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ARCHIVED REPORTS_XR0005503
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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99 (STATE ROUTE 99)
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14800
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3500 - Local Oversight Program
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PR0545626
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ARCHIVED REPORTS_XR0005503
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Entry Properties
Last modified
11/19/2024 1:50:28 PM
Creation date
4/29/2020 1:38:06 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005503
RECORD_ID
PR0545626
PE
3528
FACILITY_ID
FA0000957
FACILITY_NAME
LATHROP GAS & FOOD MART*
STREET_NUMBER
14800
Direction
S
STREET_NAME
STATE ROUTE 99
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
19702004
CURRENT_STATUS
02
SITE_LOCATION
14800 S HWY 99 RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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� <br /> The pH, specific conductance, and temperature meter were calibrated each day before field <br /> activities were begun The calibration was checked once each day to verify meter performance <br /> Field meter calibrations were recorded on the Water Sample Field Data Sheet <br /> Well Sampling <br /> A Teflon bailer or bladder pump were the only equipment acceptable for well sampling When <br /> samples for volatile organic analysis were being collected, the pump flow was regulated at <br /> approximately 104 milliliters per minute to minimize pump effluent turbulence and aeration <br /> Glass bottles of at least 40 milliliters volume and fitted with Teflon-lured septa were used in <br /> sampling for volatile organics These bottles were filled completely to prevent air from <br /> remaining in the bottle A positive meniscus formed when the bottle was completely full. A <br /> convex Teflon septum was placed over the positive meniscus to ehminate air After the bottle <br /> was capped, it was inverted and tapped to verify that it contained no air bubbles The sample <br /> containers for other parameters were filled, filtered as required, and capped <br /> When required, dissolved concentrations of metals were determined using appropriate field <br /> filtration techniques When a Teflon bailer was used, the sample was filtered by emptying the <br /> contents of the bailer into a pressure transfer vessel. A disposable 0 45-micron acrylic <br /> copolymer filter was threaded onto the transfer vessel at the discharge point, and the vessel was <br /> sealed Pressure was applied to the vessel with a hand pump and the filtrate directed into the <br /> appropriate containers Each filter was used once and discarded <br /> When a bladder pump was used to collect samples for dissolved constituents, filtering was <br /> performed by attaching a disposable 0 45-micron acrylic copolymer filter directly to the pump <br /> effluent line with a pressure fitting As the pump cycled, the effluent was pressured through the <br /> filter and directed into the appropriate containers Each filter was used once and discarded <br /> SAMPLE PRESERVATION AND HANDLING <br /> The following section specifies sample containers, preservation methods, and sample handling <br /> procedures <br /> Sample Containers and Preservation _ <br /> Sample containers vary with each type of analytical parameter Container types and materials <br /> were selected to be nonreactive with the particular analytical parameter tested <br /> SA(W\P72\2520`25201000 IGS 94\pas 1 <br />
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