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ARCHIVED REPORTS XR0010644
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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DR MARTIN LUTHER KING JR
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749
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3500 - Local Oversight Program
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PR0544218
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ARCHIVED REPORTS XR0010644
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Entry Properties
Last modified
3/5/2019 11:56:00 AM
Creation date
3/5/2019 10:28:12 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010644
RECORD_ID
PR0544218
PE
3526
FACILITY_ID
FA0003870
FACILITY_NAME
SRH FOOD & GAS
STREET_NUMBER
749
Direction
E
STREET_NAME
DR MARTIN LUTHER KING JR
STREET_TYPE
BLVD
City
STOCKTON
Zip
95206
APN
14734309
CURRENT_STATUS
02
SITE_LOCATION
749 E DR MARTIN LUTHER KING JR BLVD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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This velocity equates to about 6. 3 feet per quarter. <br /> At the time the hydropunch testing was done, the groundwater level <br /> in wells BM-6 , BM--7 and BM-9 was located between 44 and 46 feet <br /> below the surface. Hydropunch HP-1 collected water between 45 <br /> and 50 feet bgs. The time to fill up the sampler was about 2 <br /> hours. We tried to perform the same test .in the same interval in <br /> HP-2, however, no water was obtained in the sampler after 2 <br /> hours. We tried lowering the sampler to between 50 and 55 feet <br />' bgs and again were unable to obtain a water sample. We rebored HP- <br /> 2 a week later and opened the sampler between 55 and 60 feet. <br /> This time a water sample was obtained. Because of this, we <br /> assessed the possibility that the aquifer was confined in this <br />' area. Figure 4 shows the cross section taking into account the <br /> data from well. BM--9 and the hydropunch logs. <br />' It appears that the aquifer is partially confined from well BM--9 <br /> east to somewhere between BM-9 and BM-7 . The aquifer is not <br /> confined under the service station site, nor the wells to the <br />' east of the site. <br /> Figure 5 shows our interpretation of the plume configurations at <br />' the time of the hydropunch work. <br /> RATIONALE FOR TWO PLUMES <br /> 1 . The hydraulic gradient has remained to the east since <br /> January, 1990. Although, gradient bearings are not known before <br /> 1990 from site data, the San Joaquin County Flood Control data <br />' shows an easterly gradient for this area since 1989. From 1990 <br /> to the present groundwater would have traveled approximately 145 <br /> feet to the east. <br />' 2 . The groundwater contamination in well BM-9 is about twice as <br /> much as in well BM-7. See Table 3 . Contamination in well BM-4 , <br /> which is near to the source area, is always above that in well <br /> t BM-7 and sometimes is close to the contamination in well BM-9 . <br /> Therefore, when profiling the contamination between BM-9 and BM-4 <br /> the contamination is high in BM-9, lower in BM-7 and rises again <br /> in BM-4 . This contamination profile is happening while moving <br />' away from the source and in an up gradient direction. We believe <br /> it is not possible for a contamination plume to increase as it <br /> moves away from the source and in an up gradient direction. <br /> 1 3. No contamination in the vadose zone was found in well BM-9, <br /> except for the sample taken at the capillary fringe or confining <br />' aquifer soil . The vadose zone contamination is defined and <br /> no contamination has been found in the area west of the property <br /> line. <br />' 4. The fact that the aquifer is partially confined adds an <br /> • additional restriction to up gradient movement of the <br /> contaminants. The groundwater velocity should increase in the <br /> Page 3 <br />
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