DRAINMOD APPLICATION

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DRAINMOD APPLICATION ABE 527 Computer Models in Environmental and Natural Resources

description

DRAINMOD APPLICATION. ABE 527 Computer Models in Environmental and Natural Resources. Review. drainage design … soil water characteristic… hourly rainfall, daily max & min temperature relative yield input data set. - PowerPoint PPT Presentation

Transcript of DRAINMOD APPLICATION

Page 1: DRAINMOD APPLICATION

DRAINMOD APPLICATION

ABE 527 Computer Models in Environmental and

Natural Resources

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Review

drainage design…

soil water characteristic…

hourly rainfall, daily max & min temperature

relative yield input data set

Note: A DRAINMOD hydrology simulation can be run without specifying a relative yield input data set.

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Objectives

After this lecture, you should get familiar with DRAINMOD application as for:

• How to input your own data to DRAINMOD required format;• What to consider for calibration purpose; and• How to use the model to predict subsurface drain flow, water table depth, and crop yield.

for different drain spacings.

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Soil: Clermont silt loam soil

Slope: <1%; and land-leveled after

drain installation

Area: 6.2 ha

Southeast Purdue Agriculture Center Drainage Field (SEPAC)

Monitoring: Subsurface drain flow

Water quality samples

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- Hourly rainfall

- Daily maximum and minimum temperatures

(measured on site or from nearby stations)

Model Inputs

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- Hourly rainfall

- Daily maximum and minimum temperatures

Model Inputs

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- Drainage design parameters

Model Inputs

Drain spacing, L 5 m 10 m 20 m 40 mDrain depth, b 75 cm 75 cm 75 cm 75 cm

Effective radius, re1.1 cm 1.1 cm 1.1 cm 1.1 cm

Distance from surface to restricting layer, h 120 cm 120 cm 120

cm120 cm

Maximum surface storage, Sm1.0 cm 1.0 cm 1.0 cm 1.0 cm

Note: parameter to be calibrated—Surface micro storage S1

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- Soil properties: soil water characteristic, saturated hydraulic conductivity

Model Inputs cont.

Note: parameters to be calibrated— lateral Ksat; volumetric moisture at 0 cm tension; and the vertical hydraulic conductivity of the restrictive layer

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- Crop parameters

Model Inputs cont.

Month Day Root depth (cm)1 1 3.04 25 3.05 14 9.05 27 18.06 1 19.56 20 24.07 24 30.08 20 30.09 2 30.09 24 18.09 25 3.0

12 31 3.0

Time distributions of effective rooting depths

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Calibration Procedure1. Choose most uncertain parameters to be

calibrated

Range of parameter needed to be calibrated

 Volumetric soil moisture

at 0 m tension (cm3/cm3)

Layer RangeLayer 1 (0-25 cm) 0.389-0.46

Layer 2 (25-30 cm) 0.382-0.46

Layer 3 (30-120 cm) 0.405-0.46

Horizontal Ksat (cm/hr)Layer 1 (0-25 cm) 0.03-2

Layer 2 (25-30 cm) 0.03-0.65Layer 3 (30-120 cm) 0.05-0.67

Vertical Ksat of restrictive layer (cm/hr) 0.0005-0.003

Surface Micro storage S1 (cm) 0.3-1

m

Drain

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Calibration Procedure cont.

2. Choose plot and year to be calibrated

Year Drain flow ratioW20/E20 W10/E10 W5/E5

1985 1.3 2.5 1.11986 2 2.3 1.71987 2 2 1.51988 1.8 2 1.11989 1.7 2.3 1.41990 2.1 2.3 1.21991 2.2 2.4 1.41992 3.1 2.4 1.91993 1.5 2.3 1.31994 1.6 1.9 1.61995 1.5 1.5 1.21996 1.5 1.9 1.31997 1.8 2.1 1.31998 1.5 2 1.41999 1.7 1.6 1.1

--West block and east block need to be calibrated separately. --W20 and E20 in 1988-1989 were chosen.

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Range of parameter needed to be calibrated

 Volumetric soil moisture

at 0 m tension (cm3/cm3)

Layer Range

Layer 1 (0-25 cm) 0.389-0.46

Layer 2 (25-30 cm) 0.382-0.46

Layer 3 (30-120 cm) 0.405-0.46

Horizontal Ksat (cm/hr)

Layer 1 (0-25 cm) 0.03-2

Layer 2 (25-30 cm) 0.03-0.65

Layer 3 (30-120 cm) 0.05-0.67

Vertical Ksat of restrictive layer (cm/hr) 0.0005-0.003

Surface Micro storage (cm) 0.3-1

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n

ii

n

iii

n

ii

OO

OPOOEF

1

2

1

2

1

2

%100

1

11

n

ii

n

ii

n

ii

O

OP

APE

Calibration Objective Functions(1) Nash-Sutcliffe efficiency:

(2) Absolute percent error:

22 )5.0()1( APEEFFagg

Aggregated function, combining (1) and (2):

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Automatic CalibrationParameter values against model Nash-Sutcliffe efficiencies

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.05 0.15 0.25 0.35 0.45 0.55 0.65KsatH3

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.03 0.13 0.23 0.33 0.43 0.53 0.63

KsatH2

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.03 0.33 0.63 0.93 1.23 1.53 1.83KsatH1

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.0005 0.001 0.0015 0.002 0.0025 0.003KsatV

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0S1

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.389 0.409 0.429 0.449W1

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.382 0.402 0.422 0.442W2

Nas

h-S

utc

liffe

Eff

icie

nc

y

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0.405 0.415 0.425 0.435 0.445 0.455W3

Nas

h-S

utc

liffe

Eff

icie

nc

y

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0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9

Relative absolute percent error

Nash

-su

tcliff

e e

ffic

ien

cy

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0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0 2 4 6 8 10 12 14 16 18 20

Sumulation ranked by EF values

Ab

so

lute

percen

t erro

r

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

Nash

-Su

tcliff

e e

ffic

ien

cy

0.11

0.008 0.018 0.004

0.796 0.780 0.778 0.773

0.554 0.563 0.552

EF

Fagg

APE

0.643

Identify Optimum Parameter Set 22 )5.0()1( APEEFFagg

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0.0

0.3

0.6

0.9

1.2

1.5

1.8

2.1

0 20 40 60 80 100 120 140 160 180 200 220 240 260 280 300 320 340 360

Julian Date

Drai

nflo

w (c

m/d

ay)

Observed

Predicted

Representative observed and predicted drain flow graph

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Observed and predicted water table graph

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Predicted and observed relative yields

30

40

50

60

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80

90

100

1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999Year

Rel

ativ

e Y

ield

(%

)

Obs_5 m Obs_10 m Obs_20 m Obs_40 mPre_5 m Pre_10 m Pre_20 m Pre_ 40 m

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SUMMARY

Nash-Sutcliffe efficiency (EF) for daily drain flow ranging from -0.66 to 0.81;

EF for water table depth from -0.66 to 0.9;

Statistical tests of EF indicating insignificant difference among the three drain spacings;

Both observed and predicted relative yields indicating yields decreasing with the increase of drain spacing;

Average percent errors ranging from 1.3 to 9.7% for corn yield and from -0.8 to 10.3% for soybean yield.