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PR0545129
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
1/7/2020 9:00:08 AM
Creation date
1/7/2020 8:37:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0545129
PE
3528
FACILITY_ID
FA0006171
FACILITY_NAME
Mizkan America, Inc.
STREET_NUMBER
1400
Direction
E
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95205-3743
APN
14115002
CURRENT_STATUS
02
SITE_LOCATION
1400 E WATERLOO RD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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08/06/96 09:47 0510 372 5220 IT CORP MARTINEZ <br /> t <br /> 2. MODEL CONCEPTUALIZATION,ASSUMPTIONS, <br /> AND LIMITATIONS <br /> VLEACH describes the movement of an organic conta1 unant within and between three <br /> } different phases_ (1) as a solute dissolved in water, (2) as a gas in the�ya�r phase, and (3) as an <br /> ' adsorbed compound in the solid phase (see Figure 1). Equilibration between the phases occurs <br /> according to distribution coefficients defined by the user. In particular,VLEACH simulates vertical <br /> transport by advection in the liquid phase and by gaseous diffusion inthc vapor phase. <br /> i <br /> These processes are conceptualized as occurring in a inurnbcr of distinct, user-defined <br /> polygons that am vertically divided into a series of user-defined cells. The polygons may differ in <br /> t soil properties, recharge rate, and depth to water(see Figure 2)'. However, within each polygon <br /> homogeneous conditions are assumed except for contaminant concentration, which can vary <br /> between layered cells(see Figure 3). During each time step the nugra"of time contaminant within <br /> t ' and between cells is calculated. Hence,VLFACH can account for heterogeneities laterally but is <br /> limited when simulating vertical heterogeneity. r <br /> Initially,VLEACH calculates the equilibrium distribution of contaminant mass between the <br /> 1 liquid,gas,and sorbed phases. Transport processes we then simulated.1�Liquid advective transport <br /> is calculated based on values defined by the user for infiltration and soil water content. The <br /> contaminant in the vapor phase migrates into or out of adjacent ceps based on the calculated <br /> concentration gradients that exist between adjacent cells. After the mass is exchanged between the <br /> cells, the total mass in each cell is recalculated and re-equilibrated between the different phases. <br /> ' Theses s are conducted for each times ,and each polygon is simulated independently. At the <br /> � steps mP Po YS ,� �M <br /> end of the model simulation,the results from each polygon ate cotnpiledtodetermine an overall area- <br /> weighted groundwater impact for the entre modeled area. <br /> For computational purposes each polygon is divided vertically into a series of cells. When <br /> developing a model simulation,it is important to fully understand the implications of the VLEACH <br /> conceptualization. The following assumptions are trade in the development of VLEACH. <br /> { Ip ;; <br /> 1. Linear isotherms describe the partitioning of the pollutant between the liquid,vapor and soil <br /> _ phases.Local orinstantaneous equilibrium between these'phasesis assumed within each cell. <br /> f 2. The vadose zone is in a steady state condition with respect to water movement. More <br /> specifically,the moisture content profile within the vadose zone is constant. This assumption <br /> will rarely occur in the field. Although moisture gradients cannot be simulated,the user can <br /> estimate the impact of various moisture contents by,!icom sarin results from several <br /> comparing <br /> simulations that cover the common or possible ranges in,soil zrioisture conditions. <br /> 3 " <br />
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