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ARCHIVED REPORTS SECOND SEMIANNUAL AND 2013 ANNUAL GROUNDWATER MONITORING REPORT
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ARCHIVED REPORTS SECOND SEMIANNUAL AND 2013 ANNUAL GROUNDWATER MONITORING REPORT
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Last modified
6/18/2019 11:08:16 AM
Creation date
6/18/2019 10:58:16 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
SECOND SEMIANNUAL AND 2013 ANNUAL GROUNDWATER MONITORING REPORT
RECORD_ID
PR0505378
PE
2960
FACILITY_ID
FA0006743
FACILITY_NAME
HOLT LEAK SITE
STREET_NUMBER
0
STREET_NAME
COOK
STREET_TYPE
RD
City
HOLT
Zip
95234
CURRENT_STATUS
01
SITE_LOCATION
COOK RD
P_LOCATION
99
QC Status
Approved
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2.RESULTS FOR SECOND SEMIANNUAL PERIOD 2013 <br /> Gauging ' <br /> All wells were gauged prior to any sample collection. Depth to groundwater was measured <br /> using an electronic water-level meter. The measurements were made to the nearest 0.01 foot <br /> from a surveyed measuring point at each well location. Groundwater elevations were <br /> calculated by subtracting the depth to groundwater from the surveyed elevation at the <br /> surface of the measuring point. <br /> Groundwater Sampling <br /> After gauging, groundwater samples were collected using HydraSleeve samplers as <br /> approved in a November 10, 2011,email from the RWQCB to SFPP. Blaine Tech Services <br /> installed the HydraSleeve samplers on March 12,2013, after collecting the samples for the <br /> prior semiannual sampling event. , <br /> The top of the HydraSleeve samplers were set at approximately the midpoint of the well <br /> screens (or slightly below) if the water table was above the screen,or in the middle of the <br /> water column (or slightly below) if the water table was below the top of screen. After <br /> retrieval,the water from the samplers was transferred into sample containers. Physical <br /> parameters (temperature, electrical conductivity [EC], pH, dissolved oxygen [DO], <br /> oxidation-reduction potential [ORP],and turbidity) were measured from a portion of the <br /> sample as follows,after the sample containers were filled: <br /> • Pour water into a Myron L Ultrameter to read temperature,pH, EC, and ORP <br /> • Pour water into the Hach Turbidimeter to measure turbidity <br /> • Fill a measurement cup and measure DO with a YSI 550 DO Meter <br /> Because of insufficient water, samples were collected from M-8 or M-10 with bailers. There <br /> were 1.35 feet of water in the bottom of well M-8 and 2.12 feet of water in the bottom of well <br /> M-10 during the sampling event, as calculated by subtracting the depth to water from the , <br /> total depth of the well measurements on the field data forms (Appendix A). <br /> The samples were labeled,placed in a chilled cooler,and delivered to Alpha Analytical, Inc. <br /> for analysis. Chain-of-custody protocol was maintained throughout the sample-handling <br /> process. <br /> Groundwater Analytical Methods <br /> Groundwater samples collected from the sampled monitoring wells were submitted to <br /> Alpha Analytical,Inc., a California-certified analytical laboratory located in Sparks,Nevada. <br /> Copies of the laboratory reports from Alpha Analytical are provided in Appendix B. <br /> Groundwater and quality assurance/quality control (QA/QC) samples were analyzed for <br /> the following: <br /> • Total petroleum hydrocarbons as gasoline (TPHg) and as diesel (TPHd)using United <br /> States Environmental Protection Agency (EPA) Method 8015 modified , <br /> • Benzene,toluene, ethylbenzene, and total xylenes (BTEX)using EPA Method 8260B <br /> The following QA/QC samples were collected: <br /> • Duplicate sample from well N-7(labeled DUP-1) <br /> • Two equipment blank samples (labeled EB-1A and EB-1B) <br /> 2-2 WBG101513183707SC0/HOLT_2SA13_REPORT_FINAL <br />
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