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ARCHIVED REPORTS XR0009997
EnvironmentalHealth
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3500 - Local Oversight Program
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ARCHIVED REPORTS XR0009997
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Last modified
11/19/2024 10:19:02 AM
Creation date
9/4/2019 10:24:52 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009997
RECORD_ID
PR0544800
PE
3528
FACILITY_ID
FA0010235
FACILITY_NAME
AMERICAN TRUCK & TRAILER BODY CO
STREET_NUMBER
7474
Direction
W
STREET_NAME
ELEVENTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
25020001
CURRENT_STATUS
02
SITE_LOCATION
7474 W ELEVENTH ST
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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------------ <br /> -------------- <br /> Geofogicaf7echnics 2nc. <br /> C&B Equipment Page 2 <br /> Groundwater Monitoring Report <br /> Project No.336.2 <br /> April 13, 1998 <br /> >_ 40.37 feet AMSL. The gradient was North 13° West with a slope of 0.0052 ft/ft (as <br /> determined from MW-1,2 &3). <br /> Table 1 of Appendix A summarizes the groundwater level measurements to date. <br /> Groundwater gradient calculations show that the dominant groundwater flow is in a north- <br /> northwesterly direction with the slope ranging from 0.007 ft/ft to 0.0036 ft/ft. Figure 2 is a <br /> groundwater gradient map from this latest sampling event. Figure 3 is a rose diagram of the <br /> gradients from the four monitoring events. <br /> `i <br /> 1.2 Groundwater Sampling Procedure <br /> On March 18, 1998, Del-Tech Geotechnical Support personnel arrived on-site, opened the <br /> wells, and measured the depth to water with an electrically actuated sounding tape.e. The <br /> -_ water level reading was recorded to an accuracy of O.01 foot. In wells where free floating <br /> "j product was suspected, a clear disposable bailer is used to gauge the interface. <br /> Stagnant water in the well casing was purged using centrifugal pump as recorded in the field <br /> logs (Appendix Q. The rate of well purging was monitored. The well was purged of at least <br /> three casing volumes and until the groundwater parameters (temperature, conductivity, and <br /> pH) had stabilized (Appendix C)' indicating that water, representative of actual aquifer <br /> conditions, was entering the well. Groundwater parameter stabilization was characterized by <br /> three successive readings within 10%. <br /> �I <br /> Before a sample was collected, the well's water level was allowed to recharge to at least 80% <br /> of it's initial level. All water removed from the monitoring well and not used as a sample, <br /> was placed in a 55 gallon DOT (Department of Transportation 17-H) approved container that <br /> is properly labeled and temporally stored on-site. <br /> A bailer was used to collect each sample. Bailer cleanliness was assured by collecting a <br /> bailer blank (pouring distilled water through the bailer and collecting it in a VOA vial) prior <br /> to collecting the analytical sample. <br /> Extreme care was exercised while collecting samples to prevent agitation of the water <br /> contained in the bailer. Water samples were transferred from the bailer into 40 ml VOA vials <br /> __s preserved with hydrochloric acid using a bottom emptying device which minimizes sample <br /> aeration during transfer of the sample. All samples were checked for head space bubbles, <br /> labeled, inserted into foam holders and placed in an ice chest cooled to 4°C for transport to <br /> the laboratory. <br /> Disposable gloves were worn by the sampling technician while collecting all samples. <br />
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