Universal high-frequency behavior of periodically driven ...
Applications of SWAT to Climate- Driven Low Flow Frequency Analysis
Transcript of Applications of SWAT to Climate- Driven Low Flow Frequency Analysis
Applications of SWAT to Climate-Driven Low Flow Frequency Analysis
2009 5th International SWAT ConferenceAugust 3-7 2009, Boulder, Colorado, University of Colorado
http://www.drought.unl.edu
Jae Ryu, University of Nebraska-LincolnSangman Jeong, Kongju National University
Seon Ki Park, Ewha Womans UniversityJoo Heon Lee, Joongbu UniversityKyuha Han, Hyundai Engineering
Presentation Outline
1. Climate change on water resources2. Modeling issues and challenges3. Study basin and water issues4. Application of SWAT for climate-
driven water yield and drought frequency analysis
5. Future work
Early snowmelt in PNW
(Monte et al. 2003; Whitely Binder 2006)
Shrinking Glaciers
(USGS, 2009)
Sea level arise
(Jeong, 2009)
Annual water yield
(Jeong et al, 2008;Ryu et al, 2009)
70% rainfed areas, food security
Water for Food, Water for Life, Comprehensive Assessment of Water Management in Agriculture, 2007
Desertification, severe drought, flood
Impacts of Climate Change on World
Implications of Climate Change on Regional Water Resources
• Increased temperatures (up to 5.4 degree C in East Asia)
• Precipitation response from -13% to -42% runoff patterns will differ
• Annual water yield will change due to monsoonal time shift
• Higher evaporation and transpiration rates
• Greater flooding and less water available during dry months
Research Approach
• Climate variable perturbation (precipitation and temperature) and Carbon Dioxide
• Application of SWAT
• Setup Base Scenario and Climate Scenarios (IPCC 2007)
• Model calibration and validation
• Low Flow Frequency Analysis
Role of CO2 in ET(Challenges and Issues)
• How to implement enriched CO2 into SWAT framework (Net radiation: x1.4 and x1.2 for 2xCO2 and 1.5xCO2, respectively)
• Enriched CO2 Increase or Decrease ET?
• Enriched CO2 Decrease ET or Increase depending on crop types (C3 group: small grains, root crops, and most trees, C4 group: corn, sorghum efficient ET) (Kimball et al, 1999)
• Kimball et al (1999): Enriched CO2 effect of CO2 on ET is small
SWAT Model• Water balance
( )∑=
−−−−+=t
igwseepasurfdayt QwEQRSWSW
10
• Surface runoff: SCS CN method( ) ( )SIRIRQ adayadaysurf +−−= /2
• Evapotranspiration: Penman-Monteith equation (Monteith 1965)
• Tile flow or Lateral flow: Kinematic storage model (Sloan et al. 1983; Sloan and Moore 1984)
• Channel Routing: Muskingum routing method (Chow et al. 1988)
Guem River Basin • Guem River Basin
– 9,800 km2 (3,780 mi2 : watershed area)– 400 km (250 mile : mainstem length)
• Daechong Dam (1971)– 2,656 km2 : drainage area– Multi-objective dam– 1.5 billion m3 (53 billion ft3 : reservoir size)– 3 million people
• Yongdam Dam (2001)– 1,513 km2 : drainage area– Multi-objective dam (water supply)– 815 million m3 (29 billion ft3 : reservoir size)– 1.5 million people
N
Dam
Yongdam Dam
Daechong Dam
Daejon City
Jonju City
Instream flowIssue areaMajor cityPotentialPopulationIncrease area
5.4 m3/s (191cfs)12.4 m3/s (438cfs)
21 m3/s (741cfs)
3.5 million 2.5 million
(2021)
Water Conflicts
Land Use and Soil ClassificationLand Use
Description Area (km2)
Area (%)
PAST Pasture 109.1 2.62
WATR Water 92.7 2.22
WETL Wetlands-Mixed 22.2 0.53
FRST Forest-Mixed 3463.0 83.05
AGRL Agricultural Land 432.8 10.38
URLD Residential-Low Density
49.7 1.19
UTRN Transportation 0.3 0.01
Total 4170 100
SoilSymbol
Area (km2)
Area (%)
SoilSymbol
Area (km2)
Area (%)
ms 324.4 7.78 ra 338.0 8.11
mv 245.3 5.88 re 86.9 2.08
an 317.5 7.61 rs 35.1 0.84
ap 94.4 2.26 ma 1786.8 42.85
rva 123.6 2.96 mlb 3.3 0.08
rvb 14.9 0.36 mm 547.2 13.12
rvc 70.2 1.68 af 182.4 4.38
Total: 4170 km2
Climate Scenario• Baseline implies current climate condition
• 1988-2002, 15 years records (Boxplot: Precip, Lineplot: Temp)• Utilized as a reference for future hydro-climate simulations
Key Model ParametersParameter Name
Description (input file) Units Initial value
Final estimate Possible range of values
AlphaBF Baseflow recession constant (.gw)
none 0.05 0.06 0.04-1
CN2 Curve Number II for soil moisture condition (.mgt)
none 60 44.7 0-100
EPCO Plant uptake compensation factor (.hru)
none 1.0 0.8 0-1
ESCO Soil evaporation compensation factor (.hru)
none 0 0.3 0.1-1
GW_DELAY Groundwater delay time (.gw)
days 31 31 0-400
GW_REVAP Groundwater “revap” coefficient (.gw)
none 0.02 0.15 0.02-0.3
GWQMN Threshold depth for baseflow to occur (.gw)
mm 0 1,087 0-5,000
SOL_AWC Soil available water capacity (.sol)
mm 0.16 0.19 0-1
Model Calibration and Validation• Coefficient of determination
• Model efficiency criteria (Nash-Sutcliffe, 1970)
2
2
11
2
1
2
1
2
112
−
−
−=
∑∑∑ ∑
∑∑
=== =
==
N
ii
N
ii
N
i
N
iii
N
ii
N
iii
OONSSN
OOSNR
( )
∑
∑
=
=
−
−−=
N
ii
N
iii
OO
OSE
1
2_
1
2
0.1
Where, S = Simulated flow, O = Observed flow
• Nash
• R and E: 0.9 and 0.7, respectively during calibration periods
• R and E: 0.86 and 0.68, respectively during validation periods
Climate Scenarios• Scenario 1 : 1.5 x CO2
• Scenario 2 : 1.5 x CO2 + Severe Drought
• Scenario 3 : 1.5 x CO2 + Severe Drought + Earlier monsoon
• Scenario 4 : 1.5 x CO2 + Severe Drought + Later monsoon
• Scenario 5 : 2.0 x CO2 + Extreme Drought (Worst case)
Low Flow Frequency Analysis• Extreme Value Type III Distribution (EV3 -
Gumbel 1958)
0,)(1exp1)(/1
≠
−−−−= kxkxF
k
αξ
• Three-Parameter Lognormal (LN3-Stedinger 1980)
{ }
−−Φ=
y
yxxF
σµτ )ln(
)(
• Log-Pearson Type III (LP3-Ames 2006;ASCE 1980)
)()()(
)(1
βξλ ξλββ
Γ−
=−−− xexxf