| DMSTA Case Index - Datasets North of Lake Okeechobee |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Starting Date for Simulation |
First Calib Date |
Last Calib Date |
Surface Area |
Tanks in Series |
Hydraulic Load |
Load |
Depth |
Inflow Conc |
Storage |
Obs Geo Mean |
Obs Flow Wtd Conc |
Residual Std Error - Ln C |
C1 =WC Conc at 1 g/m2 P
storage |
Calib K |
Std Error of K |
| Case |
Type |
Case Description |
- |
- |
- |
km2 |
- |
cm/d |
mg/m2-yr |
cm |
ppb |
mg/m2 |
ppb |
ppb |
- |
ppb |
m/yr |
m/yr |
| Harney |
Lake |
lake/reservoir with 2
tributary arms; P data monthly; gap in inflow conc time series 1985-1989;
5-yr initialization; short HRT & high water load |
07/77 |
10/89 |
12/98 |
24.5 |
2 |
22.1 |
4047 |
179 |
50 |
2610 |
49 |
51 |
0.28 |
22 |
5.3 |
0.9 |
| Sawgrass |
Lake |
lake/reservoir; depths
estimated; gap in inflow conc time series 1985-1990; high water load; short
hrt ~ 1.5 days; 5-yr initialization;p simulation insensitive to calibration |
12/74 |
03/96 |
09/99 |
2.0 |
2 |
89.9 |
45493 |
133 |
139 |
5975 |
123 |
122 |
0.24 |
22 |
0.3 |
0.3 |
| HellnBlazes |
Lake |
lake/reservoir; depths
estimated; sparse inflow conc prior to 3/1996; high water load & short
HRT (1 day); 5-yr initialization;p simulation insensitive to calibration |
12/74 |
03/96 |
09/99 |
1.5 |
2 |
113.8 |
66503 |
115 |
160 |
9202 |
152 |
140 |
0.30 |
22 |
0.8 |
0.5 |
| Poinsett |
Lake |
lake/reservoir; depths
estimated; inflow P data sparse after 1990; 5-yr initialization period;
depths lower & more variable than other DMSTA lake/reservoir datasets |
10/68 |
01/79 |
12/90 |
17.5 |
2 |
11.0 |
3960 |
87 |
98 |
3722 |
78 |
96 |
0.43 |
22 |
15.2 |
1.7 |
| Istokpoga |
Lake |
lake/reservoir;
sav/hydrilla dominated; data from walker & havens, 2003; 5 yr
initialization |
01/83 |
01/93 |
09/00 |
110.0 |
2 |
0.9 |
351 |
170 |
105 |
2750 |
45 |
54 |
0.34 |
22 |
3.4 |
0.5 |
| Okeechobee |
Lake |
lake/reservoir; calibrated
to 1990-1999; startup period 1973-1989; observed concentrations in pelagic
zone; simulation affected by intial condition |
11/72 |
01/90 |
12/99 |
1732.0 |
1 |
0.4 |
263 |
271 |
162 |
4998 |
96 |
114 |
0.27 |
22 |
0.4 |
0.1 |
| Lakeland |
Tmt Wetland |
High inlet P ~6000 ppb;
clay soils; built on phosphate mine; poor hydraulics; used 10 iterations to
stabilize biomass P |
01/93 |
06/96 |
09/99 |
4.8 |
6 |
0.7 |
12824 |
114 |
4716 |
202882 |
3004 |
2922 |
0.22 |
22 |
1.3 |
0.1 |
| Oew |
Tmt Wetland |
Orlando Easterly Wetlands /
Iron Bridge; 1989-2003; Heterogeneous multi-cell treatment wetlands; deep & shallow cells; emergents,
hardwoods, lake; started on cow pasture (high initial P?); depth information
limited; P detection limit = 20 ppb; inflow p declined from 600 to 100 ppb;
experimental manipulations began in mid 1997 (southern flow path taken off
line) |
07/83 |
07/88 |
08/03 |
4.8 |
6 |
1.2 |
1119 |
70 |
266 |
6611 |
51 |
61 |
0.50 |
22 |
10.6 |
0.2 |
| Oew_8991 |
Tmt Wetland |
Orlando Easterly Wetlands /
Iron Bridge; Cells 1-17 + Lake; calibrated to 1989-1991 (inflow P ~ 500 ppb) |
07/83 |
07/88 |
12/91 |
4.8 |
6 |
1.0 |
1824 |
70 |
488 |
11290 |
79 |
87 |
0.22 |
22 |
8.4 |
0.3 |
| Oew_9397 |
Tmt Wetland |
Orlando Easterly Wetlands /
Iron Bridge; Cells 1-17 + Lake; calibrated to 1993-1997 (inflow P ~ 100-200
ppb) |
07/83 |
01/93 |
12/97 |
4.8 |
6 |
1.1 |
667 |
70 |
164 |
4814 |
37 |
41 |
0.38 |
22 |
13.3 |
0.3 |
| Oew_8997 |
Tmt Wetland |
Orlando Easterly Wetlands /
Iron Bridge; Cells 1-17 + Lake; calibrated to 1989-1997 data; C1 = 66 ppb. |
07/83 |
07/88 |
12/97 |
4.8 |
6 |
1.1 |
1109 |
70 |
284 |
2013 |
51 |
61 |
0.27 |
66 |
9.6 |
0.1 |
| Oew_1_15_8991 |
Tmt Wetland |
Orlando Easterly Wetlands,
Cells 1-15 (excluding lake); calibrated to 1989-1991 (inflow P ~ 500 ppb) |
07/83 |
07/88 |
12/91 |
3.2 |
6 |
1.5 |
2763 |
76 |
488 |
11955 |
62 |
72 |
0.52 |
22 |
10.7 |
0.9 |
| Oew_1_15_9397 |
Tmt Wetland |
Orlando Easterly Wetlands,
Cells 1-15 (excluding lake); calibrated to 1993-1997 (inflow P ~ 100-200 ppb) |
07/83 |
01/93 |
12/97 |
3.2 |
6 |
1.7 |
1010 |
76 |
164 |
4404 |
38 |
42 |
0.39 |
22 |
18.3 |
0.5 |
| Oew_1_15_8997 |
Tmt Wetland |
Orlando Easterly Wetlands,
Cells 1-15 (excluding lake); calibrated to 1989-1997; C1 = ? |
07/83 |
07/88 |
12/97 |
3.2 |
6 |
1.6 |
1680 |
76 |
284 |
1869 |
46 |
53 |
0.44 |
66 |
14.7 |
0.4 |
| Titusville_9799 |
Tmt Wetland |
Treatment wetland; 3 cells in series: shallow marsh - pond - deep marsh; calib
to 1997-1999 |
01/92 |
01/98 |
05/00 |
0.4 |
6 |
2.0 |
2192 |
89 |
299 |
8289 |
61 |
60 |
0.55 |
22 |
11.7 |
1.4 |
| Titusville_0002 |
Tmt Wetland |
Treatment wetland; 3 cells in series: shallow marsh - pond - deep marsh;calib to
2000-2002 |
01/92 |
06/00 |
04/03 |
0.4 |
6 |
1.8 |
1345 |
90 |
209 |
4099 |
27 |
34 |
0.58 |
22 |
22.8 |
1.4 |
| Titusville_9702 |
Tmt Wetland |
Treatment wetland; 3 cells in series; shallow marsh - pond - deep marsh; calib to
1979-2002 ; C1 = 66 ppb |
01/92 |
01/97 |
04/03 |
0.4 |
6 |
1.9 |
1881 |
90 |
277 |
1595 |
40 |
49 |
0.60 |
66 |
17.8 |
0.8 |
| BoneyMarsh |
Tmt Wetland |
Boney Marsh; emergent
wetland treating diversions from kissimee river; depths driven by regulation
schedule; 3-yr initialization; DMSTA prototype dataset for emergent
vegetation |
03/76 |
01/82 |
12/85 |
0.5 |
6 |
2.0 |
424 |
46 |
58 |
919 |
19 |
20 |
0.44 |
22 |
16.1 |
1.4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
| Statistics are
for calibration period |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
| 10/30/2003 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|