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ARCHIVED REPORTS XR0012749
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0522479
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ARCHIVED REPORTS XR0012749
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Last modified
5/17/2019 3:28:57 PM
Creation date
5/17/2019 2:06:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012749
RECORD_ID
PR0522479
PE
2957
FACILITY_ID
FA0015299
FACILITY_NAME
GEWEKE LAND DEVELOPMENT & MARKETING
STREET_NUMBER
16
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04323013
CURRENT_STATUS
01
SITE_LOCATION
16 S CHEROKEE LN
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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= <br /> s <br /> 1r:7 <br /> „i <br /> 10 <br /> vapor meter to detect hydrocarbon vapors, These data will be recorded on the log. Soil samples <br /> will be collected for laborr,ory analysis at 10-foot intervals. The sample analyzed will be that <br /> sample having the highest detected vapor reading in that 10-foot interval. <br /> Brass liners conmining soil samples selected for laboratory analysis will be covered with <br /> aluminum foil and plastic caps and sealed with plastic tape. Each sample will be labeled on site <br /> to show the date,project numb:.r, sample location,and depth interval. The sealed samples will <br /> be stored on ice in closed chests and protected from meltwater. <br /> Selected soil samples will be t:nalyzed for BTX and TPH by U.S. Environmental Protection <br /> Agency(EPA)Method 8015,modiftpd, Extraction Method 5030. The samples will be delivered <br /> to Brown and Caldwell Analytir:; Laboratories, Inc. (KCAL), in Emeryville. <br /> Construction of Monitoring Wells. The monitoring wells will be completed with 30 feet <br /> of nominal 2-inch-diameter, PVC, 0.020-inch slotted flush-threaded easing. The slotted casing <br /> will extend approximately 20 feet below the groundwater surface and 10 feet above. This design <br /> will accommodate any seasonal groundwater level fluctuations that might cr_eur at the site. Blank <br /> casing will extend from the top of the perforated section to ground surface. PVC caps will be <br /> installed at the top and bottom of the v;ell. Actual depth of the borehole and screened interval <br /> will depend on the conditions encountered during drilling. 'The wells will be packed with No. <br /> 1/20 sand from the bottom of the screen to approximately 2 feet above the top of the screen. A. <br /> 2-foot-thick layer of bentonite pellets will be placed on the tap of the sand puck. The remaining <br /> - annular space will be grouted with bentonite-cement siurry placed by tremie pipe. The well will <br /> be complete''at grads:using a water-right locking cover. Typical well construction is illustrated <br /> on Figure 4. <br /> Well Development. The well will i;e de ver fed by surging,bailing,or pumping until clean, <br /> sediment-free water is produced from the well. The length of development time will vary <br /> depending upon field conditions. Water produced during development and sampling will be <br /> contained in 55-gallon barrels. GLDM will be responsible for the disposal of water and ai=:y <br /> recovered petroleum product. Prior to and following development, the depth to wtit!r will be <br /> mcasured with ar oil/water interface probe. <br /> Groundwater Sampling. Prior to sample collection, at Ieast three well volumes <br /> groundwater will be removed. A well volumc is defined as the amount of groundwater in the <br /> well casing and the sand pack with an assumed porosity of 35 percent. The pH and electrical <br /> conductivity of the water will be measured periodically prior to sample collection. <br /> All water samples will be collected, labeled, Stored, and transported as described in the <br /> groundwater sampling section above. The water samples will be submitted to BCAL for analysis <br /> "� of BTX and TPH by EPA Method 8015, modified, Extraction Method 5030. <br />
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