Improved understanding of the impacts of hydroclimate ...Improved understanding of the impacts of...
Transcript of Improved understanding of the impacts of hydroclimate ...Improved understanding of the impacts of...
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Improved understanding of the impacts of hydroclimate, land use and agricultural management on nitrate concentration dynamics using SWAT
Bano Mehdi1,2, Christoph Schürz1 and
Karsten Schulz1
1 Institute of Water Resources Management andHydraulic Engineering
2 Division of Agronomy
University of Natural Resources and Life Sciences, Vienna (BOKU)
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Chemodynamics of NO3--N
From Dupas et al. (2016)
Source limited Transport limited
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Dilution or accretion
From Schwientek et al. (2013)
accretiondilution
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Research questions
Can SWAT reproduce the chemodynamics of NO3--N
concentrations observed in a watershed?
Is it possible to use SWAT to determine if an event (a watershed)
is tranport-limited or source-limited?
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Available observed data at Takern II
5 Minute NO3--N (mg L-1) samples
NO
3- -
N (m
g/L
)Q
(m
3/s
)
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The Raab watershed (988 km2)
Takern II
Neumarkt/Raab5
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Multicriteria sensitivity analysis. 16 parameters selected forcalibration
LHS with 100 000 parameter combinations
Statistical criteria for calibration
Results for NO3--N calibration:
NSE KGEIndex ofAgreement
0.42 0.62 0.63
Calibration at daily time step
Q daily: KGE > 0.6, RSR (FDC) < 1NO3
- daily: KGE > 0.4, |pbias| < 0.5, RSR (FDC) < 2
v__SFTMP.bsnv__SNOCOVMX.bsnv__SURLAG.bsnv__GW_DELAY.gw v__GW_REVAP.gw v__GWQMN.gwv__RCHRG_DP.gw r__SOL_K...solr__SOL_AWC...solv__SLSOIL.hruv__ESCO.hruv__LAT_TTIME.hrua__OV_N.hrur__CNOP....6..mgt v__RCN.bsnv__NPERCO.bsn
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Available observed data at Takern II
5 Minute NO3--N (mg L-1) samples
NO
3- -
N (m
g/L
)Q
(m
3/s
)
1, 2 3 4 5 6 7 8 9 10,11 12, 13, 14-16
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16 peak discharge events were selected, hourly resolution.
NO
3- -
N (m
g/L
)Q
(m
3/s
)
Observed NO3--N and discharge for 16 events
2d 3d 3d 6d 4d 3d 2d 5d 2d 5d 4d 4d 3d 2d 2d 2d
Spring (MAM) Summer (JJA) Fall (SON) Winter (DJF)
4 6 5 1
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NO
3- -
N (m
g/L
)Q
(m
3/s
)Observed NO3
--N and discharge for 16 events
The events were aggregated to daily resolution.
2d 3d 3d 6d 4d 3d 2d 5d 2d 5d 4d 4d 3d 2d 2d 2d
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Observed patterns of hysteresis with hourly dataN
O3
- -N
(mg
/L)
Q (m3/s)
- - - - - - - - - - + - - - - -
Positive slopes (accretion) occured for one event in May 2013
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Observed patterns of hysteresis with daily data
- - - - - - - - - - + - - - - -
Positive slopes (accretion) occured for one event in May 2013
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SWAT Results
Results
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2d 3d 3d 6d 4d 3d 2d 5d 2d 5d 4d 4d 3d 2d 2d 2d
SWAT simulated NO3--N and discharge for the same events
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Simulated daily hysteresis
- - - - - - + - - - - - + - + 0
Positive slopes occured in Sept. 2007, July and August 2014
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Discussion
Chemodynamics of observations at daily aggregation were
different than SWAT simulated daily
Are processes not being represented in SWAT?
Simulated nitrate concentrations are affected by errors in loads
and errors in discharge
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Future research
Undertake an improved calibration
Examine seasonality of hysteresis
Relationship to timing of management (fertilizer) practices
Examine SWAT NO3- processes closer
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Thank you
Bano Mehdi
University of Natural Resources and Life Sciences, Vienna (BOKU)
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Uncertainty of nitrate parameters?
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