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ARCHIVED REPORTS_XR0007792
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0506077
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ARCHIVED REPORTS_XR0007792
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Last modified
6/18/2020 5:01:37 PM
Creation date
6/18/2020 4:30:34 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007792
RECORD_ID
PR0506077
PE
2950
FACILITY_ID
FA0007187
FACILITY_NAME
WELLS FARGO BANK
STREET_NUMBER
49
Direction
S
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
15121034
CURRENT_STATUS
01
SITE_LOCATION
49 S WILSON WAY
P_LOCATION
01
QC Status
Approved
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LSauers
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EHD - Public
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' PRIVILEGED & CONFIDENTIAL <br /> bailer to remove fine grained materials from the well. Approximately three feet of hydrated <br /> bentonite pellets were placed on top of the sand pack before grouting the wells. The wells <br /> were then grouted to the surface with Portland Cement, using a grout pump and tremie <br /> pipe. Following the sealing of the wells, a traffic rated well box and locking cap were <br /> installed at each wellhead. A well construction diagram is included in Appendix B. <br />' Wellhead Surveying <br /> On October 28, 1997 the wellhead elevation and location of MW-4 was surveyed by <br />' Morrow Surveying, Inc. of Sacramento, California. The elevation and location of MW4 <br /> was tied into the existing site plan. The newly installed wellhead elevation is included in <br /> Table 1. The complete well survey is included as Appendix C. <br /> Groundwater Elevation Measurements <br />' On October 20, 1997 the static groundwater elevations were measured in the four <br /> groundwater monitoring wells, by lowering a decontaminated Solinst groundwater <br /> elevation probe and measuring the groundwater elevation to the nearest 0.01 foot. Well <br />' elevation data are included in Table 1. <br /> The calculated groundwater elevation indicates that the groundwater gradient is <br /> approximately 0.0055 to the northeast. A groundwater contour map is presented as Figure <br /> 3. <br /> P11 Groundwater Monitoring and Sampling <br /> On October 20, 1997 the monitoring wells were purged a minimum of three well volumes <br /> ' using a submersible pump. Field parameters were measured during the purging of <br /> groundwater with a Hydac conductivity/temperature/pH meter. The pH of the groundwater <br /> ranged from 6.81 in MW-1 to 7.05 in MW-3. Groundwater temperature ranged from 20.5 <br /> degrees Celsius in MW-4 to 22.8 degrees Celsius in MW-3. Conductivity ranged from <br /> ' 860 micro ohms in MW-2 to 2,450 micro ohms in MW-3. The wells were allowed to <br /> recharge a minimum of 80% before sampling. Samples were collected from each <br /> monitoring well along with a blind duplicate. Water samples were collected by lowering a <br /> ' new disposable bailer below the static water level, and raising the bailer slowly in order to <br /> minimize agitation of the water sample in the bailer. <br /> Water was discharged from the bailer through a bottom discharge valve. Discharge to the <br /> sample container was at a rate slow enough to minimize agitation of the liquid. The sample <br /> container was filled to the top (from the bottom up) and overfilled leaving no headspace. <br /> ' The samples were collected in laboratory-approved glass vials and bottles. Following <br /> collection of the samples, they were placed in an ice chest cooled with ice and sent to SPL <br /> Laboratories of Houston via overnight courier. Sample handling, transport, and delivery to <br /> ' the laboratories were documented using chain-of-custody procedures, including the use of <br /> chain-of-custody forms. <br /> 1 <br /> 5 197501 -Stavkron <br />
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