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COMPLIANCE INFO_2019
Environmental Health - Public
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COMPLIANCE INFO_2019
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Last modified
9/17/2020 11:35:50 AM
Creation date
9/17/2020 10:26:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
2019
RECORD_ID
PR0538355
PE
2227
FACILITY_ID
FA0022165
FACILITY_NAME
LATHROP WATER TREATMENT FACILITY / CORP YARD
STREET_NUMBER
2112
Direction
E
STREET_NAME
LOUISE
STREET_TYPE
Ave
City
Lathrop
Zip
95330
APN
19816003
CURRENT_STATUS
01
SITE_LOCATION
2112 E Louise Ave
QC Status
Approved
Scanner
KBlackwell
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EHD - Public
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EnviroTech Consultants, Inc. Page 13 <br /> Site Investigation: Sampling Report <br /> Louise Avenue Water Treatment Facility <br /> 4.0 SECONDARY SOIL SAMPLE COLLECTION <br /> 4.1 Secondary Sampling (September 12, 2018) <br /> Following the initial sampling on April 16, 2018, EnviroTech recommended collecting a resample at COL2- <br /> 1 from the surface to 6 inches, collecting an additional background sample and additional sample locations <br /> in Area 3 to determine the full vertical and lateral extents of the arsenic impacted soil within the retention <br /> pond. <br /> On September 12, 2018, soil samples were collected using a hand auger at pre-determined locations. The <br /> latitude and longitude of soil sampling locations were determined with a hand-held GPS and coordinates <br /> are provided in Attachment 5. The soil sampling locations are identified in Figures 7 and 8. <br /> The second background sample was collected from the surface to 6 inches bgs northwest of the retention <br /> pond. The resample of COL2-1 was collected from the surface to 6 inches bgs in the same location as the <br /> original COL2-1 (Figure 5). <br /> At the original sample locations in Area 3, COL3-4 was advanced to 5 feet using a hand auger and samples <br /> were collected from 2 to 3 feet bgs, 3 to 4 feet bgs, and at 5 feet bgs. Due to the high density of cobbles <br /> and boulders, sample locations COL 3-1, 3-2, 3-3 and 3-5 were not extended to 5 feet, and secondary <br /> samples for these locations were not collected. <br /> Eight additional sample locations in the retention pond were selected south of COL3-5 and east of COL3- <br /> 4 in an area approximately 20 feet by 40 feet. In each sampling location (where possible) the hand auger <br /> was advanced to 5 feet bgs. The soil was examined to determine if there is any discoloration or staining. <br /> A soil sample was collected from the surface to 6 inches bgs, 1 to 2 feet bgs, 2 to 3 feet bgs, 3 to 4 feet <br /> bgs,and 5 feet bgs.At COL3-10 and COL3-12,the hand auger could not be advanced to 5 feet bgs because <br /> of the high density of cobbles and boulders. Samples were collected from surface to 6 inches and 1 to 2 <br /> feet bgs at COL3-10 and from the surface to 6 inches, 1 to 2 feet bgs, and 2 to 3 feet bgs at COL3-12. <br /> The soil sampling equipment was cleaned and washed with a non-phosphate containing detergent, rinsed <br /> with water, and dried before use and between each soil sample collection. All soil samples were placed in <br /> glass jars capped with Teflon-lined lids, labeled with the soil sample location number, depth, time and date. <br /> The labeled jars were placed in zip-lock bags in a cold ice chest and transported under chain-of-custody <br /> procedures to BC Laboratories for analysis. All soil samples were analyzed for the presence of arsenic by <br /> EPA Method 6010-B, with solubility testing conducted as needed. Analytical testing was accomplished in <br /> accordance with the guidelines established in BC Laboratories Quality Assurance Manual, applicable <br /> standard operating procedures, and other related documentation. <br /> 5400 Rosedale Highway 0 Bakersfield, CA 93308 0 Tel 661.377.0073 Fax 661.377.0074 <br />
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