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SR0078487
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2900 - Site Mitigation Program
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SR0078487
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Last modified
3/2/2022 11:09:36 AM
Creation date
3/2/2022 11:04:57 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
CORRESPONDENCE
RECORD_ID
SR0078487
PE
2903
FACILITY_ID
FA0023388
FACILITY_NAME
PUBLIC WORKS
STREET_NUMBER
1810
Direction
E
STREET_NAME
HAZELTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
15518002
ENTERED_DATE
12/12/2017 12:00:00 AM
SITE_LOCATION
1810 E HAZELTON AVE
QC Status
Approved
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EHD - Public
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MONITORING AND REPORTING PROGRAM ORDER NO. R5-2015-0012-043 4 <br />SAN JOAQUIN COUNTY PUBLIC WORKS <br />SAN JOAQUIN COUNTY <br />without Central Valley Water Board concurrence. Additional requirements are <br />detailed in the REPORTING section below. <br />2. Samples should be representative of the volume and nature of the discharge or <br />matrix of material sampled. The time, date, and location of each grab sample shall <br />be recorded on the legal chain of custody form. <br />GROUNDWATER MONITORING <br />3. As shown on Figure 1, there are 10 monitor wells, 7 ozone injection wells, 1 soil <br />vapor extraction (SVE) well, and 1 SVE/air-sparge (AS) well associated with this <br />Site. The groundwater monitoring program for these wells and any treatment system <br />wells installed subsequent to the issuance of this MRP shall follow the schedule <br />below. Monitoring wells with free NAPH or visible sheen shall be monitored, at a <br />minimum, for NAPH thickness and depth to water. The volume of extracted <br />groundwater, if applicable, shall also be provided in quarterly monitoring reports. <br />Sample collection and analysis shall follow standard EPA protocol. <br />For the purpose of the proposed full-scale implementation, all Site wells have been <br />divided and identified as Background Zone wells (MW -5, MW -6, MW -7), Treatment <br />Zone Wells (MW -1, MW -2), Transition Zone wells (MW -9, MW -10), and Compliance <br />Zone wells (MW -3, MW -4, MW -8). <br />The monitoring wells, extraction wells and/or injection wells shall be sampled <br />according to the schedule in Tables 1A and 1 B and the samples analyzed by the <br />methods in Table 2, as follows: <br />Table 1A: Samplings Frequency (Prior to Full -Scale Implementation) <br />Well Number' <br />Frequency2 <br />Constituent3 <br />Monitoring <br />Objective <br />MW -1, MW -2 <br />Other8 <br />Suite A, Suite B <br />Treatment Zone <br />MW -9, MW -10 <br />Other8 <br />Suite A, Suite B <br />Transition Zones <br />MW -3, MW -4, MW -8 <br />Other8 <br />Suite A, Suite B <br />Compliance Zone6 <br />MW -5, MW -6, MW -7 <br />Other8 <br />Suite A, Suite B <br />Background Zone? <br />1 Well Numbers and location as shown on Figure 1 <br />2 i.e. weekly, monthly, quarterly, semi-annually, annually, other. Semi-annual sampling <br />occurs 1 st and 3rd quarters, annual sampling occurs 1 st quarter, biennial sampling <br />occurs every two years in 1 st quarter, with the first sampling during year two. <br />3 Constituent analytical methods are listed in Table 2 <br />4 Well used to evaluate in-situ bioremediation progress inside the treatment zone, to <br />gauge effectiveness of ISCO injection in reducing the dissolved petroleum hydrocarbon <br />concentrations, and to monitor potential changes in groundwater geochemistry that <br />could be attributed to the injection of oxidizing agents. <br />
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