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ARCHIVED REPORTS XR0012602
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544294
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ARCHIVED REPORTS XR0012602
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Entry Properties
Last modified
3/29/2019 4:30:38 PM
Creation date
3/29/2019 4:09:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012602
RECORD_ID
PR0544294
PE
3528
FACILITY_ID
FA0007044
FACILITY_NAME
SAFEWAY MEAT PROCESSING PLANT
STREET_NUMBER
1111
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16326007
CURRENT_STATUS
02
SITE_LOCATION
1111 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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z 1 <br /> k' <br /> r <br /> 'Mo-W- <br /> :s <br /> J.N11moi/1 AlIF l'14'r <br /> 'fir 3D MarctLjg�4._-'1St?i.��11>14x�..���Lti <br /> An investicjaLion was conducted by WA between 12 and 15 March to determine <br /> 3 whether the 13-inch thick concrete slab in the bottom of the excavation <br /> could be left in place. Eleven soil samples were collected from 0.5 fL <br /> to 1 ft below the slab. Four samples were analyzed for total petroleum <br /> t1 centration of <br /> hydrocarbons by Canonic Environmental (CC). The highest con <br /> TPII was detected at 55 ppm in sample SL-D collected at 0.5 ft below the <br /> trio slab in the southwestern corner of the excavation. Analytic results are <br /> presented in Table ,, and sample locations are presented in Figure 4. <br /> 14,- A groundwater elevation contour map for depth to-„pater measurements on 2 <br /> March 1988 indicated that the estimated direction of groundwater flow was <br /> to the north, Which was contradictory to the northwestward direction <br /> 1�xi,s determined on 15 October 1987 (Figure 5). The variation was attributed <br /> pz� to seasonal changes in groundwater recharge conditions. <br /> S <br /> An additional downgradient well MW-4, to be located on the north side of <br /> the excavation, was recommended for installation. <br /> Un ut Locs1� 1.11i1�i�tLi� <br /> Jg May 19Q�_liardio_fhlil <br /> IRK <br /> A request was made by WA to the San Joaquin Local Health District (SJLHi)) <br /> to aerate 1000 cubic yards of pea gravel and soil removed from the tank <br /> excavation on site. Samples of the pea gravel PG-East and PG..We:t had <br /> been collected on 25 August 1987, and samples TP-B-2A and TP-B-3A hl� --aen <br /> collected on 23 January 1988, prior to the removal of the pea gravel from <br /> r the excavation pit. One composite of the stockpiled native soil had also <br /> been collected on 14 March 1988. The analytic results of these previously <br /> r collected samples indicated that an average of between 100 ppm and 500 ppm <br /> of hydrocarbons remained in the stockpiled material . <br /> 10 June 19P - QQrdQD Boggs, Cal j[grnia Eggional Water Qual itY COOL 1 <br />' - CenLrjal �99jgn <br /> zT A request was made by WA to the California Regional Water Qu lity Control <br /> Board - Central Valley Region (RWQCB-CVR) to leave the 13-inch thick <br /> concrete slab in the excavation based on the data obtained from past <br /> (U% sampling of soil beneath the slab, soil and groundwater sampling related <br /> to installation of the three monitoring wel :,, and soil sampling during <br /> excavation of the tank pit. The basic argument presented by WA suggester <br /> that hydrocarbons, which leaked from the tanks, had migrated laterally and <br /> �_ downward away from the edges of the slab and are contained in soil <br /> adjacent to the southwestern corner of the excavation. <br /> 07611 nta9 <br /> l <br /> —;Iiibi 11100! <br /> mei! <br />
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