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ARCHIVED REPORTS XR0012677
EnvironmentalHealth
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EIGHT MILE
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11530
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2900 - Site Mitigation Program
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PR0541077
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ARCHIVED REPORTS XR0012677
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Last modified
7/10/2019 7:46:09 PM
Creation date
7/10/2019 9:54:21 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012677
RECORD_ID
PR0541077
PE
2960
FACILITY_ID
FA0023517
FACILITY_NAME
PS MARINA 5 / KING ISLAND RESORT
STREET_NUMBER
11530
Direction
W
STREET_NAME
EIGHT MILE
STREET_TYPE
RD
City
STOCKTON
Zip
95219
APN
07119006
CURRENT_STATUS
01
SITE_LOCATION
11530 W EIGHT MILE RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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MIN <br /> e <br /> Between sampling events, equipment was cleaned using a three'nucket wash system. In this <br /> system, the brass liners and samplers are scrubbed in a bucket of tip water and detergent, rinsed <br /> in a second bucket of tap water and given a final rinse in a bucket of distilled vrater. <br /> 5.:2 Monitoring Well fnstalflation <br /> on <br /> All boring? were advanced to approximately 15 feet below static groundwater and converted to <br /> monitoring wells by the installation of 2-inch diameter, flush threaded, schedule 40 PVC screen <br /> �^ (0.010 slot) and casing. The wells were filter packed using pre-washed silica said with an <br /> z appro Timate .5-foot thick hydrated bentonite seal planed above the Hlter pack. An annular seal <br /> of neat cement was placed above the bentonite seal. All wells were completed at grade in water- <br /> tight, street-rated, well protectors and fitted :with locking caps for security purposes. All <br /> " procedures and protocol for groundwater monitoring well construction, conformed to standards <br /> set by the California Department of.Water Resources (CDWR) and the California Regional <br /> Water Quality Control Board (CRWQCB). <br /> .a <br /> Subsequent to well installation the monitoring wells were developed�1 � g peal using swab and pump <br /> methods. Development water was contained in DOT 17H drums and stored on-site pending <br /> laboratory analyses. <br /> The top, north side of the weIl casing was surveyed relative to a common datum for determining <br /> groundwater gradient information. Surveying was performed under the direct supervision of a <br /> California Registered Civil Engineer. Groundwater contours were constructed using a kriging <br /> program. <br /> Groundwater monitorng data(Table 1)collected during April 1991, indicate groundwater flow <br /> is toward the northeast at al proximately .07 ft/ft or 370 feet per mile(Figure 6). The estimated <br /> groundwater velocity at the site is 1.88 x 10-' feet per day using a porosity of .50 and a <br /> hydraulic conductivity of 10' gallons per day per square foot. These values of porosity and <br /> t, <br /> King talmW FWewt•387 <br /> M61691.wp tl <br /> r <br /> f, <br />
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