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Environmental Health - Public
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EHD Program Facility Records by Street Name
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H
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HAM
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2900 - Site Mitigation Program
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PR0548453
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Entry Properties
Last modified
3/16/2026 10:35:46 AM
Creation date
7/23/2025 2:14:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0548453
PE
2950 - ENVIRON ASSESS
FACILITY_ID
FA0027675
FACILITY_NAME
LAKEWOOD PLAZA
STREET_NUMBER
306
Direction
N
STREET_NAME
HAM
STREET_TYPE
LN
City
LODI
Zip
95252
APN
03710030
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
306 N HAM LN LODI 95252
Tags
EHD - Public
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22 November 2023 AdvancedGeo <br /> Project No. 23-7523 An Employee-Owned Company <br /> Page 4 of 7 Q W <br /> closed after reaching 2 to 6 inches' mercury (Hg). The final pressure and time were <br /> recorded. The sampling ports on the sampling canisters were then capped with brass <br /> endcaps and the canisters were placed in a dry container (room temperature). Following <br /> sample collection, organic vapor in the wells was measured using a PID. Soil-vapor <br /> samples were labeled with sample ID, project name, date, time, and samplers' initials. <br /> The samples were logged on a chain-of-custody form and placed into dry containers. <br /> The soil-vapor samples were logged on a chain-of-custody form and delivered to Eurofins <br /> Air Toxics, LLC, (Eurofins), a California Environmental Laboratory Accreditation Program <br /> (ELAP)-certified analytical laboratory. Soil-vapor samples were analyzed for the following <br /> chemical constituents: <br /> • VOCs in accordance with EPA Method TO-15. <br /> • Helium in accordance with ASTM D1946M. <br /> 2.3. SUB-SLAB WELL INSTALLATION AND SAMPLING <br /> On 30 October 2023, sub-slab vapor implants SS-7 and SS-8 were installed in each of <br /> the two suites (306 and 308 North Ham Lane; Figure 1). The sub-slab soil gas implant <br /> was installed by drilling a 5/8-inch diameter hole completely through the foundation slab. <br /> Once the slab was penetrated approximately 1-to 2-inches into the underlying soil to form <br /> a void, the drill bit was removed, and the borehole was cleared. The slab thickness was <br /> measured and a 5/8-inch Vapor Pin® with silicone sleeve was inserted flush into the <br /> 5/8-inch drilled hole using a dead blow hammer to tap it into place and form an air-tight <br /> seal between the silicone sleeve and the slab. A protective plastic cap was placed on the <br /> Vapor Pin® to prevent vapor loss and it was allowed to re-equilibrate before sampling. <br /> 2.4. BORING ABANDONMENT <br /> Following sample collection, each boring was permanently sealed to prevent vertical <br /> migration of potential contaminants. Soil borings were abandoned by backfilling with <br /> Portland cement from the total depth to surface grade and patched to match the <br /> surrounding surface. <br /> 3.0. FINDINGS <br /> The soil and soil-vapor sample results are summarized in Tables 1 and 2, respectively. <br /> The laboratory reports (MAI Work Order No. 2310030 and BSK Associates report No. <br /> AGK0458; Eurofins Lab ID No. 2307097A and 2307098A), QA/QC reports and chain of <br /> custody forms are included in Appendix B. <br /> The following is a summary of the soil and soil-vapor analytical results from this <br /> investigation. <br />
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