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PR0522547
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Last modified
5/18/2020 4:40:38 PM
Creation date
5/18/2020 4:35:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0522547
PE
2960
FACILITY_ID
FA0015361
FACILITY_NAME
RICE TERMINALS
STREET_NUMBER
0
STREET_NAME
PORT
STREET_TYPE
RD
City
STOCKTON
Zip
95212
APN
14502009
CURRENT_STATUS
01
SITE_LOCATION
PORT RD A
P_LOCATION
01
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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KLEINFELDER <br /> 5 DISCUSSION OF RESULTS <br /> The probe locations advanced as part of this soil and groundwater assessment were selected by <br /> Kleinfelder with direction by Mr. Tom Kramer of IRM and in consideration of subsurface <br /> utilities. The primary emphasis of the assessment was near AST No. 2 and in proximity to <br /> potential impact areas including pumps, discharge areas, sumps and subsurface piping. Based on <br /> groundwater analytical results Nitrate as N and Ammonia as N isocontour maps have been <br /> developed (See Plates 3 and 4). This assessment has not included an assessment of groundwater <br /> flow, as only grab groundwater samples were collected and survey points were not obtained. <br /> The following is a discussion of analytical results and field observations. <br /> 5.1 SOIL SAMPLING ANALYTICAL RESULTS <br /> Concentrations of ammonia as N detected in soil samples at the subject site ranged from none- <br /> detect (ND) to 14,000 mg/kg. Nitrate as N ranged from none-detect to 18,000 mg/kg and TKN <br /> concentrations ranged from 25 mg/kg to 10,000 mg/kg. The highest concentrations of nitrate as <br /> N and ammonia as N were detected from push probe boring location (PP6 ) at a depth of 5.5 feet <br /> bgs located southeast of Tank No. 2 and near a surface pump. Other locations with elevated <br /> concentrations of each of the requested analytes (nitrates, ammonia and TKN) in soil (above first <br /> encountered groundwater) includes PP7 and PP8 located near a sump structure and between <br /> Tank No's 2, 5 and 6, respectively. Elevated concentrations of these same analytes were also <br /> detected in PP1 at 11 foot depth, but this sample was likely collected beneath first encountered <br /> groundwater and therefore may be influenced by the groundwater contaminant plume discussed <br /> below. Therefore these elevated concentrations from PPI at 11 feet bgs may not be only a result <br /> of surface infiltration at this specific location. TKN values were reported in each of the soil <br /> samples submitted for analyses indicating a nitrate source in each of the pushprobe locations. <br /> The highest TKN concentrations in soil above groundwater was primarily detected from <br /> pushprobes PP-5, PP-6, PP-7 and PP-8, located near Tanks No's 2 and 4 , near a surface pump, a <br /> sump and product discharge area, located generally south of Tanks Nos. 2 and 4. <br /> 5.2 GROUNDWATER SAMPLING ANALYTICAL RESULTS <br /> Concentrations of Ammonia as N detected in groundwater samples at the subject site ranged <br /> from 7.7 milligrams per liter(mg/1) to 24,000 mg/l. Nitrate as N ranged from 7.6 mg/l to 15,000 <br /> mg/l and TKN concentrations ranged from none-detect to 17,000 mg/l. Nitrate as N and <br /> ammonia as N isocontour maps were developed based on the analytical data. Please note <br /> however that the extent of the contaminant plume has not been defined either laterally or <br /> vertically, although attenuation with lateral distance is shown based on the data obtained. <br /> Therefore a 0-line for both isocontour maps is not included. <br /> The highest concentrations of ammonia as N and TKN were reported from push probe sample <br /> location PP8 located between Tank No's 2, 5, and 6. The highest concentration of nitrate as N <br /> 43851.E0I/ST05RI58/DH:Iv Page 7 of 12 <br /> ©2005,Kleinfelder,Inc. February 9,2005 <br />
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