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ARCHIVED REPORTS XR0006555
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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4491
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3500 - Local Oversight Program
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PR0544625
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ARCHIVED REPORTS XR0006555
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Entry Properties
Last modified
7/3/2019 8:33:21 PM
Creation date
7/3/2019 4:46:57 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006555
RECORD_ID
PR0544625
PE
3528
FACILITY_ID
FA0003113
FACILITY_NAME
ZAPIEN MARKET
STREET_NUMBER
4491
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25504003
CURRENT_STATUS
02
SITE_LOCATION
4491 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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CLEARWATER GROUP, INC <br /> Groundwater Monitoring and Sampling Protocols <br /> Groundwater Monitoring <br /> Prior to beginning, a decontamination area is established Decontamination procedures consist of scrubbing <br /> downhole equipment in an Alconox® solution wash (wash solution is pumped through any purging pumps used), <br /> and rinsing in a first rinse of potable water and a second rinse of potable water or deionized water if the latter is <br /> required Any non-dedicated down hole equipment is decontaminated prior to use <br /> Prior to purging and sampling a well, the static water level is measured to the nearest 0 01 feet with an electronic <br /> water sounder Depth to bottom is typically measured once per year, at the request of the project manager, and <br /> during Clearwater's first visit to a site If historical analytical data are not available, with which to establish a <br /> reliable order of increasing well contamination, the water sounder and tape will be decontaminated between each well <br /> If floating separate-phase hydrocarbons (SPH) are suspected or observed, SPH is collected using a clear, open-ended <br /> product bailer, and the thickness is measured to the nearest 0 01 feet in the bailer SPH may alternatively be <br /> measured with an electronic interface probe Any monitoring well containing a measurable thickness of SPH before <br /> or during purging is not additionally purged and no sample is collected from that well Wells containing a <br /> hydrocarbon sheen are sampled unless otherwise specified by the project manager Field observations such as well <br /> integrity as well as water level measurements and floating product thicknesses are noted on the Gauging Data/Purge <br /> Calculations form <br /> Well Pur ins <br /> • Each monitoring well to be sampled is purged using either a PVC bailer or a submersible pump Physical <br /> parameters (pH, temperature and conductivity)of the purge water are monitored during purging activities to assess if <br /> the water sample collected is representative of the aquifer If required,parameters such as dissolved oxygen, turbidity, <br /> salinity etc are also measured Samples are considered representative if parameter stability is achieved Stability is <br /> defined as a change of less than 0 25 pH units, less than 10% change in conductivity in micro mhos, and less than <br /> 10 degree centigrade(1 8 degrees Fahrenheit)change in temperature Parameters are measured in a discreet sample <br /> decanted from the bailer separately from the rest of the purge water Parameters are measured at least four times <br /> during purging, initially, and at volume intervals of one well volume Purging continues until three well casing <br /> volumes have been removed or until the well completely dewaters Wells which dewater or demonstrate a slow <br /> recharge, may be sampled after fewer than three well volumes have been removed Well purging information is <br /> recorded on the Purge Data sheet All meters used to measure parameters are calibrated daily Purge water is sealed, <br /> labeled, and stored on site in DOT-approved 55-gallon drums After being chemically profiled,the water is removed <br /> to an appropriate disposal facility by a licensed waste hauler <br /> Groundwater Sample Collection <br /> Groundwater samples are collected immediately after purging or,if purging rate exceeds well recharge rate, when the <br /> well has recharged to at least 80% of its static water level If recharge is extremely slow, the well is allowed to <br /> recharge for at least two hours, if practicable, or until sufficient volume has accumulated for sampling The well is <br /> sampled within 24 hours of purging or repurged Samples are collected using polyethylene bailers, either disposable <br /> or dedicated to the well Samples being analyzed for compounds most sensitive to volatilization are collected first <br /> Water samples are placed in appropriate laboratory-supplied containers, labeled, documented on a chain of custody <br /> form and placed on ice in a cooler for transport to a state-certified analytical laboratory Analytical detection limits <br /> match or surpass standards required by relevant Iocal or regional guidelines <br /> Quality Assurance Procedures <br /> To prevent contamination of the samples, Clearwater personnel adhere to the following procedures in the field <br /> A new, clean pair of latex gloves are put on prior to sampling each well <br /> o Wells are gauged, purged and groundwater samples are collected in the expected order of increasing degree of <br /> contanimation based on historical analytical results <br />
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