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2900 - Site Mitigation Program
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PR0505804
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Last modified
1/31/2020 6:06:16 PM
Creation date
1/31/2020 3:51:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0505804
PE
2960
FACILITY_ID
FA0007013
FACILITY_NAME
KOPPEL STOCKTON TERMINAL
STREET_NUMBER
2025
Direction
W
STREET_NAME
HAZELTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95203
CURRENT_STATUS
01
SITE_LOCATION
2025 W HAZELTON AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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£0. ;N1E44%41'WR <br /> and a deionized water rinse, replaced in the hole, and the soil sample was collected by augering. <br /> Each sample was placed in a clean plastic trash bag within a bucket and mixed thoroughly before <br /> being split into laboratory supplied glass containers appropriate for each analysis. All samples <br /> were labeled and placed in a chilled cooler with ice and transported, along with chain-of-custody <br /> ' documents to separate laboratories. The WESTON samples were transported for analysis to <br /> Sequoia Analytical Laboratory and the Board samples were transported to AnLab. Both <br /> laboratories are located in Sacramento, California and are certified by the State of California to <br /> ' perform the required analyses. <br /> During hand augering, soil samples were collected continuously for lithologic description of soil. <br /> The samples were described using the Unified Soil Classification System (USCS)and a lithologic <br /> log of each boring was produced. The boring logs are presented in Appendix A of this report. <br /> An equipment rinse sample (SB2-EB) was collected in the field to check decontamination <br /> procedures. After collection of one of the soil samples, the hand auger was decontaminated as <br /> discussed above. The equipment rinse sample was then prepared by pouring deionized water <br /> ' through the auger bucket and into a laboratory prepared container. The equipment rinse sample <br /> was placed on ice for transport to the lab along with the other samples. <br /> ' Soil samples were submitted for extraction by TCLP and for analysis using the following EPA <br /> methods: <br /> ' EPA Method EPA Method <br /> Analysis Used by WESTON Used by the Board <br /> Nitrate as N 300.0 353.2 <br /> Ammonia as N 350.3 350.1 <br /> ' After sampling was completed, the hand auger borings were backfilled and compacted with the <br /> ' soil cuttings that were removed except where clay was encountered. A dark grey clay layer was <br /> encountered in all three borings between 0.5 and 3 feet in thickness. The borings were <br /> backfilled across the clay layer with bentonite chips which were hydrated in order to prevent <br /> ' vertical migration of water along the boring. <br /> 3.0 RESULTS <br /> Table 1 provides a summary of the analytical results. The results represent leachable quantities <br /> of ammonia and nitrate (as N) in soil. The results from both the Board and WESTON split <br /> ' sample analyses have been included in the table for comparison. Results for ammonia as N and <br /> nitrate as N have been added together to simplify comparison between the two sets of samples. <br /> The Board's total leachable nitrogen results were significantly higher than the WESTON sample <br /> results. Total nitrogen results for the Board samples varied from 121% to 192% of the <br /> WESTON sample results. <br /> ' L'ROJEC"UNCWLIBSMA 3 NIM <br />
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