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Last modified
5/8/2020 3:51:22 PM
Creation date
5/8/2020 3:42:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0542087
PE
2965
FACILITY_ID
FA0016554
FACILITY_NAME
ESCALON CITY OF WATER TREATMENT PLA
STREET_NUMBER
25100
STREET_NAME
RIVER
STREET_TYPE
RD
City
ESCALON
Zip
95320
APN
24709015
CURRENT_STATUS
01
SITE_LOCATION
25100 RIVER RD
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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t GW &SW Monitoring Report <br /> COE-WDR <br /> Project No. 894.2 <br /> ' September 1,2011 <br /> • Volatile Organic Compounds (VOCs) were reported to be non-detect in all <br /> ' monitoring wells during the 3rd quarter 2011 groundwater monitoring event. <br /> • Total Coliform Bacteria— was reported to be below laboratory reporting limits for all <br /> monitoring wells during the 3rd quarter 2011 groundwater monitoring event with the <br /> exception of MW-3 (542 MPN/100mL). Total Coliform has decreased or remained <br /> the same from the previous monitoring event in all other wells and is within historical <br /> ' <br /> • ranges. <br /> Fecal Coliform Bacteria was reported to be below laboratory reporting limits for all <br /> monitoring wells during the 3rd quarter 2011 groundwater monitoring event. <br /> Coliform is ubiquitous in the environment and has been detected intermittently in <br /> ' various monitoring wells at the site. <br /> ' 4.0 SURFACE WATER MONITORING <br /> On August 2, 2011, GTI personnel performed the surface water sampling at the two sampling <br /> stations along the north bank of the Stanislaus River. R-1 is approximately 100 feet upstream <br /> of the railroad trestle and R-2 is located approximately 100 feet downstream of the <br /> ' westernmost boundary, as shown in Figure 2. <br /> 4.1 Surface Water Sampling Procedure <br /> The samples were collected with a long-handled dipper. The sample containers were <br /> identified and labeled with a unique designation and placed in a chilled ice chest for transport <br /> to the laboratory. <br /> ' All non-disposable sampling equipment was decontaminated using an Alconox® solution <br /> before and between uses. Disposable gloves were used by the geologist to collect all samples <br /> ' and were changed between each sample. <br /> A chain of custody document, listing all samples collected, accompanied the samples from <br /> field to laboratory, thereby providing a means to track the movement of the samples and <br /> ensure their integrity. <br /> ' Field measurements were made at the time of sample collection for Temperature, pH, <br /> Specific Conductance (EC) and Dissolved Oxygen (DO). The field parameters are included <br /> in the field data log sheets of Appendix C. <br /> ' 4.2 Surface Water Sample Analysis <br /> The two surface water samples were submitted to Denele Laboratory Services in Turlock, <br /> California (FLAP# 1203) for the following analyses: <br /> • Five Day 20°C Biochemical Oxygen Demand (BODS) <br /> t • Nitrate as Nitrogen <br /> • Total Dissolved Solids (TDS) <br /> • Fixed Dissolved Solids (FDS) <br /> ' Geological Technics Inc. 6 <br /> 894 3rd QMR I Ldoc <br />
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