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3500 - Local Oversight Program
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PR0545262
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Last modified
2/3/2020 10:51:19 AM
Creation date
2/3/2020 10:01:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545262
PE
3528
FACILITY_ID
FA0009940
FACILITY_NAME
SAN JOAQUIN CATHOLIC CEMETERY
STREET_NUMBER
719
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12720002
CURRENT_STATUS
02
SITE_LOCATION
719 E HARDING WAY
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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i <br /> qj <br /> 1.2.2 Remediation System -Operation and Confirmation Sampling ; <br /> From June 1999 through June 2000, ENSR operated a soil vapor extraction (SVE) system at the <br /> site. Initially, ENSR extracted from U0-1;D, VW-1 S, VW-2S, VW-3, and VW-4. After several <br /> months of operation, air sparging was initiated in MW-1. According to ENSR, the remediation <br /> 911,11t. 11j <br /> system removed over 7,000 pounds of gasoline hydrocarbons from the subsurface. In July <br /> 2000, ENSR decommissioned theisystem and removed the equipment from the site. <br /> On November 28, 2000, Ramage Environmental published Environmental Site Investigation <br /> Report documenting the results of al.sensitive receptor survey and the drilling of confirmation soil <br /> borings. <br /> 1 According to available records, three property parcels_ within 2,000-feet of the site have <br /> operating water wells. These properties include the San Joaquin Catholic Cemetery (site), St. <br /> Joseph's Hospital, and a residential!dwelling at 1821 North Hunter Street. The locations of the ' <br /> wells on the cemetery and hospital properties are shown on Figure 3. <br /> To confirm the effectiveness of,remediation efforts, soil samples were collected every 10 feet to <br /> a total depth of 100 feet directly beneath.the former USTs. The soil sample results indicated <br /> I .4'7:1!1' i F 11 <br /> that except for 560 milligrams per kilog'ra"m (mg/kg) of Total Petroleum Hydrocarbons (TPH)-as- <br /> gasoline in soil at a depth of approximately 10 feet below ground surface (bgs), the vadose zone <br /> was almost completely remediated by the SVE system. <br /> To delineate the vertical extent of impacted groundwater, discrete groundwater samples were <br /> collected at 75, 90, and 125 feet bgs,from soil borings located approximately 20 feet northeast <br /> (downgradient) of the former USTs.-Thei;discrete groundwater sample results indicated that the <br /> vertical extent of impacted groundwater was mostly delineated. Concentrations of methyl tertiary <br /> th depth and are not present in the 125-foot <br /> butyl ether (MTBE) decline significantly wi <br /> groundwater-bearing interval. Only:.1,2=d�ichloroethane (1,2-DCA) was detected in the 125-foot <br /> groundwater sample, at a low concentration of 0.5 micrograms per liter (µg11). These <br /> � � <br /> ' groundwater analytical results are sum+Imai�rized in Table 1. <br /> 5 �, i <br /> On February 7, 2001, Ramage Envirloinmental met with PHSIEHD and RWQCB to review the <br /> project. In the meeting, RWQCB requested that the extent of impacted groundwater be further <br /> defined, a downgradient monitoring:well cluster be installed, and quarterly groundwater <br /> ,..e {1 ai <br /> ! monitoring continue at the site. On February 13, 2001, Ramage Environmental requested I <br /> written regulatory directive to prepare the:!subject work plan, and on March 16, 2001, PHSIEHD <br /> documented their directive. <br /> L 5 <br /> I <br /> L - <br />
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