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2900 - Site Mitigation Program
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PR0540816
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Last modified
5/28/2021 11:16:53 AM
Creation date
5/28/2021 11:08:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0540816
PE
2960
FACILITY_ID
FA0023388
FACILITY_NAME
PUBLIC WORKS
STREET_NUMBER
1810
Direction
E
STREET_NAME
HAZELTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
15518002
CURRENT_STATUS
01
SITE_LOCATION
1810 E HAZELTON AVE
P_LOCATION
01
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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Additional Subsurface Investigation and Well Installation Work Plan <br />San Joaquin County Public Works <br />June 19, 2017 <br />Page 5 <br />with hollow stem augers. Soil samples will be collected at 5-foot intervals using a 2-inch diameter <br />California-modified split spoon sampler for soil characterization using the Unified Soil Classification <br />System (USCS). Condor does not anticipate collecting any soil samples from the shallow monitoring <br />wells for laboratory analyses. <br />The shallow monitoring wells will be constructed with 15 feet of 2-inch outside diameter, Schedule 40, <br />flush-threaded, machine-slotted PVC screen (slot size 0.010). A flush-threaded PVC bottom cap will be <br />placed at the bottom of the screen section in each well. Blank PVC casing will be installed above the <br />screen to the ground surface. A filter pack of #2/12 or #2/16 sand will be placed in the annular space to <br />approximately two feet above the screen while the augers are in place. The depth of the sand in the <br />annulus of the well will be monitored with a weighted tape measure while the sand is being placed and <br />the augers are being gradually retracted to avoid bridging. To form a protective seal, approximately two <br />feet of bentonite chips will be installed above the sand in the well. The bentonite chips will be installed as <br />the augers are retracted. The bentonite chips will be hydrated with potable water. A surface seal of neat <br />cement will be poured into the annulus of the well using a tremie pipe and will extend from the bentonite <br />to the ground surface. The monitoring wells will be completed at the ground surface with traffic-rated, <br />locking well boxes. Details of well construction will be noted on the geologic logs, including the depth <br />intervals of the screen, sand pack, and seal. A typical monitoring well construction diagram is shown on <br />Figure 7 (Appendix A). <br />All down-hole drilling equipment will be decontaminated prior to use in each well boring. The drill <br />cuttings and any cleaning effluent will be placed in Department of Transportation (DOT)-approved 55- <br />gallon drums, sealed, labeled, and left on site pending laboratory analyses. <br />4.5 OZONE INJECTION WELL INSTALLATION PROCEDURES <br />One additional ozone injection well will be installed at the Site to provide adequate injection of ozone <br />throughout the heart of the dissolved contaminant plume. The ozone injection well (0W-7) will be <br />installed between the southern dispenser and UST #2, where ozone injection well OW-7 was previously <br />proposed but not installed. The proposed location is shown on Figure 6 (Appendix A). <br />The ozone injection well will be installed using hollow-stem auger drilling methods. Drilling activities <br />will be performed under the supervision of a Condor geologist. The soil cuttings from the borings will be <br />logged in accordance with the Unified Soil Classification System (USCS). Descriptions of soil types <br />encountered will be recorded on geologic logs. All down-hole drilling equipment will be decontaminated <br />prior to use in each well boring. The drill cuttings and any cleaning effluent will be placed in Department <br />of Transportation (DOT)-approved 55-gallon drums, sealed, labeled, and left on site pending laboratory <br />analyses. <br />The ozone injection well bore hole will be drilled to a total depth between approximately 45 to 48 feet <br />bgs. The actual installation depth may be modified after completion of the deep boring investigation <br />confirms the lithology beneath the Site. The anticipated depth of the ozone sparge point is intended to <br />correlate with a poorly graded sand layer identified during the installation of MW-1 and shown cross <br />section B-B' (Figure 4, Appendix A). The ozone injection well will be constructed with an 18-inch long, <br />1.5-inch outside diameter (0.D.) porous Kynar sparge point. Blank 1-inch Schedule 80 PVC casing will <br />be installed above the sparge point to the ground surface. A filter pack of #3 or #2/12 Monterey sand will <br />be placed in the annular space to approximately 1.5 feet above the sparge point while the augers are in <br />place. The depth of the sand in the annulus of the well will be monitored with a weighted tape measure <br />while the sand is being placed and the augers are being gradually retracted to avoid bridging. <br />Approximately two feet of time-release bentonite pellets will be placed above the sand to form a <br />CONDOR
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