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2900 - Site Mitigation Program
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PR0535375
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Last modified
7/7/2020 9:15:19 AM
Creation date
7/7/2020 9:11:32 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0535375
PE
2960
FACILITY_ID
FA0020405
FACILITY_NAME
ERNIES GENERAL STORE
STREET_NUMBER
4407
Direction
E
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95215
APN
08710059
CURRENT_STATUS
01
SITE_LOCATION
4407 E WATERLOO RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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' 20 June 2006 <br /> AGE-NC Project No. 01-0839 <br /> Page 5 of 8 <br /> ' of the second sleeve will be covered with Teflon sheets, capped, and sealed with tape. <br /> Appropriately sealed and labeled samples will be placed in a chilled container and transported under <br /> chain of custody procedures to a DHS-certified laboratory for analysis for the constituents listed in <br /> Section 2.2.. Each sample sleeve will be labeled with the boring designation,depth,time,date,and <br /> sampler's initials. Soil encountered in the borings will be visually classified by an AGE geologist in <br /> ' accordance with the Unified Soil Classification System(USCS). Additionally, soil samples will be <br /> field-screened for the presence of volatile organic compounds using an organic vapor meter(OVM), <br /> equipped with photo-ionization detector(PID). Soil sample descriptions and OVM readings will be <br /> recorded on a log for each boring. <br /> 3.1.2. Grab Ground Water Sample Collection and Analysis <br /> One grab ground water sample will be collected from the proposed soil boring. The boring will be <br /> ' advanced to the top of the ground water table, as identified by collection of a saturated soil sample, <br /> to collect a grab ground water sample. Once ground water has been encountered, samples will be <br /> collected with a Hydropunch water sampling assembly; a 2-inch diameter polyvinylchloride(PVC) <br /> ' casing with a 5-foot long, 0.010-inch slotted well screen at the lower end will be temporarily <br /> installed in the borehole and a grab ground water sample will be collected by lowering a Teflon, <br /> ' disposable bailer through the hollow center of the auger rods into the screened section. <br /> Ground water samples will be transferred into laboratory-supplied,40-milliliter(ml)volatile organic <br /> analysis (VOA) vials containing 0.5 ml 18% hydrochloric acid solution as a sample preservative. <br /> Following collection, the samples will be appropriately labeled, placed in a chilled container, and <br /> transported under chain of custody procedures to a DHS-certified laboratory for analysis for the <br /> constituents listed in Section 2.2.. <br /> 3.2. WELL INSTALLATION PROCEDURES <br /> Utilizing a CME-75HT truck-mounted, hollow-stem drill rig equipped with 8.25-inch diameter <br /> ' hollow-stem augers,the monitoring well pilot soil boring will be advanced to a depth of 80 feet bsg <br /> and the SVE well pilot soil borings will be advanced to depths of 30 feet and 60 feet bsg.Relatively <br /> undisturbed soil samples will be collected from each soil boring at 5-foot intervals using a California <br /> modified split-spoon sampler fitted with 2-inch diameter, 6-inch long brass sleeves.Upon removal <br /> from the sampler,the sample sleeves will be separated with a knife.The exposed ends of the second <br /> sleeve will be covered with Teflon sheets,capped,and sealed with tape. Soils sampled in the borings <br /> ' will be visually classified by an AGE geologist in accordance with the USCS. Additionally, soil <br /> samples will be field screened for the presence of volatile organic compounds using an OVM <br /> equipped with a photo-ionization detector PID. Soil sample descriptions and PID readings will be <br /> Advanced GeoEnvironmental,Inc. <br />
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