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SITE INFORMATION AND CORRESPONDENCE
EnvironmentalHealth
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120 (STATE ROUTE 120)
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17000
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2900 - Site Mitigation Program
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PR0523467
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
11/19/2024 4:01:10 PM
Creation date
4/2/2020 4:34:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0523467
PE
2965
FACILITY_ID
FA0007060
FACILITY_NAME
WINE GROUP, THE
STREET_NUMBER
17000
Direction
E
STREET_NAME
STATE ROUTE 120
City
RIPON
Zip
95366
APN
24506030
CURRENT_STATUS
01
SITE_LOCATION
17000 E HWY 120
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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Modeling Guidelines Page 2 <br /> 7. What are the critical conditions that you are trying to model?Flow?Temperature?pH? Critical <br /> conditions may be combinations of conditions for several parameters that occur at the same time, <br /> e.g. simultaneous low flow and low hardness. Explain why these are critical conditions. Where <br /> parameters are not independent, explain and justify the assumed relations. <br /> 8. What is the model's performance objective or target? An example is: "Reproduce total nitrogen <br /> and total phosph orus concentrations within t 25% for 90%of observed data within the <br /> calibration and validation periods." [Surface Water Quality Modeling: An Introduction, May <br /> 2002,pg 15.] <br /> 9. How will model performance be demonstrated, and what efforts will be taken to improve the <br /> model's accuracy? Model performance may be improved through calibration and validation to <br /> reduce model uncertainty, and a sensitivity analysis can provide insight into the model <br /> uncertainty. <br /> a. How will the model be calibrated and validated? Calibration is the process of selecting <br /> model parameters to"fit"the model to the physical world that it simulates. Validation is <br /> the process of testing the model with the selected parameters to show that it simulates an <br /> independent data set. Calibration and validation information that should be provided <br /> include: (1) identification of the empirical data used, (2) discussion of the physical <br /> constants or other model variables that were modified or adjusted and why, (3)the <br /> procedures that were used to improve model accuracy, and(4)the results of calibration <br /> and validation. <br /> b. A sensitivity analysis evaluates whether a change in a model parameter results in either a <br /> relatively small change in a water quality response or a relatively large change in water <br /> quality response. It is typically performed by varying one calibration parameter or one <br /> model input at a time,usually by a fixed percentage,through an accepted range of values. <br /> A sensitivity analysis can identify the parameters that may be significant contributors to <br /> uncertainty in the model predictions. These parameters may then be further developed to <br /> reduce the uncertainty. The extent of sensitivity analysis that will be completed, <br /> including the parameters that will be analyzed, and the basis for selecting those <br /> parameters should be agreed upon prior to conducting the analysis. <br /> C. How will the model uncertainty be quantified? Model uncertainty describes how close <br /> the model results are to reality,and can be expressed as bias,precision, error,or as the <br /> margin of safety in the results. There should be agreement with Regional Board staff <br /> regarding the acceptable level of uncertainty in the model results. The quantification of <br /> uncertainty typically comes from the calibration, validation,and sensitivity analyses. <br /> There should be a goal to minimize the model uncertainty to a certain value if the model <br /> is being used to predict exact water quality constituent concentrations. However, if the <br /> model is being used to rank best and worst alternatives,the accuracy of the model may <br /> not be as important if the error in the model results is the same for each alternative. <br />
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