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2900 - Site Mitigation Program
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PR0508009
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WORK PLANS
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Last modified
5/20/2019 1:52:10 PM
Creation date
5/20/2019 1:44:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0508009
PE
2957
FACILITY_ID
FA0007882
FACILITY_NAME
ARCO #760
STREET_NUMBER
225
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04314058
CURRENT_STATUS
01
SITE_LOCATION
225 S CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Work Plan for Soil and Groundwater i vestigation E C O R <br /> Former ARCO Service Station#0760 <br /> December 13,2006 <br /> Page 4 <br /> Groundwater Monitoring Well Installation <br /> In order to evaluate the current extent of fuel-related hydrocarbons the installation of three <br /> groundwater monitoring wells (MW-6 through MW-8) are proposed at the approximate locations <br /> shown on Figure 2. Locations of proposed wells may require modification due to field conditions <br /> (obstructions). It is also possible that the locations of some wells may be moved for space <br /> constraints and/or to accommodate drilling equipment. <br /> Each boring will be advanced to approximately 70 feet bgs using a hollow-stem auger drill rig <br /> equipped with 8-inch diameter continuous flight augers. During advancement, soil samples for <br /> chemical analyses will be collected at five-foot intervals using a California-modified split-spoon <br /> sampler driven approximately 18 inches using a 140-pound hammer falling 30 inches(blow count). <br /> Soil contained in the sampler will also be classified according to the Unified Soil Classification <br /> System (USCS)by a geologist under the direction of a State of California Professional Geologist or <br /> Engineer. Soil will be screened in the field for the presence of volatile organic compounds (VOCs) <br /> using a photoionization detector (PID). Soil classifications, PID measurements, sample intervals <br /> and other pertinent geologic information will be recorded on the boring logs. All down-hole drilling <br /> equipment will be steam-cleaned following the completion of each soil boring. Down-hole sampling <br /> equipment will be washed in an Alconox solution between samples. <br /> At the terminal depth of each boring, a groundwater monitoring well will be installed within the <br /> annulus of the auger. Each well will be constructed using 2-inch diameter,flush-threaded,schedule <br /> 40 polyvinyl chloride (PVC)well casing with approximately 20 feet of 0.020-inch factory-slotted well <br /> screen placed from approximately 50 to 70 feet bgs. A filter pack consisting of sand will be placed in <br /> the annular space surrounding the entire screened interval,and will extend approximately one foot <br /> above the top of the screen interval. A bentonite pellet annular seal will be placed above the filter <br /> pack, and each well will be completed with cement and/or grout from the top of the seal to the <br /> ground surface. The well will be secured with a locking well cap, and completed with a watertight <br /> traffic-rated well box installed at grade. <br /> Monitoring Well Development/Sampling/Analysis <br /> The newly installed groundwater monitoring wells will be developed by vigorously surging the well <br /> over the length of the screen interval and by purging approximately 10 casing volumes of water. <br /> Groundwater samples will be collected and analyzed for the presence of TPHg, BTEX, MtBE, <br /> ethanol, TBA DIPE, ETBE, TAME, 1,2-DCA and EDB using EPA Method 8260B. <br /> Soil Vapor Probe Installation <br /> In order to evaluate the vapor intrusion pathway, SECOR proposes to install three soil vapor probes <br /> at the approximate locations shown on Figure 2. The vapor probes will be installed using 3-inch <br /> diameter hand-auger borings or air knife to a depth of approximately 6 feet bgs. Tygon®tubing will <br /> be placed into each open boring with the tubing bottom at approximately 5'/4 feet bgs. A 6-inch long <br /> section of 1-inch diameter, machine slotted PVC(or stainless steel)will extend from approximately 5 <br /> '/4 to 5 3/4 feet bgs. A filter pack consisting of#3 Monterey Sand (or the equivalent)will be placed in <br /> the annular space surrounding the entire screened interval from 5 feet to 6 feet bgs. The sand pack <br /> will be covered with 1 foot of dry granular bentonite followed by hydrated bentonite to 1 foot bgs. <br /> Each probe will then be completed with cement and/or grout from the top of the seal to the ground <br /> surface. The tubing will be capped with a gas-tight cap (such as Swagelok® cap) at the ground <br /> surface to prevent the potential for barometric pressure fluctuations to induce vapor transport <br /> between the subsurface and atmosphere. The excess length of Tygon®tubing with the Swagelok® <br /> type valve will be coiled up inside the well box. The probe will be secured in a watertight traffic-rated <br /> well box installed at grade. A typical vapor probe detail is included as Figure 3 <br /> ARCO 00760 Soil and Groundwater Investigation WP.doc <br />
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