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SITE INFORMATION AND CORRESPONDENCE_FILE 2
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0505534
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SITE INFORMATION AND CORRESPONDENCE_FILE 2
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Last modified
3/31/2020 4:22:10 PM
Creation date
3/31/2020 4:10:44 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 2
RECORD_ID
PR0505534
PE
2950
FACILITY_ID
FA0006840
FACILITY_NAME
TOSCO SUPER T MARKET
STREET_NUMBER
7647
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
07748014
CURRENT_STATUS
02
SITE_LOCATION
7647 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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GeoHydrologic Consultants, Inc. <br /> The results of ozone treatment on secondary water quality parameters are shown in Table <br /> 7 of the Prima Report located in Appendix B. <br /> 4.3.5 Ozone Demand <br /> The ozone demand for soil was 112— 115 mg ozone/kg of soil, and this result was <br /> anticipated given the low concentrations of COCs and total organic carbor. in the site soil <br /> sample. <br /> The ozone demand for groundwater was 337 —350 mg ozone/L of groundwater, and this <br /> result was lower than anticipated. Based on the concentrations of COCs in untreated soil <br /> and the stoichemetries for ozone reaction, the theoretical ozone demand was 1,850 mg/L. <br /> A possible explanation is that COCs were not completely destroyed in the empirical <br /> ozone demand test, rendering the measured ozone demand lower than expected. <br /> The ozone demand for soil and groundwater are shown in Figure's 1 and 2, respectively, <br /> of the Prima Report located in Appendix B. <br /> 4.3.6 Attenuation of Bromate and Cr(VI) <br /> Because bromate and Cr(VI) were observed during ozone treatment additional tests were <br /> conducted to determine whether these compounds are likely to attenuate within the <br /> treatment area at the site (once ozone treatment stops) and downgradient of the site. <br /> 4.3.6. 1 Cr(VI) <br /> Untreated soil and soil treated with a low dose of ozone reduced up to 1.9 mg Cr(Vl)/kg <br /> soil, while treated with a high dose of ozone reduced up to 1.4 mg Cr(VI)/kg soil. These <br /> results indicate that the soil has some ability to reduce Cr(VI) and that ozone may affect <br /> the ability of the soil to attenuate Cr(VI), but the magnitude of the effect depends on the <br /> amount of ozone applied. The results of the long-term Cr(VI) attenuation test showed that <br /> Cr(VI) readily attenuated in simulated downgradient conditions with complete removal of <br /> Cr(VI) in only seven days. In contrast, the concentration of Cr(VI) initially increased <br /> within the treatment area, but then slowly attenuated. Complete removal had not occurred <br /> with 60 days, however, a trend of attenuation had clearly been established. The results of <br /> available Cr(VI) reducing capacity test are shown in Table 9, and the long-term Cr(VI) <br /> attenuation test results are presented in Table 10 of the Prima Report located in <br /> Appendix B. <br /> 4.3.6.2 Bromate <br /> The results of the long-term bromate attenuation tests showed that bromate appeared to <br /> attenuate slowly in tests simulating downgradient conditions; by 28 days the bromate <br /> concentration had decreased from 0.31 mg/L to 0.16 mg/L. In contrast no attenuation was <br /> TOC 4172 Rench Scale lest Page 14 <br />
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