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Welcome to Xinjiang Zhao Chengyi, Sheng Yu, Han Ming, Li Jun AKSU Water Balance Experimental Station [email protected] Soil Water and Salinity Movement and Management of Farmland in Tarim River Basin
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Welcome to Xinjiang

Zhao Chengyi, Sheng Yu, Han Ming, Li Jun AKSU Water Balance Experimental Station

[email protected]

Soil Water and Salinity Movement and

Management of Farmland in Tarim River Basin

Brief Introduction of Akesu Water Balance

Experimental Station

Soil Water and Salinity movement and Management

of Farmland in Tarim River Basin

Outlines

E80˚45′

N 40˚37′

Sea Level 1028 m

Urumqi

1100 km

Precipitation<50 mm

Evaporation>2500 mm

AKSU Water Balance Experimental Station

The extreme arid zone is 10 million km2 in the world China accounted for 1/5

Oasis Area 9.3%,95%of Population

China Oasis Map

Akesu Station

Evaporation: 2500-3000 mm;

Annual rainfall: < 50 mm;

Aridity:1.5- 4

Challenges on Sustainable Irrigation

Background of Tarim

River Basin

Rich in nature resources, but friable in ecosystem

Main Research

● Process of water, salt and heat

exchange in oasis cropland ecosystem.

● Theory of water-saving irrigation in

oasis cropland and new technology.

● Water and salt balance from soil

profile to watershed scale and water

resource management

Xinjiang Irrigation Experimental Station

AKSU Water Balance Experimental

Station, CAS

Agro-ecological Station, Chinese

Ecosystem Research Network (CERN)

1982

2002

2005 National Field Research Station of Agro-

ecosystem

2008

History of AKSU Station

Equipment

34 meters

meteorological tower Laser-radar emission instrument

PTM-48M system

Platform for monitoring oasis cropland system

Station---Farm---Basin

Sketch map of mountain ,oasis and desert(MOD)

Soil Water and Salinity movement and Management

of Farmland in Tarim River Basin

Challenges on Sustainable Irrigation

●Drip irrigation farmland is approximately 2 million hm2 in Xinjiang.

●Improve the utilize efficient of canal water from 0.48 to 0.65,

●Save water resource 1.0 billion cubic meter.

Drip irrigation in

Xinjiang

Water Saving Strategies

Maximum or optimal yield?

Shallow groundwater management

Sequential water use

Sequential land use

Ecosystem effect???

Soil water movement under drip irrigation

Comparing drip irrigation with traditional irrigation, drip irrigation can save

water 50%, save fertilizer 20%, save pesticide 10%, improve the irrigation

efficiency from 0.48 to 0.65, improve yield 20%, and total economic benefit is

more than 40%.

save money Increase earning

Improve the using efficiency of

irrigation water

Improve the using efficiency of

fertilizer

Save energy sources

Save pesticide and fertilizer

Save labours

Improve the output

of crop

Improve the quality

of farm produce

Maintaining high productivity

Low irrigation requirement (90% of total water)

Good soil quality (60% of total arable land)

Less soil salt input (soil salt content<1%)

Environmentally (ecosystem) friendly

Ecosystem health

Less adverse environmental effect such as

runoff and leaching

● How much is the irrigation requirement under drip irrigation.

● What is the threshold salinity for cotton growth

● How much is the salt leaching requirement under drip irrigation

Key Questions:

Numerical model

△y=0.5cm

△y=1cm

△y=3cm

△x=3cm

Depth thr ths Alfa n Ks L

10 0.04 0.453 0.012 2 27.3 0.5

20 0.04 0.483 0.011 1.7 12.5 0.5

30 0.04 0.482 0.01 1.5 8.9 0.5

40 0.0386 0.453 0.004 1.8 11.4 0.5

60 0.0386 0.482 0.009 1.37 9.3 0.5

80 0.0386 0.474 0.005 1.35 4.7 0.5

100 0.043 0.486 0.006 1.35 4.5 0.5

表4 – 1 利用PEST获得以及实测的土壤水力学参数

Tab 4 – 1 The van Genchten parameter got though measurement and PEST inverse

solution

Colum selected with blue means all the value

is measured in the field

Colum selected with means all the value is

get via inverse solution using PEST

Material distribution map(left) , boundary condition and grid map

Pink Nodes means variable-flux boundary

Red Nodes means Free-drainage boundary

Green Nodes means Atmosphere boundary

White Nodes means No-flux boundary

Data preparation ----- Plant transpiration and Soil evaporation

Reference crop evapotransipiration and

potential evapotranspiration

Basic plant coefficient , soil evaporation

coefficient and crop coefficient calculated by

FAO-56

Using FAO-56 calculating the soil

evaporation and plant transpiration

Soil water movement under drip irrigation

Data preparation -----Root Distribution and water uptake distribution

function

The parameter in the function above is get though inverse

solution compared with normalized root length density

R² = 0.831

eyy

Y

pxx

X

p

mm

m

y

m

x

Y

y

X

xyxb

11),(

----water uptake distribution function

Result of water uptake

distribution function

Model Calibration ----- Compared with observation measurement

Variation of soil water

content is decrease as

the increase in x and

depth

The influence of irrigation

and evapotranspiration

on soil water content is

more significant in the

depth of 0-50 cm of soil

layer

Result and discussion ----- soil water exchange between upper layer

(0 – 50 cm) and lower layer (> 50 cm )

Soil water exchange process is highly consistent with irrigation process

Maximum infiltration happen in the second day of irrigation and after forth day

the lower soil layer begin to recharge upper soil layer

Total infiltration amount due to irrigation is 349.50cm3, 11% of total irrigation

amount. Total recharge from lower layer to upper layer is 74.145cm3.

0

10

20

30

40

50

60

70

80

90

100

0.0 0.5 1.0 1.5土壤含盐量(%)

土壤

深度

(cm)

滴灌后

滴灌前

4265 m3/hm2

峰值

0

10

20

30

40

50

60

70

80

90

100

0.0 0.5 1.0 1.5土壤含盐量(%)

土壤

深度

(cm)

3926m3/hm2

峰值

0

10

20

30

40

50

60

70

80

90

100

0.0 0.5 1.0 1.5土壤含盐量(%)

土壤

深度

(cm)

3600 m3/hm2

峰值

3271m3/hm2

0

10

20

30

40

50

60

70

80

90

100

0.0 0.5 1.0 1.5土壤含盐量(%)

土壤深度(cm)

峰值

2947m3/hm2

0

10

20

30

40

50

60

70

80

90

100

0.0 0.5 1.0 1.5土壤含盐量(%)

土壤

深度

(cm)

峰值

0

10

20

30

40

50

60

70

80

90

100

0.0 0.5 1.0 1.5土壤含盐量(%)

土壤

深度

(cm)

2618m3/hm2

峰值

Salinity peak value under different irrigation demand before (black line) and after

irrigation (pink line)

Soil salt movement under drip irrigation

0102030405060708090

100

0.0 0.3 0.6 0.9 1.2 1.5 1.8

盐分含量(%)

土层

深度

(cm)

膜间

膜下

Three times

积盐区

0102030405060708090

100

0.0 0.3 0.6 0.9 1.2 1.5 1.8

盐分含量(%)

土层

深度

(cm)

膜间

膜下

Six times

积盐区

0102030405060708090

100

0.0 0.3 0.6 0.9 1.2 1.5 1.8

盐分含量(%)

土层深度(cm)

膜间

膜下

Ten times

积盐区

The range of salinity movement with soil water is about 0-70cm after several

times of irrigation, and there is no percolation in deep soil. Meantime, the

depth of salinity peak value is 40cm, then the desalted zone was formed in

0-40cm, and next was salinity balance zone.

Character of salinity distribution under irrigation demand( 3600 m3/hm2 )after irrigation

Soil salt movement under drip irrigation

盐分水平方向分布值 z

d

h

含盐量分布值x

盐分垂直方向分布值

分值

含盐

Horizontal distribution of salt Vertical distribution of salt

0.0%

1.0%

2.0%

3.0%

4.0%

5.0%

6.0%

7.0%

0 10 20 30 40 50 60 70

土层深度(cm)

含盐量(g/g)

t=530mint=1320mint=1680mint=1920min初始含盐量

0.00

0.05

0.10

0.15

0.20

0.25

0.30

0.35

0 10 20 30 40 50土层深度(cm)

盐分浓度(g/g)

t=530mint=1320mint=1680mint=1920min

S=menzC=C0e

dz

盐分水平方向分布值 z

d

h

含盐量分布值x

盐分垂直方向分布值

分值

含盐

Horizontal distribution of salt Vertical distribution of salt

0.0%

1.0%

2.0%

3.0%

4.0%

5.0%

6.0%

7.0%

0 10 20 30 40 50 60 70

土层深度(cm)

含盐量(g/g)

t=530mint=1320mint=1680mint=1920min初始含盐量

0.00

0.05

0.10

0.15

0.20

0.25

0.30

0.35

0 10 20 30 40 50土层深度(cm)

盐分浓度(g/g)

t=530mint=1320mint=1680mint=1920min

S=menzC=C0e

dz

0.0%

1.0%

2.0%

3.0%

4.0%

5.0%

6.0%

7.0%

0 10 20 30 40 50 60 70

土层深度(cm)

含盐量(g/g)

t=530mint=1320mint=1680mint=1920min初始含盐量

0.00

0.05

0.10

0.15

0.20

0.25

0.30

0.35

0 10 20 30 40 50土层深度(cm)

盐分浓度(g/g)

t=530mint=1320mint=1680mint=1920min

S=menzC=C0e

dz

0

10

20

30

40

50

60

70

80

0.00 0.50 1.00 1.50土壤总盐(%)

土壤

深度

(cm)

2005年 2006年 2007年

b

0.00

0.20

0.40

0.60

0.80

1.00

1.20

1.40

Ⅰ Ⅱ Ⅲ Ⅳ

土壤

总盐

含量

(%)

2005-6-26 2006-6-21 2007-6-23

a

2001-2008年0-60cm土壤盐分变化

0.00

0.05

0.10

0.15

0.20

0.25

0.30

1 2 3 4 5 6 7

滴灌年限(年)

土壤含盐量(

µs·

cm-1)

Alaer

No.142

Farm

(张伟,2008,农业工程学报)

Annual variation of salinity distribution under drip irrigation

Soil salt content (%)

So

il dep

th (c

m)

Year

Soil salt movement under drip irrigation

AKSU Station

Sequential Land Use? If you do not have sufficient leaching, salinity is going to build

up. Crop rotation may temporally prolong the land use.

Salinity sensitive

plants

Year 1.2.3……N

Salinity sensitive

plants

Salinity resistant

plants

After Year N…

Soil salt movement under drip irrigation

LR Calculation

Empirical equation (3):

⊿S = aⅠi+b

Where ⊿S = S2-S1 , S1—soil salinity content before irrigation, S2—soil salinity content after irrigation, Ⅰi -- irrigation water requirement, it include cotton irrigation demand and leaching requirement.

For⊿ S =S2-S1 , S1 , S2—salinity before and after irrigation(g/kg)if ⊿S﹥0,then salification; if⊿ S<0, then desalinization

Relationship between the absolute difference of salinity

before and after irrigation and the actual irrigation demand

in depth of 0- 60cm and 0-100cm

0-60cm: ⊿ S =-0.0035I+0.5787, R=0.9584**

0-100cm: ⊿ S =-0.0036I+0.5872, R=0.9731**

△S = -0.0036I + 0.5872

R2 = 0.9731**-0.500

-0.450

-0.400

-0.350

-0.300

-0.250

-0.200

-0.150

-0.100

-0.050

0.000

0 50 100 150 200 250 300 350

滴灌量(m3/hm2×15)

△S(g/kg×10)

0-100cm

△S = -0.0035I+ 0.5787

R2 = 0.9584**-0.500

-0.450

-0.400

-0.350

-0.300

-0.250

-0.200

-0.150

-0.100

-0.050

0.000

0 50 100 150 200 250 300 350

滴灌量(m3/hm2×15)

△S(

g/kg

×10

0-60cm

Desalinization ratio in 0-60cm is 34.8 %、29.7 %、18.5 %、13.9 %、7.9 %、6.0 %, and in 0-100 cm is 36.0 %、34.7 %、26.1 %、17.5 %、6.8 %、5.0 %

under different irrigation demand

Degree of

salinity

S1

(g/kg)

S2

(g/kg) I

(m3/hm)

I1

(m3/hm) I2

(m3/hm)

Suitability demand

LR

Light 0.3-0.6 1.0 5432 3465 0 2909 Y

Middle 0.6-1.0 1.0 5432 3465 0 2909 Y

Heavy

1.0-1.5 1.0 5432 3465 1158 2909 M

1.5-1.7 1.0 5432 3465 2010 2909 M

1.7-2.0 1.0 5432 3465 3300 4728 N

Solonchak >2.0 Cotton dead N

Irrigation norm and suitability evaluation of cotton drip

irrigation under mulching

I1--irrigation norm in cotton growing season, it include cotton water

demand and LR; I2---added irrigation in winter or spring

Conclusion

The peak curve of soil salt under mulch moved downward with the increases of drip irrigation. Wet peak moved downward from 40 cm to 100 cm and peak value of salt also moved downward from 30 cm to 70 cm. The desalinization rate increased with the increase of drip irrigation requirement.

As a new water-saving technology, drip irrigation under mulch can be used to irrigate farmland in dry land area.

Considering long-term soil salt balance, drip irrigation under mulch will be unfavorable to salt-leaching in irrigation area. After harvest of cotton, quantity of water must be increased to leach salt.

-

Thanks for your Attention!

Chengyi Zhao AKSU Water Balance Experimental Station

Xinjiang Institute of Ecology and Geography

[email protected]

2013. 08.15


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