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ARCHIVED REPORTS_XR0006492
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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YOSEMITE
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1012
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3500 - Local Oversight Program
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PR0545948
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ARCHIVED REPORTS_XR0006492
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Last modified
9/29/2020 10:17:19 PM
Creation date
8/5/2020 3:53:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006492
RECORD_ID
PR0545948
PE
3528
FACILITY_ID
FA0005159
FACILITY_NAME
FILL-EM FAST
STREET_NUMBER
1012
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21903024
CURRENT_STATUS
02
SITE_LOCATION
1012 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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1 <br /> 0%.X; <br /> • GROUNDWATER MONITORING AND SAMPLING PROCEDURES <br /> (Includes No-Purge Sampling) <br /> ' Groundwater Monitoring and Decontamination Method <br /> Prior to beginning, a decontamination area is established Decontamination procedures consist of scrubbing <br /> down-well equipment in a Liquidnox� solution wash (or equivalent degreasing compound), and rnismg in <br /> potable water and a final rinse of de-ionized (or distilled) water before and after each well Any non- <br /> dedicated down-well equipment is decontaminated prior to use on site <br /> ' Prior to purging and sampling a well, the static water level is measured to the nearest 0 01 feet with an <br /> electronic interface probe and/or water level meter Depth to bottom is typically measured every quarterly <br /> event The water level meter and tape will be decontaminated between each well If floating phase- <br /> separated hydrocarbons (PSI) are suspected or previously confirmed, an electronic interface probe is used <br /> to measure the well fluids to the nearest 0 01 feet PSH may alternatively be measured using a clear, open- <br /> ended product bailer, and the thickness is measured to the nearest 0 01 feet in the bailer Any monitoring <br /> well containing a measurable thickness of PSH before or during purging is not additionally purged and no <br /> sample is collected from that well Wells containing hydrocarbon sheen are sampled unless otherwise <br /> specified by the project manager Field observations such as well integrity as well as water level <br /> measurements and PSH thickness are recorded in the field <br /> Well Pur igen <br /> When well purging is required, each monitoring well to be sampled is purged using, a truck-mounted <br /> lievacuum pump, a polyvinyl chloride (PVC) bailer or a submersible pump Physical parameters (pH, <br /> temperature, and conductivity) of the purge groundwater 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, <br /> turbichty, salinity etc are also measured Samples are considered representative if parameter stability is <br /> achieved Stability is defined as a change of less than 0 25 pH units, less than 10%change in conductivity m <br /> micro mhos, and less than 1 0 degree centigrade (1 8 degrees Fahrenheit)change in temperature Parameters <br /> ' are measured in a discreet sample decanted from the bailer separately from the rest of the purge <br /> groundwater Parameters are measured during purging, initially, and at volume intervals of one well or <br /> borehole volume (dependent on local regulations) Purging continues until the required well or borehole <br /> volumes have been removed, until the well completely dewaters, or until measured parameters stabilize as <br /> indicated above When wells dewater or demonstrate a slow recharge, wells may be sampled although <br /> fewer than required volumes have been removed Well purging information is recorded on the Purge Data <br /> sheet All meters used to measure parameters are calibrated daily Purge water is sealed, labeled, and stored <br /> ' on site in DO T-approved 55-gallon drums After being chemically profiled,the water is transported to an <br /> appropnate'disposal facility by a licensed waste hauler <br /> Groundwater Sample Collection <br /> After purging, groundwater samples are collected after at least 80% of its static water level is recovered in <br /> the well If recharge is extremely slow, the well is allowed to recharge until sufficient volume has <br /> accumulated for sample collection No-purge groundwater samples are collected when prior approval <br /> by the lead regulatory agency has been permitted When no-purge samples are collected the same <br /> procedures are followed excluding well purging. All groundwater samples are collected using <br /> ,polyethylene disposable bailers attached with new, clean string or rope Groundwater samples being <br /> analyzed for compounds most sensitive to volatilization are collected first Groundwater samples are placed <br /> in appropriate laboratory-supplied containers, labeled, documented on a chain of custodyl form and ! <br /> preserved on ice in a cooler for transport to a state-certified analytical laboratory After collection, all I <br /> ' samples are stored in a chilled cooler and,refrigerated,to approximately four (4) degrees Celsius while a !I! <br /> laboratory representative transports the samples to their facility Analytical detection limits match or <br /> surpass standards required by relevant local or regional guidelines <br />
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