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2900 - Site Mitigation Program
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PR0505810
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
3/13/2020 11:32:57 AM
Creation date
3/13/2020 11:01:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0505810
PE
2950
FACILITY_ID
FA0007016
FACILITY_NAME
RICH FRUIT PACKING
STREET_NUMBER
19901
Direction
S
STREET_NAME
MCHENRY
STREET_TYPE
AVE
City
ESCALON
Zip
95320
CURRENT_STATUS
02
SITE_LOCATION
19901 S MCHENRY AVE
P_LOCATION
06
P_DISTRICT
005
QC Status
Approved
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y <br /> URS <br /> AN INTERNATIONAL PROFESSIONAL SERVICES ORGANIZATION <br /> URS CONSULTANTS, INC. ATLANT <br /> OSTON <br /> 282 DELAWARE AVENUE BUFFALO <br /> BUFFALO,NEW YORK 14202-1805 CLEVELAND <br /> O <br /> September 21, 1995 (716)856-5636 DEENVER US <br /> FAX:(716)856-2545 NEW YORK <br /> PARAMUS.NJ <br /> NEW ORLEANS <br /> SAN FRANCISCO <br /> SAN MATEO <br /> Mr. Brent Hudson SEATTLE <br /> VIRGINIA BEACH <br /> Corporate Environmental Services Manager WASHINGTON D.0 <br /> Rich Products Corporation <br /> 1150 Niagara Street <br /> Buffalo, New York 14213 <br /> RE: COMMENTS ON WHF, INC. REPORT OF THE ESCALON, CA SITE <br /> Dear Brent: <br /> We have reviewed the WHF, Inc. (WHF) report on the Rich Products Fruit Pak facility at Escalon, CA. <br /> The report is entitled, Underground Tank Investigation, Phase I Report of Findings," and dated <br /> September 12, 1995. The report covers an investigation by WHF in the vicinity of 4 former USTs that <br /> were removed properly from the property in 1987 and obtained clean closure by San Joaquin County <br /> Public Health Department on February 3, 1994. <br /> Our comments are as follows: <br /> 1. Contamination at boring B-l: There appears to be some diesel contamination at soil boring B-1 <br /> between 10 ft. and 30 ft. BGS. The contamination did not extend to any of the other borings <br /> proximate to B-I (B-2, -3, -4, and -5). B-5 was approximately 15 ft. from B-1, while B-3 and <br /> B-2 were approximately 20 ft. from B-1. It should be noted that surficial or near surficial soils <br /> contaminated by diesel may have fallen into boring B-1 during sampling (see Comment 3). <br /> 2. Site geology evaluated by D. Lenhardt, PhD, CPG, URS Sr. Geologist: The site geology is <br /> consistent and uniform across the area investigated by WHF to a depth of 60 ft. BGS. From the <br /> logs of all the WHF borings, the very dense silt found at approximately 35 ft. and clay at <br /> approximately 40 ft. will be an effective barrier to prevent the migration of the diesel <br /> contamination to the water table at 57.5 ft. This is evident by the fact that no contamination at <br /> soil boring B-1 was found below 30 ft. <br /> 3. Slight contamination at soil boring B-3, 55 ft.: The slight contamination found at soil boring B-3 <br /> at 55 ft. is unrelated to the diesel contamination at B-1, because of the following: <br /> • No contamination was found at 50 ft. of B-3 boring, below the silt and clay barriers at <br /> 35 ft. for the reasons mentioned in Comment 2. <br /> • WHF used a solid stem auger to bore holes for sampling. As a solid stem auger passes <br /> through a contaminated area, it could drag contamination downward as the boring <br /> continues. The drilling and sampling methods used by WHF also could have introduced <br /> soils from above 55 ft. into the sample. The solid stem auger, used by WHF, must be <br /> withdrawn before split spoon sampling can occur. Loose soils above the 55 ft. level, <br /> even from the surface, could have been introduced into the boring before the split spoon <br /> sampler could collect a sample at the 55 ft. depth. URS recommends the use of hollow <br /> stem augering to avoid this potential source of contamination. <br /> j:1353971wp\cor\9-20-95.bb <br />
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