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2900 - Site Mitigation Program
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PR0540433
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Last modified
7/27/2020 9:10:25 PM
Creation date
7/27/2020 4:03:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0540433
PE
2953
FACILITY_ID
FA0023104
FACILITY_NAME
FORMER MANTECA POLICE FIRING RANGE
STREET_NUMBER
2516
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95337
APN
24131044
CURRENT_STATUS
01
SITE_LOCATION
2516 W YOSEMITE AVE
P_LOCATION
04
QC Status
Approved
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EHD - Public
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' Confirmation samples were collected for every 25-by 25-foot area(every 625 square feet) <br /> ' within the limits of excavation(bottom samples)and at discrete locations approximately every <br /> 25-linear feet along the perimeter of the excavation(sidewall samples). Samples were generally <br /> collected at the surface to a depth of three inches. Sample locations were marked with flags prior <br /> ' to sample collection. Confirmation sample locations were sketched in field notes,with <br /> approximate distances to each sample point measured from the existing fence line east of the <br /> ' excavation. Approximate confirmation sample locations and March 2017 excavation limits are <br /> depicted on Figure 2. <br /> ' Confirmation samples were collected with a stainless-steel trowel. Prior to collection of the <br /> sample,the area to be sampled was scraped with a decontaminated trowel to expose a fresh <br /> ' surface. Samples were collected in pre-cleaned glass jars. Glass jars were filled completely with <br /> soil from the exposed sampling face using a decontaminated stainless-steel trowel. A sample <br /> label was attached to each sample container. Sample jars were packaged in zip-closure plastic <br /> ' bags and then placed on ice in a cooler for storage and transport to the analytical laboratory <br /> under chain-of-custody procedures. <br /> Reusable sampling equipment was cleaned prior to and after each use by washing with Liquinox <br /> (or equivalent non-phosphate containing detergent)solution in water and subsequent rinsing with <br /> ' clean water. <br /> 3.1.1 March 2017 Analytical Results <br /> Confirmation samples(63samples total) were analyzed by Asset Laboratories for total lead by <br /> ' EPA Method 6010B. A total of 15 samples(-25%of the confirmation samples) were analyzed <br /> for California Assessment Manual (CAM)Metals by EPA Method 601013/7471A and <br /> ' polynuclear aromatic hydrocarbons(PAHs)by EPA Method 8270C/SIM. <br /> Analytical results for lead and CAM metals are summarized on Table 1 and analytical results for <br /> ' PAHs are summarized on Table 2. Analytical reports and chain-of-custody documentation for <br /> the March 2017 confirmation samples are included in Appendix D. <br /> The cleanup goal for lead(80 mg/kg)was exceeded in four samples(MFR-B-9,MFR-B-11, <br /> MFR-SW-9, AND MFR-SW-10). All other metal concentrations were below cleanup goals. <br /> ' Cleanup goals were not established in the SREW for PAHs. PAHs were only detected at low <br /> ' concentrations in six of the 15 samples analyzed. While most organic chemicals are considered <br /> to be man-made and not naturally occurring,there is historical evidence that PAHs are found in <br /> surface soils throughout California. A background study for carcinogenic PAHs in Northern <br /> ' Alift PACIFIC EDGE ENGINEERING 3 Closure Report_final.doc <br /> ' (949)470-1937;(949)470-0943(FARC) <br />
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