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F. Ghidey, C. Baffaut, N. Kitchen, K. Sudduth, M. Yost, R, Lerch, and 
E. J. Sadler
Goodwater Creek Experimental Watershed (GCEW)
GCEW – 7250 ha, located in the claypan soil
region of North-central Missouri
Plots – 18 m wide and 189 m long
(0.374 ha (0.92 ac))
Research Plots
 Three Cropping Systems
 CS 1 – Mulch tillage corn-soybean rotation with herbicide
and fertilizers surface applied and incorporated
 CS 2 – No-till corn-soybean rotation herbicide and P
surface applied and not incorporated. N was injected.
 CS 5- No-till corn-soybean-wheat rotation with split
herbicides application, cover crops, and no incorporation.
Time Series Data Measured
 Corn, Soybean, and wheat yields were measured from 1992
– 2009.
 Flow and Water Quality were measured during the corn
phase of the rotation from 1997 – 2002.
 Each CS had 3 replications. Only 2 replications were
instrumented to measure the quantity and quality of surface
runoff
 Surface runoff was measured and runoff samples were
collected only from plots that were planted to corn.
Corn crops CS1Corn crops CS1
(after Lerch, R.N.)
Research Plots
Objectives
 To evaluate Long‐Term effects of the three 
cropping systems (CSs) on yield and water 
quality
 To calibrate and validate APEX model using 
measured data
 To use the model to estimate the long‐term 
effects of CSs on yield and water quality
Discretization
Plot 20
Distance from The Top (m)
0255075100125150175200
Elevation(m)
261.0
261.5
262.0
262.5
263.0
263.5
264.0
264.5
Elevation
Clay-Elevation
Hillslope segments
based on depth to clay /  slope
Foot             Backslope Shoulder       Summit
23 cm
15 cm
3 cm
EastWest
APEX Model Inputs and Outputs
Input data Selected Outputs
 Daily weather
 Measured topography
 Measured soil properties
 Cropping and management
 Crop yields
 Daily runoff
 Atrazine, nitrate, and dissolved
P losses
Calibration/Validation Process
 Each cropping system had four plots instrumented for 
water quality measurement
 For each CS, data measured from one plot was used for 
calibration of APEX model, and the remaining three 
plots for validation.
 Performance of the model was evaluated using r2, 
Nash and Sutcliffe (Ens), and percent bias (Pbias) 
statistical methods
APEX calibration and Validation Results
Calibration (1 plot) Validation (3 plots)
r2 Ens Pbias r2 Ens Pbias
CS1
Runoff 0.81 0.72 19.5 0.93 0.84 7.2
Atrazine 0.80 0.74 20.5 0.83 0.87 -3.3
Nitrate 0.66 0.68 20.5 0.61 0.53 -15.9
Phosphorus 0.71 -3.7 -84.0 0.41 0.27 2.7
CS2 Runoff 0.96 0.88 -12.1 0.90 0.85 -5.1
Atrazine 0.95 0.81 15.1 0.80 0.69 -29.7
Nitrate 0.62 0.58 1.6 0.58 0.57 12.1
Phosphorus 0.94 0.62 -56.2 0.74 0.73 5.2
CS5 Runoff 0.90 0.89 1.1 0.87 0.74 6.1
Atrazine 0.84 0.60 51.8 0.64 0.58 35.4
Nitrate 0.35 0.26 41.7 0.79 0.63 49.5
Phosphorus 0.95 0.88 22.1 0.45 0.36 32.4
CS1 – Measured and simulated events data (All Plots)
Measured Runoff (mm)
0 20 40 60 80 100 120
SimulatedRunoff(mm)
0
20
40
60
80
100
120
Measured Atrazine (g/ha)
0 20 40 60 80 100
SimulatedAtrazine(g/ha)
0
20
40
60
80
100
Measured Nitrate (kg/ha)
0 5 10 15 20
SimulatedNitrate(kg/ha)
0
5
10
15
20
Measured Phosphorus (g/ha)
0 50 100 150 200
SimulatedPhosphorus(g/ha)
0
50
100
150
200
Y = 0.76 X
R2
= 0.89
Ens = 0.84
Pbias = 9.3%
Y = 1.13 X
R2
= 0.94
Ens = 0.89
Pbias = 0.1%
Y = 0.87 X
R2
= 0.68
Ens = 0.62
Pbias = -7.4%
Y = 0.99 X
R2
= 0.52
Ens = 0.46
Pbias = -15.4%
Measured and Simulated CS1 Corn Yields
CS1-Corn
Year
1996 1998 2000 2002 2004 2006 2008 2010
CornYield(T/ha)
0
2
4
6
8
10
12
Measured
Simulated
Low measured yields 
are over‐estimated
Comparing CS1, CS2, and CS5 Measured and Simulated
Average Yields (1997-2009)
Measured Simulated
CornYield(T/ha)
0
2
4
6
8
CS1
CS2
CS5
CORN
a a
a
a
c
b
Measured Simulated
SoybeanYield(T/ha)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
CS1
CS2
CS5
Soybean
b
a
a a
c
b
Simulated Average Annual Runoff (1997-2009)
CS1 CS2 CS5AverageAnnualRunoff(mm)
0
100
200
300
400
500
Soybean Years
a
a
a
CS1 CS2 CS5
AverageAnnualRunoff(mm)
0
100
200
300
400
500
Corn Years
a
a a
Percent Atrazine Applied (1997-2009) lost to Runoff
CS1 CS2 CS5
AtrazineAppliedLosttoRunoff(%)
0
2
4
6
8
10
a
b
c
CS2 - 2.1 times higher than CS1
CS5 - 3.4 times higher than CS1
Nitrate Losses to Runoff (1997 – 2009)
Applied N (corn years) Lost to 
Runoff (%)
Average Annual N losses during 
Corn and Soybean Years
CS1 CS2 CS5
NitrogenAppliedLosttoRunoff(%)
0
5
10
15
20
25
30
a
a
a
CS1 CS2 CS5
AverageAnnualN-Losses(kg/ha)
0
2
4
6
8
10
12
14
16
18
Corn-Years
Soybean-Years
26% 27%
34%
Dissolved Phosphorus Losses to Runoff (1997 – 2009)
Applied P (corn years)Lost to 
Runoff (%)
Average Annual P losses during Corn 
and Soybean Years
CS1 CS2 CS5
AverageAnnualP-Losses(g/ha)
0
200
400
600
800
1000
1200
1400
1600
Corn-Years
Soybean-Years
86%
94%
105%
CS1 CS2 CS5
PhosphorusAppliedLosttoRunoff(%)
0
1
2
3
4
5
6
c
a
b
CS2 - 3.9 times higher than CS1
CS5 - 2.7 times higher than CS1
Pathways for Nitrate Losses
SURQ PERC DNIT VOL HARV
%NitrogenLoss
0
10
20
30
40
50
CS1
CS2
CS5
Pathways for Dissolved Phosphorus Losses
SURQ PERC HARV
%DissolvedPhosphorusLoss
0
20
40
60
80
100
CS1
CS2
CS5
Summary and Conclusion
 The performance of APEX model in estimating
atrazine, nitrate, and dissolved P losses to runoff was
satisfactory.
 APEX overestimated crop yield, particularly corn
yield, for the dry seasons.
 Average atrazine losses from CS2 and CS5 (no-till)
were 2 and 3 times higher than from CS1 (mulch-
tillage). Split atrazine application in no-till (CS5)
further increased atrazine loss in surface runoff.
 Average dissolved P losses from CS2 and CS5(no-till)
were 4 and 3 times higher than CS1(mulch-tillage).
Summary and Conclusion
 Dissolved P losses during the soybean years were more
the same as those lost during the corn years.
 Approx. 45 and 90% of N and P applied was harvested
with crop.
 N and P losses to runoff were less than 10 and 5%.
 N and P percolation were higher for no-till systems
because of higher Ksat.
 Denitrification and volatilization represented ~25% of
applied N.
Thank you!

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Long term effect grain cropping - ghidey

  • 2. Goodwater Creek Experimental Watershed (GCEW) GCEW – 7250 ha, located in the claypan soil region of North-central Missouri Plots – 18 m wide and 189 m long (0.374 ha (0.92 ac))
  • 3. Research Plots  Three Cropping Systems  CS 1 – Mulch tillage corn-soybean rotation with herbicide and fertilizers surface applied and incorporated  CS 2 – No-till corn-soybean rotation herbicide and P surface applied and not incorporated. N was injected.  CS 5- No-till corn-soybean-wheat rotation with split herbicides application, cover crops, and no incorporation.
  • 4. Time Series Data Measured  Corn, Soybean, and wheat yields were measured from 1992 – 2009.  Flow and Water Quality were measured during the corn phase of the rotation from 1997 – 2002.  Each CS had 3 replications. Only 2 replications were instrumented to measure the quantity and quality of surface runoff  Surface runoff was measured and runoff samples were collected only from plots that were planted to corn.
  • 5. Corn crops CS1Corn crops CS1 (after Lerch, R.N.) Research Plots
  • 7. Discretization Plot 20 Distance from The Top (m) 0255075100125150175200 Elevation(m) 261.0 261.5 262.0 262.5 263.0 263.5 264.0 264.5 Elevation Clay-Elevation Hillslope segments based on depth to clay /  slope Foot             Backslope Shoulder       Summit 23 cm 15 cm 3 cm EastWest
  • 8. APEX Model Inputs and Outputs Input data Selected Outputs  Daily weather  Measured topography  Measured soil properties  Cropping and management  Crop yields  Daily runoff  Atrazine, nitrate, and dissolved P losses
  • 9. Calibration/Validation Process  Each cropping system had four plots instrumented for  water quality measurement  For each CS, data measured from one plot was used for  calibration of APEX model, and the remaining three  plots for validation.  Performance of the model was evaluated using r2,  Nash and Sutcliffe (Ens), and percent bias (Pbias)  statistical methods
  • 10. APEX calibration and Validation Results Calibration (1 plot) Validation (3 plots) r2 Ens Pbias r2 Ens Pbias CS1 Runoff 0.81 0.72 19.5 0.93 0.84 7.2 Atrazine 0.80 0.74 20.5 0.83 0.87 -3.3 Nitrate 0.66 0.68 20.5 0.61 0.53 -15.9 Phosphorus 0.71 -3.7 -84.0 0.41 0.27 2.7 CS2 Runoff 0.96 0.88 -12.1 0.90 0.85 -5.1 Atrazine 0.95 0.81 15.1 0.80 0.69 -29.7 Nitrate 0.62 0.58 1.6 0.58 0.57 12.1 Phosphorus 0.94 0.62 -56.2 0.74 0.73 5.2 CS5 Runoff 0.90 0.89 1.1 0.87 0.74 6.1 Atrazine 0.84 0.60 51.8 0.64 0.58 35.4 Nitrate 0.35 0.26 41.7 0.79 0.63 49.5 Phosphorus 0.95 0.88 22.1 0.45 0.36 32.4
  • 11. CS1 – Measured and simulated events data (All Plots) Measured Runoff (mm) 0 20 40 60 80 100 120 SimulatedRunoff(mm) 0 20 40 60 80 100 120 Measured Atrazine (g/ha) 0 20 40 60 80 100 SimulatedAtrazine(g/ha) 0 20 40 60 80 100 Measured Nitrate (kg/ha) 0 5 10 15 20 SimulatedNitrate(kg/ha) 0 5 10 15 20 Measured Phosphorus (g/ha) 0 50 100 150 200 SimulatedPhosphorus(g/ha) 0 50 100 150 200 Y = 0.76 X R2 = 0.89 Ens = 0.84 Pbias = 9.3% Y = 1.13 X R2 = 0.94 Ens = 0.89 Pbias = 0.1% Y = 0.87 X R2 = 0.68 Ens = 0.62 Pbias = -7.4% Y = 0.99 X R2 = 0.52 Ens = 0.46 Pbias = -15.4%
  • 12. Measured and Simulated CS1 Corn Yields CS1-Corn Year 1996 1998 2000 2002 2004 2006 2008 2010 CornYield(T/ha) 0 2 4 6 8 10 12 Measured Simulated Low measured yields  are over‐estimated
  • 13. Comparing CS1, CS2, and CS5 Measured and Simulated Average Yields (1997-2009) Measured Simulated CornYield(T/ha) 0 2 4 6 8 CS1 CS2 CS5 CORN a a a a c b Measured Simulated SoybeanYield(T/ha) 0.0 0.5 1.0 1.5 2.0 2.5 3.0 CS1 CS2 CS5 Soybean b a a a c b
  • 14. Simulated Average Annual Runoff (1997-2009) CS1 CS2 CS5AverageAnnualRunoff(mm) 0 100 200 300 400 500 Soybean Years a a a CS1 CS2 CS5 AverageAnnualRunoff(mm) 0 100 200 300 400 500 Corn Years a a a
  • 15. Percent Atrazine Applied (1997-2009) lost to Runoff CS1 CS2 CS5 AtrazineAppliedLosttoRunoff(%) 0 2 4 6 8 10 a b c CS2 - 2.1 times higher than CS1 CS5 - 3.4 times higher than CS1
  • 16. Nitrate Losses to Runoff (1997 – 2009) Applied N (corn years) Lost to  Runoff (%) Average Annual N losses during  Corn and Soybean Years CS1 CS2 CS5 NitrogenAppliedLosttoRunoff(%) 0 5 10 15 20 25 30 a a a CS1 CS2 CS5 AverageAnnualN-Losses(kg/ha) 0 2 4 6 8 10 12 14 16 18 Corn-Years Soybean-Years 26% 27% 34%
  • 17. Dissolved Phosphorus Losses to Runoff (1997 – 2009) Applied P (corn years)Lost to  Runoff (%) Average Annual P losses during Corn  and Soybean Years CS1 CS2 CS5 AverageAnnualP-Losses(g/ha) 0 200 400 600 800 1000 1200 1400 1600 Corn-Years Soybean-Years 86% 94% 105% CS1 CS2 CS5 PhosphorusAppliedLosttoRunoff(%) 0 1 2 3 4 5 6 c a b CS2 - 3.9 times higher than CS1 CS5 - 2.7 times higher than CS1
  • 18. Pathways for Nitrate Losses SURQ PERC DNIT VOL HARV %NitrogenLoss 0 10 20 30 40 50 CS1 CS2 CS5
  • 19. Pathways for Dissolved Phosphorus Losses SURQ PERC HARV %DissolvedPhosphorusLoss 0 20 40 60 80 100 CS1 CS2 CS5
  • 20. Summary and Conclusion  The performance of APEX model in estimating atrazine, nitrate, and dissolved P losses to runoff was satisfactory.  APEX overestimated crop yield, particularly corn yield, for the dry seasons.  Average atrazine losses from CS2 and CS5 (no-till) were 2 and 3 times higher than from CS1 (mulch- tillage). Split atrazine application in no-till (CS5) further increased atrazine loss in surface runoff.  Average dissolved P losses from CS2 and CS5(no-till) were 4 and 3 times higher than CS1(mulch-tillage).
  • 21. Summary and Conclusion  Dissolved P losses during the soybean years were more the same as those lost during the corn years.  Approx. 45 and 90% of N and P applied was harvested with crop.  N and P losses to runoff were less than 10 and 5%.  N and P percolation were higher for no-till systems because of higher Ksat.  Denitrification and volatilization represented ~25% of applied N.