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ARCHIVED REPORTS_XR0002475
Environmental Health - Public
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1817
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2900 - Site Mitigation Program
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PR0540859
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ARCHIVED REPORTS_XR0002475
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Last modified
1/15/2020 3:48:27 PM
Creation date
1/15/2020 2:59:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002475
RECORD_ID
PR0540859
PE
2960
FACILITY_ID
FA0023361
FACILITY_NAME
PLAY N PARK (FORMER BARNES TRUCKING)
STREET_NUMBER
1817
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1817 S FRESNO AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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.l <br /> ,a7 <br /> a <br /> CLEARWATER GROUP <br /> Groundwater Monitoring and Sampling Field Procedures <br /> Groundwater Momtortn <br /> Prior to beginning, a decontamination area is established Decontamination procedures consist of scmbbmg <br /> downhole equipment in an Alconox®solution wash(wash solution is pumped through any purging pumps>sed), <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 /> regwred. Any non-dedicated downhole 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 <br /> well If floating separate-phase hydrocarbons (SPH) are suspected or observed, SPH is collected using a clear, <br /> open-ended product bailer, and the thickness is measured to the nearest 0 01 feet in the bailer SPH may <br /> alternatively be measured with an electronic interface probe Any monitoring well containing a measurable <br /> thickness of SPH before or during purging is not additionally purged and no sample is collected from that well <br /> Wells containing hydrocarbon sheen are sampled unless otherwise specified by the project manager Field <br /> observations such as well integrity as well as water level measurements and floating product thicknesses are noted <br /> on the Gauging Data/Purge Calculations form. <br /> Well Puriin9 <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 <br /> if the water sample collected is representative of the aquifer If required, parameters such as dissolved oxygen, <br /> turbidity, salinity etc are also measured. Samples are cDa%dered representative if parameter stability is achieved <br /> Stability is defined as a change of less than 0 25 pH units, less than IO%chanParameter conductivity in i cro in as <br /> and less than 10 degree centigrade(1 S degrees Fahrenheit)change in temperature <br /> discreet sample decanted from the bailer separately from the rest of the purge water Parameters am >tinues d til <br /> at <br /> least four times during purging initially, and at volume intervals of one well volume Purging <br /> three well casing volumes have been removed or until the well completely dewaters Wells which dewater or <br /> demonstrate a slow recharge may be sampled after fewer than three well volumes have been removed. Well <br /> purging information is recorded on the Purge Data sheet All meters used to measure parameters are calibrated <br /> daily Purge water is sealed, labeled, and stored on site in D 0T-approvedlicensed wasted u r After being <br /> chemically profiled,the water is removed to an appropriate disposal ty by <br /> Groundwater Samyle Collection <br /> Groundwater samples are collected immediately after purging or, if purging rate exceeds well recharge rate,when <br /> the well has recharged to at least$010 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 <br /> compounds most sensitive to volatilization are <br /> disposable or dedicated to the well Samples being analyzed forlied containers, labeled, documented on a <br /> collected first Water samples are placed in appropriate laborator <br /> y �-supe <br /> chain of custody form and placed on ice in a cooler for transport to a state-certified analytical laboratory <br /> Analytical detection hints match or surpass standards required by relevant local or regional guidelines <br /> iy Assurance Procedures adhere to the following <br /> p procedures in the field <br /> To prevent contamination of the samples,Clearwater personnel <br /> • A new,clean parr of latex gloves is put on prior to mmphng each welt <br /> . Wells are gauged,purged and groundwater samples are collected in the expected order of increasing degree of <br /> contamination based on historical analytical results <br /> CLEARWATER GROUP(GWS) 1 revised Apnl 4,2002 <br />
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