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ARCHIVED REPORTS_XR0009414
EnvironmentalHealth
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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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EHD - Public
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RISKPRO'S SESOIL for Windows User's Guide <br /> employs a stochastic approach for the hydrologic and washload cycles, and a deterministic <br /> approach for the pollutant transport cycle <br /> 3.1 The Soil Compartment <br /> In SESOIL, the soil compartment (or column) is a cell extending from the surface through the <br /> unsaturated zone to the upper level of the saturated soil zone, also referred to as the aquifer or I <br /> groundwater table While SESOIL estimates the pollutant mass added to the groundwater, the <br /> saturated-zone is not modeled _The output from SESOIL can be used-for generating input values <br /> for groundwater transport models (In RISKPRO, the Analytic Transient 1-2-3 Dimensional <br /> Model, AT123D (Yeh, 1981), has been adapted to use SESOIL results for groundwater runoff <br /> [recharge]to simulate chemical movement-in the saturated-zone.-) <br /> In SESOIL the soil compartment is treated different) by the hydrologic cycle and the pollutant ' <br /> p Y <br /> cycle In the hydrologic cycle, the whole soil column is treated as a single homogeneous <br /> compartment extending from the land surface to the water table The pollutant cycle breaks the ' <br /> soil column into several corffpartments, also called layers.' The layers in the pollutant cycle can <br /> be further broken-up into,sublayers Each soil layer (sublayer) is considered as a compartment <br /> with a set volume and the total soil column is treated as a series of interconnected layers ' <br /> (sublayers) Each layer (sublayer) can receive and release pollutant to and from adjacent layers <br /> (sublayers) 4 <br /> The dimensions of the soil compartment are defined by the user The width and length of the <br /> column are defined as the area of application of pollutant released to the soil, and the depth to <br /> _the groundwater-is-determined-from-the thickness of user-defined soil layers that are used in the -' <br /> pollutant cyclo.- The soil column can be-represented Ch 2, 3, of-4 distinct layers Up to 10 <br /> sublayers can-be-specified-for-each-layer,-each having the same soil properties as the layer in _I <br /> which they reside <br /> There is no optimal size for the soil layers (sublayers); the dimensions of the soil column can ' <br /> be specified to cover any area from one square centimeter to several square kilometers The <br /> area of the compartments is important for mass balance, but in terms of pollutant concentration <br /> the area of application is irrelevant since it is constant for all layers (sublayers) Note that the ' <br /> equations in SESOIL have been normalized to an area of one square centimeter <br /> It is suggested that the minimum depth of a layer be one centimeter. Depending on the t <br /> application, layer depths can range from a shallow root zone of 5-25 centimeters to a deep layer <br /> of more than 10 meters When the pollutant enters a layer (sublayer), the model assumes <br /> instantaneous and uniform distribution of the chemical throughout that layer (sublayer) The <br /> model performs mass balance calculations over each entire soil layer (sublayer), there is no <br /> concentration gradient within a layer (sublayer) For a given amount of chemical releasers, the <br /> I <br /> Page 6 <br /> I <br /> �1 <br />
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