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SPDSS_Task48-2_AlluvialGroundwaterModelingCalibration
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SPDSS_Task48-2_AlluvialGroundwaterModelingCalibration
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Last modified
4/17/2013 9:26:40 AM
Creation date
8/11/2008 1:11:50 PM
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Decision Support Systems
Title
SPDSS Task 48.2 - Development of Calibration Targets and Criteria - Phase 4
Description
This Technical Memorandum was undertaken under Task 48.2 of Phase 4 of the SPDSS, to develop calibration criteria, including selection of field data (targets) to be used during the model calibration. This TM summarizes the methodology and data that are anticipated to be used in the model calibration process.
Decision Support - Doc Type
Task Memorandum
Date
10/8/2008
DSS Category
Groundwater
DSS
South Platte
Basin
South Platte
Contract/PO #
C153953
Grant Type
Non-Reimbursable
Bill Number
SB01-157, HB02-1152, SB03-110, HB04-1221, SB05-084, HB06-1313, SB07-122
Prepared By
CDM
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and observed values, called the residuals. These are defined prior to beginning fl1e calibration <br />process and are considered as goals based on the modeling objectives and measurement or <br />other errors inherent in the field measurements. Calibration criteria are defined for each type of <br />calibration target. The criteria for each calibration target are discussed in Section 4.1. In <br />addition to the evaluation of residuals, the model calibration process will also include maps, <br />1listograms, and scatterplots of residuals to help identify spatial trends. <br />The head and flow criteria are compared to the results provided uz the automated model <br />calibration package (PEST; Doherty, 2004) through its parameter estimation objective function, <br />discussed in Section 4.2. T11e head and flow data used for calibration have varying degrees of <br />uncertainty. This uncertainty in the observed values is factored into the calibration process by <br />assign>11g weighting factors. Weighting factors that will be assigned to each calibration criterion <br />are discussed in Section 4.3. <br />4.1 Target Criteria <br />Calibration targets have been developed for use with the automated parameter estimation <br />objective function ('numeric' targets, described in Sections 3.2 through 3.4) and for the manual <br />evaluation of model calibration using other targets ('non-numeric' targets, described in Section <br />3.5). The model calibration will first rely on the numeric targets and their criteria, with <br />simulations meeting these criteria in fl1e objective function being further evaluated with the <br />non-numeric targets and their criteria to determine if additional calibration is needed. Eac11 set <br />of targets and criteria are presented in the sections below. <br />4.1.1 Criteria for Head and Flow Targets <br />The calibration criteria are listed below. They are considered to be reasonable calibration goals <br />based on review of the data and eng>1leering judgment but may need to be revised based on the <br />>1litial model calibration efforts. There are no generally accepted standards for an acceptable <br />agreement between modeled and observed heads and flows in guidance documents from <br />organizations such as the ASTM or various state agencies. <br />• T11e absolute value of t11e mean difference of head residuals for wells with surveyed <br />elevations across all time periods will be less fllan 5 feet. <br />• The absolute value of fl1e difference between observed 1leads at surveyed wells across all <br />time periods will be less fllan 5 feet for 75 percent of the observations. <br />• Observed and calculated average annual streaniflows will be withi1110 percent for all <br />flows greater than 25,000 acre-feet/year. <br />• Observed and calculated average annual stream gain/loss within a given reach will be <br />wifllin 10 percent for all flows greater than 25,000 acre-feet/year. <br />4.1.2 Criteria for Other Non-numeric Targets <br />• Residuals for head and flows should be randomly distributed on a geographic and <br />temporal basis. <br />• T11e model volumetric water balance calculated by the model will be within 1 percent for <br />fl1e steady-state calibration simulation and within 5 percent at the end of fl1e transient <br />simulations. <br />• The residual for each of the components of the groundwater budget will be less than ten <br />percent for 75 percent of the budget components. <br />P~ SPDSS T~8 2 Final TM 10-08-0t~.doc 16 <br />
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