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ARCHIVED REPORTS XR0000055
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3500 - Local Oversight Program
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PR0543386
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ARCHIVED REPORTS XR0000055
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Last modified
10/31/2018 3:19:43 PM
Creation date
10/31/2018 2:41:41 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS XR0000055
FileName_PostFix
XR0000055
RECORD_ID
PR0543386
PE
3528
FACILITY_ID
FA0003791
FACILITY_NAME
TUFF BOY INC
STREET_NUMBER
5151
STREET_NAME
ALMONDWOOD
STREET_TYPE
DR
City
MANTECA
Zip
95337
APN
22606017
CURRENT_STATUS
02
SITE_LOCATION
5151 ALMONDWOOD DR
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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r,41M n <br /> Mr Martin Harris <br /> April 27,2004 <br /> Page 4 of 7 <br /> l <br /> 2.7 Well Development and Groundwater Sampling <br /> A Ground Zero technician developed the new wells and collected groundwater samples on <br /> January 23, 2004 Water levels were monitored prior to well development <br /> Each new well was developed by surging, bailing and pumping until turbidity was minimized <br /> The temperature, pH, and electrical conductivity of the purged water were measured during well <br /> development and were allowed to stabilize prior to collecting a groundwater sample <br /> Groundwater purged from the wells was placed into DOT approved 55-gallon drums, which were <br /> eventually transported off-site for disposal/recycling <br /> Groundwater samples were collected from each well after the physical parameters stabilized and <br /> the water in the well recovered to at least 80% of pre-purged levels Samples were placed in an <br /> ice chest at a temperature of 4° Centigrade and submitted to Argon under chain of custody <br /> protocol The samples were analyzed for the presence of TPHg, BTEX, and oxygenated gasoline <br /> additives, including 1,2-DCA and EDB Field development/purge logs are included in <br /> Attachment C <br /> To determine the groundwater elevation, the static depth to groundwater was measured in each well <br /> and subtracted from the surveyed wellhead elevation The potentiometric surface ranged from <br /> • 18 00 feet above mean sea level (msl) in well MW7 to 18 14 feet above msl in wells MW2 and <br /> MW4 Groundwater flowed in a westerly direction with a hydraulic gradient of approximately <br /> 0 001 ft/ft, or approximately 5 6 ft/mi Due to an apparent groundwater elevation anomaly, the data <br /> from well MW7 was omitted from the calculation Groundwater elevations are summarized in <br /> Table 1 A potentiometric surface map generated using the January 23, 2004 well monitoring data <br /> is depicted on Figure 3 Groundwater monitoring and purge logs are included in Attachment C <br /> 3.0 RESULTS <br /> 3.1 Subsurface Conditions <br /> CPT methods were used to classify soil from the ground surface to a depth of approximately 35 <br /> feet bgs in boring CPT1 Traditional soil logging methods were used to classify the soil in <br /> bonngs MWS, MW6, and MW7 to a depth of 19 feet bgs The lithology observed in borings <br /> MW5 through MW7 correlated well with the CPT data <br /> Shallow soil beneath the site consists of sandy soil (SW, SW-SM, and SW-SC) from the ground <br /> surface to approximately 11-12 feet bgs, silt (ML) and clay (CL) from approximately 11-12 feet <br /> bgs to approximately 16 feet bgs, and poorly graded sand (SP) to well graded sand (SW) from <br /> approximately 16 feet bgs to approximately 17 5-19 feet bgs, which corresponds to the bottom of <br /> borings MW5 through MW7 Accurate soil classification was not possible in boring MW6 <br /> beyond 12 feet bgs due to heaving sands <br /> Groundze/souzah�,portsAVELLRPT2b doc <br />
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