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ARCHIVED REPORTS_XR0011714
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0545317
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ARCHIVED REPORTS_XR0011714
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Last modified
2/11/2020 10:59:33 AM
Creation date
2/11/2020 9:31:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011714
RECORD_ID
PR0545317
PE
2952
FACILITY_ID
FA0005251
FACILITY_NAME
M L GRENZ
STREET_NUMBER
6540
Direction
E
STREET_NAME
JAHANT
STREET_TYPE
RD
City
ACAMPO
Zip
95220
APN
00526003
CURRENT_STATUS
02
SITE_LOCATION
6540 E JAHANT RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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320 PETROLEUM OONVAMINATEO SOILS IEST1MATES FOR HYDROCARBON VAPOR EMISSIONS 321 <br /> 1V. AIR DISPERSION MODELING stud} Included gradual plume rise,buoyancy-induced dispersion,and stack down- <br /> wash The source was assumed to be located in an urban env Ironrnenl <br /> IV 7 Model Description The "box model" illustrated in Figure 14 was used to predict conservative <br /> ambient cuncenlration estimates for receptors located on the downwind edge of <br /> The EPA-recommended Industrial Source Complex (ISC) Model, %,,hich can the area sources considered in this chapter It was assumed that vapors within <br /> be used to predict ambient concenirattons from both stack and arca sources for lite box were "well-mixed," and the height of the box, S, was set to be equal <br /> receptors located at least 100 m from a sourer, %as used to perform the err dis- to human breathing zone height — 2 in Given the wind speed <u>,breathing <br /> persion modeling For this analysts,a polar-coordinate grid was generated with zone height S, length of emission source parallel to the wind direction L, and <br /> receptors located on concentric rings at radii of 100 ni, 300 m, 500 m, 700 m, emissions flux XF,, then the ambient concentration C, ,.b. is <br /> and 1000 in from each source Thtrty-six receptors, at 10 degree intervals, wereC ff,L (�4) <br /> located on each ring, snaking a total of 180 receptors The ISC model employs iiib r S<u> <br /> standard gaussian dispersion algorithms to calculate the hourly concentration at <br /> cacti receptor If an entire year of meteorological data Is Input to the model,then IV.2 ISC Model Predictions <br /> a full year of hourly concentrations can be calculated for each receptor These <br /> hourly values can then be averaged to give an annual average for each receptor, ISC model predictions are summarized in Table 3. Each scenario modeled is <br /> or they can be sorted and ranked to give inaxinsnni F. 8-, and 24-h averages, described bredly below <br /> For this modeling,irleteorological data from Long Beach,California for the year <br /> 1964 was used Other required mtdeoralogical parameters include wind speed Table 3 Air Dispersion Modeling Results <br /> and direction, ambient temperature, mixing height, and stability class For area Beene vapor Contvawlons 'l <br /> sources, the size and height of the release a% well as the einission flux are re- Reaudpistsncs <br /> quired input parameters For stack releases, the Stack height and diameter and Sornarto 0uratim 100 m 300 m 34n m 100 m 100D m sox Model <br /> exit-,as velocity and temperature are needed Modeling options selected for this i excaealwrr" 039 0A77 004 OD3 002 24 <br /> (70yaveTage) 3d <001101 <0OD01 <00001 <00001 <00001 <001 <br /> 2 M8vallo11" 015 003 002 001 001 42 <br /> 170 y average) 341 <00001 <0 DON <0 0001 <O D001 <00001 <001 <br /> 3 sod pleb 75 is 079 0 S7 041 4110 <br /> {TO i average) 3x8 h <0001 <00001 <0 DWI <OA00I <OODD1 <001 <br /> 4 venting unlreatedvaprs" 66 09 038 02 011 NA <br /> r� ^� (701 average) 160 d 045 <0 01 <0 01 <0 01 <0 001 NA <br /> � <br /> < � 3 venting,unhealed v>Ap e D D8 001 <001 <001 <001 RA <br /> (70yaverage) 180d <0WOt <00001 <0 DWI <00001 <OOWl 11A <br /> 6 verging lresled%apanc 012 0im 0112 001 <001 NA <br /> 1110- {70 y average) 180 d <OOOt <90D1 <0001 <0A001 <O 0001 NA <br /> 7 venting healed vapors` <001 <OOOF <0001 <DAol <000i NA <br /> (70)average) 1ODd <OODOi <0OD0D1 <OWD01 <00=1 <00DD01 NA <br /> 8 trw4quld pumping` <0001 <0 DDI <0001 <0001 <0001 NA <br /> (70 y averege) 60d <O D0041 <0 DD001 <0 09001 <0 DOM <OODDOI RA <br /> 9 gwohri"eturaled GW puW 060 008 D05 002 <001 NA <br /> (70 y emeragel 6 y 007 <11)01 <001 <0 01 <O wl NA <br /> 10 1ppm benreneGthfgrirtlp° 00; <001 <001 <DWI <0001 NA <br /> 1 (70 y average) 6 y <001 <D 001 <0001 <00001 <0 0001 NA <br /> 11 alr4trlppei gas sal Of 12 025 DID 006 0 03 NA <br /> 170yavemp) Si 004 002 <0 Of `041 `001 t0A <br /> % s>,if;3 x> 12 an stripper I ppm Wrims Gff 007 001 <0 D1 <001 <021 14A <br /> t r=y1 .t ry j--+ ; j} {, `c ;, (70 y average) 5 y <001 <0 001 <0001 <O ODI <0001 NA <br /> { ` ���i-5` 1 13 boned soilsleflnplaoe 0044 <0 01 <001 `001 <DOi 09� <br /> (70yaverage) 70y 0444 <001 <001 <001 <001 094 <br /> Contaminated Soil 'peak 24hncetraAfan <br /> mak&h caxenrrarron <br /> `annual average euncenlral.ort <br /> i, Ftgute 14 Bax model schematic 4nrndnmm 1wnq neo M Jnr vIod i nr Md� A unrn.•r Poi qrn ati"111 I-P <br />
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