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geer > 2008 > hindcasting water levels for eden gaging stations, 2000-2006
Hindcasting Water Levels for EDEN Gaging Stations, 2000-2006
Paul Conrads, USGS South Carolina Water Science Center
Ed Roehl, Advanced Data Mining
What's on tap?
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- Methods development in WCA3a
- Application to EDEN
- Quiet desperation
- The fix
- Results and discussion
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Problem : How to Estimate Water Depths at Ungaged Sites
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- Dataset WCA 3a
- Water-level from 3 sites
- Water-depth data from 17 sites
- EDEN grid and vegetation attributes
- % prairie
- % sawgrass
- % slough
- % upland
- UTM North
- UTM South
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Approach
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- Two step ANN model
- First step: estimate mean water-depths using static model spatially interpolating ANN scheme
- Second step: estimate water-depths variability using dynamic variables
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Static Model Results
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- Each step represents a different site
- Model able to generalize water level difference but not the variability
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Dynamic Model
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- 5 index stations (red dots)
- Combination of static and dynamic data
- 5 validation stations (green dots)
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Final Model Results
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| Figure 5. Plot showing measured (light trace) and predicted (dark trace) water depths for Site W8. Predictions are not continuous due to missing data for one or more of the index stations. [larger image] |
Hindcasting 25 EDEN Sites
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- Existing EDEN sites : 7 years (61,400 data points)
- New EDEN sites : 4 -12 months of data (925-8,760 data points)
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| Figure 1. Locations of Everglades Depth Estimation Network (EDEN) gaging stations in southern Florida (modified from Pearlstine and others, 2007). [larger image] |
Approach: Similar 2-Step Model
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- Separate models for each area
- Number of potential inputs sites reduced using dynamic clustering
- Hindcast example W2
- Input Sites
- Sites 63, 64, 65, 3ASW3, and 3AWS
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Spatially Interpolating ANN Model Stacked Dataset
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Initial Water Level Estimate - W2 Quiet Desperation
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What is going on? |
| Data for W2 not used to train models |
Possible Causes
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- Datum confusion
- Gage offset
- W2 located lower edge of area covered by input sites
- Limited information content of static variables
- Did not use difference from a standard signal (decorrelated dynamic variables)
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Third-step Model: Error correction
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| Figure 7. Three-step modeling approach to make final water-level estimates at a station. [larger image] |
Summary Statistics for Hindcasting Models
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| Table 4. Summary statistics for water-level estimates for new Everglades Depth Estimation Network (EDEN) stations.
[n, number of data values; R, Pearson coefficient; R2, coefficient of determination; Min, minimum; ft, feet; Max, maximum; ME, mean error; RMSE, root mean square error; PME, percent model error]
[Please note: This table is from Open File Report 2007-1350, and the figures referred to in this table are station location maps featured in the report.]
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| Site |
n |
R |
R2 |
Data range |
ME |
RMSE |
PME |
| Min, in ft |
Max, in ft |
| Water Conservation Area 1 (fig. 15) |
| North_CA1 |
41,721 |
0.943 |
0.889 |
13.82 |
16.38 |
-0.046 |
0.134 |
5.2 |
| South_CA1 |
43,409 |
0.991 |
0.983 |
12.85 |
15.90 |
0.008 |
0.088 |
2.9 |
| Water Conservation Area 2 (fig. 17) |
| EDEN11 |
2,637 |
0.950 |
0.902 |
10.97 |
13.19 |
-0.054 |
0.044 |
2.0 |
| EDEN13 |
1,968 |
0.955 |
0.912 |
7.07 |
7.69 |
-0.018 |
0.006 |
1.0 |
| Water Conservation Area 3A (fig. 20) |
| 3A-5 |
5,684 |
0.998 |
0.995 |
8.15 |
10.10 |
0.002 |
0.001 |
0.1 |
| EDEN4 |
2,399 |
0.999 |
0.998 |
6.96 |
10.30 |
0.001 |
0.002 |
0.1 |
| EDEN5 |
1,653 |
0.999 |
0.999 |
8.01 |
10.20 |
0.004 |
0.001 |
0.1 |
| EDEN8 |
2,442 |
0.999 |
0.999 |
6.79 |
9.19 |
0.001 |
0.001 |
0.0 |
| EDEN9 |
925 |
0.999 |
0.998 |
7.69 |
10.55 |
-0.006 |
0.004 |
0.1 |
| EDEN12 |
7,648 |
0.999 |
0.998 |
6.84 |
9.59 |
-0.002 |
0.001 |
0.0 |
| EDEN14 |
969 |
0.906 |
0.821 |
8.66 |
9.59 |
0.011 |
0.010 |
1.1 |
| W2 |
7,648 |
0.998 |
0.995 |
6.86 |
9.42 |
0.008 |
0.003 |
0.1 |
| W5 |
7,648 |
0.999 |
0.998 |
6.84 |
9.59 |
-0.001 |
0.001 |
0.0 |
| W11 |
7,628 |
0.999 |
0.998 |
7.08 |
10.08 |
-0.012 |
0.002 |
0.1 |
| W14 |
7,628 |
0.998 |
0.997 |
7.00 |
10.00 |
-0.013 |
0.003 |
0.1 |
| W15 |
3,859 |
0.999 |
0.998 |
7.47 |
9.67 |
-0.001 |
0.001 |
0.0 |
| W18 |
7,628 |
0.998 |
0.996 |
7.92 |
10.21 |
-0.000 |
0.002 |
0.1 |
| Water Conservation Area 3B (fig. 26) |
| TI-8 |
5,684 |
0.996 |
0.993 |
4.59 |
6.16 |
0.002 |
0.001 |
0.1 |
| TI-9 |
5,684 |
0.996 |
0.992 |
5.29 |
6.42 |
0.009 |
0.001 |
0.1 |
| EDEN7 |
2,419 |
0.998 |
0.996 |
5.24 |
6.96 |
0.008 |
0.001 |
0.1 |
| EDEN10 |
2,419 |
0.995 |
0.990 |
5.06 |
6.32 |
0.007 |
0.002 |
0.1 |
| Big Cypress National Preserve (fig. 29) |
| EDEN1 |
3,864 |
0.960 |
0.921 |
7.13 |
7.82 |
0.018 |
0.003 |
0.4 |
| EDEN6 |
1,591 |
0.984 |
0.968 |
8.76 |
10.73 |
0.030 |
0.007 |
0.4 |
| Everglades National Park (fig. 31) |
| EDEN3 |
5,294 |
0.989 |
0.978 |
0.07 |
1.75 |
-0.042 |
0.006 |
0.4 |
| Met1 |
1,238 |
0.994 |
0.989 |
5.23 |
5.76 |
0.000 |
0.000 |
0.0 |
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Summary
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- Estimation of water depth at ungaged sites
- ANNs able to accurately predict water depths at ungaged sites
- Use of static and dynamic variable produce a multi-variate kreiging of water depths
- Methodology will be used to hindcast new network stations
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