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ARCHIVED REPORTS_XR0012651
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545129
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ARCHIVED REPORTS_XR0012651
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Last modified
10/12/2020 10:34:06 PM
Creation date
1/7/2020 8:42:11 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012651
RECORD_ID
PR0545129
PE
3528
FACILITY_ID
FA0006171
FACILITY_NAME
Mizkan America, Inc.
STREET_NUMBER
1400
Direction
E
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95205-3743
APN
14115002
CURRENT_STATUS
02
SITE_LOCATION
1400 E WATERLOO RD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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2 <br /> To extract the analytes of interest from the soil matrix, 50-9 <br /> sub--samples of soil were combined with 50 mL of dichloromethane <br /> solvent and enough water was added to wet the soil. The analytes <br /> were extracted into the solvent by shaking for one hour. The <br /> solvent was separated from the soil and water by centrifugation. <br /> Aromatic volatile organic concentrations were determined by <br /> comparison to an external standard which contained all components <br /> listed in EPA Method 8020. Aliquots of the dichloromethane <br /> extracts were analyzed on a Hewlett-Packard 5880 capillary gas <br /> chromatograph equipped with a 30 m x 0.25 mm, 0.25 um film <br /> thickness, J & W DB 1301 capillary column and a Hewlett-Packard <br /> Model 5970 mass selective detector operating in the selective ion <br /> monitoring mode. This type of detector was used instead of the <br /> photoionzation detector suggested in EPA Method 8020 because <br /> other petroleum products present in the samples might have <br /> interfered with correct identification of the analytes specified <br /> in Method 8020, particularly the dichlorobenzene components. <br /> Determination of diesel fuel levels in the samples followed EPA <br /> Method 8015. Aliquots of the dichloromethane extracts prepared <br /> as described above were analyzed on a Hewlett-Packard 5880 <br /> capillary gas chromatogra}h equipped with a 30 m x 0.25 mm, 0.25 <br /> um film thickness, J & W DB 17 capillary column and a flame <br /> ionization detector. The carbon number range of diesel in the <br /> samples was from C11 to C22. Reference diesel fuel No. 2 was <br /> obtained locally and used as an external standard to calibrate <br /> the gas chromatograph. The summation of the peak area responses <br /> from C14, C16 and C18 was used for calibration and calculation of <br /> the diesel concentration in the sample. <br /> Soil from the 150 level from R-1, R-2 and R-3 and from the 30' <br /> level from R-1 were: analyzed for the halogenated volatiles <br /> described in EPA Method 8010. In addition to the dichloromethane <br /> extract, a separate: sub-sample of each four soil samples was <br /> extracted in toluene by the procedure described above to allow <br /> determination. of all analytes listed in EPA Method 8010. The <br /> extracts were analyzed by high resolution gas chromatography/mass <br /> spectrometry'. <br /> Results and Discussion <br /> Results for all samples for aromatic volatile organics and diesel <br /> are presented in Table 1. Diesel, at levels ranging from 14000 to <br /> 61000 ug/g and xylenes at levels ranging from 0.4 to 22 ug/g were <br /> found in all samples from R-1. Benzene, toluene and ethyl <br /> benzene were detected in some samples from R-1 at levels ranging <br /> from 0.7 to 4.4 ug/g. No aromatic volatile organics were <br /> detected i:z any samples from R-2 or R-3; diesel was detected in <br /> only one sample from R-3 at a level of 30 ug/g. No halogenated <br /> — -..-- ----- --__ -_volatile.--compounds_-were-_detected--in--t:he--samples_analy.z.ed._.-._ __-- <br />
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