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ARCHIVED REPORTS_XR0006837
Environmental Health - Public
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EHD Program Facility Records by Street Name
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YOSEMITE
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2900 - Site Mitigation Program
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PR0537485
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ARCHIVED REPORTS_XR0006837
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Last modified
7/27/2020 5:26:27 PM
Creation date
7/27/2020 3:36:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006837
RECORD_ID
PR0537485
PE
2957
FACILITY_ID
FA0021568
FACILITY_NAME
FORMER RAINWATER CAR WASH
STREET_NUMBER
420
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21931206
CURRENT_STATUS
01
SITE_LOCATION
420 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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1 <br /> 20 September 2000 <br /> AGE-NC Project No 97-0333 <br /> ' Page 6ofII <br /> ' an average permeability of 1 x 101 ,porosity at 42 78 percent, moisture at 5 1 percent and organic <br /> content at 12 percent MW5-15 (sandy clayey)had an average permeability of 2 x 10 7,porosity at <br /> 42 43 percent,moisture at 25 8 percent and organic content at 1 4 percent MW5-25 (fine to coarse <br /> ' sand)had an average permeability of 3 x 10-3,porosity at 39 12 percent, moisture at 22 3 percent and <br /> organic content at 0 1 percent The laboratory results of the analysis are summarized in Table 2 The <br /> laboratory reports (Cooper Testing Laboratory Job No 255-015) and chain-of-custody forms are <br /> included in Appendix E <br /> Two soil samples (MW2-20 and MW4-20) were submitted for microbial enumeration and <br /> ' physicochemical laboratory analysis The results of the analysis indicated that hydrocarbon- <br /> degrading microorganisms were detected at 300 CFU(colony forming units)per gram from MW2-20 <br /> and detected at 6,400 CFU from MW4-20 The laboratory indicated that these physicochemical <br /> conditions at the site were well within the range necessary to support microbial growth and <br /> bioremedial activity Copies of the microbial enumeration and physicochemical laboratory reports <br /> tare included with Appendix F <br /> lie <br /> 3.0, QUARTERLY GROUND WATER MONITORING AND SAMPLING <br /> Ou l 1 July 2000, ground water monitoring and sampling was performed at wells MW-1, MW-Z, <br /> ' MW-3, MW-4 and MW-5, ground water elevation, flow direction and gradient were determined <br /> from the field data <br /> t3 1 MONITORING WEI L PURGE PROCEDURES <br /> ' Depths to ground water were measured in each well from the tops of the well casings at the site to { <br /> the nearest 0 01-foot utilizing a Solinst water level meter The ground water elevation in each well <br /> at the site was calculated by subtracting the measured depth to ground water from the surveyed <br /> ' casing elevation (Table 3) Ground water eleNations were plotted and contoured on a scaled site map <br /> (Figure 1 1) I <br /> tAfter watei levels were measured, approximately 9 gallons of ground water (a minimum of three <br /> casing water volumes per well) were removed frorn wells MW-1, MW-2, MW-3 and MW-4 utilising <br /> a submersible pump, approximately 25 gallons of ground water were removed from well MW-5 <br /> Temperature, pH and conductivity were measured for stabilization at regular purge-volume intervals <br /> fiom each well using a Hydac water analyzer Field data and logs are included with Appendix G <br /> ' Purged ground water was containen/ed in 55-gallon drums and was stored on-site in ar, area lacklm, <br /> general public access <br /> Ir I all C_' C erF ni� >nnec i7i ! risk <br /> 1 <br />
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