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ARCHIVED REPORTS_XR0010284
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545695
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ARCHIVED REPORTS_XR0010284
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Last modified
10/10/2020 10:42:54 PM
Creation date
5/27/2020 4:44:34 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010284
RECORD_ID
PR0545695
PE
3528
FACILITY_ID
FA0003877
FACILITY_NAME
CITY OF STOCKTON FIRE STATION #2
STREET_NUMBER
110
Direction
W
STREET_NAME
SONORA
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13731025
CURRENT_STATUS
02
SITE_LOCATION
110 W SONORA ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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SNTH <br /> The casings de th to water measurements and the elevations of the wellable 1 were used to <br /> P (T ) <br /> evaluate the groundwater flow direction and gradient beneath the site (refer to attached Field <br /> Procedures) Groundwater elevation beneath the site rose an average of 6 88 feet since <br /> December 30, 1994 <br /> The groundwater gradient magnitude and direction was generally consistent during the <br /> reporting period The calculated average gradients for January (0 0053 ft/ft), February <br /> (0 0044 ft/ft), and March (0 0058 ft/ft) are depicted on Figures 3, 4 and 5, respectively. <br /> Groundwater flow direction was to the northeast during the reporting period. <br /> On March 23, 1995, groundwater samples were collected from wells MW-1 through MW-5 <br /> for laboratory analyses The field methods used are presented in Attachment 1 Field purge <br /> logs are included in Attachment 2 Groundwater samples were analyzed by Sequoia Analytical <br /> for total purgeable petroleum hydrocarbons (TPHg) using Environmental Protection Agency <br /> (EPA) Method 8015 modified, total extractable petroleum hydrocarbons (TPHd) using EPA <br /> Method 8015 modified, and benzene, toluene, ethylbenzene, and total xylenes (BTEX) using <br /> EPA Method 8020 Copes of the laboratory reports and chain of custody documentation are <br /> included in Attachment 3 <br /> Results of laboratory analyses indicated dissolved TPHg was detected in the samples from <br /> wells MW-1 and MW-2 at 830 parts per billion (ppb) and 51 ppb, respectively. The TPHg in <br /> well MW-2 was reported by the laboratory as an unidentified hydrocarbon <C8. No TPHg <br /> was detected in any other site monitoring wells <br /> BTEX constituents were detected in well MW-1, most notably benzene at 59 ppb <br /> Hydrocarbon constituents detected in well MW-1 generally decreased an average of 38% since <br /> December 1994 However, toluene increased 19% in the well over the same penod No <br /> BTEX constituents were detected in any other site monitoring wells <br /> TPHd was detected in wells MW-1 and MW-5 at 300 ppb, and 250 ppb, respectively. The <br /> laboratory results of TPHd were reported as unidentified hydrocarbons in the C9-C24 range <br /> No TPHd was detected in any other site monitoring wells. <br /> No petroleum hydrocarbons were detected in monitoring wells MW-3 or MW-4 Results of <br /> laboratory analyses are summarized in Table 2 <br /> SUMMARY AND RECOMMENDATIONS <br /> The groundwater flow direction and gradient were generally consistent with those evaluated <br /> during previous events Hence, fluid levels will be monitored on a quarterly basis Dissolved <br /> gasoline hydrocarbons were detected in the samples from wells MW-1 and MW-2 Dissolved <br /> 38009 I OUQSR95doc 2 <br />
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