conversion of forest to coffee-based agroforestry in indonesia:

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Widianto, K. Hairiah, W.S. Dewi, Hascaryo, D. Saputra, F.K. Aini, D. Suprayogo, N.Khasanah and M. van Noordwijk L Litter layer, population density of earthworm and soil macroporosity UNIV. UNIV. BRAWIJAYA BRAWIJAYA [email protected]

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UNIV. BRAWIJAYA. L itter layer, population density of earthworm and soil macroporosity. Widianto, K. Hairiah, W.S. Dewi, Hascaryo, D. Saputra, F.K. Aini, D. Suprayogo, N.Khasanah and M. van Noordwijk. Conversion of forest to coffee-based Agroforestry in Indonesia:. [email protected]. - PowerPoint PPT Presentation

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Page 1: Conversion of forest to coffee-based Agroforestry in Indonesia:

Widianto, K. Hairiah, W.S. Dewi, Hascaryo, D. Saputra, F.K. Aini, D. Suprayogo, N.Khasanah and M. van Noordwijk

LLitter layer, population density of earthworm and soil macroporosity

UNIV. BRAWIJAYAUNIV. BRAWIJAYA

[email protected]

Page 2: Conversion of forest to coffee-based Agroforestry in Indonesia:

Land Cover in East Java (Malang)

Land Cover in Sumatra (West Lampung)

Page 3: Conversion of forest to coffee-based Agroforestry in Indonesia:

stem-flow

through-fall

rainfall cloudinterception

lateral

outflow

percolation

rechargeinfiltrasi

surfaceevaporation

transpiration

canopy waterevaporation

uptake

Quick flow

baseflow

{

surface run-on

sub-surfacelateral

inflow

surface run-off

Flow:

tree

Soil

Hydrology function of ‘forest’:

lanscape

?

Page 4: Conversion of forest to coffee-based Agroforestry in Indonesia:

Forest Agriculture: Monoculture / Polyculture

De

co

mp

osi

tio

n &

M

ine

ralis

atio

n

Water QualityRun - off

Other macrofauna

Earthworm

SOM Macroporosity &

Water Infiltration

Thickness of Surface Litter

Slope and rainfall

Protection to soil surface

Page 5: Conversion of forest to coffee-based Agroforestry in Indonesia:

Reduced Run-off IF:Reduced Run-off IF:

1. Good and long soil cover ~ Litter

thickness, slowly decomposed litter

2. High soil roughness ~ branches,

understorey3. Good water infiltration ~ enough soil

macro pore

Page 6: Conversion of forest to coffee-based Agroforestry in Indonesia:

PurposePurpose

Page 7: Conversion of forest to coffee-based Agroforestry in Indonesia:

West Lampung

Malang

SUMATRA

JAVA

Page 8: Conversion of forest to coffee-based Agroforestry in Indonesia:

2.Multistrata coffee

3. Shaded coffee

1.Forest

4.Monoculture Coffee

SurveySurvey

Page 9: Conversion of forest to coffee-based Agroforestry in Indonesia:
Page 10: Conversion of forest to coffee-based Agroforestry in Indonesia:

1. Litterfall

2. Prunning

Do litter composition of LUS differs one to another?

Page 11: Conversion of forest to coffee-based Agroforestry in Indonesia:

11.5

9.210.0

6.1

3.6

0

2

4

6

8

10

12

14

Fores

t

Mul

tistra

ta

Shaded

-Par

Shaded

-Glir

i

Coffee

Mono

Lit

ter

inp

ut,

Mg

/ha/

yr

0%

20%

40%

60%

80%

100%

Forest

Mult

istra

ta

Shade

d -Par

Shade

d -Glir

i

Coffe

e M

ono

Lit

ter

co

mp

os

itio

n

Branch Leaf Flower Fruit

Annual Litter Input in Sumatra

Page 12: Conversion of forest to coffee-based Agroforestry in Indonesia:

LUSLitterfall

Mg ha-1yr-1

N L P(L+P)/N

--------------%-----------

Forest 11.1 1.24 21.1 6.37 22.2

Multistrata C. 7.7 2.2 34.9 6.12 18.6

Shaded C. 6.0 2.15 32.3 4.25 17.0Monoculture C. 3.9 1.95 37.7 5.19 22.0

Annual Litter input and its quality of Annual Litter input and its quality of various LUS in Javavarious LUS in Java

(L+P)/N > 10 low quality slow decompose (Van Lauwe et al, 1997)

Page 13: Conversion of forest to coffee-based Agroforestry in Indonesia:

DECOMPOSITION RATE OF DECOMPOSITION RATE OF LITTERLITTERLUS Equation R2 k

week-1

Residence time (1/k),

week

Half life time, week

Forest Y = - 0.0068 x – 0.0101 0.6 0.0068 147 101Multi. Y = - 0.0131 x – 0.0553 0.7 0.0131 76 53Shaded Y = - 0.0143 x – 0.0408 0.9 0.0143 70 48Monocul. Y = - 0.0176 x – 0.0367 0.9 0.0176 57 39

Page 14: Conversion of forest to coffee-based Agroforestry in Indonesia:
Page 15: Conversion of forest to coffee-based Agroforestry in Indonesia:

Cast production weekly observed

Measurement of Earthworm

Page 16: Conversion of forest to coffee-based Agroforestry in Indonesia:

Klitelum

Dominant Spesies in Indonesian Agriculture:

Pontoscolex corethrurus

Prostomium

Seta

cocon

Genetal pore & TP

Anterior

Taken by: Dewi

Taken by: Fragoso

Total: 11 species

Page 17: Conversion of forest to coffee-based Agroforestry in Indonesia:

Earthworm population

0

0.05

0.1

0.15

0.2

0.25

0.3

0.35

0.4

0.45

RemnantForest

Multistrata Shaded Monoculture

Ra

tio

to

t. b

iom

as

s t

o p

op

ula

tio

n, g

/ in

div

.

0

20

40

60

80

100

120

140

160

No

an

ec

ic +

en

do

ge

ic, i

nd

iv m

-2

Number anecic + endogeic

Forest: Amynthas gracillis & Peryonix excavatus (bigger size)

Coffee based: Dichogaster bolaui (smaller size)

Page 18: Conversion of forest to coffee-based Agroforestry in Indonesia:
Page 19: Conversion of forest to coffee-based Agroforestry in Indonesia:

(Lavelle, 1997) (Van Noordwijk, 1985)

Role of Earthworm and Roots on Macropore

Page 20: Conversion of forest to coffee-based Agroforestry in Indonesia:

Soil Macro porosity measurement (Methylen Blue), Feb. 2008

Page 21: Conversion of forest to coffee-based Agroforestry in Indonesia:

Macropore in- vertical plane

Coffee monoculture

Imperata grassland

Coffee-based Agroforestry

Forest

100 cm

30

cm

30

cm

30

cm

30

cm

20 %

8 %

6 %

12 %

Page 22: Conversion of forest to coffee-based Agroforestry in Indonesia:

Measurement of water infiltration

Page 23: Conversion of forest to coffee-based Agroforestry in Indonesia:

Macroporosity and Infiltration

Page 24: Conversion of forest to coffee-based Agroforestry in Indonesia:

Earthworm (Pontoscolex) vs Soil porosity

Page 25: Conversion of forest to coffee-based Agroforestry in Indonesia:

Macropore = 0.78 Roots – 15.6 B/Pnon-Pontoscolex + 5.02

Litter thickness (R2 = 0.98**)

Managing Crop Diversity is the key factor for maintaining Soil macropore

Variable T-value

P-value

Y R2

Roots DW 9.37 0.001** PV = 4.79 + 0.74 Root Dw 0.85** Litter

thickness 6.10 0.004** PV = - 0.40 + 10.1 Litter thickness 0.58*

Ratio B:Pnon

Pontoscolex -3.27 0.031* PV = 9.65 + 34.5 B/P non

Pontoscolex 0.47*

Litter, earthworm, roots and MacroporeLitter, earthworm, roots and MacroporeDewi et al., 2006)

Page 26: Conversion of forest to coffee-based Agroforestry in Indonesia:
Page 27: Conversion of forest to coffee-based Agroforestry in Indonesia:

Worm size+po-pulation

Worm Biomass

SOM

LITTER

LAYER

Litter Input (various shade trees in AF

coffee based systems)

Worm Activity

Macro pore

“SoilStructDyn” (as a part of WaNuLCAS model)Van Noordwijk et al, 2005

Page 28: Conversion of forest to coffee-based Agroforestry in Indonesia:

LUS

Surface litter,

Mg ha-1

Corg relative

to Corg forest,

%

Macropore, %

EarthwormBiomass,

g m-2

M S M S M S M S

Forest4.2 4.9 1.0 1.0 12.3 12.5 31 25.8

Multistrata3.3 2.3 0.44 0.47 3.6 4.8 18 17.8

Shaded3 1.1 0.55 0.42 3.5 2.6 7 14.1

Monokulture

1.6 1.5 0.43 0.40 3 2.2 12 9.5

Estimation of “SoilStruct Dyn” Estimation of “SoilStruct Dyn” ModellingModelling

Page 29: Conversion of forest to coffee-based Agroforestry in Indonesia:

1. Better litter layer improved soil macroporosity and Water infiltration

2.2. Improvement of macroporosity in AF ~ Improvement of macroporosity in AF ~ Size of Earthworms (anecic group)

3. A combination of trees with slowly decomposing litter protect the soil surface, and trees with deep root systems create macroporosity

Page 30: Conversion of forest to coffee-based Agroforestry in Indonesia:

This activity was funded by ACIAR- ICRAF S.E. Asia, Ministry of Education (DIKTI- A2 Program) and CIFOR

- Tropical Forest and Climate Change Adaptation (TroFCCA) project

Page 31: Conversion of forest to coffee-based Agroforestry in Indonesia: