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COMPLIANCE INFO_PRE 2019
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2900 - Site Mitigation Program
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PR0527808
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COMPLIANCE INFO_PRE 2019
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Last modified
5/4/2021 11:16:36 AM
Creation date
5/4/2021 10:15:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0527808
PE
2960
FACILITY_ID
FA0018851
FACILITY_NAME
PORT OF STOCKTON-ROUGH & READY ISLAND
STREET_NUMBER
2201
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14503001
CURRENT_STATUS
02
SITE_LOCATION
2201 WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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GROUND WATER INVESTIGATION WORK PLAN <br />BULK TERMINALS SITE, PORT OF STOCKTON, STOCKTON, CALIFORNIA <br />over a period of 5 to 10 minutes to establish the equilibrated depth to water. Measurements will <br />continue until the depth to water is stable to within 0.05 feet over a 5-minute period. Water <br />samples will be collected according to the methods provided below and after measurements of <br />depth to water are complete. <br />3.1.2.4 Soil Sampling <br />As described above, the borehole will be advanced sequentially into and through each of the <br />geologic materials: surficial materials, underlying clay layers, and sandy to silty-sand water- <br />bearing zone. Soil samples will be collected continuously and described with regard to soil <br />type, relative moisture, and color in accordance with the Unified Soil Classification System. Soil <br />samples will be collected within clear acetate tubes lining the inside of the boring equipment. In <br />the event that CPT borings are advanced in selected locations, continuous cone physical data <br />will be collected first, and a second adjacent boring will be advanced to collect samples at <br />targeted intervals for chemical analysis and conventional lithologic logging. <br />Vadose zone soils will be analyzed for chemical constituents in borings C-1, C-3, C-4, C-7, C-8, <br />C-10, C-11 and C-12. Soils will be analyzed for the contaminants associated with the adjacent <br />potential sources, as well as for soil pH, total organic carbon (TOC) and cation exchange <br />capacity (CEC). Soil sample intervals for potential laboratory analysis will be collected from <br />approximately 0 to 0.5 feet, 3 to 3.5 feet, and 6 to 6.5 feet bgs. Samples from the surface and 6 <br />feet bgs will be analyzed initially, and the 3-foot sample will be placed on hold at the laboratory <br />pending results of the upper and lower vadose zone soils. If results indicate the need for <br />intermediate-depth analytical data, the 3-foot sample will be analyzed. <br />The selected soil sample intervals will be cut to length, capped at both ends, labeled, and placed <br />in a chest containing water ice pending transport to the laboratory under standard chain-of- <br />custody procedures. The label will identify the top of the sample interval and will include <br />boring number, sample depth, date and time of sample collection, and sampler's initials. A <br />field log will be recorded in the field for each boring and will include geologic descriptions and <br />symbols, depth to water, sample intervals, and date and time of sample collection. <br />3.1.2.5 Water Sampling Within Borings <br />Grab ground water samples will be collected from the first coarse-grained shallow water- <br />bearing zone. Upon reaching the desired water-bearing material, a hydro-punch system, or 5 <br />feet of slotted PVC screen, will be lowered into the boring to serve as temporary well casing to <br />collect ground water samples. <br />Ground water grab samples will be collected using either a bailer constructed of Teflon, PVC, or <br />stainless steel, or a peristaltic pump outfitted with PVC or Teflon tubing. The samples will be <br />collected in laboratory-supplied containers appropriate for the types of analyses specified <br />July 2005 Page 11 Environmental Risk Services Corp.
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