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ARCHIVED REPORTS_XR0009414
Environmental Health - Public
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EHD Program Facility Records by Street Name
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12 (STATE ROUTE 12)
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3049
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3500 - Local Oversight Program
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PR0545717
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ARCHIVED REPORTS_XR0009414
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Last modified
11/19/2024 3:45:51 PM
Creation date
6/3/2020 11:16:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009414
RECORD_ID
PR0545717
PE
3528
FACILITY_ID
FA0003912
FACILITY_NAME
MARTINIS BAIT & TACKLE
STREET_NUMBER
3049
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95240
APN
02514016
CURRENT_STATUS
02
SITE_LOCATION
3049 W HWY 12
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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LSauers
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EHD - Public
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1 <br /> RISKPRO'S SESOIL for Windows User's Guide <br /> In SESOIL, each soil layer (sublayer) has a set volume and the total soil column is treated a <br /> a series of interconnected layers Each layer (sublayer) has its own mass balance equation (Eq 1 <br /> [61) and can,,receive and release pollutant to and from adjacent layers (sublayers) Again, the <br /> individual fate processes that compose the SESOIL mass balance equations (e.g., volatilization, ' <br /> degradation) are functions of the pollutant concentration in the soil water of each zone and a <br /> variety of first-order rate constants, partitioning coefficients, and other constants. An iterative <br /> solution procedure is used to solve the system (the iteration parameter is c) See Bonazountas ' <br /> and Wagner (1984) for the numerical solution procedure <br /> The pollutant cycleequationsare formulated on a monthly basis and results are given for each ' <br /> month simulated. However, to account for the dynamic processes in the model more accurately, <br /> - an-explicit-time-step-of-l- day-is-used-in-the-equations The-monthly output_represents-the— <br /> summation of results from each day ' <br /> In the event that the dissolved concentration exceeds the aqueous solubility of the pollutant, the <br /> dissolved concentration is assumed to equal the aqueous solubility That is, if during solution ' <br /> of the mass balance equation for any one layer, the dissolved concentration exceeds the solubility <br /> of the chemical, the iteration is stopped for that time step and the solubility is used as the <br /> dissolved concentration The adsorbed and soil-aur concentrations are calculated using the ' <br /> chemical partitioning equations as before (Eqs [7] and [81). To maintain the mass balance, the <br /> remaining pollutant is assumed to remain in a pure phase (undissolved). Transport of the pure <br /> phase is not considered, but the mass of the chemical in the pure phase is used as input to that/ <br /> same layer in the next time step Simulation continues until the pure phase eventually <br /> disappears The pure phase: capability was not part of the original model and was added to <br /> SESOIL by Hetrick et al (1989) <br /> The discussion in the subsections that follow introduces the user to major algorithms and -' <br /> processes simulated in the pollutant cycle of-SESOIL <br /> 3.5.2 The Pollutant Depth Algorithm ' <br /> The pollutanf cycle in SESOIL is based on the pollutant concentration in soil moisture. In <br /> theory, a non-reactive dissolved pollutant originating in any unsaturated soil layer will travel to ' <br /> another soil layer or to the groundwater at the same speed as the moisture mass onginatsng in <br /> the same soil layer. The movement of a reactive pollutant, however, will be retarded in relation <br /> to the movement of the bulk moisture mass due to vapor phase partitioning and the adsorpuon <br /> of the pollutant on the soil particles If it is assumed that no adsorption occurs, and the vapor <br /> phase is negligible, the pollutant will move at the same rate as water through the soil <br /> 1 <br /> 1 <br /> Page 20 ' <br /> I <br />
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