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ARCHIVED REPORTS_XR0009414
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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T
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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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T <br /> r , I <br /> RISKPRO'S SESOILfor Windows User's Guide <br /> Pollutant loss via washload is computed by taking the sediment yield from the washload cycle <br /> multiplied by the adsorbed pollutant concentration in the surface Iayer While studies have been ' <br /> conducted comparing results of sediment yield with field data (Hetrick and Travis, 1988), <br /> pollutant loss via washload has not been validated in SESOIL. <br /> 3.5.8 Soil Temperature' , <br /> I <br /> The anginal SESOIL model assumed that soil temperature was equal to the user-supplied air I <br /> temperature. The model was modified by Hetrick et al. (1989) to predict soil temperature from <br /> air temperature according to the following (Toy et al 1978). <br /> r <br /> Summer Y= 16:1-15---+---0-856X, <br /> Fall: Y = 1578 + I023X, 1 <br /> Winter. Y 15 322 + 0 656X, <br /> Spring Y = 0 179 + 1 052X, <br /> where• <br /> Y = the mean monthly soil temperature (°F). ' <br /> X = the mean monthly air temperature ff) <br /> These regression -equations-are very crude and not depth dependent. However, furthe <br /> complexity is not warranted since ,soil temperature is used only in Eq. (7) and does nc <br /> significantly affect results. It should be noted that some chemical parameters and processes are <br /> dependent on temperature (for example, solubility, Henry's law constant, and rate constants for <br /> biodegradation and hydrolysis) No explicit consideration of these effects is included in <br /> ^SESOIL,,and the user should adjust the--input values for such parameters-if temperature effects T <br /> -are judged_to be.important __ _ -- - __- — ___ - - -_ _ I 1 <br /> 3.5.9 Pollutant Cycle Evaluation <br /> There are several approaches used to evaluate the reliability and usefulness of an environmental ' <br /> model, such as verification, calibration, sensitivity analysis, uncertainty analysis, and validation <br /> Verification establishes that results from each of the algorithms of the model are correct <br /> Calibration is the process bf adlissting-selected_model parameters within an accepted range until <br /> the differences between model predictions and field observations are within selected cntena of <br /> performance (Doniiigan and Dean, 1985). Sensitivity analysis focuses on the relative impact each <br /> parameter or term has on the model output, in order to determine the effect of data quality on <br /> output reliability. Uncertainty analysis seeks to quantify the uncertainty in the model output as ' <br /> a function of uncertainty in both model input and model operations. Validation also compares <br /> measured with predicted results, but includes analysis of the theoretical foundations of the <br /> model, focusing on the model's performance in simulating actual behavior of the chemical in the , <br /> Page 30 ' <br />
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