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SITE INFORMATION AND CORRESPONDENCE CASE 2
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE CASE 2
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Last modified
8/5/2019 1:25:48 PM
Creation date
8/5/2019 10:50:52 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
CASE 2
RECORD_ID
PR0521881
PE
2960
FACILITY_ID
FA0014865
FACILITY_NAME
CALIFORNIA NATURAL PRODUCTS
STREET_NUMBER
1250
Direction
E
STREET_NAME
LATHROP
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19804001
CURRENT_STATUS
01
SITE_LOCATION
1250 E LATHROP RD
QC Status
Approved
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EHD - Public
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L%NFELDEF7 <br /> eronw«wi..wen.xiwon,. <br /> ' custody seal is also placed on the sample in such a way that any attempt to tamper with the <br /> sample is easily visible. An example of a sample label and custody seal are attached at the end <br /> of this appendix. <br /> A-2.4 Qualitative Field Screening <br /> An organic vapor detector, such as a Photovac TIP, using a photoionization detector (PID) or a <br /> Foxboro flame ionization detector (FID), is used to provide a qualitative screening of each soil <br /> sample collected from the borings. The organic vapor detector measures ionizable compounds <br /> in the air in parts per million by volume (ppmv). Field calibration is performed using a calibrated <br /> ispan gas. Ambient air is used to set the instrument zero. A calibration form is attached. The <br /> soil contained in the cone of the sampler or in a brass tube is exposed and screened with the <br /> organic vapor detector. The vapor reading is noted as the field screening result. <br /> For the protection of the drilling crew, the organic vapor detector is also used to measure the <br /> volatile concentrations in the breathing zone prior to and during the drilling of the samples. Total <br /> i ionizable hydrocarbon readings in excess of one ppmv may necessitate respiratory protection <br /> for the affected crew members. This requirement is included in the complete field health and <br /> safety plan developed for the project prior to the start of field work. <br /> A-2.5 Sample Handling <br /> iAfter labeling, the sample is immediately stored in an iced cooler for transport to Kleinfelder's <br /> office sample control or to the analytical laboratory. A Kleinfelder chain-of-custody form is <br /> Iattached to the cooler. The chain-of-custody form includes Kleinfelder's name, address and <br /> telephone number, the employee number of the individual who performed the sampling, the <br /> ' sample numbers, the date and time the samples were collected, the number of containers each <br /> sample occupies, and the analyses for which the samples are being submitted, if any. The <br /> i chain-of-custody form is signed by each person who handles the samples, including all <br /> Kleinfelder employees and the receiving employee of the analytical laboratory when the <br /> samples are delivered. An example of the chain-of-custody form is attached to this appendix. <br /> A-2.6 Soil Sample Selection for Laboratory Analysis <br /> iThe selection of soil samples for laboratory analysis is based upon: 1) the project objectives <br /> and requirements, 2) qualitative field screening performed in the field using the organic vapor <br /> idetector, and 3) field observations such as lithology, odor, discoloration, or high moisture <br /> content. Generally, samples are submitted from the bottom of the boring and from soil horizons <br /> 101486.6/SAC14R0504 Page A-2 April 28, 2014 <br /> Copyright 2014 Kleinfelder <br /> i <br />
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