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FIELD DOCUMENTS_CASE 2
Environmental Health - Public
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FIELD DOCUMENTS_CASE 2
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Last modified
5/12/2020 3:46:46 PM
Creation date
5/12/2020 2:57:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
FileName_PostFix
CASE 2
RECORD_ID
PR0545660
PE
3528
FACILITY_ID
FA0003909
FACILITY_NAME
PORT OF STOCKTON
STREET_NUMBER
2201
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14503001
CURRENT_STATUS
02
SITE_LOCATION
2201 W WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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y <br /> Lobserved in the core sample collected from 4 to b feet bgs in boring B5-5, and moderate to <br /> strong petroleum product odor was detected in the headspace of boring B5-5 at this depth <br /> (Appendix A). Soil discoloration was absent in the subsequent core sample collected from 9 <br /> L to I I feet bgs in boring B5-5, and no volatile organics were detected using the PID in this core <br /> sample. The PID readings within the headspace of boring B5-5 diminished to non-detect with <br /> continued drilling to the total depth (Appendix A). No soil discoloration or petroleum product <br /> L odors were detected in the core samples collected from boring B5-4 (Appendix A). Based on <br /> these field observations, Carol Oz requested that soil samples be submitted for laboratory <br /> Lanalysis of PHCs at 5, 10, 15, and 20 feet bgs in boring B5-5, and at 10 and 15 feet bgs in <br /> boring B5-4. Groundwater samples were collected at 21 feet bgs in both borings using the <br /> method described above. A replicate groundwater sample was collected from boring B5-4. <br /> L <br /> Soil and groundwater samples from the five borings were placed in an ice-cooled chest and <br /> Lsubmitted under chain-of-custody procedures to BSK Analytical Laboratories (BSK), a <br /> California DHS-certified laboratory for PHC analyses. Samples were analyzed for BTEX, <br /> TPHg, and MTBE using EPA Methods 801518020. The groundwater samples collected from <br /> Lw boring B5-1 (W-003), and boring B5-5 (W-006) were also analyzed for oxygenates using EPA <br /> Method 8260. The Work Plan stated that EPA Method,200.8 would be used for analysis of <br /> L lead in soil and water samples. .This method uses inductively coupled plasma and mass <br /> spectrometry (ICP/MS) as the analytical technique and is typically used on low turbidity <br /> drinking water samples. However;=due to the high turbidity in water samples collected during <br /> Lthis investigation, BSK performed lead analyses for water samples using EPA Method 200.7. <br /> Soil samples were analyzed using,EPA Method 6010. Both these methods use ICP as the <br /> analytical technique. According to BSK, these ICP methods provide the same detection limits <br /> Las the ICP/MS method while offering the advantage of being able to accommodate analysis of <br /> turbid water samples. <br /> 9 <br /> 4.0 INVESTIGATION FINDINGS <br /> L <br /> Findings of the investigation, including geologic and hydrologic characteristics, and analytical <br /> Lresults of the soil and groundwater samples, are discussed in the following sections. <br /> L4.1 GEOLOGIC AND HYDROLOGIC CHARACTERISTICS <br /> The site is located on the delta of the San Joaquin River, approximately 2--miles east of the <br /> Lconfluence of the San Joaquin and Calaveras Rivers. The subsurface geology consists of a <br /> thick sequence of alluvial deposits of late Tertiary to Holocene Age, overlying sedimentary <br /> Lrocks of Cretaceous to Tertiary age, which in turn overlie crystalline basement rocks (Bartow <br /> 5 "117U rvurraWusrMV.xrr <br /> L <br /> BOYAJIAN & ROSS, INC. <br /> Environmental Scientists & Engineers <br />
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