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CORRESPONDENCE_1994-1998
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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4400 - Solid Waste Program
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PR0440007
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CORRESPONDENCE_1994-1998
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Last modified
6/7/2021 9:24:25 AM
Creation date
7/3/2020 11:08:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
1994-1998
RECORD_ID
PR0440007
PE
4434
FACILITY_ID
FA0000595
FACILITY_NAME
HARNEY LANE LANDFILL
STREET_NUMBER
14750
Direction
E
STREET_NAME
HARNEY
STREET_TYPE
LN
City
LODI
Zip
95240
APN
06503006
CURRENT_STATUS
01
SITE_LOCATION
14750 E HARNEY LN
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\cfield
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FilePath
\MIGRATIONS\SW\SW_4434_PR0440007_14750 E HARNEY_1990-1994.tif
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EHD - Public
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Water Level and Total Well Depth Measurements <br /> Immediately before a monitoring well is purged, the water level and total well depth will <br /> be measured using an electric sounder as described in the previous section "Groundwater <br /> Elevation Survey." The electric sounder will be decontaminated by being rinsed with <br /> deionized water after each use. <br /> Well Purging <br /> Before sampling occurs, standing water in the casing and gravel pack will be purged from <br /> the monitoring well using a dedicated Well Wizard® bladder pump, pneumatic <br /> displacement pump, or a polyvinyl chloride or Teflon® bailer. Monitoring wells will be <br /> purged according to the protocol presented in Figure A-1. In most monitoring wells, the <br /> amount of water purged before sampling will be equal to or greater than four casing <br /> volumes. Some monitoring wells are expected to be evacuated to dryness after the <br /> removal of less than four casing volumes. These low-yield monitoring wells will be <br /> allowed to recharge for up to 24 hours. Samples will be obtained as soon as the <br /> monitoring wells have recharged to a level sufficient for sample collection. If insufficient <br /> water has recharged after 24 hours, the monitoring well will be recorded as dry for the <br /> sampling event. <br /> Field measurements will be recorded in a waterproof field logbook. Figure A-2 shows an <br /> example of the Water Sample Field Data Sheet on which field data are recorded. Field <br /> data sheets will be reviewed by the sampling coordinator after the sampling event is <br /> completed. <br /> The pH, specific conductance, temperature and turbidity meters will be calibrated each <br /> day before beginning field activities. The calibration will be checked once each day to <br /> verify meter performance. Field meter calibrations will be recorded on a Field Data Sheet <br /> (see Figure A-2). <br /> Well Sampling <br /> A Teflon bailer or bladder pump will be the only equipment acceptable for well sampling. <br /> When samples for volatile organic analysis are being collected with a bladder pump, the <br /> pump flow will be regulated to approximately 100 milliliters per minute to minimize <br /> pump effluent turbulence and aeration. Glass bottles of at least 40 milliliters volume and <br /> fitted with Teflon-lined septa will be used in sampling for volatile organics. These bottles <br /> will be filled completely to prevent air from remaining in the bottle. A positive meniscus <br /> forms when the bottle is completely full. A convex Teflon septum is placed over the <br /> positive meniscus to eliminate air. After the bottle is capped, it is inverted and tapped to <br /> verify that it contains no air bubbles. The sample containers for other parameters will be <br /> filled, filtered as required, and capped. <br /> SAC/pjft93M9390011.8a1-94/1fc:9 Rev.0, 10/17/94 <br /> 0939-001.18 A-3 <br />
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