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ARCHIVED REPORTS_XR0012141
Environmental Health - Public
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PR0541875
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ARCHIVED REPORTS_XR0012141
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Last modified
3/16/2020 4:57:02 PM
Creation date
3/16/2020 2:57:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012141
RECORD_ID
PR0541875
PE
2960
FACILITY_ID
FA0024017
FACILITY_NAME
CHEVRON SITE 306415
STREET_NUMBER
437
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
APN
1392417
CURRENT_STATUS
01
SITE_LOCATION
437 E MINER AVE
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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HV0C,51F.X REMOVAL <br />• The bubble zone,-A-as still expanding during the ten-day test Based upon the time <br /> sequence. a long axis extending outs ab <br /> --cards out 30 m(98 ft) in a westerly and easterly direction <br /> would be reached.with a minor axis (at right angles) of about 18 m (59 fit Each well would <br /> then treat a region 61 m (200 ft) long;by about 30 5 in (100 ft) wide and 27 m (90 ft) deep <br /> Although an elliptical zone exists here,the occurrence of bubbles at mimwell 126 about day five <br /> complicates the picture We must aNcume that a hurled gravel ctreamhed, ahneit 10 m (i-1 ft) <br /> wide,was originally intercepted and either small streamlets{braided streams) intercepted it Or <br /> some secondary fracturing by air pockets was occurring to create the offshoot to miniwell 126 <br /> A geological basis exists for assuming gravel streambeds originating east-west across the region <br /> from glacial streams Side connections could occur(see Table 2) <br /> GROUNDWATER FLOW-CIRCULATION PATTERN DEFE41MON <br /> -- Dingy groundwater flow measurements were perfor-mod with a KVA Model 40 GeoFlo R <br /> meter prior to the startup and during the operation to determine backgroundsvelocityW and <br /> changes Initial measurements indicated a flow near the spargewell(TW) _ <br /> " direction it a velocjjr of'TietWE= -2 ml.6 ftp and-24 in (8 ft)per day,coinciding with the <br /> direction of movement of the plume <br /> Additional measurements were taken after beginning injection to determine the velocity <br /> of groundwater eddies created by the double-screen well system and nsmg bubbles which <br /> expand the treatment zone both vemcally and horizontally across the site The observed change <br /> in direction and rate coincided with a slow vertical mixing rate set up at right angles to the main <br /> axis of mixing. At well A(which is 5.4 m [18 ft] east of TW)the change was measured at about <br /> i9 m (3 ft)per day in an easterly direction. At well B (which is 1 I m [36 ft] west of TW) a <br /> velocity change of 15 m ( 5 ft)per day occurred towards the TW well Well A is shallow <br /> (13 m [43 ft]below grade)and well B significantly lower(15 m [49 ft]below grade) <br /> Groundwater moving in towards the spargewel}would reach a maximum at about 27 in (71 ft) <br /> below grade <br /> The outward gyre(Figure 5)would reach a maximum velocity at about 12 m (39 ft) The <br /> vertical eddy for mixing appeared to reach a velocity with a diameter of about 20 m (66 ft)by <br /> day ten of the test,with an estimated velocity of about 3 3 m(10.8 ft)per day. This is slow by <br /> normal standards and probably the result of loss of pressure along the narrow gravel streambed, <br /> intercepted between 20m and 25 m deep(65 6 ft and 82 ft) <br /> RESULTS <br /> The site held a combination of a lower dissolved chlorinated solvent plume, dominated <br /> by TCE principally and PCE,and an upper dissolved fuel spill, dominated by BTEX compounds. <br /> A large region of the wells exhibited elevated HVOCs in groundwater, with initial samples from <br /> wells D,B,C, and mmiwell 129 (14m to 15 m [46 ft to 49 ft]) showing concentrations of <br /> 2,100 ggll, 14,500 µg11, 12,500 µg11, and 1,450 gg/l, respectively, well above the 800 µg11 <br /> originally expected Groundwater from the spargeweil (TW)and wells A,B,C, and D exhibited <br /> total BTEX concentrations ranging from 62 to 95 ggll <br /> Concentration of HVOCs located in the gravel zone underwent immediate rapid <br /> reduction(wells TW, D, 129) Nearby wells located at right angles(probably in fine sands)to <br /> the buried gravel streambed, showed a slower removal, converging on a logarithmic decay rate <br />• Those in the outlying wells,mainly requiring recirculation to treat the groundwater,tended to <br /> 6 <br />
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