMW-3
•
B10i
•
B5
•
B4
TANK
PAD
DRIVE WAY A/C
A'
B2 B1
SOLVENT
TANKSI
B'
B3
SMW-2
•
GATE
SEMCO BLDG
LEGEND
SMW-2 = Monitor Well Location and Number
• B9
= Soil Boring Location and Number
A A' = Line of Cross Section
(PA
0 20
FEET
Locations of SoII Borings, Monitor Wells, and Cross -Sections FIGURE
4-1
oar
WESTEC Services. Inc.
4-2
Attachment B
A
B7
B6
B5 B2
5, _
SP
SM
Silty Med. •••
Grained Sand •
10 - • • - Sitty Mad.
SC Grained Sand..... ••
15 1
LEGEND
SM = Silty Sand
SP = Well Sorted Sand
SW = Poorly Sorted Sand
= Lithologic Contact
=' Approximate Water
Table Location,
5 10
15 sP
sP
SP
sP
V
Lt. Brown Clean,
Well Sorted
Medium -Grained Sand
5 sP
SP
—10--
,]SM
15 Clayey
SC Med.-Gr. Sand
1 SM
•
♦
♦ ♦
•
♦
•
10 •
SP
V
SP
15 SM ♦�
Tan, Silty, Medium -Grained Sand
Cross -Section Locatioq
SJMPmrr
CONCRETE
PAD
A
i
B8
B8
SrnW-
B6
SMW-3
Bs
84 DRIVE WAY MC
GATE
DEMO &IDO
4 5
A'
Bi
SP
HORIZONTAL SCALE
0 10
FEET
Cross -Section A -A'
FIGURE
4-2
Of
WESTEC Services, Inc.
4-3
Attachment B
B
B9
B8
B4
B'
B3
5 Tan, Well Sorted
`` Medium -Grained Sand
�•
• -a%`
!10
SP/SW
Tan, Poorly
SP
SP
-
SM
10 sPisw'
Sorted Sand 4 5•
/ SM
/ �
/
/ 10
5 SP
/' 5
/
.4- .
.•��
i
SM
15 SW
SM
SM
••'10
SP
/s
/
Tan, Silty, Medium -Grained Sand
.' _Weil Sorted Sand
15 -
SM
SP/SW
15 SM
15 SM
LEGEND
SM = Silty Sand
SP = Well Sorted Sand
SW = Poorly Sorted Sand
SP/SW = Moderately Well Sorted Sand
-- -- = Lithologic Contact
= Approximate Water Table Location
i
Cross -Section Location;
Sl1MPIPR
CONCRETE
PAD
A
• _
B7
B
B9
5 c.MW-1
B6
SMW-3
80 84
TAM<
PAD
B5
B
DRIVE WAY NC
B'
83 A' SMw-t
81 CATE'\,
SEMCO BLDG
/,,
HORIZONTAL SCALE;
0 10
FEET
Cross -Section B -B'
FIGURE
4-3
"%V
WESTEC Services, Inc.
4-4
Attachment B
GOLF COURSE
M M x x x x x x x x
ONB9
rrrrrr
N/ORTH BUIILDING
rlrrlr r
PARKING LOT
O NB17
NB22&
(MW11)
NB 14
(Mw7)
NB12 l
(MW6)
S
BUILDING NB27
(MW12)
DB4
SMW3
��SMWi
MW10 •
D'B3
NB4 NB3 . NB1
+O lB2
� � w'. I NB 15
E=MCO�/�r/ (MW8) O. NB19
LANDSCAPED
AREA
OLD FOUNDATION
NB7
(MW5)
B
0 100
FEET
INDUSTRIAL PARKWAY
-x x
WELL 2AS
VA
x
x
LEGEND
MONITOR WELL LOCATION
® BORING LOCATION
- CROSS-SECTION TRANSECT
� ERC
i . Environmental
and Energy
Services Co.
Cross -Section Location Map
FIGURE
4-2
Attachment B
A
WEST
0-
20 -
H
w
w
LL
z
w
U
< 40 -
to
cc
z
O
a
O
60 -
O
w
co
2 w
0 80 -
100
A'
EAST
NB6 NB13 DB1 NB11 NB10 NB16
SP
SP/SM
SM
SC/SM
SP
SP
SP/SM
SP/SC
SP/SM
SP
SP/SM
SP
SP
SP/SC
SP
SP
SP
SP
ML
SP
SM/ML
GC
GC
SP
SP/SC
SP/SM
SM
SP
SP/SM
SP
CUML
SM
SP
SP
SC
SM/ML
SM/SP
SP
SP
SP/SM
SM
AAI
ML
CL
ML
SP
SP
SM
SM
SM
SP/SM
SP
SP
SC
SC
GROUND SURFACE
TAN TO LIGHT BROWN,
SILTY AND CLEAN
FINE -TO -MEDIUM -GRAINED SANDS
ML
ML
BROWN TO TAN SILT, CLAYEY SILT,
SILTY CLAY, CLAYEY GRAVEL,
AND SANDY SILT
SW/GW
SW/SP
SP
SP
SW/SP
SW/SP
WELL -TO POORLY -SORTED
FINE -TO COARSE -GRAINED SANDS
WITH MINOR GRAVEL
LEGEND
ML= UNIFIED SOIL
CLASSIFICATION
SYSTEM
CLASSIFICATION
HORIZONTAL SCALE: 1" = 100'
!' ERC
Environmental
and Energy
Services Co.
Cross -Section A - A'
FIGURE
4-3
Attachment B
B
WEST
0-
20 -
E.
w
w
U-
Z
W
U
< 40 -
C
C
Z
O
cc
60 -
O
LU
CO
2 I-
0 LU
0 80 -
100 -
B'
EAST
NB20 DB2 NB7 NB8
SP
SP
SC ML
MLSP
SP
SM
SM/SC
SM
SP
SP/SC
ML
SM
SM
SC/CL
SP
SP
SM/SP
SP
SP
SP
GROUND SURFACE
TAN TO LIGHT BROWN,
SILTY AND CLEAN
FINE -TO -MEDIUM -GRAINED SANDS
ML SM
SM CL
ML
CL CL
ML.
SW/SP
SW
BROWN TO TAN SILT, CLAYEY SILT,
SILTY CLAY, CLAYEY GRAVEL,
AND SANDY SILT
GP
SP
SP
SW
SP
SW
SP
WELL -TO POORLY -SORTED
FINE -TO COARSE -GRAINED SANDS
WITH MINOR GRAVEL
LEGEND
ML = UNIFIED SOIL
CLASSIFICATION
SYSTEM
CLASSIFICATION
2- = WATER -TABLE
HORIZONTAL SCALE: 1" = 100'
ERC
Environmental
and Energy
Services Co.
Cross -Section B - B'
FIGURE
4-4
Attachment B
C
NORTH
0-
20 -
I-
w
w
z
w
0 LL 40 -
D
CC)
z
O
60 -
O
J
w
Z
F-
a_
w
80 -
100 -
DB3 DB4
DB1 SMW j/ SMW2 \NB15
SP
SP
SP/SC
SP
SP
SP
SP
SP
SP
SM
SP
SP
SP
SM
SW
SW
SP
SP
SP/SC
SP
C'
SOUTH
DB2
SP
SM
SM/SC
SM
SP
ML
SP
SM/ML
GC
GC
SW/GW
SW/SP
SP
SP
SW/SP
SW/SP
ML
ML
SM
SM
SP
SW
SP
SP
SP
GW
GM/GC
ML
SM
CI
SM
GC
SM
SP/SC
ML
; ML
SM
CL
ML
SW
GP
SP
SP
SW
SP
GROUND SURFACE
TAN TO LIGHT BROWN,
SILTY AND CLEAN
FINE -TO -MEDIUM -GRAINED SANDS
SM
CL
ML
CL
BROWN TO TAN SILT, CLAYEY SILT,
SILTY CLAY, CLAYEY GRAVEL,
AND SANDY SILT
SW/SP
SW
SP
V
WELL -TO POORLY -SORTED
FINE -TO COARSE -GRAINED SANDS
WITH MINOR GRAVEL
LEGEND
ML= UNIFIED SOIL
CLASSIFICATION
SYSTEM
CLASSIFICATION
= WATER -TABLE
HORIZONTAL SCALE: 1" = 100'
ERC
Environmental
and Energy
Services Co.
Cross -Section C - C'
FIGURE
4-5
Attachment B
A
-- 5000
L__
i
B226
Dept1 TCF c' 2-DCF
10' nd nd
15' nd nd
20' nd nd
25' 0.0028 nd
30' 0.011 0.0018
35' 0.024 0.0034
40' 0.064 0.0077
45' 0.13 0.018
50' 0.10 0.022
B223
Depth TCF c12-nCF
5' 0.56 0.018
10' 0.39 0.061
15' 2.1 0.35
20' 2.6 0.37
25' 6.5 1.0
30' 2.6 0.24
35' 3.3 0.57
40' 3.8 1.4
45' 1.8 0.42
50' 1.9 0.61
Santa Mar' -- B221 iI
T
_feptl TCF c1 2-DCF_ — —
5' 10 1.5
10' 4.8 6.0
15' 75 12
20' 97 2.4
25' 8.5 1.8
30' 3.1 0.12
35' 15 2.5
40' 20 0.75
45' 5.1 0.31
50' 9.5 0.33
i _ A'T
Dept
B227
1 TCF c' 2-DCF
5' nd nd
10' nd nd
15' nd nd
20' nd nd
25' 0.0033 nd
30' 0.012 nd
35' 0 0031 nd
40' 0.016 0.0019
45' 0.13 0.0060
50' 0.096 0.0052
B226
B223
B227
- -/
B228
B221
B222
i
Pept 1
Soil borings - continuous core
Sample results shown in mg/kg
Results > ESL in Red
A'
rs
Cross-section line
Contour lines are TCE in soil vapor in pg/m3
5'
10'
15'
20'
22'
25'
30'
35'
40'
45'
50'
TCF c12-nCF- B225
B225
nd
0.0026
0.0031
0.026
0.018
0.0029
0.0019
0.078
0.082
0.018
0.041
nd
nd
nd
0.0063
0.0058
nd
nd
0.019
0.023
0.0095
0.022
i
i
7 B228
Depti TCF c12-DCF
5' nd nd
10' nd nd
15' nd nd
20' nd nd
25' nd nd
30' 0.0076 nd
35' 0.022 0.0021
40' 0.043 0.0033
45' 0.40 0.0036
50' 0.055 0.0024
B224
J \
ustrial Parkway
A
B222
Dept1 TCE r.12-DCF
5' nd nd
10' nd nd
15' nd nd
20' nd nd
25' nd nd
30' 0.0092 nd
35' 0.020 0.0041
38' 0.44 0.022
40' 0.11 0.014
45' 16 0.50
50' 3.6 _ 0.22
I
ACg
B224
Depti TCF c12-DCF
5' nd nd
10' nd nd
15' nd nd
20' nd nd
25' 0.056 0.0038
30' 0.018 0.0025
35' 0.074 0.0091
40' 0.10 0.012
45' 0.26 0.034
46.5' nd nd
50' 0.57 0.023
Scale
50 0 50 100 150feet
1 inch = 100 feet
Figure 2
Analytical
Consulting
group, inc.
DRAWN BY
Michael Tiffany
DATE:
May 2022
Soil Boring Location Map
Former SEMCO Twist Drill & Tool Company
2936 Industrial Parkway, Santa Maria, California
Attachment B
Parking
Depth (in Feet bgs)
100 150 200 250
Distance (in feet)
Vertical Exaggeration 1:3
300
350
400
0 A
Soil Boring
B221
SM-30
Soil type sm— 2.1 TCE concentration
sm— 0.09 mg/kg
CL— nd
ML— nd
2936
Industrial Parkway
Legend
Silty sand (SM)
Silt (ML) includes clayey and sandy silts
= Clay (CL) includes silty and sandy clays
and clayey sand (SC)
Estimated extent of TCE Impacts > 1 mg/kg
Yard Area
Analytical
Consulting
group, inc.
Driveway
DRAWN BY:
Michael Tiffany
DATE:
May 2022
2986
Industrial Parkway
450
500
A'
Figure 3
Cross Section A -A'
Former SEMCO Twist Drill & Tool Company
2936 Industrial Parkway, Santa Maria, California
Attachment B
(3ealo�io a�
Formation and symbol an plats 2
Thick ai (Beet)
Jurassic (1) , Tertiary -,+ Quaternary
•
1 Dune sand (Qs)
0-100-
Unconformity
River -channel deposits (Qrc)
0-25 ±
Recent
Unconformity -
Alluvium (Qal)
0-230
_
_Unconformity
Terrace deposits (Qt)
0-75
Pleistocene
Unconformity
Orcutt formation (Qc)
0-225
P
Unconformity
Paso Robles formation (Tpr)
0-2,000 ±
Pliocene (upper)
Local
- - - - unconformity
Careage sand (Tc)
100-650 ±
Local
-
unconformity - - - -
Pliocene (upper)
to Miocene (lower)
Unconsolidated Tertiary rocks,
undifferentiated (Tu). (Includes
Foxen mudetone, Sisquoc forma-
tion and Monterey shale.)
0-10, 000�-
--
Major
- - - unconformity - - - -
Franciscan and Knoxville (t)
formation (Jfk)
(After Worts, 1951)
ERC
Environmental
and Energy
Services Co.
Stratigraphic Units of the Santa Maria Valley
FIGURE
2-2
2-4
Attachment B
APPENDIX C
HISTORICAL GROUNDWATER, SOIL, SOIL VAPOR, AND
INDOOR AIR DATA
LANGAN
Table C1
Historical Groundwater Data (Shallow/Perched Zone)
SEMCO, Santa Maria, California
LANe nMesct: 781016901
September 2025
Analyte
Volatile Organic Compounds
Semi Volatile
Organic Compounds
Petroleum Hydrocarbons
(1)
c
co
a)
o
o
U
H
a)
c
ca
465
0 o
U
IT
1,2-Dichloroethane
Cis-1,2-Dichloroethene
Dibromochloromethane
Tetrachloroethene (PCE)
Toluene
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
1,4-Dioxane (P-Dioxane)
Petroleum Hydrocarbons
(C04 -C12) GRO
Petroleum Hydrocarbons
(C13 -C22) DRO
Petroleum Hydrocarbons
(C23 -C40) ORO
Petroleum Hydrocarbons
(C14 -C34)
CAS Number
71-55-6
79-00-5
107-06-2
156-59-2
124-48-1
127-18-4
108-88-3
156-60-5
79-01-6
75-01-4
123-91-1
PHCC4C12
PHCC13C22
PHCC23C40
PHCC14C34
Groundwater Direct Exposure ESL - MCL Priority
200
5 0.5
6 80
5 40
10 5
0.5 0.38
NS
NS
NS
NS
Groundwater VI Commercial ESL
6,300
23 9.8
210
NS
2.8 4,900
920
7.5 0.14
8,000
NS
NS
NS
NS
Location
Sample Name
Original Sample
Name
Sample Date
pg/I
pg/I
pg/I
µg/I
µg/I
µg/I
pg/I
µg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
Extraction
Wells
EW-1
EW-1_080494
EW1
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
6,600
U
NA
NA
NA
NA
NA
EW-2
EW-2_080494
EW2
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
43,000
ND U
NA
NA
NA
NA
NA
EW-3
EW-3_080494
EW3
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
180,000
ND U
NA
NA
NA
NA
NA
EW-4
EW-4_080494
EW4
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
38,000
ND U
NA
NA
NA
NA
NA
EW-5
EW-5_080494
EW5
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
2,100
ND U
NA
NA
NA
NA
NA
Monitoring Wells
MW -1
SMW-1_111088
SMW1
11/10/1988
ND U
ND U
ND U
NA
ND U
ND U
NA
2,800
260,000
ND U
NA
NA
NA
NA
NA
SMW-1_110589
SMW1
11/05/1989
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
320,000
ND U
NA
NA
NA
NA
NA
SMW-1_020390
SMW1-2-90
02/03/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
430,000
ND U
NA
NA
NA
NA
NA
MW -1_060690
MW1
06/06/1990
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
250,000
ND U
NA
NA
NA
NA
NA
MW -1_121498
MW -1
12/14/1998
ND U
ND U
NA
0.6 NA
ND U
ND U
ND U
24 ND U
NA
NA
NA
NA
NA
MW -1_092203
GWMW1-092203
09/22/2003
ND U
ND U
NA
490
ND U
ND U
ND U
0.7 300
ND U
69 NA
NA
NA
290
MW -1_062921
MW1
06/29/2021
ND U
ND U
ND U
47 ND U
ND U
ND U
ND U
260
ND U
2 ND U
490
660
NA
MW -2
SMW-2_111088
SMW2
11/11/1988
ND U
ND U
ND U
NA
ND U
ND U
NA
7,700
200
ND U
NA
NA
NA
NA
NA
SMW-2_110589
SMW2
11/05/1989
100
ND U
ND U
NA
ND U
ND U
ND U
NA
220
ND U
NA
NA
NA
NA
NA
SMW-2_020590
SMW2-2-90
02/03/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
ND U
ND U
NA
NA
NA
NA
NA
MW -3
SMW-3_111088
SMW3
11/10/1988
ND U
ND U
ND U
NA
ND U
ND U
NA
220
5,500
ND U
NA
NA
NA
NA
NA
SMW-3_110589
SMW3
11/05/1989
200
ND U
ND U
NA
ND U
ND U
ND U
NA
42,000
ND U
NA
NA
NA
NA
NA
SMW-3_020190
SMW3-2-90
02/01/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
57,000
ND U
NA
NA
NA
NA
NA
MW -3_060790
MW3
06/07/1990
ND U
ND U
ND U
13,000
ND U
ND U
ND U
ND U
110,000
ND U
NA
NA
NA
NA
NA
SMW-3_121498
SMW-3
12/14/1998
ND U
ND U
NA
3,000
NA
1,500
ND U
ND U
35,000
ND U
NA
NA
NA
NA
NA
MW -5
MW -5_121598
MW -5
12/15/1998
ND U
ND U
NA
ND U
NA
ND U
ND U
ND U
30 ND U
NA
NA
NA
NA
NA
MW -5_092203
GWMW5-092203
09/22/2003
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
NA
NA
NA
ND U
MW -6
MW -6_110589
MW6
11/05/1989
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
18,000
ND U
NA
NA
NA
NA
NA
MW -6_020190
MW6-2-90
02/01/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
18,000
ND U
NA
NA
NA
NA
NA
MW -6_060690
MW6
06/06/1990
ND U
ND U
ND U
3,000
ND U
ND U
ND U
ND U
15,000
ND U
NA
NA
NA
NA
NA
MW -6_080494
MW6
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
1,000
ND U
NA
NA
NA
NA
NA
MW -6_121598
MW -6
12/15/1998
ND U
ND U
NA
19 NA
ND U
ND U
ND U
86 ND U
NA
NA
NA
NA
NA
MW -6_092203
GWMW6-092203
09/22/2003
ND U
ND U
ND U
20 ND U
ND U
ND U
ND U
23 ND U
ND U
NA
NA
NA
120
MW -8
MW -8_022090
MW8-2-90
02/20/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
320
ND U
NA
NA
NA
NA
NA
MW -8_060890
MW8
06/08/1990
ND U
ND U
ND U
1,300
ND U
ND U
ND U
ND U
88 ND U
NA
NA
NA
NA
NA
MW -8_080494
MW8
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
ND U
ND U
NA
NA
NA
NA
NA
MW -8_121598
MW -8
12/15/1998
ND U
ND U
NA
2.4 NA
ND U
ND U
ND U
7.8 ND U
NA
NA
NA
NA
NA
MW -8_092203
GWMW8-092203
09/22/2003
ND U
ND U
ND U
1.9 ND U
ND U
ND U
ND U
57 ND U
ND U
NA
NA
NA
120
MW -8_062821
MW8-grab
06/28/2021
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
ND U
NA
ND U
NA
NA
NA
LANIAN
Table Cl
Historical Groundwater Data (Shallow/Perched Zone)
SEMCO, Santa Maria, California
LANe nMesct: 781016901
September 2025
Analyte
Volatile Organic Compounds
Semi Volatile
Organic Compounds
Petroleum Hydrocarbons
(1)
c
co
a)
o
o
U
H
a)
c
ca
465
0 o
U
IT
1,2-Dichloroethane
Cis-1,2-Dichloroethene
Dibromochloromethane
Tetrachloroethene (PCE)
Toluene
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
1,4-Dioxane (P-Dioxane)
Petroleum Hydrocarbons
(C04 -C12) GRO
Petroleum Hydrocarbons
(C13 -C22) DRO
Petroleum Hydrocarbons
(C23 -C40) ORO
Petroleum Hydrocarbons
(C14 -C34)
CAS Number
71-55-6
79-00-5
107-06-2
156-59-2
124-48-1
127-18-4
108-88-3
156-60-5
79-01-6
75-01-4
123-91-1
PHCC4C12
PHCC13C22
PHCC23C40
PHCC14C34
Groundwater Direct Exposure ESL - MCL Priority
200
5 0.5
6 80
5 40
10 5
0.5 0.38
NS
NS
NS
NS
Groundwater VI Commercial ESL
6,300
23 9.8
210
NS
2.8 4,900
920
7.5 0.14
8,000
NS
NS
NS
NS
Location
Sample Name
Original Sample
Name
Sample Date
pg/I
pg/I
pg/I
µg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
pg/I
Monitoring Wells
MW -10
MW -10_022090
MW10-2-90
02/20/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
N,
130,000
ND U
NA
NA
NA
NA
NA
MW -10_060890
MW10
06/08/1990
ND U
ND U
ND U
43,000
ND U
ND U
ND U
ND U
270,000
ND U
NA
NA
NA
NA
NA
MW -10_080494
MW10
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
270,000
ND U
NA
NA
NA
NA
NA
MW -10_121498
MW -10
12/14/1998
ND U
64 NA
15,000
NA
ND U
ND U
ND U
530,000
ND U
NA
NA
NA
NA
NA
MW -10_062921
MW10
06/29/2021
ND U
ND U
ND U
2,000
ND U
ND U
ND U
ND U
83,000
ND U
NA
56,000
NA
NA
NA
MW 11
MW -11_020390
MW11-2-90
02/03/1990
ND U
ND U
ND U
NA
ND U
ND U
ND U
NA
290
ND U
NA
NA
NA
NA
NA
MW -11_060790
MW11
06/07/1990
ND U
ND U
ND U
8.9 ND U
ND U
ND U
ND U
54 ND U
NA
NA
NA
NA
NA
MW -11_080494
MW11
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
20 ND U
NA
NA
NA
NA
NA
MW -11_121598
MW -11
12/15/1998
ND U
ND U
NA
1.3 NA
ND U
ND U
ND U
38 ND U
NA
NA
NA
NA
NA
MW -12
MW -12_060890
MW12
06/08/1990
170
ND U
ND U
8,500
ND U
ND U
ND U
ND U
3,600
ND U
NA
NA
NA
NA
NA
MW -12_080494
MW12
08/04/1994
ND U
ND U
ND U
NA
ND U
ND U
NA
ND U
4,600
ND U
NA
NA
NA
NA
NA
MW -12_121498
MW -12
12/14/1998
ND U
ND U
NA
4,200
NA
ND U
ND U
ND U
3,200
ND U
NA
NA
NA
NA
NA
MW -18D
MW -18D_060890
MW -18D
06/08/1990
ND U
ND U
ND U
1,300
ND U
ND U
ND U
ND U
80 ND U
NA
NA
NA
NA
NA
Notes:
Historical data from the following reports:
Monitoring Well Investigation Report, Former Semco Twist Drill & Tool Company, 2936 Industrial Parkway, Santa Maria, California , dated 16 July 2021 by Analytical Consulting Group, Inc. 2003 Third Quarter Report For Groundwater Monitoring Activities at 2936 Industrial Parkway, APNs 111-291-027 & 028, Santa Maria, California dated 24 February 2004 by Everest Services, Inc.
Semi Annual Report of Groundwater Monitoring, SEMCO Twist Drill and Tool Company, Santa Maria, California dated December 1998 by Tetra Tech, Inc.
SEMCO Groundwater Remediation System Repair and Maintenance -Status Report, 2936 Industrial Parkway, Santa Maria, California, Contract No. 91-T0087, Task Order No. 3-087-1.0-300478 dated 19 August 1994 by Tetra Tech, Inc.
Shallow and Deep Ground -water Investigation SEMCO Twist Drill and Tool Company Facility, Santa Maria, California dated July 1990 by ERC Environmental and Energy Services Co.
Supplemental Subsurface Investigation, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California dated March 1990 by ERC Environmental and Energy Services Co.
Subsurface Investigation: Phase 2, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California dated December 1989 by ERC Environmental and Energy Services Co.
Subsurface Investigation SEMCO Twist Drill and Tool Company, Santa Maria, California dated January 1989 by WESTEC Services Groundwater results were compared to San Francisco Bay RWQCB Groundwater Direct Exposure ESL - MCL Priority and Vapor Intrusion Human Health Risk Levels - Commercial ESL, Lower of Cancer Risk and Noncancer Hazard Values (July 2019) CAS - Chemical Abstract Service
ESL - Environmental Screening Level
MCL - Maximum Contaminant Level
NA - Not Analyzed or Not Available (Historical Data)
ND - Not detected
NS - No standard
RWQCB - Regional Water Quality Control Board
pg/I - micrograms per liter
Qualifiers:
U -The analyte was analyzed for, but was not detected at a level greater than or equal to the RL Exceedance Summary:
1 - Result exceeds Groundwater Direct Exposure ESL - MCL Priority 1 - Result exceeds Groundwater Vapor Intrusion Commercial ESL
LANIAN
Table C2
Historical Soil Analytical Data
SEMCO, Santa Maria, California
781016901
Attachment B September2025
Analyte
Volatile Organic Compounds
Semi -
Volatile
Organic
Compounds
Petroleum Hydrocarbons
Metals
1,1,1-Trichloroethane
m
s
o
O
U
IT
N
1,2-Dichloroethane
Cis-1,2-Dichloroethene
Dibromochlorometha ne
Tetrachloroethene (PCE)
a
N
S
Ip
Total 1, 2-Dichloroethene
(Cis and Trans)
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
1,4-Dioxane (P-Dioxane)
Petroleum Hydrocarbons
(C04 -C12) GRO
Petroleum Hydrocarbons
(C13 -C22) DRO
Petroleum Hydrocarbons
(C23 -C40) ORO
Total Petroleum
Hydrocarbons
Arsenic
Barium
Beryllium
Cadmium
Chromium, Total
Cobalt
Copper
0 J
Mercury
Molybdenum
U
U
z
Vanadium
U
C
N
CAS Number
71-55-6
79-00-5
107-06-2
156-59-2
124-48-1
127-18-4
108-88-3
540-59-0
156-60-5
79-01-6
75-01-4
123-91-1
PHCC4C12
PHCC13C22
PHCC23C40
TPH
7440-38-2
7440-39-3
7440-41-7
7440-43-9
7440-47-3
7440-48-4
7440-50-8
7439-92-1
7439-97-6
7439-98-7
7440-02-0
7440-62-2
7440-66-6
Leaching to Groundwater ESL
7 0.076
0.007
0.19 0.35
0.08 3.2
NS
0.65 0.085
0.0015
0.00017
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
Soil Direct Exposure Commercial/Industrial ESL
7,300
5.1 2.1
85 39
2.7 5,300
NS
600
6.1 0.15
22 2,000
1,200
NS
NS
0.31 220,000
230
1,100
NS
350
47,000
320
190
5,800
11,000
5,800
350,000
Soil Direct Exposure Construction Worker: Any Land Use ESL 7,200
6.3 45
78 290
33 4,700
NS
570
18 3.4
210
NS
NS
NS
NS
0.98 3,000
27 51
NS
28 14,000
160
44 1,800
86 470
110,000
Location
Sample Name
p
Original
Sample Name
Sample
Date
Sample
Depth
mg/kg
9/ g
mg/kg
9 g
mg/kg
g g
mg/kg
9/ 9
mg/kg
g g
mg/kg
9 g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Historic Soil Investigations (1986-1991)
B1
B1-1_6.0-6.5_110988
B1-1
11/09/1988
6-6.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
01 U<0.01
U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B1-2_11.0-11.5_110988
B1-2
11/09/1988
11-11.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
0.23 <0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B2
B2-1_1.5-2.0_110988
B2-1
11/09/1988
1.5-2
<2 U
<2 U
<2 U
NA
<2 U
<2 U
NA
NA
<2 U
170
<2 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B2-2_6.0-6.5_110988
B2-2
11/09/1988
6-6.5
<20 U
<20 U
<20 U
NA
<20 U
<20 U
NA
NA
<20 U
1,800
-.20 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B3
B3-3_11.0-11.5_110988
B3-3
11/09/1988
11-11.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
0.12 0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B4
B4-2_5.5-6.0_110988
B4-2
11/09/1988
5.5-6
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
0.3 0.49
0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B4-3_11.0-11.5_110988
B4-3
11/09/1988
11-11.5
<0.04 U
<0.04 U
<0.04 U
NA
<0.04 U
<0.04 U
NA
NA
<0.it.-I
6.3 11.04 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B5
B5-1_2.0-2.5_110988
B5-1
11/09/1988
2-2.5
<100 U
<100 U
<100 U
NA
<100 U
<100 U
NA
NA
<100 U
7,400
. 100 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B5-2_5.5-6.0_110988
B5-2
11/09/1988
5.5-6
<100 U
<100 U
<100 U
NA
<100 U
<100 U
NA
NA
<100 U
4,500
.100 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
66 B6-1_2.0-2.5_110988
B6-1
11/09/1988
2-2.5
<0.5 U
<0.5 U
<0.5 U
NA
<0.5 U
<0.5 U
NA
NA
<0.5 U
38 :0.5 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B6-2_6.0-6.5_110988
B6-2
11/09/1988
6-6.5
<20 U
<20 U
<20 U
NA
<20 U
<20 U
NA
NA
<20 U
1,300
•.20 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B7
B7-1_2.0-2.5_110988
B7-1
11/09/1988
2-2.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
0.52 0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B7-2_6.0-6.5_110988
B7-2
11/09/1988
6-6.5
<0.1 U
<0.1 U
<0.1 U
NA
<0.1 U
0.27 NA
NA
0.1 9.9
.-0.1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B8
B8-2_6.0-6.5_110988
B8-2
11/09/1988
6-6.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
0.046
.r 0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B8-3_11.0-11.5_110988
B8-3
11/09/1988
11-11.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
4.4 :11.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B9
B9-2_6.0-6.5_110988
B9-2
11/09/1988
6-6.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
0.033
0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B10
B10-2_6.0-6.5_110988
B10-2
11/10/1988
6-6.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
0.046
.0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B10-3_11.0-11.5_110988
B10-3
11/10/1988
11-11.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
<0.01 U
0.018
.0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3
DB3-1_40.0-45.5_013190
DB3-1
01/31/1990
40-45.5
<0.05 U
<0.05 U
<0.05 U
NA
<0.05 U
<0.05 U
<0.12 U
66 NA
430
.0.05 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-2_50.0-50.5_013190
DB3-2
01/31/1990
50-50.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.015
NA
0.066
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-3_55.5-56.0_013190
DB3-3
01/31/1990
55.5-56
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-4_60.5-61.0_013190
DB3-4
01/31/1990
60.5-61
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0'01 'lJ
<0.01 U
NA
NA
NA
NA
<1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-5_65.5-66.0_013190
DB3-5
01/31/1990
65.5-66
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
0.017
11.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-6_70.0-70.5_013190
DB3-6
01/31/1990
70-70.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.u1 U
<0.01 U
NA
NA
NA
NA
<1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-7_75.5-76.0_013190
DB3-7
01/31/1990
75.5-76
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-8_82.5-83.0_013190
DB3-8
01/31/1990
82.5-83
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.019
NA
0.03 <0.01 U
NA
NA
NA
NA
3 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB3-9_87.5-88.0_013190
DB3-9
01/31/1990
87.5-88
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
0.014
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
064
DB4-1_40.0-40.5_020290
DB4-1
02/02/1990
40-40.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.017
NA
0.026
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB4-2_45.5-46.0_020290
DB4-2
02/02/1990
45.5-46
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.081
NA
0.2 <0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB4-3_50.0-55.5_020290
DB4-3
02/02/1990
50-55.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
0.019
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB4-4_60.0-60.5_020290
DB4-4
02/02/1990
60-60.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0,01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB4-5_65.5-66.0_020290
DB4-5
02/02/1990
65.5-66
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
0.016
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DB4-6_70.5-71.0_020290
DB4-6
02/02/1990
70.5-71
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA.
NA
DMW 1
DMW-1-1_56.5_112890
DMW1-1
11/28/1990
56.5-56.5
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
0.04 NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-1-2_64.5_112890
DMW1-2
11/28/1990
64.5-64.5
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
0.05 NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-1-3_110.5_112890
DMW1-3
11/28/1990
110.5-110.5
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-1-4_148.5_112990
DMW1-4
11/29/1990
148.5-148.5
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
0.03 NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-3
DMW-3-1_39.0_030791
DMW3-1
03/07/1991
39-39
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-3-2_49.0_030791
DMW3-2
03/07/1991
49-49
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
0.078
NA
<0.01 U
<0,01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-3-3_60.5_030791
DMW3-3
03/07/1991
60.5-60.5
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-3-4_90.0_030791
DMW3-4
03/07/1991
90-90
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0,01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-4
DMW-4-1_39.0_030891
DMW4-1
03/08/1991
39-39
<0.01 U
<0.01 U
<0.01 U
0.02 <0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
0.25 <0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-4-249.0_030891
DMW4-2
03/08/1991
49-49
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U_
0.05 <0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DMW-4-3_68.5_030891
DMW4-3
03/08/1991
68.5-68.5
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0.01 U
<0.01 U
NA
NA.
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
LANGAN
Table C2
Historical Soil Analytical Data
SEMCO, Santa Maria, California
781016901
Attachment B September2025
Analyte
Volatile Organic Compounds
Semi -
Volatile
Organic
Compounds
Petroleum Hydrocarbons
Metals
1,1,1-Trichloroethane
m
s
o
O
U
I-
N
1,2-Dichloroethane
Cis-1,2-Dichloroethene
Dibromochlorometha ne
Tetrachloroethene (PCE)
a
N
S
Ip
Total 1, 2-Dichloroethene
(Cis and Trans)
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
1,4-Dioxane (P-Dioxane)
Petroleum Hydrocarbons
(C04 -C12) GRO
Petroleum Hydrocarbons
(C13 -C22) DRO
Petroleum Hydrocarbons
(C23 -C40) ORO
Total Petroleum
Hydrocarbons
Arsenic
Barium
Beryllium
Cadmium
Chromium, Total
Cobalt
Copper
0 J
Mercury
Molybdenum
U
U
z
Vanadium
U
C
N
CAS Number
71-55-6
79-00-5
107-06-2
156-59-2
124-48-1
127-18-4
108-88-3
540-59-0
156-60-5
79-01-6
75-01-4
123-91-1
PHCC4C12
PHCC13C22
PHCC23C40
TPH
7440-38-2
7440-39-3
7440-41-7
7440-43-9
7440-47-3
7440-48-4
7440-50-8
7439-92-1
7439-97-6
7439-98-7
7440-02-0
7440-62-2
7440-66-6
Leaching to Groundwater ESL
7 0.076
0.007
0.19 0.35
0.08 3.2
NS
0.65 0.085
0.0015
0.00017
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
Soil Direct Exposure Commercial/Industrial ESL
7,300
5.1 2.1
85 39
2.7 5,300
NS
600
6.1 0.15
22 2,000
1,200
NS
NS
0.31 220,000
230
1,100
NS
350
47,000
320
190
5,800
11,000
5,800
350,000
Soil Direct Exposure Construction Worker: Any Land Use ESL 7,200
6.3 45
78 290
33 4,700
NS
570
18 3.4
210
NS
NS
NS
NS
0.98 3,000
27 51
NS
28 14,000
160
44 1,800
86 470
110,000
Location
Sample Name
p
Original
Sample Name
Sample
Date
Sample
Depth
mg/kg
9/ g
mg/kg
g g
mg/kg
g/ g
mg/kg
9/ g
mg/kg
g/ g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
Historic Soil Investigations (1986-1991)
NB23
NB23-1_1.5-2.0_020390
NB23-1
02/03/1990
1.5-2
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB23-2_6.5-7.0_020390
NB23-2
02/03/1990
6.5-7
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.038
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
5,600
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB23-3_10.0-10.5_020390
NB23-3
02/03/1990
10-10.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.15 NA
<0.01 U
<0.01 U
NA
NA
NA
NA
1,900
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB23-4_15.0-15.5_020390
NB23-4
02/03/1990
15-15.5
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.02 NA
<0,01 U
<0.01 U
NA
NA
NA
NA
2 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB24
N824-1_1.5-2.0_020390
NB24-1
02/03/1990
1.5-2
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB24-2_5.5-6.0_020390
NB24-2
02/03/1990
5.5-6
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
0.016
NA
0.042
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB24-3_10.5-11.0_020390
NB24-3
02/03/1990
10.5-11
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
<0.025 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
2 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB31
NB31-1_5.5-6.0_052990
NB31-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NIA
NA
NA
NA
NA
NA
NA
<1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB31-2_10.5-11.0_052990
NB31-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
18,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB32
NB32-1_5.5-6.0_052990
NB32-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
230
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB32-2_10.5-11.0_052990
NB32-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NIA
NA
NA
NA
NA
NA
NA
1,700
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB33
NB33-1_5.5-6.0_052990
NB33-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
<1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB33-2_10.5-11.0_052990
NB33-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
._c1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB34
NB34-1_5.5-6.0_052990
NB34-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB34-2_10.5-11.0_052990
NB34-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8,300
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB35
NB35-1_5.5-6.0_052990
NB35-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NIA
NA
NA
NA
NA
NA
NA
U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB35-2_10.5-11.0_052990
NB35-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1,400
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
N636
NB36-1_5.5-6.0_052990
NB36-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
110
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB36-2_10.5-11.0_052990
NB36-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NIA
NA
NA
NA
NA
NA
NA
< I
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB37
NB37-1_5.5-6.0_052990
NB37-1
05/29/1990
5.5-6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
62 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB37-2_10.5-11.0_052990
NB37-2
05/29/1990
10.5-11
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
<1 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
N839
N839-1_5.5-6.0_053090
NB39-1
05/30/1990
5.5-6
<0.01 U
<0.01 U
<0.01 U
NA
<0.01 U
<0.01 U
NA
<0.01 U
NA
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
N641
NB41-2_39.5-40.0_053190
NB41-2
05/31/1990
39.5-40
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB41-5_110.5-111.0_060190
NB41-5
06/01/1990
110.5-111
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
<0.01 U
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
N642
NB42-2_49.5-50.0_060490
NB42-2
06/04/1990
49.5-50
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
0.035
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB43
NB43-1_59.5-60.0_060690
NB43-1
06/06/1990
59.5-60
<0.01 U
<0.01 U
<0.01 U
0.037
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
0.18 <0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NB43-2_169.5-170.0_060896
NB43-2
06/08/1990
169.5-170
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.01 U
<0.025 U
NA
<0.01 U
0.021
<0.01 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SB-1
SB-1_6.0-6.5_030288
SB-1
03/02/1988
6-6.5
<5 U
<5 U
<5 U
NA
<5 U
<5 U
<5 U
NA
45 <5 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SB-2
SB-2_11.0-11.5_030288
SB-2
03/02/1988
11-11.5
<5 U
<5 U
<5 U
NA
<5 U
<5 U
<5 U
NA
18 <5 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SB-3
SB-3_15.5-16.0_030288
SB-3
03/02/1988
15.5-16
<0.05 U
<0.05 U
0.23 NA
<0.05 U
<0.05 U
<0.05 U
NA
<0.05 U
<0.05 U
<0.05 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SB-4
SB-4_20.5-21.0_030288
SB-4
03/02/1988
20.5-21
<0.05 U
<0.05 U
<0.05 U
NA
<0.05 L1
<0.05 U
<0.05 U
NA
0.51 <0.05 IJ
<0.05 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SP -1
SP -1_0.75_060391
SP -1
06/03/1991
0.75-0.75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
921
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SP -2
SP -2_0.75_060391
SP -2
06/03/1991
0.75-0.75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
905
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SP -3
SP -3_0.75_060391
SP -3
06/03/1991
0.75-0.75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SP -4
SP -4_0.75_060391
SP -4
06/03/1991
0.75-0.75
NA
NA
NA
NA
NA
NA
NA
NA
NIA
NA
NA
NA
NA
NA
NA
NA
NA
1,030
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
LANGAN
Table C2
Historical Soil Analytical Data
SEMCO, Santa Maria, California
781016901
Attachment B September2025
Analyte
Volatile Organic Compounds
Semi -
Volatile
Organic
Compounds
Petroleum Hydrocarbons
Metals
1,1,1-Trichloroethane
m
s
o
O
U
IT
N
1,2-Dichloroethane
Cis-1,2-Dichloroethene
Dibromochlorometha ne
Tetrachloroethene (PCE)
a
N
S
l-
Total 1, 2-Dichloroethene
(Cis and Trans)
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
1,4-Dioxane (P-Dioxane)
Petroleum Hydrocarbons
(C04 -C12) GRO
Petroleum Hydrocarbons
(C13 -C22) DRO
Petroleum Hydrocarbons
(C23 -C40) ORO
Total Petroleum
Hydrocarbons
Arsenic
Barium
Beryllium
Cadmium
Chromium, Total
Cobalt
Copper
0 J
Mercury
Molybdenum
U L'
U
z
Vanadium
C
N
CAS Number
71-55-6
79-00-5
107-06-2
156-59-2
124-48-1
127-18-4
108-88-3
540-59-0
156-60-5
79-01-6
75-01-4
123-91-1
PHCC4C12
PHCC13C22
PHCC23C40
TPH
7440-38-2
7440-39-3
7440-41-7
7440-43-9
7440-47-3
7440-48-4
7440-50-8
7439-92-1
7439-97-6
7439-98-7
7440-02-0
7440-62-2
7440-66-6
Leaching to Groundwater ESL
7 0.076
0.007
0.19 0.35
0.08 3.2
NS
0.65 0.085
0.0015
0.00017
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
Soil Direct Exposure Commercial/Industrial ESL
7,300
5.1 2.1
85 39
2.7 5,300
NS
600
6.1 0.15
22 2,000
1,200
NS
NS
0.31 220,000
230
1,100
NS
350
47,000
320
190
5,800
11,000
5,800
350,000
Soil Direct Exposure Construction Worker: Any Land Use ESL 7,200
6.3 45
78 290
33 4,700
NS
570
18 3.4
210
NS
NS
NS
NS
0.98 3,000
27 51
NS
28 14,000
160
44 1,800
86 470
110,000
Location
Sample Name
p
Original
Sample Name
Sample
Date
Sample
Depth
mg/kg
9/ g
mg/kg
g g
mg/kg
g/ g
mg/kg
9/ 9
mg/kg
g/ g
mg/kg
9 g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
2022 Soil Investigation
B221
B221_5_032122
B221-5
03/21/2022
5-5
<-0.0043 L<0.0043
L:0.0043
L
1.5 <0.0043 L
0.019
,0,00431
NA
:0.0043 l
10 00431
<0.1 U
160
660
3,100
NA
<1 '2
17 <0.47 U
<0.23 U
2.4 0.81
2.1 1.6
0.02J
<0.47 U
1.4 5.3
5.9 B221_10_032122
B221-10
03/21/2022
10-10
<0.27 U
<0.27 U
<0.27 U
6 <0.27 U
<0.27 U
<0.27 U
NA
<0.27 U
4.8 .2.27 U
<0.1 U
<27 U
<10 U
<50 U
NA
T.3 J
39 <0.49 U
<0-25 U
5 3
4.4 2.8
0.04 J
<0.49 U
6.9 8,5
9.6 B221_15_032122
B221-15
03/21/2022
15-15
<2 U
<2 U
<2 U
12 <2 U
<2 U
<2 U
NA
<2 U
75 <2 U
<0.1 U
<200
<9.9 U
<50 U
N2
1.1 J
26 <0.47 U
<0.23 U
4.2 0.96
3.8 2.2
0.036 J
<0.47 U
4.3 6
7.8 B221_20_032122
B221-20
03/21/2022
20-20
<2.8 U
<2.8 U
<2-8 U
2.4J
<2.8 U
<2.8 U
<2.8 U
NA
<2.8 U
97 ?.8 U
<0.1 U
<280 U
<10 U
<50 U
NA
<1.9 U
52 0.27 J
<0.23 U
8.8 1.7
4.6 4.6
0.084 J
<0-47 U
11 10
20 B221_25_032122
B221-25
03/21/2022
25-25
<0.15 U
<0.15 U
<0.15 U
1.8 <0.15 U
<0.15 U
<0.15 U
NA
<0.15 U
8.5 0.15 U
0.049 J
47 <9.9 U
<50 U
NA
<2 U
30 <0.49 U
<0.25 U
5.6 2.8
4.6 2.8
0.032 J
<0.49 U
5.9 12
12 B221_30_032122
B221-30
03/21/2022
30-30
<0.17 U
<0.17 U
<0.17 U
0.12 J
<0.17 U
<0.17 U
<0.17 U
NA
<0.17 U
3.1 0.17 U
<0.099 U
<17 U
<9.9 U
<50 U
NA
<1.9 U
10 <0.48 U
<0.24 U
3 0.62
1.9 1.4
0.022 J
<0.48 U
1.7 3
4.9 B221_35_032122
B221-35
03/21/2022
35-35
<2.3 U
<2.3 U
<2.3 U
2.5 <2.3 U
<2.3 U
<2.3 U
NA
<2.3 U
15 2.3 U
<0.1 U
<230 U
<10 U
<50 U
NA
<1.9 U
27 <0.48 U
<0.24 U
5.5 2.2
4.7 2.9
0.026 J
<0.48 U
4.8 8.5
11 B221_40_032122
B221-40
03/21/2022
40-40
<0.32 U
<0.32 U
<0.32 U
0.75 <0.32 U
<0.32 U
<0.32 U
NA
<0.32 U
_ 20
<.32 U
<0.1 U
19 J
<10 U
<50 U
NA
_
53 0.49
<0-24 U
13 2.9
13 5
0.052 J
1.2 23
46 35
B221_45_032122
B221-45
03/21/2022
45-45
<0.19 U
<0.19 U
<0.19 U
0.31 <0.19 U
<0.19 U
<0.19 U
NA
<0.19 U
5.1 0 19 U
<0.099 U
<19 U
<9.9 U
<50 U
NA
36 <0.47 U
<0-24 U
8.9 2
8.7 3.1
0.039 J
0.54 10
15 28
B221_50_032122
B221-50
03/21/2022
50-50
<0.19 U
<0.19 U
<0.19 U
0.33 <0.19 U
<0.19 U
<0.19 U
NA
<0.19 U
9.5 .0 .19 U
<0.1 U
8.2J
9.7 J
<50 U
NA
51 <0.5 U
<0-25 U
13 4.5
7.8 4.6
0.058 J
0.47 J
10 19
24 B222
B222_5_032122
8222-5
03/21/2022
5-5
<0.0054 L:0.00541:0.0054
L<0.0054
L<0.0054
L<0.0054
L(0.00541
NA
<0.0054 l
0 UU..'
.0 00541
<0.1 U
<0.54 U
<10 U
<50 U
NA
14 <0.46 U
<0.23 U
2.7 1.2
1.9 1.3
0.021 J
1.6 1.3
5.7 4.2
B222_10_032122
B222-10
03/21/2022
10-10
<0.0037 1<0.0037
l<0-00371.<0
0037 l<0.0037
L<0.0037
L:0.0037
L
NA
<0.0037 L
0.0037
:0.0037 1
<0.1 U
<0.37 U
<10 U
<50 U
NA
<1 9 U
35 <0.48 U
<0.24 U
4.6 2.6
3.3 2.2
0.066 J
<0-48 U
4.5 6.5
7.1 B222_15_032122
B222-15
03/21/2022
15-15
:0.0036 L<0.0036
L(0.0036
L<0.0036
L<0.0036
L<0.0036
L(0.0036
l
NA
<0.0036 L
0.0036
0.0036'
<0.1 U
<0.36 U
<10 U
<50 U
NA
<1.9 U
32 <0.48 U
<0.24 U
5 0.77
3.9 2.6
0.033 J
<0.48 U
4.7 5.6
8.3 B222_20_032122
B222-20
03/21/2022
20-20
<0.003 U
<0.003 U
<0.003 U
<0.003 U
<0.003 U
<0.003 U
<0.003 U
NA
<0.003 U(0.003
l<0.003
l
<0.1 U
<0.3 U
9.4 J
<50 U
NA
<1.8 U
35 <0.46 U
<0.23 U
4.9 1.6
5.9 3.5
0.042 J
<0.46 U
5.2 7.1
14 B222_25_032122
B222-25
03/21/2022
25-25
:0.0032 1<0.0032
L:0.0032
L:0.0032
L<0.0032
1<0.0032
L(0.0032
L
NA
<0.0032 L
0.0032
:0.0032 1
<0.099 U
<0.32 U
<9.9 U
<50 U
NA
<2 U
25 <0.49 U
<0.24 U
4.4 1.3
4.4 3.2
0.036 J
<0.49 U
6.5 6.3
12 B222_30_032122
B222-30
03/21/2022
30-30
<0.0039 l<0.0039
L:0.00391:0.0039
L<0.0039
1<0.0039
L:0.00391
NA
<0.0039 l
0.009
:0.0039 1
<0.1 U
<0.39 U
<10 U
<50 U
NA
<1.9 U
9.1 <0.47 U
<0.23 U
1.8 0.97
1.4 1.3
0.021 J
<0.47 U
1.9 3
5.9 B222_35_032122
B222-35
03/21/2022
35-35
(0.0041 1:0.0041
1<0.0041
1 0.0041
<0.0041 L<0.0041
L<0.0041
L
NA
<0.0041 L
0.02 .0.0041 I
<0 1 U
<0.41 U
<10 U
<50 U
NA
<1-9 U
18 <0.48 U
<0-24 U
4.4 0.48
2.9 2.1
0.023 J
<0.48 U
4.5 5.1
8.8 B222_38_032122
8222-38
03/21/2022
38-38
(0.0044 L<0.0044
1:0.0044
L
0.022
<0.0044 L<0.0044
Lc0.0044
I
NA
<0.0044 L
0.44 :0.0044 I
NA
<0.44 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B222_40_032122
8222-40
03/21/2022
40-40
<0.0038 l<0.0038
l<0.0038
L
0.014
<0.0038 1<0.0038
L(0.0038
L
NA
<0.0038 l
0.11 :0.00381
<0.099 U
<0.38 U
<9.9 U
<50 U
NA
1.1 J
37 <0.48 U
<0.24 U
6.3 5.3
7.2 4.2
0.032 J
<0,48 U
7 16
18 B222_45_032122
B222-45
03/21/2022
45-45
<0.3 U
<0.3 U
<0.3 U
0.5 <0.3 U
<0.3 U
<0.3 U
NA
<0.3 U
16.1 <0.3 U
<0.1 U
<30 U
<10 U
<50 U
NA
10 63
<0.49 U
<0.24 U
13 3.6
17 7.2
0.051 J
1.3 17
27 51
8222_50_032122
8222-50
03/21/2022
50-50
<0.18 U
<0.18 U
<0.18 U
0.22 <0.18 U
<0.18 U
<0.18 U
NA
<0.18 U
3.6 0.18 U
<0.099 U
<18 U
<9.9 U
<50 U
NA
4_4
42 <0.5 U
<0.25 U
9.4 3.1
6.9 5.5
0.032 J
0.36 J
9.8 17
21 6223
B223_5_032122
B223-5
03/21/2022
5-5
<0.0023 L<0.0023
L<0.0023
l
0.018
<0.0023 2<0.0023
L(0.0023
L
NA
<0.0023 L
0.56 0 0023'
<0.1 U
<0.23 U
130
960
NA
2.6 40
<0.48 U
<0.24 U
6.9 1.8
11 2.6
0.026 J
1.2 7.8
11 18
B223_10_032122
B223-10
03/21/2022
10-10
:0.0034 L<0.0034
1:0.0034
L
0.061
<0,0034 2<0.0034
L:0.0034
l
NA
<0.0034 1
0.39 0.0034'
<0.1 U
0.14J
<10 U
<50 U
NA
1.7 J
38 <0.49 U
<0.24 U
5.5 1.4
4.5 3.4
0.039 J
<0.49 U
4.8 9.8
10 B223_15_032122
8223-15
03/21/2022
15-15
<0.18 U
<0.18 U
<0.18 U
0.35 <0.18 U
<0.18 U
<0.18 U
NA
<0.18 U
2.1 -0.18 U
<0.099 U
<18 U
<9.9 U
<50 U
NA
1.3 J
24 <0.5 U
<0.25 U
3.9 1.3
3.6 2.9
0.026 J
<0.5 U
4 6
8.1 B223_20_032122
B223-20
03/21/2022
20-20
<016 U
<0.16 U
<0.16 U
0.37 <0.16 U
<0.16 U
<0.16 U
NA
<0.16 U
2.6 .0.16 U
<0.1 U
<16 U
<10 U
<50 U
NA
1.1 J
25 <0.47 U
<0.23 U
5 1.2
4.2 2.6
0.015 J
<0.47 U
4.7 6.7
9.4 B223_25_032122
8223-25
03/22/2022
25-25
<0.19 U
<0.19 U
<0.19 U
1 <0.19 U
<0.19 U
<0.19 U
NA
<0.19 U
6.5_4
<0.19 U
<0.1 U
<19 U
<10 U
<50 U
NA
1.1 J
22 <0.48 U
<0-24 U
4.2 0.64
3.5 2.8
0.011 J
<0.48 0
3.9 8.5
9 B223_30_032122
8223-30
03/22/2022
30-30
<0.16 U
<0.16 U
<0.16 U
0.24 <0.16 U
<0.16 U
<0.16 U
NA
<0.16 U
2.6 <0.16 U
<0.1 U
<16 U
<10 U
<50 U
NA
15 <0.49 U
<0.25 U
2.6 0.44 J
2.7 2.1
0.0092 J
<0,49 U
2.7 4
5.8 B223_35_032122
B223-35
03/22/2022
35-35
<0.2 U
<0.2 U
<0.2 U
0.57 <0.2 U
<0.2 U
<0.2 U
NA
<0.2 U
3.3 <0.2 U
<0.1 U
<20 U
<10 U
<50 U
NA
21 <0.48 U
<0.24 U
4.8 2.2
3.5 2.8
<0.088 U
<0.48 U
5.2 5.6
9.9 B223_40_032122
8223-40
03/22/2022
40-40
<0.21 U
<0.21 U
<0.21 U
1.4 <0.21 U
<0.21 U
<0.21 U
NA
<0.21 U
3.8 <0.21 U
<0.1 U
<21 U
<10 U
<50 U
NA
1.4 J
36 <0.46 U
<0.23 U
7.5 2
5.9 4.4
0.029 J
<0.46 U
6.6 16
17 B223_45_032222
8223-45
03/22/2022
45-45
<0.22 U
<0.22 U
<0.22 U
0.42 <0.22 U
<0.22 U
<0.22 U
NA
<0.22 U
1.8 <0.22 U
<0.1 U
<22 U
<10 U
<50 U
NA
4J
90 <0.5 U
<0.25 U
8.2 15
12 9.3
0.037 J
1 20
20 38
B223_50_032222
B223-50
03/22/2022
50-50
:0.00571
: 0 0057 1<0.0057
l
0.61 <0.0057 L<0.0057
1<0.0057
1 NA
<0.0057 L
1.9 :0.0057 1
<0.1 U
0.51 J
<10 U
<50 U
NA
4.1 36
<0.49 U
<0.24 U
10 5
7.3 4.5
0.024 J
0.55 13
18 22
B224
B224_5_032322
8224-5
03/23/2022
5-5
:0.003:
0033 L(0.0033
L<0.0033
L<0.0033
L<0.0033
L:0.0033
L
NA
<0.0033 L
0.0033
.0.0033 I
<0.099 U
<0.33 U
<9.9 U
<50 U
NA
1 J
12 <0.5 U
<0.25 U
2.6 0.65
2.1 1.3
<0 088 U
0.27 J
1.4 6
4.4 B224_10_032322
B224-10
03/23/2022
10-10
:0.003-
0037 1(0.0037
1<0.0037
l<0.0037
2<0.0037
1:0.0037
L
NA
<0.0037 2
0.0037
:0.00371
<0.1 U
<0.37 U
<10 U
<50 U
NA
1.2 J
49 <0.46 U
<0-23 U
5.5 2.8
4.1 2.8
0.023 J
<0.46 U
6.2 8
9.6 B224_15_032322
8224-15
03/23/2022
15-15
<0.003<
0033 L(0.0033
L<0.0033
L<0.0033
1<0.0033
1:0.0033
l
NA
<0.0033 L
0.0033
:0.0033 I
<0.1 U
<0.33 U
<10 U
<50 U
NA
1.5 J
42 <0.47 U
<0-24 U
7.8 3.6
6.8 3.3
0.024 J
<0.47 U
8.4 17
17 B224_20_032322
B224-20
03/23/2022
20-20
<0.002._
0029 1<0.0029
l<0.0029
L<0.0029
L<0.0029
L(0.0029
L
NA
<0.0029 1
0.0029
:0.00291
<0.099 U
<0.29 U
<9.9 U
<50 U
NA
_ 0.94 0
55 <0.45 U
<0.23 U
6.5 3.4
4.6 4.4
0.024 J
<0,45 U
6.8 11
16 B224_25_032322
B224-25
03/23/2022
25-25
<0.003 ,.
0.003 U
<0.003 U
0.0038
<0.003 U
<0.003 U
<0.003 U
NA
<0.003 U
0.056
<0.003 L
<0.099 U
<0.3 U
<9.9 U
<50 U
NA
25 <0.46 U
<0.23 U
4.9 1.7
3.1 2.2
0.017 J
<0.46 U
4.8 9.3
11 B224_30_032322
8224-30
03/23/2022
30-30
(0.0031 l<0.0031 L:0.0031 L
0.0025)
<0.0031 1<0.0031 L(0.0031 L
NA
<0.0031 1
0.018
:0.0031 I
<0.1 U
<0.31 U
<10 U
<50 U
NA
<1.42
8.9 <0.46 U
<0.23 U
2.1 0.42
1.8 0.96
<0 083 U
<0.46 U
1.5 3.1
4.1 B224_35_032322
8224-35
03/23/2022
35-35
;0.0025 1<0.0025 1(0.0025 L
0.0091
<0.0025 L<0.0025 L:0.0025 L
NA
<0.0025 L
0.074
.0.0025 i
<0.1 U
<0.25 U
<10 U
<50 U
N
<2.4 U
22 <0.48 U
<0.24 U
4 1.6
3.6 2.3
0.014 J
<0.48 U
4.3 5.2
8.4 B224_40_032322
B224-40
03/23/2022
40-40
_0.0027 l<0.0027 L<0.0027 l
0.012
<0.0027 L<0.0027 1:0.0027 l
NA
<0.0027 L
0.1 :0.00271
<0.1 U
<0.27 U
<10 U
<50 U
Nr
3.7 54
<0.48 U
<0.24 U
8.4 2.7
9.1 3.8
0.052 J
0.57 18
43 27
B224_45_032322
B224-45
03/23/2022
45-45
:0.0037 l<0.0037 1(0.0037 L
0.034
<0.0037 1<0.0037 L:0.0037 L
NA
<0.0037 2
0.26E
.0.00371
NA
0.21 J
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
NA
NA
B224_46.5_032322
8224-46.5
03/23/2022
46.5-46.5
:0.0049 l<0.0049 L<0.0049 1:0.0049
1<0.0049
2<0.0049 1<0.0049 1
NA
<0.0049 1
0.0049
0.0049 I
<0.099 U
<0.49 U
<9-9 U
<50 U
NA
_ 7.3
85 <0.47 U
<0.23 U
14 5.9
17 6.1
0.038 J
1.3 20
29 54
B224_50_032322
8224-50
03/23/2022
50-50
:0.0029 L<0.0029 1(0.0029 1
0.023
<0.0029 L<0.0029 1<0.0029 1
NA
<0.0029 L
0.57 ;0.00291
<0 1 U
0.16'J
<10 U
<50 U
NA
4.6 51
<0.49 U
<0.25 U
98 4.7
8.2 4.1
0.019 J
0.62 11
19 23
LANGAN
Table C2
Historical Soil Analytical Data
SEMCO, Santa Maria, California
781016901
Attachment B September2025
Analyte
Volatile Organic Compounds
Semi -
Volatile
Organic
Compounds
Petroleum Hydrocarbons
Metals
1,1,1-Trichloroethane
m
s
o
O
U
IT
N
1,2-Dichloroethane
Cis-1,2-Dichloroethene
Dibromochlorometha ne
Tetrachloroethene (PCE)
a
1p
Total 1, 2-Dichloroethene
(Cis and Trans)
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
1,4-Dioxane (P-Dioxane)
Petroleum Hydrocarbons
(C04 -C12) GRO
Petroleum Hydrocarbons
(C13 -C22) DRO
Petroleum Hydrocarbons
(C23 -C40) ORO
Total Petroleum
Hydrocarbons
Arsenic
Barium
Beryllium
Cadmium
Chromium, Total
Cobalt
Copper
J
Mercury
Molybdenum
U
U
z
Vanadium
a
C
N
CAS Number
71-55-6
79-00-5
107-06-2
156-59-2
124-48-1
127-18-4
108-88-3
540-59-0
156-60-5
79-01-6
75-01-4
123-91-1
PHCC4C12
PHCC13C22
PHCC23C40
TPH
7440-38-2
7440-39-3
7440-41-7
7440-43-9
7440-47-3
7440-48-4
7440-50-8
7439-92-1
7439-97-6
7439-98-7
7440-02-0
7440-62-2
7440-66-6
Leaching to Groundwater ESL
7 0.076
0.007
0.19 0.35
0.08 3.2
NS
0.65 0.085
0.0015
0.00017
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
Soil Direct Exposure Commercial/Industrial ESL
7,300
5.1 2.1
85 39
2.7 5,300
NS
600
6.1 0.15
22 2,000
1,200
NS
NS
0.31 220,000
230
1,100
NS
350
47,000
320
190
5,800
11,000
5,800
350,000
Soil Direct Exposure Construction Worker: Any Land Use ESL 7,200
6.3 45
78 290
33 4,700
NS
570
18 3.4
210
NS
NS
NS
NS
0.98 3,000
27 51
NS
28 14,000
160
44 1,800
86 470
110,000
Location
Sample Name
p
B225_5_032322
Original
Sample Name
B225-5
Sample
Date
03/23/2022
Sample
Depth
5-5
mg/kg
9/ g
mg/kg
g g
mg/kg
g/ g
mg/kg
9/ g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g g
mg/kg
g
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
mg/kg
2022 Soil Investigation
B225
0 0045 1(0.0045
L(0.0045
L<0.0045
L<0.0045
L<0.0045
1,-0.0045
l
NA
<0.0045 L
0004.5
.0 0045 I
<0.099 U
<0.45 U
<9.9 U
<50 U
NA
t 2_7
38 <0.47 U
<0.24 U
7.8 1.7
3.3 3.2
0.01 J
0.32 J
4.8 15
8.7 B225_10_032322
B225-10
03/23/2022
10-10
0 0044 1(0.0044
L:0.0044
L(0.0044
l<0.0044
L<0.0044
1<0.0044
L
NA
<0.0044 10.0026
,
0 0044 I
<0.1 U
<0.44 U
<10 U
<50 U
NA
F 1.8 J
33 <0.48 U
<0.24 U
5.2 0.39 J
2.5 2.6
0.018 J
<0.48 U
3.8 9.1
5.7 B225_15_032322
B225-15
03/23/2022
15-15
0 0057 L<0.0057
L<0.0057
1:0.0057
1<0,0057
L<0.0057
1<0.0057
1 NA
<0.0057 10.0031
-
: 0057 I
<0.1 U
<0.57 U
<10 U
<50 U
NA
, 1.3 J
37 <0.46 U
<023 U
7.7 1.1
4.7 3.2
0.019 J
<0.46 U
5.8 10
13 B225_20_032322
B225-20
03/23/2022
20-20
0.0036 1<0.0036
1(0.0036
1 0.0063
<0.0036 1<0.0036
L<0.0036
1 NA
<0.0036 1
0.026
! 0036 1
<0.1 U
<0.36 U
<10 U
<50 U
NA
<2 U
27 <0.5 U
<0.25 U
6 8.3
5 2.2
0.019 J
<0.5 U
7.8 14
14 B225_22_032322
8225-22
03/23/2022
22-22
0.0034 1<0.0034
1<0.0034
L
0.0058
<0.0034 1<0.0034
L(0.0034
I
NA
<0.0034 1
0.018
0034 1
NA
<0.34 U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
B225_25_032322
B225-25
03/23/2022
25-25
0.0034 1<0.0034
(<0.0034
1<0.0034
1<0.0034
1<0.0034
1(0.0034
1 NA
<0.0034 10.0029..'
00341
<0.099 U
<0.34 U
<9.9 U
<50 U
NA
<1.9 U
22 <0.49 U
<0.24 U
7 1.8
3.5 2.3
0.017 J
<0.49 U
4.7 6.7
10 B225_30_032322
B225-30
03/23/2022
30-30
- 0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004. U
NA
<0.004 U
0.0019..
.1.004 L
<0.099 U
<0.4 U
<9.9 U
<50 U
NA
<1 9 1 i
7.6 <0.46 U
<0.23 U
2.8 2.9
1.7 1.1
<0.09 U
<0 46 U
1.8 2.6
4 B225_35_032322
B225-35
03/23/2022
35-35
ri 0026 1<0.0026
1<0.0026
L
0.019
<0.0026 1<0.0026
L<0.0026
I
NA
<0.0026 1
0.078
0026 I
<0.1 U
<0.26 U
<10 U
<50 U
NA
21 <0.49 U
<0.25 U
6.5 0.68
4 2.6
0.013 J
I
4.4 6.3
9.7 B225_40_032322
8225-40
03/23/2022
40-40
0 0028 1<0.0028
L<0.0028
1 0.023
<0.0028 L<0.0028
1(0.0028
1 NA
<0.0028 L
0.082
' 0028 I
<0.1 U
<0.28 U
<10 U
<50 U
NA
3.4 68
1 <0.24 U
44 6.1
15 <0.48 U
0.28 5.8
35 190
38 B225_45_032322
B225-45
03/23/2022
45-45
:0 0037 1(0.0037
1<0.0037
1 0.0095
<0,0037 1<0.0037
1(0.0037
1 NA
<0.0037 1
0.018
' 0037 1
<0.1 U
<0.37 U
<10 U
<50 U
NA
3.2 27
<0.49 U
<0.25 U
5.7 2.4
6.1 2.7
0.019J
<li . '
6.9 12
18 B225_50_032322
B225-50
03/23/2022
50-50
0 0029 L<0.0029
1<0.0029
L
0.022
<0.0029 L<0.0029
1,-0.0029
1 NA
<0.0029 1
0.041
a 0029 I
<0.1 U
<0.29 U
18 <50 U
NA
3_4
52 <0.49 U
<0.25 U
7.8 6.7
7.7 4.4
0.022 J
0.48 J
11 15
20 B226
B226_10_032222
B226-10
03/22/2022
10-10
- 0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
NA
<0.004 U
<0.004 1<0.004
1 <0.1 U
<0.4 U
<10 U
<50 U
NA
1.5 J
510
<0.5 U
<0.25 U
4.6 0.72
3.6 3
0.019J
<!
4.6 9.1
8 B226_15_032222
B226-15
03/22/2022
15-15
0.0035 1<0.0035
1<0.0035
1(0.0035
L<0.0035
1<0.0035
L<0.0035
1 NA
<0.0035 L-0.0035
:0.0035 1
<0.099 U
<0.35 U
<9.9 U
<50 U
1 J
320
<0.48 U
<0.24 U
4.5 0.83
4.1 3.4
0.029 J
< 0
4.5 8.3
12 B226_20_032222
B226-20
03/22/2022
20-20
0.0061 1<0.0061
1(0.0061
1,-0.0061
1<0.0061
1<0.0061
1(0.0061
1 NA
<0.0061 L
0.0061
:0.0061 I
<0.1 U
<0.61 U
<10 U
<50 U
2.8 92
0.49 <0.23 U
15 4.4
8.8 6.1
0.043 J
1 22
22 37
B226_25_032222
B226-25
03/22/2022
25-25
0.0044 L(0.0044
1<0.0044
1<0
0044 1.<0.0044
L<0.0044
1<0.0044
1 NA
<0.0044 10.0028,.-0.0044
I
<0.1 U
<0.44 U
<10 U
<50 U
NA
<1.10 U
120
<0.48 U
<0.24 U
2.9 1.3
3.1 2.6
0.0095 J
<0 45 U
3.7 6.6
9.7 B226_30_032222
B226-30
03/22/2022
30-30
:0 0035 1<0.0035
1<0.0035
L
0.0018 J
<0.0035 1<0.0035
L(0.0035
I
NA
<0.0035 1
0.011
:0.0035 I
<0.1 U
<0.35 U
<10 U
<50 U
NA
<1.9 U
470
<0.49 U
<0.24 U
3.9 2.5
4.9 2.5
0.013 J
<0.49 U
5.8 12
12 B226_35_032222
B226-35
03/22/2022
35-35
<0.0045 1<0.0045
L<0.0045
1 0.0034 J
<0.0045 L<0.0045
1(0.0045
1 NA
<0.0045 L
0.024
.0 0045 I
<0.1 U
<0.45 U
<10 U
<50 U
NA
<1.9 U
64 <0.49 U
<0.24 U
3.9 3
3.7 2.3
0.016 J
<0.49 U
4.4 7.5
9.5 B226_40_032222
B226-40
03/22/2022
40-40
<0.0043 1<0.0043
l<0.0043
1 0.0077
<0.0043 1<0.0043
1(0.0043
L
NA
<0.0043 L
0.064
:0.0043 1
<0.1 U
<0.43 U
<10 U
<50 U
NA
220
<0.5 U
0.68 8.6
17 9.3
3.5 0.085
1.1 17
19 27
B226_45_032222
8226-45
03/22/2022
45-45
0 0029 (<0.0029
1:0.0029
1 0.018
<0.0029 L<0.0029
1<0.0029
1 NA
<0.0029 1
0.13 E
:0 0029 I
<0.1 U
0.12 J
<10 U
<50 U
NA
28 <0.48 U
<0.24 U
6.5 1.5
5.8 2.6
0.026 J
0.47 J
8.4 12
22 B226_50_032222
8226-50
03/22/2022
50-50
-0.004 U
<0.004 U
<0,004 U
0.022
<0.004 U
<0.004 U
<0.004 U
NA
<0.004 U
0.1 <0.004 1
<0.1 U
<0.4 U
<10 U
<50 U
NA
44 <0.46 U
<0.23 U
9 3.4
7.8 3.7
0.021 J
0.34 J
10 16
23 B227
B227_5_032322
B227-5
03/23/2022
5-5
0 0029 L<0.0029
1<0.0029
1<0.0029
1<0.0029
1<0.0029
L(0.0029
I
NA
<0.0029 1
0.0029
:0.0029 I
<0.1 U
<0.29 U
<10 U
<50 U
NA
17 <0.48 U
<0.24 U
3.4 0.91
2.7 1.5
<0.089 U
0.49 1.8
5.7 5.3
B227_10_032322
8227-10
03/23/2022
10-10
0.0042 L<0.0042
1<0.0042
L<0.0042
1<0.0042
1<0.0042
L<0.0042
1 NA
<0.0042 1
0.0042
:0.0042 I
<0.1 U
<0.42 U
<10 U
<50 U
NA
38 <0.48 U
<0.24 U
7.4 0.79
5.5 3.1
0.022 J
<0.48 U
6 13
10 B227_15_032322
B227-15
03/23/2022
15-15
0.0028 1<0.0028
1<0.0028
1<0.0028
l<0.0028
L<0.0028
L<0.0028
1 NA
<0.0028 1
0.0028
.0.0028 1
<0.1 U
<0.28 U
<10 U
<50 U
NA
<1 9 U
48 <0.47 U
<0.23 U
14 1.2
6 5.3
0.088 J
<0.47 U
7.5 8,1
13 B227_20_032322
8227-20
03/23/2022
20-20
O 0039 1<0.0039
1<0.0039
1<0.0039
1<0.0039
1<0.0039
L<0.0039
1 NA
<0.0039 1
n r1? <
n 0039 I
<0.1 U
<0.39 U
<10 U
<50 U
NA
<1 8 U
30 <0.46 U
<0.23 U
6.8 1.4
5.4 3.5
0.029 J
<0.46 U
5.8 9.2
13 B227_25_032322
8227-25
03/23/2022
25-25
:0 0039 1<0.0039
1<0.0039
1:0.0039
1<0.0039
1<0.0039
1(0.0039
1 NA
<0.0039 10.0033
-
.' 0039 1
<0.1 U
<0.39 U
<10 U
<50 U
NA
<1.9 U
21 <0.46 U
<0.23 U
4.6 2.9
3.8 2.6
0.017 J
<0.46 U
6.5 6.9
10 B227_30_032322
B227-30
03/23/2022
30-30
0 0028 1<0.0028
1<0.0028
1:0.0028
1<0.0028
1<0.0028
1<0.0028
1 NA
<0.0028 1
0.012
00281
<0.1 U
<0.28 U
<10 U
<50 U
NA
<1.8 U
24 <0.46 U
<0.23 U
4.6 3.3
5.2 2.8
0.011 J
<0.46 U
6.6 7.9
13 B227_35_032322
8227-35
03/23/2022
35-35
0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
<0.004 U
NA
<0.004 100.0031
-
0 004 1
<0.1 U
<0.4 U
<10 U
<50 U
NA
<7 I I
27 <0.49 U
<0.24 U
5.9 7.9
4.6 3
)3 U
<0.49 U
8.6 8.2
12 B227_40_032322
B227-40
03/23/2022
40-40
0.0047 1<0.0047
1(0.0047
1 0.0019 J
<0.0047 L<0.0047
L(0.0047
L
NA
<0.0047 L
0.016
1 00471
NA
<0.47 U
NA
NA
NA
NA
NA
NA
NA
NA
NA.
NA
NA
NA
NA.
['IA
B227_45_032322
8227-45
03/23/2022
45-45
0.0031 1<0.0031
1<0.0031
1 0.006
<0.0031 1<0.0031
1(0.0031
1 NA
<0.0031 1
0.13E
7.0031 1
<0.1 U
0.13 J
<10 U
<50 U
NA
4.6 100
<0.49 U
0.6 16
11 13
7.9 0.046 J
1.5 31
24 49
B227_50_032322
B227-50
03/23/2022
50-50
0.0025 1:0.0025
L(0.0025
1 0.0052
<0.0025 1<0.0025
L<0.0025
1 NA
<0.0025 1
0.096
.0.0025 I
<0.099 U
<0.25 U
<9.9 U
<50 U
NA
1.8 J
32 <0.47 U
<0.23 U
7 2.1
6.8 2.9
0.046 J
0.29 J
14 12
20 B228
8228_5_032222
B228-5
03/22/2022
5-5
<0.005 U
<0 005 U
<0.005 U
<0.005 U
<0.005 U
<0.005 U
<0.005 U
NA
<0.005 U
, UG5 1<0.005
1 <0.1 U
<0.5 U
<10 U
<50 U
NA
1.1 J
13 <0.49 U
<0.25 U
2.3 0.66
1.9 1.4
3.7 1.3
5 4.5
8228_10_032222
8228-10
03/22/2022
10-10
O 0049 1<0.0049
1<0.0049
1<0.0049
L<0.0049
L<0.0049
L(0.0049
1 NA
<0.0049 1
0.0049
:0.0049 1
<0.099 U
<0.49 U
<9.9 U
<50 U
NA
1.7 J
38 <0.47 U
<0.23 U
3.8 1.5
3.4 3
0.042 J
11 5
8.3 8.1
B228_15_032222
8228-15
03/22/2022
15-15
:0 0037 1<0.0037
1<0.0037
1<0.0037
1<0.0037
1<0.0037
1(0.0037
1 NA
<0.0037 l
0.0037
.0.0037 1
<0.1 U
<0.37 U
<10 U
<50 U
NA
28 <0.5 U
<0.25 U
3.4 1
3.6 2.8
0.017 J
1.2 3.7
9.4 9
8228_20_032222
B228-20
03/22/2022
20-20
10033 1<0.0033
1<0.0033
1<0.0033
1<0.0033
1<0
0033 L(0.0033
1 NA
<0.0033 L
0.0033
0.0033 1
<0.1 U
<0.33 U
<10 U
<50 U
NA
1.2 J
23 <0.46 U
<0.23 U
3.4 1.8
4.3 2.7
0.013 J
3.9 8.9
9.1 8228_25_032222
8228-25
03/22/2022
25-25
(0.003 U
<0.003 U
<0.003 U
<0.003 U
<0.003 U
<0.003 U
<0.003 U
NA
<0.003 U
C,' ' I
-: 0 003 1
<0.099 U
0.12 J
<9.9 U
<50 U
NA
1.2 J
24 <0.48 U
<0.24 U
4.2 1.4
5.5 3.2
<0.091 .'
0.34 J
4.6 8.6
11 B228_30_032222
B228-30
03/22/2022
30-30
0.0046 1<0.0046 1(0.0046 L<0.0046
1<0.0046
1<0.0046 1(0 0046 1
NA
<0.0046 1
0.008
.' 0046 1
<0.099 U
<0.46 U
<9.9 U
<50 U
NA
19 <0.49 U
<0.24 U
2.8 1.2
3.4 2.5
<0.08 U
3.2 5.3
9.1 B228_35_032222
8228-35
03/22/2022
35-35
0.0036 1<0.0036 l<0.0036 L
0.0021 J
<0.0036 1<0.0036 1<0.0036 1
NA
<0.0036 1
0.022
0036 1
<0.1 U
<0.36 U
<10 U
<50 U
NA
15 <0.49 U
<0.24 U
3 1.9
2.3 1.6
3.4 4
7.9 8228_40_032222
8228-40
03/22/2022
40-40
:0.0028 1:0.0028 L<0.0028 1
0.0033
<0.0028 L<0.0028 1<0.0028 1
NA
<0.0028 1
0.043
' 0028 I
<0.099 U
<0.28 U
<9.9 U
<50 U
NA
9_5
43 <0.5 U
<0.25 U
11 2.4
7.7 3.4
0.029 J
0.65 13
24 26
B228_45_032222
B228-45
03/22/2022
45-45
_0.0016 1<0.0016 1<0.0016 1
0.0036
<0.0016 1<0.0016 1(0.0016 1
NA
<0.0016 1
0.4 .0.0016 1
<0.1 U
0.132
<10 U
<50 U
NA
6_9
69 <0.47 U
<0.23 U
13 5
15 5.9
0.13 9.1
19 29
50 8228_50_032222
8228-50
03/22/2022
50-50
<0.0028 1<0.0028 L<0.0028 L
0.0024 J
<0.0028 1<0.0028 1(0.0028 1
NA
<0.0028 1
0.055
:0.0028 I
<0.099 U
<0.28 U
<9.9 U
<50 U
NA
3.9 74
<0.47 U
1.3 7.8
6.3 8.4
6 0.03 J
0.74 18
20 23
LANGAN
Table C2
Historical Soil Analytical Data
SEMCO, Santa Maria, California
Notes:
Historical data from the following reports:
Site Assessment Report, Vadose Zone Soil Sampling, Former SEMCO Twist Drill & Tool Company, 2936 Industrial Parkway, Santa Maria, California dated 25 May 2022 by Analytical Consulting Group, Inc.
Results of Soil Sampling Beneath the Concrete Pond Structure Located at the SEMCO Facility, Santa Maria, California dated 3 December 1991 by ERC Environmental and Energy Services Co. Inc.
Supplementary Subsurface Investigation, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California dated March 1990 by ERC Environmental and Energy Services Co.
Subsurface Investigation Letter Report, SEMCO Twist Drill and Tool Company, Santa Maria, California dated 1 April 1988 by WESTEC Services, Inc.
CAS - Chemical Abstract Service
ESL - Environmental Screening Level
mg/kg - Milligrams per kilogram
NA - Not Analyzed or Not Available (Historical Data)
NS - No standard
Only detected results were reported for metals data
RL - Reporting Limit
` irl 6901
September 2025
LANGAN
Table C3
Historical Soil Gas Analytical Data
SEMCO, Santa Maria, California
Attachment g 781016901
September 2025
Analyte
Volatile Organic Compounds
1,1,1-Trichloroethane
1,1,2-Trichloro-1, 2, 2-
Trifluoroethane
i ,1-Dichloroethane
1,1-Dichloroethene
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
(Mesitylene)
1-Chlorohexane
2,2,4-Trimethylpentane
2-Hexanone (MBK)
2 -Methyl Propane
4-Ethyltoluene
Acetone
Allyl Chloride (3-
Chloropropene)
Benzene
Carbon Disulfide
Chloroethane
Chloroform
Chloromethane
Cis-1,2-Dichloroethene
Cyclohexane
Cymene
CAS Number
71-55-6
76-13-1
75-34-3
75-35-4
95-63-6
108-67-8
544-10-5
540-84-1
591-78-6
75-28-5
622-96-8
67-64-1
107-05-1
71-43-2
75-15-0
75-00-3
67-66-3
74-87-3
156-59-2
110-82-7
99-87-6
Subslab/Soil Gas VI Commercial/Industrial ESL
150,000
NS
260
10,000
NS
NS
NS
NS
NS
NS
NS
4,500,000
NS
14 NS
1,500,000
18 13,000
1,200
NS
NS
Location
Sample Name
p
Original
Sample Name
Sample Date
p
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
Soil Vapor
SG -1
SG -1-5_091389
SG1-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -2
SG -2-5_091389
SG2-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -3
SG -3-5_091389
SG3-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -4
SG -4-5_091389
SG4-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -5
SG -5-5_091389
SG5-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -6
SG -6-5_013989
SG6-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -6-5_091389
SG6-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -7
SG -7-5_091389
SG7-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -8
SG -8-5_091389
SG8-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -9
SG -9-5_091389
SG9-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -10
SG -10-5_091389
SG10-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -11
SG -11-5_091389
SG11-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -12
SG -12-5_091389
SG12-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG 13
SG -13-5_091389
SG13-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -13-5_130989
SG13-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -14
SG -14-5_091389
SG14-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -15
SG -15-5_091389
SG15-5
09/13/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -16
SG -16-5_091489
SG16-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -17
SG -17-5_091489
SG17-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -18
SG -18-5_091489
SG18-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -19
SG -19-5_091489
SG19-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -20
SG -20-5_091489
SG20-11
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -21
SG -21-5_091489
SG21-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -22
SG -22-5_091489
SG22-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -23
SG -23-5_091489
SG23-4
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -24
SG -24-5_091489
SG24-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -25
SG -25-5_091489
SG25-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -26
SG -26-5_091489
SG26-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -27
SG -27-5_091489
SG27-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -28
SG -28-5_091489
SG28-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -29
SG -29-4_091489
SG29-4
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -30
SG -30-8_091489
SG30-8
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -31
SG -31-5_091489
SG31-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -32
SG -32-5_091489
SG32-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -33
SG -33-5_091489
SG33-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SG -34
SG -34-5_091489
SG34-5
09/14/1989
NA
NA
NA
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
SV-1
SV-1-5_040721
SV1-5
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
6.8 NA
19 NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-2
SV-2-5_040721
SV2-5
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
14 NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-3
SV-3-5_040521
SV3-5
04/05/2021
ND U
NA
NA
NA
25 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-4
SV-4-5_040521
SV4-5
04/05/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-5
SV-5-5_040521
SV5-5
04/05/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-6
SV-6-5_040521
SV6-5
04/05/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-7
SV-7-5_040521
SV7-5
04/05/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-8
SV-8-5_040521
SV8-5
04/05/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
45 NA
160
NA
NA
SV-9
SV-9-5_040521
SV9-5
04/05/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-10
SV-10-5_040621
SV10-5
04/06/2021
3.7 NA
13 NA
19 8.9
NA
NA
19 21
15 110 E
NA
4.2 47
4.5 ND U
NA
52 NA
4.8 SV-11
SV-11-5_040621
SV11-5
04/06/2021
ND U
NA
ND U
NA
ND U
ND U
NA
NA
ND U
ND U
ND U
ND U
NA
ND U
ND U
ND U
ND U
NA
ND U
NA
ND U
SV-12
SV-12-5_040621
SV12-5
04/06/2021
3.2 NA
ND U
3.6 6.0
3.3 NA
NA
ND U
7.3 2.6
51 NA
12 6.9
ND U
6.5 NA
160 E
NA
ND U
SV-13
SV-13-5_040621
SV13-5
04/06/2021
ND U
NA
NA
NA
NA
NA
NA
3.2 NA
48 NA
220
NA
18 52
NA
NA
NA
140
NA
NA
SV-14
SV-14-5_040621
SV14-5
04/06/2021
ND U
NA
NA
NA
32 13
NA
8.5 NA
12 6.9
45 NA
11 NA
NA
NA
NA
ND U
NA
3.6
LANGAN
Table C3
Historical Soil Gas Analytical Data
SEMCO, Santa Maria, California
Attachment g 781016901
September 2025
Analyte
Volatile Organic Compounds
Ethyl Acetate
Ethylbenzene
0 Q
o
Q
o
Isopropylbenzene
(Cumene)
M,P-Xylene
Methyl Ethyl Ketone (2-
Butanone)
Methyl Isobutyl Ketone (4-
Methyl-2-Pentanone)
Methylene Chloride
n-Heptane
n -Hexane
n-Propylbenzene
o-Xylene (1,2-
Dimethylbenzene)
Propylene
Sec-Butylbenzene
Styrene
Tetrachloroethene (PCE)
Tetrahydrofuran
c
0 I -
Trans-1,2-Dichloroethene
Trichloroethane
Trichloroethene (TCE)
Vinyl Chloride
CAS Number
141-78-6
100-41-4
67-63-0
98-82-8
179601-23-'
78-93-3
108-10-1
75-09-2
142-82-5
110-54-3
103-65-1
95-47-6
115-07-1
135-98-8
100-42-5
127-18-4
109-99-9
108-88-3
156-60-5
25323-89-1
79-01-6
75-01-4
Subslab/Soil Gas VI Commercial/Industrial ESL
NS
160
NS
NS
NS
730,000
440,000
410
NS
NS
NS
NS
NS
NS
130,000
67 NS
44,000
12,000
NS
100
5.2 Location
Sample Name
Original
Sample Name
Sample Date
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/rn3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
Soil Vapor
SG -1
SG -1-5_091389
SG1-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.1 0.2
N-'-
SG -2
SG -2-5_091389
SG2-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.4 650
NA
SG -3
SG -3-5_091389
SG3-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 550
NA
SG -4
SG -4-5_091389
SG4-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 470
NA
SG -5
SG -5-5_091389
SG5-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.4 730
NA
SG -6
SG -6-5_013989
SG6-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.6 NA
NA
SG -6-5_091389
SG6-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
560
NA
SG -7
SG -7-5_091389
SG7-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.1 160
NA
SG -8
SG -8-5_091389
SG8-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.08 0.6
NA
SG -9
SG -9-5_091389
SG9-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.09 17
NA
SG -10
SG -10-5_091389
SG10-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 6
NA
SG -11
SG -11-5_091389
SG11-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.9 5,300
NA
SG -12
SG -12-5_091389
SG12-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.08 24
NA
SG 13
SG -13-5_091389
SG13-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
74 NA
SG -13-5_130989
SG13-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.1 NA
NA
SG -14
SG -14-5_091389
SG14-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.04 0.06
NA
SG -15
SG -15-5_091389
SG15-5
09/13/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.05 0.009
NA
SG -16
SG -16-5_091489
SG16-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 1
NA
SG -17
SG -17-5_091489
SG17-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.08 0.003
NA
SG -18
SG -18-5_091489
SG18-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.02 0.02
NA
SG -19
SG -19-5_091489
SG19-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 2
NA
SG -20
SG -20-5_091489
SG20-11
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.06 10
NA
SG -21
SG -21-5_091489
SG21-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 0.8
NA
SG -22
SG -22-5_091489
SG22-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.1 0.003
NA
SG -23
SG -23-5_091489
SG23-4
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.008
ND U
NA
SG -24
SG -24-5_091489
SG24-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8 400
NA
SG -25
SG -25-5_091489
SG25-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.2 8
NA
SG -26
SG -26-5_091489
SG26-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.05 34
NA
SG -27
SG -27-5_091489
SG27-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.02 0.0008
NA
SG -28
SG -28-5_091489
SG28-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
780
2,200
NA
SG -29
SG -29-4_091489
SG29-4
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
150
2 NA
SG -30
SG -30-8_091489
SG30-8
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
170
55 NA
SG -31
SG -31-5_091489
SG31-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1 28
NA
SG -32
SG -32-5_091489
SG32-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
820
ND _!
NA
SG -33
SG -33-5_091489
SG33-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.3 180
NA
SG -34
SG -34-5_091489
SG34-5
09/14/1989
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.06 0.003
NA
SV-1
SV-1-5_040721
SV1-5
04/07/2021
NA
NA
20 4.5
8.3 17
NA
NA
NA
NA
NA
4.2 NA
NA
NA
ND U
NA
ND U
ND U
NA
22 ND U
SV-2
SV-2-5_040721
SV2-5
04/07/2021
NA
2.6 NA
5.9 13
17 NA
NA
NA
NA
NA
4.0 NA
NA
NA
ND U
NA
4.4 ND U
NA
1,900
ND U
SV-3
SV-3-5_040521
SV3-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
ND U
ND U
SV-4
SV-4-5_040521
SV4-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
ND U
ND U
SV-5
SV-5-5_040521
SV5-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
ND U
ND U
SV-6
SV-6-5_040521
SV6-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
ND U
ND U
SV-7
SV-7-5_040521
SV7-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
180
ND U
SV-8
SV-8-5_040521
SV8-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
15,000
ND U
SV-9
SV-9-5_040521
SV9-5
04/05/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
ND U
ND U
NA
430
ND U
SV-10
SV-10-5_040621
SV10-5
04/06/2021
NA
11 55
6.3 53
39 10
NA
12 17
7.2 21
100 E
3.2 NA
21 NA
3.1 ND U
NA
26 3.9
SV-11
SV-11-5_040621
SV11-5
04/06/2021
NA
ND U
ND U
ND U
ND U
ND U
ND U
NA
ND U
ND U
ND U
ND U
ND U
ND U
NA
ND U
NA
ND U
ND U
NA
450,000
ND U
SV-12
SV-12-5_040621
SV12-5
04/06/2021
NA
15 120 E
ND U
59 ND U
ND U
NA
11 3.3
3.0 17
21 ND U
NA
17 NA
39 87
NA
12,000
ND U
SV-13
SV-13-5_040621
SV13-5
04/06/2021
NA
32 11
5.3 120
54 NA
NA
31 35
NA
41 400 E
NA
NA
ND U
NA
47 400
NA
36 5.7
SV-14
SV-14-5_040621
SV14-5
04/06/2021
NA
23 25
3.2 90
NA
NA
NA
17 12
7.7 31
NA
NA
NA
ND U
2.6 46
ND U
f!"
18 "ID U
LANGAN
Table C3
Historical Soil Gas Analytical Data
SEMCO, Santa Maria, California
Attachment E 781016901
September 2025
Analyte
Volatile Organic Compounds
1,1,1-Trichloroethane
1,1,2-Trichloro-1, 2, 2-
Trifluoroethane
i ,1-Dichloroethane
1,1-Dichloroethene
1,2,4-Trimethylbenzene
1,3,5-Trimethylbenzene
(Mesitylene)
1-Chlorohexane
2,2,4-Trimethylpentane
2-Hexanone (MBK)
2 -Methyl Propane
4-Ethyltoluene
Acetone
Allyl Chloride (3-
Chloropropene)
Benzene
Carbon Disulfide
Chloroethane
Chloroform
Chloromethane
Cis-1,2-Dichloroethene
Cyclohexane
Cymene
CAS Number
71-55-6
76-13-1
75-34-3
75-35-4
95-63-6
108-67-8
544-10-5
540-84-1
591-78-6
75-28-5
622-96-8
67-64-1
107-05-1
71-43-2
75-15-0
75-00-3
67-66-3
74-87-3
156-59-2
110-82-7
99-87-6
Subslab/Soil Gas VI Commercial/Industrial ESL
150,000
NS
260
10,000
NS
NS
NS
NS
NS
NS
NS
4,500,000
NS
14 NS
1,500,000
18 13,000
1,200
NS
NS
Location
Sample Name
p
Original
Sample Name
Sample Date
p
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
3 Ng/m
Soil Vapor
SV-15
SV-15-5_040621
SV15-5
04/06/2021
ND U
NA
NA
18,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
4,000,000
NA
NA
SV-16
SV-16-5_040621
SV16-5
04/06/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2,600
NA
NA
SV-17
SV-17-5_040621
SV17-5
04/06/2021
3.8 NA
NA
NA
9.4 5.7
NA
NA
NA
4 2.7
15 NA
6.7 NA
NA
12 NA
73 NA
NA
SV-18
SV-18-5_040621
SV18-5
04/06/2021
ND U
8.6 NA
NA
3.7 NA
NA
NA
NA
4.4 NA
16 NA
NA
11 NA
2.7 NA
ND U
NA
NA
SV 19
SV-19-5_040621
SV19-5
04/06/2021
ND U
NA
NA
NA
29 23
NA
NA
NA
3.7 11
37 NA
10 5.7
ND U
9.9 NA
ND U
NA
6.2 SV-19-5_040621_DUP
SV19-5_DUP
04/06/2021
NA
NA
NA
NA
22 16
NA
NA
NA
NA
9.1 24
NA
6.9 3.8
NA
6.5 NA
NA
NA
4.7 SV-20
SV-20-5_040621
SV20-5
04/06/2021
ND U
NA
NA
NA
14 9.1
3.1 10
NA
15 4.2
29 NA
15 15
NA
NA
2.5 4.2
3.1 NA
SV-21
SV-21-5_040621
SV21-5
04/06/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
3.1 NA
14 NA
4.4 NA
NA
NA
NA
ND U
NA
NA
SV-22
SV-22-5_040721
SV22-5
04/07/2021
ND U
NA
NA
NA
3.6 NA
NA
NA
NA
2.6 NA
19 NA
NA
NA
NA
2.5 NA
2.6 NA
NA
SV-23
SV-23-5_040721
SV23-5
04/07/2021
ND U
NA
NA
NA
71 47
NA
NA
NA
5.1 38
62 E
NA
5.8 7.9
NA
NA
NA
19 NA
9.9 SV-24
SV-24-5_040721
SV24-5
04/07/2021
ND U
NA
NA
NA
2.9 NA
NA
NA
NA
35 NA
300 E
NA
8.9 5.8
NA
NA
NA
ND U
5.3 NA
SV-25
SV-25-5_040721
SV25-5
04/07/2021
ND U
17 NA
NA
2.7 NA
NA
NA
NA
16 NA
72 E
NA
13 4.6
NA
ND U
NA
ND U
5.9 NA
SV-26
SV-26-5_040721
SV26-5
04/07/2021
ND U
NA
NA
NA
15 5.7
NA
14 NA
33 7.5
86 NA
16 6.1
NA
4.4 NA
ND U
3.2 NA
SV-27
SV-27-5_040721
SV27-5
04/07/2021
ND U
NA
NA
NA
17 7.2
NA
16 NA
26 6.1
67 NA
9.3 8.2
NA
NA
NA
ND U
3.7 NA
SV-28
SV-28-5_040721
SV28-5
04/07/2021
ND U
7.2 NA
NA
110
38 NA
14 14
95 33
130
6.1 19
12 NA
NA
NA
ND U
13 8.1
SV-29
SV-29-5_040621
SV29-5
04/06/2021
ND U
NA
NA
NA
8.8 6.7
NA
30 NA
58 4.0
200
NA
38 39
NA
NA
NA
7.1 NA
NA
SV-30
SV-30-5_040721
SV30-5
04/07/2021
ND U
NA
NA
NA
6.9 4.1
NA
16 ND U
61 ND U
97 ND U
18 10
NA
NA
NA
ND U
ND U
ND U
SV-31
SV-31-5_040721
SV31-5
04/07/2021
ND U
NA
NA
NA
27 7.7
NA
7.0 NA
7.8 5.7
55 NA
4.6 NA
NA
NA
NA
ND U
3.3 NA
SV-32
SV-32-5_040721
SV32-5
04/07/2021
ND U
11 NA
NA
8.3 5.5
NA
NA
NA
3.5 2.5
13 NA
NA
NA
NA
4.6 NA
ND U
NA
NA
SV-33
SV-33-5_040721
SV33-5
04/07/2021
ND U
15 NA
NA
3.0 NA
NA
NA
NA
4.4 NA
25 NA
2.6 NA
NA
11 NA
ND U
NA
NA
SV-34
SV-34-5_040721
SV34-5
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
2.5 NA
24 NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-35
SV-35-5_040721
SV35-5
04/07/2021
ND U
NA
NA
NA
3.5 NA
NA
NA
NA
4.0 NA
22 NA
NA
NA
NA
27 NA
ND U
NA
NA
SV-36
SV-36-5_040721
SV36-5
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
17 NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-37
SV-37-5_040721
SV37-5
04/07/2021
ND U
NA
NA
NA
3.2 NA
NA
4.0 NA
37 NA
110 E
NA
21 14
NA
NA
NA
ND U
NA
NA
SV-38
SV-38-5_040721
SV38-5
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
3.0 NA
26 NA
NA
NA
NA
NA
NA
ND U
NA
NA
SV-39
SV-39-5_040721
SV39-5
04/07/2021
ND U
NA
NA
NA
3.8 NA
NA
NA
NA
NA
NA
87 NA
15 6.8
NA
NA
NA
ND U
NA
310
SV-40
SV-40-5_040721
SV40-5
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
14 NA
69 E
NA
13 10
NA
NA
NA
ND U
6.1 NA
SV-40-5_040721_DUP
SV40-5_DUP
04/07/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
3 NA
76 E
NA
14 10
NA
NA
NA
ND U
6.6 NA
Subslab
Soil Gas
SS -1
SS -1_040621
SS1
04/06/2021
3.1 NA
NA
NA
NA
NA
NA
NA
NA
6.8 NA
300 E
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SS -2
SS -2_040621
SS2
04/06/2021
ND U
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
320 E
8.5 NA
NA
NA
10 NA
10 NA
NA
SS -3
SS -3_040621
SS3
04/06/2021
ND U
NA
NA
NA
2.7 NA
NA
5.4 NA
NA
NA
280
NA
NA
NA
NA
NA
NA
ND U
NA
NA
SS -4
SS -4_040621
SS4
04/06/2021
15 NA
ND U
NA
ND U
ND U
NA
NA
19 26
ND U
380
NA
3.4 10
4.5 24
NA
21 NA
ND U
LANGAN
Table C3
Historical Soil Gas Analytical Data
SEMCO, Santa Maria, California
Attachment g 781016901
September 2025
Analyte
Volatile Organic Compounds
Ethyl Acetate
Ethylbenzene
0 Q
o
Q
o
Isopropylbenzene
(Cumene)
M,P-Xylene
Methyl Ethyl Ketone (2-
Butanone)
Methyl Isobutyl Ketone (4-
Methyl-2-Pentanone)
Methylene Chloride
n-Heptane
n -Hexane
n-Propylbenzene
o-Xylene (1,2-
Dimethylbenzene)
Propylene
Sec-Butylbenzene
Styrene
Tetrachloroethene (PCE)
Tetrahydrofuran
c
0 I -
Trans-1,2-Dichloroethene
Trichloroethane
Trichloroethene (TCE)
Vinyl Chloride
CAS Number
141-78-6
100-41-4
67-63-0
98-82-8
179601-23-'
78-93-3
108-10-1
75-09-2
142-82-5
110-54-3
103-65-1
95-47-6
115-07-1
135-98-8
100-42-5
127-18-4
109-99-9
108-88-3
156-60-5
25323-89-1
79-01-6
75-01-4
Subslab/Soil Gas VI Commercial/Industrial ESL
NS
160
NS
NS
NS
730,000
440,000
410
NS
NS
NS
NS
NS
NS
130,000
67 NS
44,000
12,000
NS
100
5.2 Location
Sample Name
Original
Sample Name
Sample Date
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/rn3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
pg/m3
Soil Vapor
SV-15
SV-15-5_040621
SV15-5
04/06/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
13,000
NA
ND U
5,600
NA
11,000,000
ND
SV-16
SV-16-5_040621
SV16-5
04/06/2021
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
220
NA
NA
ND U
NA
ND U
ND U
NA
120,000
ND U
SV-17
SV-17-5_040621
SV17-5
04/06/2021
NA
110
NA
11 310 E
19 NA
NA
4.0 NA
2.9 100
3.8 NA
NA
62 NA
15 62
NA
16,000
ND U
SV-18
SV-18-5_040621
SV18-5
04/06/2021
NA
NA
NA
7.3 14
21 NA
NA
NA
NA
NA
4.7 7.4
NA
NA
22 NA
6.9 ND U
NA
24 ND U
SV-19
SV-19-5_040621
SV19-5
04/06/2021
NA
40 NA
13 150
23 NA
NA
4.0 NA
14 48
8.7 NA
NA
5.0 NA
76 ND U
NA
110
ND U
SV-19-5_040621_DUP
SV19-5_DUP
04/06/2021
NA
29 NA
9.0 110
14 NA
NA
NA
NA
10 35
NA
NA
NA
NA
NA
56 NA
NA
83 NA
SV-20
SV-20-5_040621
SV20-5
04/06/2021
3.9 21
20 18
82 36
NA
NA
25 13
5.6 23
19 NA
NA
15 NA
60 ND U
NA
180
ND U
SV-21
SV-21-5_040621
SV21-5
04/06/2021
NA
3.4 12
6.3 12
17 NA
NA
NA
NA
NA
2.9 NA
NA
NA
3.8 NA
14 ND U
NA
61 ND U
SV-22
SV-22-5_040721
SV22-5
04/07/2021
NA
12 13
6.5 49
19 NA
NA
NA
NA
2.7 15
NA
NA
NA
ND U
NA
15 ND U
NA
1,300
ND U
SV-23
SV-23-5_040721
SV23-5
04/07/2021
NA
100
80 E
17 530
34 NA
NA
NA
NA
50 120 E
5.9 NA
3.9 6.8
4.5 87
5.2 NA
1,400
ND U
SV-24
SV-24-5_040721
SV24-5
04/07/2021
NA
6.8 2,400 E
NA
27 18
25 NA
9.3 17
NA
6.4 200 E
NA
NA
ND U
3.5 19
ND U
NA
ND U
ND U
SV-25
SV-25-5_040721
SV25-5
04/07/2021
NA
3.0 59
3.2 7.3
39 20
NA
13 23
NA
2.6 8.7
NA
NA
ND U
NA
15 ND U
NA
140
ND U
SV-26
SV-26-5_040721
SV26-5
04/07/2021
NA
28 18
4.3 110
45 18
2.6 35
24 9.0
32 210
NA
NA
ND U
NA
72 ND U
NA
190
ND U
SV-27
SV-27-5_040721
SV27-5
04/07/2021
NA
20 15
4.5 77
29 64
NA
20 28
7.5 24
190 E
NA
NA
ND U
6.8 49
ND U
NA
170
ND U
SV-28
SV-28-5_040721
SV28-5
04/07/2021
NA
8.7 27
8.6 26
66 63
NA
33 47
27 11
450
NA
NA
ND U
NA
49 ND U
NA
120
ND U
SV-29
SV-29-5_040621
SV29-5
04/06/2021
NA
31 16
6.9 110
55 NA
3.9 59
87 5.3
36 620
NA
NA
ND U
17 85
ND U
NA
34 ND U
SV-30
SV-30-5_040721
SV30-5
04/07/2021
NA
12 36
4.2 45
25 47
2.9 26
50 3.1
13 340 E
NA
NA
ND U
11 46
ND U
NA
ND U
ND U
SV-31
SV-31-5_040721
SV31-5
04/07/2021
NA
8.7 880 E
NA
36 NA
14 NA
9.8 4.4
4.9 11
14 NA
NA
26 NA
28 ND U
NA
22 ND U
SV-32
SV-32-5_040721
SV32-5
04/07/2021
NA
6.0 NA
2.7 28
NA
NA
NA
NA
NA
2.7 8.2
NA
NA
NA
71 NA
9.1 ND U
NA
1,700
ND U
SV-33
SV-33-5_040721
SV33-5
04/07/2021
NA
NA
41 NA
NA
12 14
NA
NA
NA
NA
NA
18 NA
NA
47 NA
4.3 NA
NA
3,000
NA
SV-34
SV-34-5_040721
SV34-5
04/07/2021
NA
NA
120 E
NA
7.1 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
14 NA
3.1 ND U
NA
38 ND U
SV-35
SV-35-5_040721
SV35-5
04/07/2021
NA
NA
83 E
NA
NA
NA
15 NA
NA
NA
NA
NA
11 NA
NA
23 NA
4.1 ND U
NA
1,600
ND U
SV-36
SV-36-5_040721
SV36-5
04/07/2021
NA
NA
93 E
NA
NA
NA
19 NA
NA
NA
NA
NA
5.5 NA
NA
ND U
NA
ND U
ND U
NA
ND U
ND U
SV-37
SV-37-5_040721
SV37-5
04/07/2021
NA
5.7 37
NA
18 27
18 NA
18 33
NA
7.8 NA
NA
NA
ND U
5.2 19
ND U
NA
ND U
ND U
SV-38
SV-38-5_040721
SV38-5
04/07/2021
NA
NA
24 NA
NA
NA
NA
NA
NA
NA
NA
NA
8.9 NA
NA
ND U
NA
ND U
ND U
NA
ND U
ND U
SV-39
SV-39-5_040721
SV39-5
04/07/2021
NA
3.8 NA
NA
9.4 12
NA
NA
17 20
NA
6.0 NA
NA
NA
ND U
NA
28 ND U
NA
ND U
ND U
SV-40
SV-40-5_040721
SV40-5
04/07/2021
NA
5.2 27
NA
18 18
NA
3.1 7.3
15 NA
8.4 95 E
NA
NA
ND U
NA
12 ND U
NA
ND U
ND U
SV-40-5_040721_DUP
SV40-5_DUP
04/07/2021
NA
5.4 28
NA
19 19
10 NA
7.6 16
NA
8.7 100 E
NA
NA
ND U
NA
12 ND U
NA
ND U
ND U
Subslab
Soil Gas
SS -1
SS -1_040621
SS1
04/06/2021
NA
NA
98 E
NA
NA
31 22
NA
NA
NA
NA
NA
NA
NA
NA
3.7 2.5
5.2 ND U
NA
11 ND U
SS -2
SS -2_040621
SS2
04/06/2021
5.9 NA
32 4.7
NA
31 28
NA
NA
NA
NA
NA
NA
NA
NA
4.1 2.9
2.8 ND U
NA
2,200
ND U
SS -3
SS -3_040621
SS3
04/06/2021
NA
NA
NA
6.0 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ND U
NA
6.1 ND U
NA
47 ND U
SS -4
SS -4_040621
SS4
04/06/2021
NA
ND U
300
5.1 ND U
54 47
NA
ND U
ND U
ND U
ND U
ND U
ND U
NA
42 NA
ND U
ND U
NA
3,100
ND U
LANGAN
Table C3
Historical Soil Gas Analytical Data
SEMCO, Santa Maria, California
Notes:
Attachment B 781016901
September 2025
Historical data from the following reports:
Soil Vapor Sampling Report, Former SEMCO Twist Drill & Tool Company, 2936 Industrial Parkway, Santra Maria, California, Site I.D. No. SLT3S2411351 dated 16 July 2021 by Analytical Consulting Group, Inc.
Subsurface Investigation: Phase 2, SEMCO Twist Drill and Tool Company Facility, Santa Maria, California dated December 1989 by ERC Environmental and Energy Services Co.
CAS - Chemical Abstract Service
ESL - Environmental Screening Level
NA - Not Analyzed or Not Available (Historical Data)
ND - Not detected
NS - No standard
RWQCB - Regional Water Quality Control Board
Soil gas results were compared to the San Francisco Bay RWQCB Subslab/Soil Gas Vapor Intrusion Human Health Risk Levels - pg/m3 - Micrograms per cubic meter
Qualifiers:
E - Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
U - The analyte was analyzed for, but was not detected at a level greater than or equal to the RL; the value shown in the table is the RL.
Exceedance Summary:
10 - Result exceeds Subslab/Soil Gas VI Commercial/Industrial ESL
LANGAN
Table C4
Historical Indoor Air Analytical Data
SEMCO, Santa Maria, California
Analyte
Volatile Organic Compounds
1,1,1-Trichloroethane
1,1,2-Trichloroethane
1,2-Dichloroethane
Carbon Tetrachloride
Chloroform
Cis-1,2-Dichloroethene
Tetrachloroethene (PCE)
Trans-1,2-Dichloroethene
Trichloroethene (TCE)
Vinyl Chloride
CAS Number
71-55-6
79-00-5
107-06-2
56-23-5
67-66-3
156-59-2
127-18-4
156-60-5
79-01-6
75-01-4
Indoor Air VI Commercial/Industrial ESL
4,400
0.77 0.47
2 0.53
35 2
350
3 0.16
Location
Sample
Name
Original
Sample Name
Sample
Date
3 pg/m
3 lag/m
3 pg/m
3 pg/m
3 pg/m
3 pg/m
3 pg/m
3 pg/m
3 pg/m
3 pg/m
Indoor Samples
South
Shop Area
IA -1
IA -1_032621
326 -IA -1
03/26/2021
<0.1 U
<0.1 U
0.1 0.32
0.1 <0.1 U
<0.1 U
<0.1 U
0.34 <0.009 U
IA -1_012022
120 -IA -1
01/21/2022
<0.1 U
<0.1 U
<0.1 U
0.34 0.22
<0.1 U
0.16 <0.1 U
1.1 <0.009 U
Office
IA -2
IA -2_032621
326 -IA -2
03/26/2021
<0.1 U
<0.1 U
0.15 0.62
<0.1 U
<0.1 U
<0.1 U
<0.1 U
0.12 <0.009 U
IA -2_012022
120 -IA -2
01/21/2022
<0.1 U
<0.1 U
0.33 0.46
0.16 <0.1 U
0.52 <0.1 U
0.49 <0.009 U
Storage
Building
IA -3
IA -3_032621
326 -IA -3
03/26/2021
<0.1 U
<0.1 U
0.13 0.33
0.13 <0.1 U
<0.1 U
<0.1 U
0.39 <0.009 U
IA -3_012022
120 -IA -3
01/21/2022
<0.1 U
0.17 0.15
0.31 0.18
<0.1 U
0.15 <0.1 U
1.1 <0.009 U
Outdoor Samples
Outside
North
OA 4
OA -4_032621
326 -OA -4
03/26/2021
<0.1 U
<0.1 U
0.13 0.5
0.17 <0.1 U
<0.1 U
<0.1 U
<0.1 U
<0.009 U
OA -4_012022
120 -OA -4
01/21/2022
<0.1 U
<0.1 U
<0.1 U
0.3 0.13
<0.1 U
0.13 <0.1 U
0.31 <0.009 U
Outside
East Yard
OA 5
OA -5_032621
326 -OA -5
03/26/2021
0.14 <0.1 U
<0.1 U
0.68 0.11
<0.1 U
<0.1 U
<0.1 U
0.16 <0.009 U
OA -5_012022
120 -OA -5
01/21/2022
<0.1 U
<0.1 U
<0.1 U
0.3 0.13
0.13 0.12
<0.1 U
4.1 <0.009 U
Outside
South
OA 6
OA -6_032621
326 -OA -6
03/26/2021
<0.1 U
<0.1 U
<0.1 U
0.31 0.12
<0.1 U
<0.1 U
<0.1 U
<0.1 U
<0.009 U
OA -6_012022
120 -OA -6
01/21/2022
<0.1 U
<0.1 U
<0.1 U
0.3 0.11
<0.1 U
0.25 <0.1 U
0.54 <0.009 U
Notes:
Historical data from the following reports:
Results of Indoor Air Sampling, Former Semco Twist Drill & Tool Company, 2936 Industrial Parkway, Santa Maria, California, dated 7 April 2021 by Analytical Consulting Group, Inc.
Results of Second Round Indoor Air Sampling, Former Semco Twist Drill & Tool Company, 2936 Industrial Parkway, Santa Maria, California, dated 11 February 2022 by Analytical Consulting Group, Inc.
Indoor air sample results were compared to San Francisco Bay RWQCB Indoor Air Vapor Intrusion Human Health Risk Levels - Commercial/Industrial ESL, Lower of Cancer Risk and Noncancer Hazard Values (July 2019). Outdoor air sample results do not have applicable comparison criteria and are shown for informational purposes.
CAS - Chemical Abstract Service
ESL - Environmental Screening Level
NA - not analyzed
RL - Reporting Limit
<RL - Not detected
RWQCB - Regional Water Quality Control Board
VI - vapor intrusion
pg/m3 - micrograms per cubic meter
Qualifiers:
U - The analyte was analyzed for, but was not detected at a level greater than or equal to the RL; the value shown in the table is the RL.
Exceedance Summary:
1 - Result exceeds Indoor Air VI Commercial/Industrial ESL September 2025
LANGA '
Attachment B
APPENDIX D
PERMIT APPLICATION FORMS
LANGAN
Santa MariaAll-America City
For City Use Only
New Applicant ❑ Renewal ❑
-0-Discharge ❑ Class I II ❑
Class I ❑ Class IV ❑
Class II ❑ (SIU or CIU)
Permit No:
NAIC Code:
CITY OF SANTA MARIA DEPARTM NT On FR UTILITIES
INDUSTRIAL WASTEWA Ee kSCHARGE
PERMIT APPLICATION
All businesses within the City of Santa Maria are required to complete an industrial wastewater discharge permit application. Use current operating data, if available, or your best estimate based on similar types of businesses. Please answer all questions as thoroughly as possible. If a question is inapplicable to your industry, please indicate. Incomplete applications shall be returned.
COMPANY INFORMATION
1. Company Name:
2. Facility Address:
3. Mailing Address:
4. Email Address
5. Facility Contact (name, title, telephone number:
6. Property Owner:
7. Principal Business Activity Conducted at this Facility:
8. What is the most convenient time of the workday for Regulatory Compliance staff to visit your facility?
9. Average Number of Employees: Days & Hours of Operation:
10. Wastewater Generating Processes (check all that apply) ❑ None (no water to building) ❑ Photographic processing ❑ Laboratory ❑ Automotive ❑ Electroplating or anodizing ❑ Dry cleaning ❑ Car Wash ❑ Equipment washing or rinsing ❑ Laundry facilities ❑ Dental Office ❑ Sanitary restrooms ❑ Print shop
❑ Medical Office ❑ Cafeteria or kitchen ❑ Other (describe):
❑ Mortuary ❑ Food processing, freezing, packaging
Describe wastewater generating processes checked above (attach additional sheets if necessary):
11. Do you have a sand and oil trap or clarifier? If yes, what size? Location:
12. Do you have a grease trap or interceptor? If yes, what size? Location:
13. Do you have any other type of trap? If yes, what kind? Location:
14. If the response for #10 ,#11, or #12 is YES, how often is the trap/clarifier/interceptor cleaned?
15. If the response for #10, #11, or #12 is YES, who performs the cleaning?
16. Please describe chemicals or other substances used in your processes which may enter your wastewater and the City's sewer system. Describe any alternate disposal methods (i.e., recycling, hauling) employed or contracted by you for substance disposal:
17. Do you have floor drains, floor sinks, or any other disposal connection to the City's sewer system other than restroom facilities? If yes, please describe:
18. Average volume of water used each month: Account Number:
From? ❑ City of Santa Maria or ❑ Cal -Cities If water or sewer charges are paid by someone other than your business; please provide name, address, and phone number:
19. Please estimate what percentage of total water consumed at your facility is used for each of the following (total =100%):
Employee Kitchen/Break Room Restrooms Landscape Irrigation Business Production or Process Industrial Other (explain)
Santa Maria
bitgad
All -America City
CITY OF SANTA MARIA DEPARTM NT On FR UTILITIES
INDUSTRIAL WASTEWA Ee kSCHARGE
PERMIT APPLICATION
20. List chemicals or fuels stored at this facility (attach separate sheets if necessary) that, in the event of unforeseen occurrence or accident, could create a spill event:
21. Container tyoes: ❑ Drums ❑ Tanks ❑ Bottles ❑ Other Material types: ❑ Waste ❑ Pure Product
22. Please describe any alternate disposal methods (i.e., recycle, haulers) employed or contracted by you for disposal of stored substances:
23. Does this facility currently hold a National Pollutant Discharge Elimination System (NPDES) Permit? If yes, Permit number is: List substances regulated by NPDES Permit:
24. Does this facility discharge any substances associated with industrial activities (i.e. boiler, cooling tower condensate, process wastewater, etc.) to the City's stormwater system? If yes, please describe:
25. Are any processes performed out of doors that may cause accidental or incidental contact of industrial substances with stormwater? If yes, list the processes, equipment, materials, including raw materials, intermediates or products, that may become exposed to stormwater:
26. Does this facility store any materials or substances outdoors, which may come into contact with storm water? If yes, list the materials stored outdoors:
27. Are any control measures, (i.e. berms, secondary containment) used to prevent substances from entering storm drains from any outdoor activities or storage? If yes, please describe:
28. Do you have an emergency spill clean-up plan? If yes, please attach.
The above information is accurate to the best of my knowledge and is based on (check one):
❑ Current operating data ❑ Best estimate based on
❑ Other (explain):
This application was completed by (please print):
Name/Title: Phone No:
Signature: Date:
Please Return to:
City of Santa Maria Utilities Department
Regulatory Compliance Division
2065 East Main Street
Santa Maria, CA 93454
FAX: 805-928-7240
Email: regulatorycompliancepcityofsantamaria.orq
Print Form
apcd
air pollution control district
SANTA BARBARA COUNTY
Pilot Test Soil Remediation
Application Form -07B
Santa Barbara County Air Pollution Control District
260 N. San Antonio Road, Suite A
Santa Barbara, CA 93110-1315
Use this form to request an exemption from permit requirement for conducting a soil vapor extraction pilot test for soil remediation projects. Based upon review of the submitted data, the APCD will issue a letter of exemption from permit requirement or request applications for permits to construct (install) and to operate equipment. Mail the completed form(s) and appropriate filing fee (see Schedule F.11 of Rule 210 http://www.ourair.org/wp-content/uploads/cpi-fees.pdf) at least thirty (30) days before estimated project start-up to the Air Pollution Control District (APCD) at the above address.
Facility Information
Facility Address/Location
Current APCD Permit # (if any)
Assessors Parcel No(s)
Property Owner Info
Use as Billing Contact? ❑ Yes ❑ No
Company Name
Doing Business As
Contact Name
P
Position/Title
Mailing Address
City
S
State
Zip Code
Telephone
Cell
E
Email
Equipment Owner Info
Use as Billing Contact? ❑ Yes ❑ No
Company Name
Doing Business As
Contact Name
P
Position/Title
Mailing Address
City
S
State
Zip Code
Telephone
_
Cell
_
Email
Equipment Operator Info
Use as Billing Contact?
■I
Yes ❑ No
Company Name
Doing Business As
Contact Name
P
Position/Title
Mailing Address
City
S
State
Zip Code
Telephone
Cell
E
Email
APCD -07B (07/01/2024)
For APCD use only. FID #
App. #
Attachment B
Pilot Test Soil Remediation
Application Form -07B
Authorized Agent Info*
Use as Billing Contact?
■
Yes L No
Company Name
Doing Business As
Contact Name
P
Position/Title
Mailing Address
City
S
State
Zip Code
Telephone
Cell
E
Email
*Use this section if the application is not submitted by the owner/operator and provide a completed Form -01A. Owner/Operator information above is still required.
Source of Contamination (Check all that apply)
E Leaking Underground Storage Tank
❑ Dry Cleaning Operation
❑ Oil & Gas Production
❑ Other (describe)
E Pesticides
Type of Soil Contaminants (Check all that apply)
Gasoline
❑
Crude Oil
❑
Diesel
•
❑ Dioxins/Furans (list)
❑ Polychlorinated Biphenyls (list)
E Polycyclic Aromatic Hydroxcarbons (list)
❑ Chlorinated Hydrocarbons (list)
❑ Metals (list)
❑ Other (list)
Operating Schedule
Estimated start date
Estimated end date
Daily operating schedule
J
Total test duration*
Number of wells to be tested
Duration of each well test
*If the test duration exceeds 15 days, submit a completed APCD Form -01 and this Form -07B. A permit is required.
Equipment Description
Provide a detailed description of the soil vapor extraction equipment and associated emission controls. List normal operating parameters (e.g., temperature, flow rate, pressure, et cetera).
APCD -07B (07/01/2024)
Attachment B
Pilot Test Soil Remediation
Application Form -O7B
Power Source
Provide information on the power source for the soil vapor extraction equipment. Please note portable engines with a valid California Portable Equipment Registration Program (PERP) certificate may operate under this pilot test exemption. ❑ Grid Electrical Power
n Portable Generator
E Other (describe)
Generator Fuel Type
Generator PERP Certificate Number *
Generator Engine Size (bhp)
*If the generator engine size exceeds 50 bhp and does not have a valid PERP Certificate, a permit is required.
School Information
❑ Yes ❑ No Is the remediation site property boundary line located within 1,000 feet of a school (k-12)? If yes, provide school name and address.
❑ Yes ❑No
School name
School address
If the remediation site is located within 1,000 feet of a school, can work activities occur outside of school hours (e.g., weekends, summer, holidays)? If yes, submit documentation from the school(s) to show that your operating schedule above conforms accordingly. If no, submit a completed APCD Form -03 (School Summary Form), APCD Form -01 and APCD Form -77. A permit is required.
Emissions Estimate (Attach calculations and assumptions) lb/hr
Reactive Organic Compounds (ROC)
Nitrogen Oxides (NOx)
Particulate Matter (PM)
Carbon Monoxide (CO)
Sulfur Oxides (SOx)
lb/day
Applicant/Preparer Statement
The person who prepares the application also must sign this form. The preparer may be an employee of the owner/operator or an authorized agent (contractor/consultant) working on behalf of the owner/operator (an Authorized Agent Form -01A is required).
I certify pursuant to H&SC Section 42303.5 that all information contained herein and information submitted with this application is true and correct.
Completed By
Signature
Company
Date
APCD -07B (07/01/2024)
Pilot Test Soil Re ,atjon
Application Form -07B
Application Checklist (Have you submitted all the required information? Please check off the boxes) Exemption Filing Fee (Fee = $862. This fee is COLA adjusted every July 1st. Please ensure you are remitting the current fee. See schedule F.11 of Rule 210 http://www.ourair.org/wp-content/uploads/cpi-fees.pdf ) Attached copy of Work Plan submitted to the Public Health Depatment and the Public Health Department approval letter. The APCD will not issue an exemption or permit without the Work Plan and approval letter.
Process flow diagram (piping and instrumentation) of the proposed test equipment.
Emission calculations and assumptions.
Form -01A (Authorized Agent Form) attached if this application was prepared by and/or if correspondence is requested to be sent to an Agent Authorized (e.g., contractor or consultant). This form must accompany each application.
Form -03 (School Summary Form) attached if the project's property boundary is within 1,000 feet of the outer boundary of a school (k-12) and you want to perform work during school hours.
PLEASE NOTE THAT FAILURE TO COMPLETELY PROVIDE ALL REQUIRED INFORMATION OR FEES WILL RESULT IN YOUR APPLICATION BEING RETURNED OR DEEMED INCOMPLETE. \\sbcapcd.org\ shares \ Groups \ENGR\LIBRARY\Permitting \ Application Forms\apcd-07B.doc APCD -07B (07/01/2024)
Attachment B
Pilot Test Soil Remediation
Application Form -07B
NOTICE OF CERTIFICATION:
A11 applicants must complete the following Notice of Certification. This certification must be signed by the Authorized Company Representative representing the property owner. Signatures by Authorized Agents will not be accepted.
NOTICE of CERTIFICATION
Type or Print Name of Authorized Company Representative , am employed by or represent
Type or Print Name of Business, Corporation, Company, Individual, or Agency (hereinafter referred to as the applicant), and certify pursuant to H&SC Section 42303.5 that all information contained herein and information submitted with this application is true and correct and the equipment listed herein complies or can be expected to comply with said rules and regulations when operated in the manner and under the circumstances proposed. If the project fees are required to be funded by the cost reimbursement basis, as the responsible person, I agree that I will pay the Santa Barbara County Air Pollution Control District the actual recorded cost, plus administrative cost, incurred by the APCD in the processing of the application within 30 days of the billing date. If I withdraw my application, I further understand that I shall inform the APCD in writing and I will be charged for all costs incurred through closure of the APCD files on the project.
For applications submitted for Authority to Construct, modifications to existing Authority to Construct, and Authority to Construct/Permit to Operate permits, I hereby certify that all major stationary sources in the state and all stationary sources in the air basin which are owned or operated by the applicant, or by an entity controlling, controlled by, or under common control with the applicant, are in compliance, or are on approved schedule for compliance with all applicable emission limitations and standards under the Clean Air Act (42 USC 7401 et seq.) and all applicable emission limitations and standards which are part of the State Implementation Plan approved by the Environmental Protection Agency.
I agree that as property owner I am ultimately responsible for all activities related to this project. This includes compliance, operations, and the oversight of authorized agents and equipment owners/operators. It is my responsibility, as the property owner, to notify the APCD using the Form APCD-01T of any change to the equipment operator, equipment owner, or authorized agent. within 30 days of the change.
Completed By:
Date:
Signature of Authorized Company Representative
Title:
Phone:
APCD -07B (07/01/2024)
Print Form
apcd
air pollution control district
SANTA BARBARA COUNTY
Contaminated Soil and/or Groundwater Clean -Up
Application Form -77
Santa Barbara County Air Pollution Control District
260 N. San Antonio Road, Suite A
Santa Barbara, CA 93110-1315
Use this form to request a permit for contaminated soil and/or groundwater clean-up projects. This includes gasoline, crude oil , dry cleaning fluids, metals and any other soil contaminated with toxic, hazardous or volatile compounds. Mail the completed form(s) and appropriate filing fee (see Rule 210 Schedule F.1 https://www.ourair.org/wp-content/uploads/cpi-fees . pdf) at least 120 days before estimated project start-up to the Air Pollution Control District (APCD) at the above address.
Facility Address/Location
Current APCD Permit # (if any)
Assessors Parcel No(s)
❑Yes ❑No
Yes ❑No
Is the remediation site property boundary line located within 1,000 feet of a school (k-12)? If yes, provide school name and address.
School name
If the remediation site is located within 1,000 feet of a school, can work activities occur outside of school hours (e.g., weekends, summer, holidays)? If yes, provide correspondence from the school district that confirms that no school activities will occur during this time period. If no, submit a completed APCD Form -03 (School Summary Form).
I. Operating Schedule (include estimated start date, end date, and daily operating schedule) Daily Operating Schedule
Proposed Start Date
T
II. Cleanup Method
Type of Facility (former dry cleaner, gasoline station, etc.) In -Situ Vacuum Extraction
Liquid/Air Stripper
x
x
Bio-Reclamation
Above Ground Vacuum Extraction
K
K
0 Other (describe)
D
Dual Phase Extraction
Single Phase Extraction
Will Air Sparging be used?
Yes
No
x
K
x
III. Extent of Contamination and Soil Information
Estimated Contaminated Volume?
Cubic ft
Bulk Density of Soil?
Ton/Cubic ft
Average Intrinsic Permeability of the Contaminated Soil'? L
cm '2
Depth to Groundwater?
ft. BGS
APCD -77 (07/01/2024)
For APCD use only. FID #
App. #
Attachment B
Contaminated Soil and/or Groundwater Clean -Up
Application Form -77
�. Type of Soil Contaminants (Check all that apply above 0.2 PPM and define maximum inlet concentration to control device') ❑ Total ROC2
❑ Tetrachloroethene (PCE)
❑ Ethylene Dichloride (DCE)
❑ Trichloroethylene (TCE)
❑ Vinyl Chloride (Chloroethylene)
❑ Other
❑ Other
❑ Other
❑ Other
ppmvd
ppmvd
ppmvd
ppmvd
ppmvd
ppmvd
ppmvd
ppmvd
ppmvd
❑ Benzene
Toluene
❑ EthylBenzene
❑ Xylene
❑ Methyl Tert-Butyl Ether (MTBE)
ppmvd
ppmvd
ppmvd
ppmvd
ppmvd
❑x Xylene
ppmvd
E Other
E Other
❑ Other
If dilution is used, enter contaminant concentration in ppmvd entering control device after dilution. 2 See District Rule 102 for the definition of ROC. For permitting purposes, list the maximum total hydrocarbon concentration detected by a PID calibrated to isobutylene.
ppmvd
ppmvd
ppmvd
❑Yes ❑No Is a pilot test report or detailed analysis confirming the above inlet concentrations included in this application? If not, provide the detailed basis for how the values were determined as a separate attachment.
V. Well Information
Extraction Wells
Number of Extraction Wells
Diameter of Wells
Maximum Depth
Well Spacing
Radius of Influence
ft.
ft. deep
ft.
ft.
Injection Wells
Number of Injection Wells
Diameter of Wells
Maximum Depth
Design Flowrate
Ambient Air Used?
❑ Yes
ft.
ft. deep
SCFM
❑ No
VI. Vacuum Extraction Blower
Blower Power Source (electric, diesel, etc):
Horsepower:
HP
Manufacturer:
Model:
Design Flow Rate: MAX SCFM
To
MIN SCFM
APCD -77 (07/01/2024)
Attachment B
VII. Control Device (Fill out applicable section)
Thermal Oxidizer (Phase I)
District assumes 98% control efficiency
for all calculations
Max Capacity:
r SCFM Fuel Type:
Heat Rating:
MMBTU/hr
Operating Temperature: F
To
F
Fuel Consumption rate:
Manufacturer
Model
Catalytic Oxidizer (Phase II)
District assumes 95% control efficiency for all calculations Max Capacity: SCFM
Fuel Type:
Heat Rating:
MMBTU/hr
Operating Temperature: F
To
F
Fuel Consumption rate:
Manufacturer
Model
Catalyst Specific Tn=ormation:
Catalyst Type/Material:
Catalyst Life Expectancy:
Carbon Adsorption (Phase
III)
District assumes
90% control efficiency for all calculations
Flowrate Operating Range
MIN Flowrate:
scFM
MAX Flowrate:
SCFM
Operating Temperature:
F
To
F
Carbon Weight Per Cannister:
Lb
Replacement Schedule:
Manufacturer
Model
Internal Combustion Engine
Aux Fuel Type:
Max Capacity: scFM
Horsepower:
HP
Heat Rating:
MMBTUn„
Number of Cylinders:
Fuel Consumption rate:
Manufacturer
Model
Combustion Temperature: F
Manifolding: Air Stripper Used?
❑ Yes
No
VIII. Stack Parameters
Exhaust Stack Height:
+v
Stack Diameter:
n_
Design Flow Rate:
MAX SCFM
To
MIN SCFM
Gas Exit Velocity:
MAX li/sec
To
MIN fl see
Exhaust Temperature:
MAX F
To
MIN F
Exhaust Blower Used?
r- Yes
L No
Horsepower:
HP
Manufacturer:
7 Model:
APCD -77 (07/01/2024)
Attachment B
IX. Monitoring Systems (Fill out all that apply)
System Parameter
Instrument Manufacturer
Instrument Model
Calibration Schedule
Control Device Inlet Temp (F)
Stack Outlet Temp (F)
Control Device Inlet Gas Flow (SCFM)
Stack Outlet Gas Flow (SCFM)*
Control Device Inlet Pressure (PSIG)
Control Device Outlet Pressure (PSIG)
I
System Influent Flow Rate (SCFM)
Catalytic Oxidizer Bed Temp (F)*
Amount of Supplemental Fuel Used**
« Required for thermal oxidizer and catalytic control devices.
Required for systems which use fossil fuel (e.g., Diesel oil, natural gas, propane) for any device within the system (e.g, thermal oxidizer, pump driven by an internal combustion engine)
X. Air Dilution (Fill out if air dilution will be used at the control device inlet) Estimated Turndown Ratio:
Max Dilution Air Flowrate
SCFM
Dilution Air Temperature:
MAX F
To MIN F
Air Dilution Blower Information
Ambient Air Used?
❑ Yes
❑ No
Horsepower:
HP
Manufacturer:
Model:
XI. Electrical Generator Engines (Fill out all that apply) Portable Engines Used?
Grid Power Used?
7 Yes
❑
No
x Yes
x No
Portable Engine Information
Fuel Type (gas, diesel, etc):
*Horsepower:
* If the portable engine is over 49 bhp, fill out the appropriate APCD form listed below for the engine and submit it with this application.
Form 34P - Diesel Fired Primary Engine Application
Form 70 - Spark Ignited IC Engine Application (natural gas, propane, gasoline) APCD -77 (07/01/2024)
Attachment B
Contaminated Soil and/or Groundwater Clean -Up
Application Form -77
Applicant/Preparer Statement
The person who prepares the application also must sign this form. The preparer may be an employee of the owner/operator or an authorized agent (contractor/consultant) working on behalf of the owner/operator (an Authorized Agent Form -01A is required).
I certify pursuant to H&SC Section 42303.5 that all information contained herein and information submitted with this application is tru and correct.
Completed By
Signature
Company
Date
Application Checklist (Have you submitted all the required information? Please check off the boxes) ❑K
Permit Fees (Fee = $3,065). This includes an application filing fee of $565 plus a cost reimbursement deposit of $2,500 to cover hourly costs for APCD staff time.
❑ A copy of the approved lead agency site remediation plan.* P
An Emissions Verification Test Plan consistent with the District's Guidance Document (Form 07). The District will not issue an ATC permit unless the Test Plan meets District requirements.* Maximum influent and effluent concentration calculations using the District default control efficiency for the applicable control device. (98% for Thermal Oxidizer, 95% for Catalytic Oxidizer, 90% for Carbon Adsorption) ❑ Pilot test or other analytical analysis confirming inlet concentrations of contaminants to the control device. ❑ Attached copy of any government agency's order to remediate the site (if applicable).* Attached facility plot showing tank locations, property line and surrounding area up to 2,500 feet away. Identify all land uses in the area and highlight sensitive areas such as schools, residential areas, restaurants and shopping areas. ❑ List of all equipment, supporting manufacturer information and a process flow diagram for the equipment. ❑ Form -01 (General Permit Application Form) required for every permit application.
Form -01A (Authorized Agent Form) attached if this application was prepared by and/or if correspondence is requested to be sent to an Authorized Agent (e.g., contractor or consultant). This form must accompany each application.
Form -03 (School Summary Form) attached if the project's property boundary is within 1,000 feet of the outer boundary of a school (k-12) and you want to perform work during school hours.
Form -15S (Health Risk Assessment Screening Application Form) required for every contaminated soil/groundwater ❑ cleanup project. Note that the BRA screening fee is not required as APCD costs will be assessed on an hourly basis. * Submit both a paper and electronic PDF copy of these documents.
PLEASE NOTE THAT FAILURE TO COMPLETELY PROVIDE ALL REQUIRED INFORMATION OR FEES WILL RESULT IN YOUR APPLICATION BEING RETURNED OR DEEMED INCOMPLETE.
APCD -77 (07/01/2024)
Attachment B
Contaminated Soil and/or Groundwater Clean -Up
Application Form -77
NOTICE OF CERTIFICATION:
All applicants must complete the following Notice of Certification. This certification must be signed by the Authorized Company Representative representing the property owner. Signatures by Authorized Agents will not be accepted.
I,
NOTICE of CERTIFICATION
Type or Print Name of Authorized Company Representative , am employed by or represent
Type or Print Name of Business, Corporation, Company, Individual, or Agency (hereinafter referred to as the applicant), and certify pursuant to H&SC Section 42303.5 that all information contained herein and information submitted with this application is true and correct and the equipment listed herein complies or can be expected to comply with said rules and regulations when operated in the manner and under the circumstances proposed. If the project fees are required to be funded by the cost reimbursement basis, as the responsible person, I agree that I will pay the Santa Barbara County Air Pollution Control District the actual recorded cost, plus administrative cost, incurred by the APCD in the processing of the application within 30 days of the billing date. If I withdraw my application, I further understand that I shall inform the APCD in writing and I will be charged for all costs incurred through closure of the APCD files on the project.
For applications submitted for Authority to Construct, modifications to existing Authority to Construct, and Authority to Construct/Permit to Operate permits, I hereby certify that all major stationary sources in the state and all stationary sources in the air basin which are owned or operated by the applicant, or by an entity controlling, controlled by, or under common control with the applicant, are in compliance, or are on approved schedule for compliance with all applicable emission limitations and standards under the Clean Air Act (42 USC 7401 et seq.) and all applicable emission limitations and standards which are part of the State Implementation Plan approved by the Environmental Protection Agency.
I agree that as property owner I am ultimately responsible for all activities related to this project. This includes compliance, operations, and the oversight of authorized agents and equipment owners/operators. It is my responsibility, as the property owner, to notify the APCD using the Form APCD-01T of any change to the equipment operator, equipment owner, or authorized agent. within 30 days of the change.
Completed By:
Date:
Signature of Authorized Company Representative
Title:
Phone:
APCD -77 (07/01/2024)
Attachment B
APPENDIX E
CONTINGENCY RETROFIT VAPOR MITIGATION SYSTEM BASIS OF
DESIGN
LANGAN
LANGAN
APPENDIX E
Contingency Retrofit Vapor Mitigation System Basis of Design Attachment B
Technical Excellence
Practical Experience
Client Responsiveness
On behalf of the County of Santa Barbara, the City of Santa Maria, and the Santa Maria Public Airport District (Agencies), Langan CA, Inc. (Langan) has prepared this Basis of Design for a Contingency Retrofit Vapor Mitigation System (Contingency VMS BOD) for the former SEMCO Twist Drill and Tool Company, Inc., (SEMCO) Site located at 2926, 2936, 2946, 2956, 2976, and 2986 Industrial Parkway in Santa Maria, California (the "Site"). This Contingency VMS BOD is an appendix to the Work Plan for Onsite Soil Vapor Extraction (SVE Work Plan) and the VMS retrofit will be installed concurrently with the SVE system construction. Operation of the VMS is contingent on the soil vapor concentrations following SVE system operation and sampling as set forth in the Settlement Agreement.
This Contingency VMS BOD is intended to provide a conceptual VMS design that will be installed concurrently with the SVE system construction and operated after SVE completion if greater than 1x1 0-5 human health vapor intrusion risk remains beneath the on -site SEMCO building, as outlined in the Settlement Agreement. The VMS is intended to operate, if needed, in the area beneath the building with greater than 1x10-5 vapor intrusion risk after SVE operation (target area). The purpose of the contingency VMS is to provide a preferential pathway for vapors that may be present beneath the building in the target area to be readily released to the atmosphere instead of potentially migrating through the foundation slab and into indoor air.
This Contingency VMS BOD provides a VMS schematic depicting the major system components (Figure E1) and is generally guided by the California Department of Toxic Substances Control's (DTSC) Final Vapor Intrusion Mitigation Advisory, Revision 1, dated October 2011 (DTSC, 2011).
1.0 PASSIVE VAPOR COLLECTION AND VENTING SYSTEM
The contingency VMS is intended to be a passive air inlet and venting system and will consist of a horizontal collection and venting system installed below the building slab to allow soil vapors that may otherwise collect beneath the slab to instead migrate and vent to the atmosphere outside the building. These features are described in greater detail in the following paragraphs and a conceptual design is shown on Figure E1.
The VMS will be installed in the target area which is below the eastern building slab within the planned SVE operations area where elevated trichloroethene (TCE) concentrations currently exist.
The VMS will consist of two 3 -inch diameter perforated schedule 40 polyvinyl chloride (PVC) or high -density polyethylene (HDPE) pipes installed in the two conveyance piping trenches beneath the building that will be constructed as part of the SVE system; approximate locations are shown on Figure E1. The perforated pipes are intended to be installed parallel to the solid vapor well lines for the SVE system within the trenches and the two perforated pipes will manifold at a single location outside the building at the riser. The VMS pipes will not connect to the SVE system. The perforated pipe sections will have three 5/8 -inch diameter holes across the upper one-third of the pipe at a spacing of three inches on center and periodic 5/8 -inch diameter holes on the underside of the pipe to allow potential water from condensation to drain from the pipe. 924 Anacapa Street, Suite 2X Santa Barbara, CA 93101 T: 805.957.6000 F: 805.957,6001 www.langan.com New Jersey • New York • Connecticut • Massachusetts • Pennsylvania • Ohio • Illinois • North Carolina • Virginia • Washington, DC California • Texas • Arizona • Utah • Colorado • Washington • Florida I Athens • Calgary • Dubai • London • Panama
Contingency Retrofit Vapor Mitigation System Basis of Design 2926, 2936, 2946, 2956, 2976, and 2986 Industrial Parkway Santa Maria, California
Attachment B
22 September 2025
781016901
1.1 Risers and Vent Caps
A single vent riser is proposed for the target area. The riser will be fitted with vent caps (Vacu- Stack® Model VSS or equivalent), which will allow the vapors to be released to the atmosphere at the roof level. Both subsurface perforated pipes will manifold into one riser pipe outside the building.
The riser will be constructed of 3 -inch -diameter ductile iron pipe, cast iron pipe, or galvanized steel pipe and will be labeled "CONTAINS VAPORS; DO NOT BREAK OR CUT". The top of the riser pipe will extend to an elevation of one foot above the wind screen, roof parapet, or top edge of the roof level, and the top of the riser will be located a minimum of 15 feet away from fresh air intakes for the building's heating, ventilation, and air conditioning (HVAC) system or other openings (windows, doors, etc.). The riser will be constructed of threaded pipe, or blank pipe connected with chemically resistant no -hub couplings. Although the VMS is intended to be entirely passive the riser could be fitted with a radon fan, if required.
1.2 Perimeter Inlet Vent
If a gravel or high permeability layer is present beneath the building slab, one perimeter inlet vent will be considered as part of the VMS design (Figure E1). The purpose of the perimeter inlet vent is to facilitate convective airflow up the vertical riser pipe of the collection and venting system by allowing fresh air to enter the space beneath the building slab. The inlet vent would be embedded into the gravel layer under the building and daylight at the exterior building face. The inlet vent would be constructed of 3 -inch -diameter PVC piping, positioned at least of 36 -inches away from operable windows and door jams, and the exterior inlet opening would be screened to limit intrusive material, as feasible.
2.0 CONSTRUCTION OBSERVATION
Construction observation will be performed during the installation of the SVE system and documented in the SVE Construction Completion Report.
3.0 SUMMARY
This conceptual VMS will be constructed concurrently with the SVE system outlined in the SVE Work Plan and operated after SVE completion if required by detected soil vapor concentrations.
In accordance with the Settlement Agreement requirements, VMS operation is applicable if concentrations of TCE likely remain in the subsurface beneath the SEMCO building above 3,000 µg/m3.
After installation, the VMS shall be owned, operated, and the responsibility of the current owner(s). Maintenance, repairs, and any other operation needs for the VMS shall be the responsibility of the current owner(s).
Enclosures: Figure E1 — Conceptual Vapor Mitigation System Schematic LANGAN
Attachment B
FIGURE
LANGAN
Attar,
irnent
3 Conceptual Design Only
•
p
I�
Previous Soil Vapor Sampling
Locations
Existing Extraction Well Location
Proposed Extraction Well Location
Riser
SV28
SV25
Inlet Vent
— — — Vent Pipe
Former Samoa Building
Parcel
fl
• t
ielge
_ Project
•SV22
• SV30
Notes:
1. Aerial imagery provided by Nearmap, 07101'2024.
2. All features shown are approximate.
3 SVE = Soil Vapor Extraction
4 Inlet vents will be included as allowable based on
the conditions of the building foundations.
5. Conceptual vapor mitigation system design riser number. venting spacing, and piping spacing based an the Crty of Los ;Angeles Department of Building and Safety's Standard Plan:
Methane Hazard Mitigation dated 8 March 2010
40 0 40
JIM
far
t�SV31
• SV20
•
r �
EX -1
-a.
•SV32
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LANGAN
Langan CA, Inc.
104 W Anapamu Street, Suite 2048
Santa Barbara, CA 93191
SANTA MARIA
Figure Title
CONCEPTUAL VAPOR
MITIGATION SYSTEM
SCHEMATIC
Project No.
781016901
Date
7/30/2025
Scale
1" = 40'
Drawn By
AC
Figure
E1
SCALE IN FEET
T: 805.957.6000 F: 805.957.5001 www.langan.com
SANTA BARBARA COUNTY CALIFORNIA
Path: 1'dangan.conndatalSBAldata91781016901 iProjett DatatArcGISLAPRX1781018901.aprx •
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Previous Soil Vapor Sampling
Locations
Existing Extraction Well Location
Proposed Extraction Well Location
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_ Project
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Notes:
1. Aerial imagery provided by Nearmap, 07101'2024.
2. All features shown are approximate.
3 SVE = Soil Vapor Extraction
4 Inlet vents will be included as allowable based on
the conditions of the building foundations.
5. Conceptual vapor mitigation system design riser number. venting spacing, and piping spacing based an the Crty of Los ;Angeles Department of Building and Safety's Standard Plan:
Methane Hazard Mitigation dated 8 March 2010
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LANGAN
Langan CA, Inc.
104 W Anapamu Street, Suite 2048
Santa Barbara, CA 93191
SANTA MARIA
Figure Title
CONCEPTUAL VAPOR
MITIGATION SYSTEM
SCHEMATIC
Project No.
781016901
Date
7/30/2025
Scale
1" = 40'
Drawn By
AC
Figure
E1
SCALE IN FEET
T: 805.957.6000 F: 805.957.5001 www.langan.com
SANTA BARBARA COUNTY CALIFORNIA
Path: 1'dangan.conndatalSBAldata91781016901 iProjett DatatArcGISLAPRX1781018901.aprx
TO:
FROM:
DATE:
SUBJECT:
COUNCIL AGENDA REPORT
Mayor and City Council
Thomas T. Watson, City Attorney
October 21, 2025
Adoption of Resolution Approving Settlement Agreement, and any related supporting documents necessary to effectuate the settlement of the matter of Central Coast Water Authority et al. vs. Santa Barbara County Flood Control District et al. (Case No. 21CV0
Description:
The City Council will consider adopting a resolution approving a Settlement Agreement, and any related supporting documents necessary to effectuate the settlement of the matter of Central Coast Water Authority et al. vs. Santa Barbara County Flood Control District et al. (Case No. 21 CV02432) and ratifying all prior signatures.
Environmental Notice: This action is not a project subject to the California Environmental Quality Act (CEQA) because it is an organizational or administrative activity that will not result in direct or indirect physical changes in the environment (CEQA Guideline Section 15378(b)(5)).
RECOMMENDATION
1. Adopt a Resolution approving Settlement Agreement and any related supporting documents necessary to effectuate the settlement of the matter of Central Coast Water Authority et al. vs. Santa Barbara County Flood Control District et al. (Case No. 21 CV02432) and ratifying all prior signatures; and
2. Authorizing Mayor, or designee, to execute the Settlement Agreement and any related supporting documents.
BACKGROUND:
The Central Coast Water Authority (CCWA), its eight member agencies including the City of Santa Maria (Members), and the Santa Barbara County Flood Control and Water Conservation District (District) have reached a comprehensive settlement of the claims and issues raised in the pending lawsuit initiated by CCWA and the Members against the District in June, 2021 regarding the parties' respective rights and obligations to the State Water Project (SWP) under the State Water Supply Contract (SWP Contract).
The parties have agreed to execute two contracts to settle the dispute —a Settlement Agreement and an Assignment, Assumption, and Release Agreement (Assignment Agreement). The Settlement Agreement requires the District to transfer the SWP Contract to CCWA. Contingent upon the California Department of Water Resources (DWR)
approval of the transfer, the Settlement Agreement obligates CCWA and the Members to dismiss the lawsuit with prejudice and make 10 annual payments of $580,000 to the District (reimbursing the District for the investments made by County tax payors to retain the rights to SWP water during the period 1963-1985.) The Settlement Agreement also grants the District an option to purchase up to 1,700 acre-feet of SWP water from CCWA, if CCWA elects to purchase additional water supplies from DWR in the future.
Pursuant to the Assignment Agreement, (1) the District assigns all of its rights, interests, and obligations pursuant to the SWP Contract to CCWA; (2) CCWA assumes all of the District's rights, interests, and obligations; and (3) DWR consents to the transfer of the SWP Contract to CCWA and releases the District from its obligations pursuant to the SWP Contract.
CCWA has been responsible for the conveyance, treatment, and delivery of SWP water pursuant to the SWP Contract since 1991. Assignment formalizes the existing circumstances, rights, and obligations of the parties. Assignment of the SWP Contract does not change the SWP Contract itself. The only change is that CCWA will be substituted for the District as the contracting party with DWR.
DISCUSSION:
The settlement of this lawsuit avoids continued litigation between public agencies and the associated costs for taxpayers and ratepayers. Settlement avoids future disputes between CCWA and the District regarding their respective rights, interests, and obligations with respect to the SWP Contract, and reimburses the District for the investments made by County tax payors to retain the rights to SWP water during the period 1963-1985. Settlement also provides a mechanism for assignment of the SWP Contract.
The assignment of the SWP Contract from the District to CCWA completes the transfer of responsibility for the SWP Contract from the District to CCWA, as initially contemplated in 1991 when CCWA became responsible for administration of the SWP Contract and all payments to the State (DWR). Assignment also:
• Aligns CCWA's decision -making authority with CCWA's financial responsibility for SWP supplies.
• Streamlines local decision -making with respect to the importation and management of SWP water supplies.
• Relieves the District (and thus County tax payors) of any and all liability under the SWP Contract.
• Relieves cities and other communities within Santa Barbara County who do not receive SWP water from any potential financial obligation under the SWP Contract. 2 Alternative(s)
The alternative to settlement is continued litigation which creates uncertainty on both sides and could lead to additional lawsuits as the current lawsuit does not fully address all issues between the parties as contemplated by the proposed settlement agreement and related assignment.
Fiscal Considerations
The payments associated with the settlement of this case will be made by CCWA with the City of Santa Maria paying its proportionate share along with the other member agencies which will begin upon the effectuation of the settlement and be paid annually as required.
Impact on the Community
This proposed settlement will avoid continued litigation between public agencies and the associated costs for taxpayers and ratepayers, while avoiding future disputes between CCWA and the District regarding their respective rights, interests, and obligations regarding the SWP Contract. Settlement also provides a mechanism for assignment of the SWP Contract.
ATTACHMENT(S)
1. Resolution
2. Settlement Agreement
3 Attachment A
RESOLUTION NO.
A RESOLUTION OF THE CITY COUNCIL
OF THE CITY OF SANTA MARIA, CALIFORNIA
APPROVING THE SETTLEMENT AGREEMENT AND ANY RELATED
SUPPORTING DOCUMENTS NECESSARY TO EFFECTUATE THE
SETTLEMENT OF THE MATTER OF CENTRAL COAST WATER AUTHORITY ET AL. VS. SANTA BARBARA COUNTY FLOOD CONTROL DISTRICT ET AL. (CASE NO. 21CV02432) AND RATIFYING ALL PRIOR SIGNATURES WHEREAS, The Central Coast Water Authority (CCWA), its eight member agencies including the City of Santa Maria (Members), and the Santa Barbara County Flood Control and Water Conservation District (District) have reached a comprehensive settlement of the claims and issues raised in the pending lawsuit Central Coast Water Authority et al. vs. Santa Barbara County Flood Control District et al. (Case No. 21CV02432) initiated by CCWA and the Members against the District in June, 2021 regarding the parties' respective rights and obligations to the State Water Project (SWP) under the State Water Supply Contract (SWP Contract); and WHEREAS, The parties have agreed to execute two contracts to settle the dispute —a Settlement Agreement with the member agencies of CCWA and an Assignment, Assumption, and Release Agreement between District and CCWA (Assignment Agreement); and
WHEREAS, The Settlement Agreement requires the District to transfer the SWP Contract to CCWA. Contingent upon the California Department of Water Resources (DWR) approval of the transfer, the Settlement Agreement obligates CCWA and the Members to dismiss the lawsuit with prejudice and make 10 annual payments of $580,000 to the District, (reimbursing the District for the investments made by County tax payors to retain the rights to SWP water during the period 1963-1985.) The Settlement Agreement also grants the District an option to purchase up to 1,700 acre-feet of SWP water from CCWA, if CCWA elects to purchase additional water supplies from DWR in the future; and
WHEREAS, Pursuant to the Assignment Agreement, (1) the District assigns all of its rights, interests, and obligations pursuant to the SWP Contract to CCWA; (2) CCWA assumes all of the District's rights, interests, and obligations; and (3) DWR consents to the transfer of the SWP Contract to CCWA and releases the District from its obligations pursuant to the SWP Contract; and
WHEREAS, Settlement of this lawsuit avoids continued litigation between public agencies and the associated costs for taxpayers and ratepayers, avoids future disputes between CCWA and the District regarding their respective rights, interests, and obligations with respect to the SWP Contract, and provides a mechanism for assignment of the SWP Contract.