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Validation of Spatially Continuous EDEN Water-Surface Model for the Everglades, Florida with Ecosystem Applications. Zhongwei Liu, Ph.D. 1* Aaron Higer 1 Frank Mazzotti, Ph.D. 1 Leonard Pearlstine, Ph.D. 2 1. Ft. Lauderdale Research & Education Center, University of Florida - PowerPoint PPT Presentation
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Validation of Spatially Continuous EDEN Water-Surface Model for the
Everglades, Florida withEcosystem Applications
Zhongwei Liu, Ph.D.1*
Aaron Higer1
Frank Mazzotti, Ph.D.1
Leonard Pearlstine, Ph.D.2
1. Ft. Lauderdale Research & Education Center, University of Florida2. Everglades and Dry Tortugas National Parks
* [email protected] annual conference
Boston, MA, 4/2008
2
OutlineOutline Introduction
– EDEN network – EDEN water-surface model
Methodology – Study area– Data collection– Analysis methods
Results
Ecosystem Applications
Conclusions and Discussions
3
I. IntroductionI. Introduction Efforts to measure and
link surface-water depths to biotic communities in the Everglades (Loveless, 1959; Craighead, 1971; McPherson, 1973; Cohen, 1984; Newman et al., 1996; Busch et al., 1998; Ross et al., 2000; Hendrix and Loftus, 2000; Gawlik, 2002; Chick et al., 2004; Palmer and Mazzotti, 2004; Trexler et al., 2005).
Hydrologic models could provide spatially continuous hydrologic information.
Two research objectives: model validation and applications
alligator holes
Source: www.broward.edu.
sawgrass marsh
sloughalligator holes
tree islandswet
prairiewet prairie
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Everglades Depth Estimation Network ((EDEN)
Integrated network of real-time water level monitoring, ground elevation modeling, and water-surface modeling
Daily water level/stage data (2000 - present) from 253 gage stations
Two types of gage stations: marsh stations and canal stations
a) satellite gageGulf of Mexico
Atlantic Ocean
Florida
Area of Enlargement
A marsh gage station
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WCA 1
WCA 2A
WCA 3AN
WCA 3AS
WCA 3B
WCA 2B
ENP
BCNP
±0 10 20 305
Kilometers
EDEN Water Gagesby Operating Agency
!( BCNP
# ENP
! SFWMD
XW USGS
Canals and Rivers
Study Area
Eden Boundary
South Florida
5
EDEN Water-Surface ModelEDEN Water-Surface Model Developed by Pearlstine et
al. (2007)
Spatial interpolation of 240 gage stations in ArcGIS: radial basis function (RBF)
Model outputs– Water surface of 400m x 400 m grid
spacing, to match the EDEN ground digital elevation model (DEM)
– Water depth = water surface - DEM
150
120
30
300 270
150
120
210
LegendContour
Water surface on 7/10/2007 (cm)High : 457.7
Low : 1.4
±0 10 20 305
Kilometers
6
II. II. MethodologyMethodology Study area
– WCAs 3A South and 3B
– Florida Department of Environmental Protection (FDEP) benchmark network
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WCA 3A South
WCA 3B
28 W5
W2
W18
W15
W14W11
TI-9TI-8
SRS1
3AS+
3A9+
3A-5S9A-T
3ASW+
S344+TS344+H
S340+TS340+H
S336+TS336+H
S335-TS335-H
S334-TS334-H
S333+TS333+H
S31M-H
S151+TS151+H
L28S2+
EDEN_8
EDEN_7
EDEN_5
EDEN_4
3B-SE+
SITE_76
SITE_71
SITE_69
SITE_65
SITE_64
S343B+T
S343A+T
S337M-T
S12D_UPS12C_UPS12B_UPS12A_UP
EDEN_14
EDEN_12
EDEN_103BS1W1+
3AS3W1+
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0 4 8 122Kilometers
±Legend!( Benchmark Sites
"Îi Water Level Gages
Study Area
I-75 (Alligator Alley)
Tamiami TrailTamiami Trail
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Data CollectionData Collection
Field water-level data collected by Florida Atlantic University (FAU)
At 24 benchmarks
Apr. - Sept., 2007
Via airboat and helicopter
Totalobs.: 91
Southern WCA 3A75
WCA 3B8
Dry season16
Wet season75
8
Analysis MethodsAnalysis Methods GIS
– Spatial analysis
Error statistics– MAE (Mean Absolute Error)=
– MBE (Mean Biased Error)=
– RMSE (Root Mean Squared Error)=
Nonparametric statistical methods– Spearman’s rank correlation– Wilcoxon signed rank test– Kruskal-Wallis nonparametric analysis of variance (ANOVA)
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III. ResultsIII. Results DIFF_STAGE =
predicted water stage – observed water stage.
Underestimates and overestimates are represented by negative and positive values, respectively.
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WCA 3A South
WCA 3B
I-75 (Alligator Alley)
Tamiami Canal
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± LegendDIFF_STAGE (cm)
!( -4.9 - 0.0
!( -9.9 - -5.0
!( -17.6 - -10.0
DIFF_STAGE (cm)!( 0.2 - 4.9
"Îi Water Level Gages
Canals
Study Area
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Results (cont.)Results (cont.) Major statistics of interpolation
errors for water stageType N MIN
(cm) MAX (cm)
Standard deviation
Standard error b
MAE Mean
(MBE) RMSE
WCA 3A South, 3B 91 -17.6 4.9 3.32 0.35 2.38 -0.08 3.30 WCA 3A South 83 -5.1 4.9 2.47 0.27 2.11 0.32 2.48 WCA 3B 8 -17.6 1.7 6.97 2.46 5.15 -4.2 7.76
a Interpolation error (water-stage difference) = predicted water stage – observed water stage. b Standard error = standard deviation / N .
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Spearman’s rank correlation analysis
Spearman’s rank correlation analysis for temporally detrended water stage data (Rangel et al., 2006)
Type Spearman’s rank
correlation coefficient
Corrected df a Corrected p-value
WCA 3A South, 3B 0.909 17.29 <0.001 WCA 3A South 0.882 5.542 <0.001 WCA 3B 0.833 5.277 <0.004 a Corrected degrees of freedom.
Type Variable Normality test
p-value (Shapiro-Wilk)
Spearman’s rank correlation
coefficient (rs)
P-value of rs
Observed_Stage <0.0001 WCA 3A South, 3B Predicted_Stage <0.0001 0.98 <0.0001
Observed_Stage <0.0001 WCA 3A South Predicted_Stage <0.0001 0.98 <0.0001
Observed_Stage 0.7133 WCA 3B a Predicted_Stage 0.2472 0.83 0.0102 a For WCA 3B, the parametric Pearson’s correlation coefficient is 0.8998 (p = 0.0023).
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Kruskal-Wallis nonparametric ANOVA
Wilcoxon’s signed rank tests Type Variable
Normality test p-value
(Shapiro-Wilk)
Wilcoxon’s signed rank test statistic
P-value (Wilcoxon)
WCA 3A South, 3B Difference_Stage a <0.0001 166.5 0.5129 WCA 3A South b Difference_Stage 0.10 263.0 0.2346 WCA 3B c Difference_Stage 0.079 -8.0 0.2969
a Difference_Stage = predicted water stage - observed water stage. b For WCA 3A South, the test statistic of pairwised t-test is -1.19 (p = 0.2371). c For WCA 3B, the test statistic of pairwised t-test is 1.7 (p = 0.1321).
a Median difference = the median of water stage differences (predicted – observed).
Source Class N Median
Difference a (cm)
df Kruskal-Wallis test statistic (H) P-value of H
Dry (November – May) 16 -2.15 Season Wet (June – October) 75 0.6 1 7.0428 0.008
WCA 3A South 83 0.4 Region WCA 3B 8 -1.2 1 3.4761 0.0623
3: Sawgrass 72 -0.2 4: Upland 13 3.6 Vegetation 5: Exotics and Cattail 6 1.55
2 12.4469 0.002
13
IV. EDEN Water-Surface Model Applications
Estimation of Ground Elevation:
Ground elevation =predicted water
stage -observed water
depth.
14
Estimation of Water-Depth Hydrographs:
Water depth =predicted water stage -derived ground
elevation.
15
V. Conclusions and V. Conclusions and DiscussionsDiscussions
We found there are no statistically significant differences between model-predicted and field-observed water-stage data (p-value = 0.5129). Overall, the model is reliable by a RMSE of 3.3 cm. By region, the RMSE is 2.48 cm and 7.76 cm in WCAs 3A and 3B, respectively.
Two applications of the validated EDEN water-surface model to investigate the relationship between water depth and fresh water marsh habitats.
16
DiscussionsDiscussions Boundary problems
–When a benchmark reports high interpolation errors, it is likely to be near boundaries.
Data collection
Missing gage data–Localized impacts on the water surface
The method of estimating water depth–More accurate–More cost-effective
17
Further StudiesFurther Studies More field observations of dry and wet
seasons, and in other areas
Examine WCA 3B to improve the model
Rainfall data
A better regional ground DEM
Other interpolation techniques
18
AcknowledgementsAcknowledgements Dr. John Volin from University of Connecticut (formerly
FAU) and Dr. Dianne Owen and Jenny Allen from FAU
Pamela A. Telis (USGS/USACE Liaison), Dr. John Jones, Paul Conrads, Heather Henkel, and Michael Holmes from USGS, and Roy Sonenshein from ENP
Elmar Kurzbach, U.S. Army Corps of Engineers (USACE), and Dr. Ronnie Best, USGS Priority Ecosystem Science
Dr. Laura Brandt, Kevin Chartier, Adam Daugherty, and Wingrove Duverney, Joint Ecosystems Modeling (JEM)
Others…