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3500 - Local Oversight Program
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PR0545744
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Last modified
6/9/2020 9:44:44 AM
Creation date
6/9/2020 9:40:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE HISTORY
RECORD_ID
PR0545744
PE
3528
FACILITY_ID
FA0004065
FACILITY_NAME
WATERFRONT YACHT HARBOR
STREET_NUMBER
333
STREET_NAME
TULEBURG LEVEE
City
STOCKTON
Zip
95203
APN
13701006
CURRENT_STATUS
01
SITE_LOCATION
333 TULEBURG LEVEE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Mr. Vidal Pedroza '" <br /> I <br /> March 23, 2000 <br /> Page 3 of 6 <br /> collect soil samples at the approximate depth of the bottom of the USTs and at approximately four <br /> feet below the tank bottom. However, due to the presence of underground utilities just south of the <br /> USTs, only three of the borings'(SB L SB2, SB3) were advanced as angle borings. Borings SB4, <br /> SBS, and SB6 were located approximately 4 feet south of the USTs and were advanced vertically <br /> to a depth of approximately 15.5„feet bgs, except for boring SB4, which was advanced to <br /> approximately 20.5 feet bgs. Due to surface light pole that hindered positioning of the drilling rig, <br /> the surface starting point for boring SB2 was located at an oblique angle from the long axis of the <br /> tank. The boring was advanced at a 30 degree angle to collect soil samples as previously <br /> described. <br /> A groundwater sample was collectedfrom boring SB 1 by installing a temporary well screen in the <br /> boring, inserting a 0.17 diameter PTFE tube equipped with a stainless steel check valve into the <br /> well screen, and extracting groundwater from the boring by creating a positive displacement effect <br /> within the tubing, forcing the water sample towards the surface where it was collected directly into <br /> sample containers. <br /> Borings SB7 through SB14 were advanced along the product pipeline to depths ranging from 3.5 <br /> feet bgs to 6 feet bgs. Every attempt was made to advance the soil borings along the product <br /> pipeline at 20 foot intervals. However, distances between several borings exceeded 20 feet due to <br /> certain site features which hindered access, such as a water fountain and other ornamental displays, <br /> and underground utilities. <br /> Mr. Pedraza of PHS/EHD was consulted on and approved all boring locations. Soil boring <br /> locations are presented on Figure 1. A cross section of the UST area is shown on Figure 2. <br /> The completed borings were backfilled via tremmie piping to the ground surface with neat <br /> cement grout. No soil cuttings were generated. All down-hole drilling and sampling equipment <br /> was decontaminated by washing with a laboratory grade detergent and rinsing with water. <br /> Rinseate collected from decontamination procedures was disposed of by Fisch. Soil and <br /> groundwater samples were submitted under chain of custody procedures to Argon Laboratories for <br /> analysis. <br /> 4.0 RESULTS OF INVESTIGATION <br /> 4.1 Subsurface Conditions <br /> Soil samples collected at a depth of approximately I1 feet bgs in the vicinity of the USTs <br /> consisted of lean to silty clay. Soil "samples collected at depths of approximately 14.5 and 19.5 <br /> feet bgs were generally sandy silt. Evidence of groundwater was encountered in borings SBI and <br /> SB2 at approximately 14 feet bgs, and at approximately 10 feet bgs in boring SB6. However, only ;1 <br /> boring SB 1 (North side of Tank 1)yielded enough water to collect a groundwater sample. <br /> Slight petroleum hydrocarbon odors were noted in the soil samples collected from boring SB4 at <br /> approximately 11 feet bgs and 14.5 bgs. Gray,discoloration was apparent in the sample collected <br /> from 14.5 feet bgs. Field meter readings(FID readings)ranged from 1 part per million (ppm)at 11 <br /> G:1Data%GROUNDZE1Watediont\Subswfstan.doc 3 <br /> I <br />
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