DMSTA Calibration & Enhancements for Reservoirs
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Summaries |
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Lake & Reservoir Dataset Index | |
Bar Charts of Dataset Characteristics | |
Depth & Load Ranges for Calibration Datasets vs. CERP Reservoir Designs | |
Depth & Load Ranges for Other Lake & Reservoir Datasets | |
Concentration Reductions - First Order Model | |
Concentration Reductions - Second Order Model | |
Concentration Reductions - Biomachine Model | |
Biomachine Model - Reservoir vs STA Calibrations - K & C1 | |
Steady-State Model Applied to Other Florida Lake Data |
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CERP Reservoir Simulations |
Detailed Calibration
Results - Lake
& Reservoir Datasets 6 Summaries: Map Listing Bar Charts Scatter Plots Conc Time Series Sensitivity to Model Sensitivity to Calibration Home |
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Dataset | Source | Map | Calib Years |
Area km2 |
Conc. Reduc |
HLR m/yr |
K m/yr |
Calib1 | Sensitivity to Model2 |
Sensitivity to Calib3 |
Resids4 | Notes / Limitations |
Okeechobee 1975-1978 |
WWW | 4 | 1732 | 69% | 1.3 | 4.2 | large; low HLR, wind effects;
calcium effects; trends; outflow concs from open lake (pelagic zone) |
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Okeechobee 1979-1986 |
WWW | 8 | 1732 | 53% | 1.4 | 3.2 | " | |||||
Okeechobee 1987-1994 |
WWW | 8 | 1732 | 40% | 1.3 | 2.0 | " | |||||
Okeechobee 1995-1999 |
WWW | 5 | 1732 | 28% | 1.9 | 1.2 | " | |||||
Okeechobee 1975-1999 |
25 | 1732 | 45% | 1.5 | 2.4 | " | ||||||
Okee.Outlets 1982-1999 |
WWW | 25 | 1732 | 38% | 1.5 | 1.8 | " outflow concs from outlets;
data incomplete < 1982; test sensitivity to outflow conc monitoring location |
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Istokpoga5 | WWW | 12 | 110 | 51% | 3.5 | 5.0 | inflows/outflows from Istokpoga canal ignored quarterly/bimonthly sampling |
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Istokpoga_25 | B&M | 13 | 112 | 52% | 3.2 | 5.9 | "" outflow conc series revised | |||||
Jessup5 | B&M | 8 | 53 | 38% | 3.3 | 2.3 | outlet backflow; 39% inflow ungauged | |||||
Crescent5 | B&M | 6 | 71 | 18% | 10 | 2.8 | outlet backflow; 54% inflow ungauged | |||||
Thonotosassa5 | B&M | 10 | 3.3 | 31% | 11 | 4.8 | high inflow p;inflow volumes not gauged | |||||
George5 | B&M | 6 | 5.9 | -19% | 17 | 0.1 | conc. trend;
outlet backflow;
negative p retention; missing inflows 2001; 2001-2003 data ignored |
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Rodman | B&M | 9 | 30 | 28% | 42 | 21 | high HLR; mainstem impoundment; high l/w ratio | |||||
Poinsett | WSI | 16 | 16 | 5% | 40 | 5.7 | high HLR; favorable depth regimes, but depths
were not directly measured |
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Harney | B&M | 12 | 30 | -8% | 64 | 1.6 | high HLR; negative p retention | |||||
Harney_2 | WSI | 9 | 30 | -5% | 81 | 1.9 | high HLR; negative p retention | |||||
St Johns Marsh CA |
B&M | 5 | 94 | -13% | 140 | 1.3 | high HLR; mixed marsh & lakes;
variable area;
negative p retention; 44% inflow ungauged; outflow sites in middle; simulations ignore marsh area |
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Sawgrass | WSI | 2.6 | 2.0 | 13% | 374 | 17 | high HLR; part of SJMCA | |||||
HellnBlazes | WSI | 2.7 | 1.5 | 9% | 449 | 0.4 | high HLR; part of SJMCA | |||||
1 - observed & predicted time series with
biomachine K
values calibrated to each dataset (C1= 150 ppb & C0 = 4 ppb) 2 - sensitivity to calibration using K values of 1.6, 3.2 and 6.4 m/yr. Joint calibration = 3.2 m/yr. 3 - sensitivity to model formulation (RESERV = DMSTA biomachine, RESERV_K1 = first order, RESERV_K2 = second order) using joint calibrations for each. 4 - residuals (ln (observed/predicted concentrations)) vs dataset characteristics for individual calibrations 5 - datasets with hydraulic loads in design range for typical CERP reservoirs ( 2 - 20 m/yr) 6 - in the calibration charts, red symbols represent observed values & lines represent simulated values. |
http://www.wwwalker.net/dmsta/reservoirs/figs_tabs.html 07/08/2005