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PR0544146
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Last modified
2/14/2019 12:26:36 PM
Creation date
2/14/2019 11:34:04 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0544146
PE
3527
FACILITY_ID
FA0015804
FACILITY_NAME
VACANT LOT
STREET_NUMBER
216
Direction
N
STREET_NAME
CALIFORNIA
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13925026
CURRENT_STATUS
02
SITE_LOCATION
216 N CALIFORNIA ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Tags
EHD - Public
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Underground Storage Tank Delinean Sampling Using Cone Penetration Testing <br /> With An Ultra-Violet Optical Screening Tool Report <br /> 216 N.California Street <br /> Page 5 of 7 <br /> v <br /> 3.2 ULTRA-VIOLET SCREENING TOOL RESULTS <br /> The decay signatures included in the callout windows of each boring indicated that the type of <br /> .. hydrocarbon impact was consistent within depth intervals. Waveforms shown as callouts on the UVOST <br /> logs indicate that diesel is predominant at depths of 16 to 70 feet. The waveforms at a depth of 90 feet in <br /> CPT2 and CPT3 indicate that a gas profile is present, but waveforms are highly dependent upon soil and <br /> v weathering (see UVOST Log Reference, Appendix C). The signal intensity indicated that hydrocarbons <br /> were located at relatively higher concentrations at some locations and depths: at depths of 16 to 50 feet <br /> bgs in CPTI, 5 feet from the source area; at depths of 30 to 48 feet bgs in CPT2, 25 feet from the source <br /> .. area; at depths of 31 to 42 feet bgs in CPT3, 40 feet from the source area. The maximum signal intensity <br /> was reported as 226.0% at 46.08 feet bgs in CPTI, 18.5% at 31 feet bgs in CPT2, and 12.3% at 37.84 <br /> feet bgs in CPT3. The background or base-level signal was approximately 0.9%throughout the 100 foot <br /> sampling interval for all three borings, both above and below the depth of elevated signal intensity. A <br /> slightly elevated signal intensity o approximately 2% was reported in the top 10 feet and 58 to 62 feet <br /> bgs of CPTI, CPT2 and CPT3, and at 88 to 95 feet in CPT2. <br /> 3.3 CONE PENETRATION TEST-SOIL BEHAVIOR TYPE RESULTS <br /> Cone penetration tests indicate that, in general, the tested soils are fine grained and have a high silt <br /> content (green), but are generally mixtures with clay (blue), see Boring Logs, Appendix C. The soils <br /> from the surface to 10 feet bgs classify as silt and silty sand (yellow), which lie above clays at <br /> approximately 10 to 15 feet. Clay and silty clays predominate at depths of 15 to 35 feet bgs. Sandy silt <br /> ` and clayey silt soils predominate at depths of 35 to 100 feet. Sand (brown) and very dense or stiff soils <br /> are present in the interval between 35 and 100 feet bgs, and are important because of their relative ability <br /> to transmit or retard groundwater transport, respectively. A pore pressure test conducted in CPT3 at a <br /> depth of 98.6 feet indicated the depth to groundwater was approximately 37.3 feet bgs, compared to the <br /> 30 feet bgs that was indicated in February of 2008. Very dense, stiff soil was reported at a depth of 40 to <br /> 44 feet in CPT1 and CPT3. Sand was reported with low pore pressure at depths of 46 to 50 feet and 72 to <br /> 75 feet bgs in CPTI. The shallower sand in CPTI correlates well spatially to the sand with gravel that <br /> was identified at a depth of 43 to 48 feet bgs in SB-1 in <br /> ep g February 2008. Sand was reported with low pore <br /> pressure at depths of 60 to 65 feet and 70 to 75 feet bgs in CPT2 and CPT3. The deeper sands identified <br /> in CPT2 and CPT3 correlate well spatially to the lower sand in CPT L Thin clays and silty clay were <br /> i' reported at depths of 75 to 90 feet with relatively thin inter-layering of dense/stiff soil, overlying <br /> predominantly sandy silt and clayey silt at depths of 90 to 100 feet bgs in CPT1, CPT2, and CPT3, see <br /> Figure 5 Appendix A. <br /> 3.4 DATA QUALITY ANALYSIS <br /> CPT data and SBT classifications correlate well to spatial trends and soils identified during the <br /> advancement of continuous coring completed with SB-1, and with visual identification of soil samples <br /> collected for laboratory analysis (Boring Logs, Appendix C). Laboratory analysis included laboratory <br /> blanks with a control surrogate, matrix spikes, and laboratory duplicate analysis of each of the selected <br /> analytes. Results of laboratory quality control procedures indicate that detection limits and analyte <br /> detection quantification were supported within method guidelines of+/- 30%. BTEX analyses had an <br /> average surrogate recovery of 94%. Diesel analyses had an average surrogate recovery of 92% <br /> (Laboratory Analytical Results Appendix B UVOST data did not correlate strongly to laboratory <br /> ( rY Yt� PP )• g Y <br /> analytical data using 6 data points, see Data Quality Analysis,Chart 1, and Chart 2,Appendix B.UVOST <br /> data did not correlate well at CPT1-60, CPTI-72, and CPT3-35 where laboratory analytical results, <br /> staining and odor, all indicated that higher concentrations were present compared to UVOST output. <br /> UVOST data would be expected to vary because soil samples are collected from co-located but separate <br /> n <br /> +.� CONDOR <br />
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