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ARCHIVED REPORTS_XR0002455
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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1817
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2900 - Site Mitigation Program
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PR0540859
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ARCHIVED REPORTS_XR0002455
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Last modified
1/15/2020 4:00:43 PM
Creation date
1/15/2020 2:49:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002455
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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1 <br /> CLFARWATER GROUP <br /> Groundwater Monitoring and Sampling Field Procedures <br /> Groundwater Momigruig <br /> is established Decontamination procedures consist of scrubbing <br /> Prior to beginning, a decoatamrnation area <br /> downhole equipment in an Alconox(p solution wash(wash solution isum�off&detosized waterany m, <br /> and easing in a first Trow of potable water and a second rinse of potable <br />' requinA 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 /> to bottom is typically measured once Per Year, at the req of the probed manager', and <br /> water sounder � data are not available, with which#o establish a <br /> during Clearwatees first visit to a site If histoncal analytical between each <br /> reliable order of increasing well contamination, the water sounder and tape will or observed, decontaminatedbe SPH is collected rising a clear, <br /> well if floating Separate-&= hydrocarbons (SPH} are suspected <br />' <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 merle <br /> is not additionally purged and no sample is colluded from that well <br /> thickness of SPH before or during purging led unless otbemim specdied by the pro3ed r Field <br />' Wells containing hydrocarbon sheen are camp product thicknesses are noted <br /> observations such as well integrity as well as water level measurements and floating p <br /> on the Gauging Data/Purge(tic ulatrons form- <br />' Wei either a PVC bailer or a submersible pump Physical <br /> Each monitoring well to be sampled is purged using <br /> parameters(pH,temperature and conductivity) of the purge water are monitored during purging activities to assess <br /> i esentative of the aquifer If required, param et is such as dissolved oxygen, <br /> t the ureter sample collected u rep tine parameter stability is achieved. <br /> turbidity, salinity etc. are also measured. Samples are considered representative P in micro mhos, <br /> Stability is defined as a change of less than 0.25 pH units, less than 109'0 rap virameters are measured in , <br /> and less than 10 degree centigrade(1 $degrees Fahrenheit)change <br /> in discreet sample decanted from the bailer separately from the nest of the Purge water Parameters ase measured at <br /> , and at volume intervals of one well volume Purging continues until <br /> least four furies during purging', initially, 1 dewaters Wells which dcwater or <br /> three well casing volumes have been removed or until the well completely <br />' demonstrate a slow recharge may be sampled after fewer than three well volumes have been removed- Well Data sheet. All meters used to measure parameters are calibrated <br /> purging information is recorded on the Purgerayed 55-gallon drums After being <br /> daily Purge water is sealed, labeled, and stored oe m D Of -approved a licensed waste hauler <br /> chemically profiled,the wager is removed to an appropriatedisposal ty <br />' Gro+mdwater Sample Collectionrate exceeds well recharge rate,when <br /> Groundwater samples are collected immediately after purging or, If purging <br /> recharge is extremely slow,the well is allowed to <br /> the well has recharged to at least 80%of its static water level If lumelin The well is <br />' recharge for at least two hours, if practicable, or until sufficlent volume liar accumulated for sampling <br /> ed Samples are collected using polyethylene bailers, either <br /> sampled within 24 hours of purging or regurg for compounds most sensitive to volatilization are <br /> disposable or dedicated to the Well Samples being analyzed documented on a <br /> collected first Water samples are placed in appropriate lfor transport <br /> lied containers, labeled, tiall <br />' chain of custody form and placed on ice in a cooler for transport to a state-certified analytical laboratory <br /> Analytical detection limits match or surpass <br /> standards requucd by relevant local or regional guidelines <br />' ,ally Assurance Procedures Procedures in the field <br /> To prevent contamination of the samples,Clearwater pemnnel adhere to the following p <br />' A new,clean parr of latex gloves rs put on prior to sampling each well <br /> • Wells are gauged,purged and groundwater samples are collected in the expected order of increasing degree of <br /> contanunation based on historical analytical results <br />' 1 <br /> Grevised April 4,2002 <br /> �twamR Gitoup(GWS) <br />
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