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COMPLIANCE INFO_PRE 2019
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PR0009227
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COMPLIANCE INFO_PRE 2019
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Last modified
5/4/2021 11:41:48 AM
Creation date
5/4/2021 11:20:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0009227
PE
2960
FACILITY_ID
FA0004039
FACILITY_NAME
METROPOLITAN STEVEDORE
STREET_NUMBER
2201
Direction
W
STREET_NAME
WASHINGTON
City
STOCKTON
Zip
95203
APN
145030010
CURRENT_STATUS
01
SITE_LOCATION
2201 W WASHINGTON
P_LOCATION
01
QC Status
Approved
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EHD - Public
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III. Field Observations, In-Situ Measurements, and Sampling <br />Wells MW-1, MW-2, MW-3 and MW-4 were sampled on June 23, 2003. Each <br />monitoring well was purged using calculated weii volumes based upon the depth <br />to water in each individual well casing. Depth to groundwater measurements <br />were made to the nearest one-one hundredth of one foot, and also checked for <br />the presence of separate phase product. As each purge volume is removed, <br />measurements of pH, electrical conductivity, dissolved oxygen and temperature <br />were taken until these parameters stabilize, which is interpreted to be aquifer <br />water entering the casing. Each well was allowed to recover to about 80% of the <br />initially measured water level, and then samples were collected. The sample <br />was carefully collected with a clean bailer and poured into the appropriate <br />laboratory prepared container with minimum cavitation. The well field sampling <br />note sheets are summarized in table 1 as set forth below. <br />111.1. Field Quality Assurance/Quality Control (QA/QC) Measures <br />TRE and PET employed strict field QA/QC measures to ensure the integrity of <br />the samples and the field operations. Each water sample was properly labeled, <br />logged onto a chain-of-custody form, and placed in a chilled ice chest to preserve <br />the samples by maintaining an approximate temperature of 4C° for storage and <br />transport to the laboratory as recommended by EPA. New disposable bailers <br />were used for sampling each well. PET decontaminated the monitoring wells <br />purging equipment (tubes, pump, etc) between wells by purging it with Alconox <br />detergent and DI water solution and rinsed with DI water. Care was taken by <br />PET to ensure that samples are not crossed contaminated. Upon completion of <br />well sampling, the well was closed and locked and the sampler moved to the next <br />well. All in- situ field measurement equipment (pH meter, EC meter, etc) was <br />properly calibrated by PET in the morning prior to the commencement of field <br />operations. <br />Table 1. Groundwater Monitoring Well Data <br />WELL DEPTH TO <br />WATER (FT) <br />WELL DEPTH <br />(FT) <br />CASING <br />ELEVATION (MSL <br />FT) <br />GROUNDWATER <br />ELEV. (FT) <br />COMMENTS <br />MW-1 8.95 22.20 6.95 -2.0 None <br />MW-2 4.20 22.50 6.00 1.8 None <br />MW-3 7.70 20.80 3.50 -4.2 None <br />MW-4 7.20 22.75 6.20 -1 None <br />All metal samples were properly filtered when they arrived at the laboratory <br />(PET) shortly after all samples were taken. Laboratory filtration was preferred <br />over field filtration due to the fact that foreign artifacts/particles may potentially be <br />introduced to the samples while being field filtered on site. This is particularly <br />true in any industrial setting such as the port of Stockton, where field conditions <br />5
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