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ARCHIVED REPORTS XR0012562
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0536618
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ARCHIVED REPORTS XR0012562
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Entry Properties
Last modified
3/4/2019 10:37:51 AM
Creation date
3/4/2019 8:02:28 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012562
RECORD_ID
PR0536618
PE
2960
FACILITY_ID
FA0021026
FACILITY_NAME
STOCKTON CHARTER WAY COMMON PLUME
STREET_NUMBER
440
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16503003
CURRENT_STATUS
01
SITE_LOCATION
440 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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- <br /> `i <br /> i <br /> ; <br /> JUL <br /> ENVIRONMENTAL HEALTH <br /> SERW155i <br /> Mr. R. R.Zielinski Page 2 <br /> 02320 0475 <br /> The water samples were analyzed using modified EPP methods 5030/8020/8095, which measure <br /> concentrations of total petroleum hydrocarbons-as-gasoline(fPH C),and benzene,toluene,ethyibenzene <br /> and xylenes(BTEX). Copies 0f the laboratory analysis reports and chain-of-custody martifest are presented <br /> in Attachment C. <br /> GROUNDWATER ANALYTICAL RESULTS b to 83,000 ppb; <br /> Concentrations of TPH-G In the groundwater sampies ranged tbro Twoparts <br /> n orping�ivteos record b andstantial <br /> MW 5 <br /> the range for the previous quarter was from 64Cto 84,000 MWA decr&sed from 94,000 to irom0.9 fo 2i,000 ppb. <br /> changes In dissolved TPH G concentrations, <br /> Increased from 30,004 to 83,000 ppb TPH-G. The berrzone eanceniratfons rang <br /> TPH-G and benzone concentrations In groundwater for Febr`a laboratory analyses for the la1991 are shown In st five sampiding <br /> (Attachment A). Table 2(Attachment B),presents results Of the <br /> events. j <br /> Sall VAPOR EXTPACTION TEST <br /> BACKGROUND Is and an angle <br /> installed during the <br /> Analytical results of soil samples collected <br /> a usod t delf'na the extent hydrocaborinC rbonlimpa°led soils beneath <br /> course of the subsurface investigation, a State-cs�iQm 2 iQ 2 5or00 pan°pe <br /> the Texaco service station site. These soil samples were analyzed by ranging <br /> of the samples collected contained detect <br /> able concentrations of TPH G E <br /> million(ppm).,9 samples contained detectable concentrations of benzene ranging from t to 1i ppm. <br /> acted soil appears to be confined <br /> Based on the laboratory analyses of the 6011 samples,hydrocarbon impto the r <br /> beneath the northeast corner of the site and has been definednot exten'directions <br /> fuerther than 20 feet north of the <br /> underneath Charter Way. Aseuming that the Impacted so,!do approximately 3,000 ruble yards. <br /> site,(under Charter Way),the volume of impacted soil Is estimated to be in estimated <br /> The avArage concentration of petroioum hydrocarbons <br /> weight ht of hydrocarbons oca bons between 4,300 to 0 8,700Ypound s <br /> and 1,000 parts per million(ppm)yielding a 9 <br /> Since Charter Way is State Route 4 and within the Cal Trans right <br /> hrwrtae;further subsurface exploration is <br /> .,at feasible because Cal Trans does not allow this type of enc lay to a depth of 30 to 35 fest <br /> soils encountered during drilling operations consisted predominateivs t and a fine micaceous sand, <br /> below ground surface(BGS). The clay Is underlain by water-bearing ;i <br /> SOIL VAPOR EXTRACTION PILOT TE METHOD E <br /> A soil-venitng pilot test uin <br /> was conducted on May 21, 1991• Pers isThe est wasas conducted ained to determine m the San gthe i <br /> County Air Pollution Control District prior to conducting the to ower regened f rre blower. Flaw rate <br /> radius of influence and the concentration of hydrocarbons In the soil vapor extracted from blower. <br /> , Flow and <br /> MV,4-5. Vapors were drawn from each extraction well by a 1.5 horsepas <br /> during the test was most orer'with a Kurz model a blower41 air velocity <br /> war,discharged dmeter,and irectly totheeatmosphere and <br /> cubic feet per minute(cfrn). Effluent air from the photo-Ionization detector(PiD). A sample <br /> concentrations were monitored during operation with a portable p c and shipped with a chain-of-custody <br /> from extraction wells MW-5 and Mw_4 was collected In TedlaB�5X020 for BTEX,and TPH-G. No sample <br /> Mani GTELforManalysis cause of the pto Pesence methods separate-phase petroleum to the well. <br /> was collected from <br /> ;....r..-. `GRoUNOWATiat <br /> TECHNOLOGY INC. <br /> 7 <br />
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