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Sequestering soil carbon in the low input
farming systems of the semi-arid tropics –
does litter quality matter?
Anthony Whitbread
Rod Lefroy
Graeme Blair
Yothin Konboon (Late)
Kunnika Naklang (Late)
Introduction
• Limited evidence from the drylands that soil C in arable systems
can be ‘sequestered’ under normal management.
• Apart from the aims of mitigation, managing soil C has many
other benefits (soil structure, nutrient supply capacity, ‘soil
health’) which may not payoff for several years.
• Long term trials and multiple measures of systems performance
are needed to assess a change in the system.
• In low input systems, plant residues can be used to manage soil
fertility but few examples of residue ‘quality’ being a factor.
• Simple proxies of quality (Palm et al. AGEE, 2001) are available.
• The hypothesis tested in this paper: “Will repeated applications
of low as compared to high ‘quality’ leaf litters lead to higher C
sequestration?”
Methodology
• This paper presents a unique long term application of leaf litters
with varying qualities to a rice system:
• Rainfed tropical rice system in north-east Thailand (URRC)
• Paddy field experiments (9 seasons) Split plot design
• Measured -nutrient dynamics, SOM dynamics and crop yields.
4 leaf litters+ no-leaf litter control × 2 fertiliser rates × ± rice stubble
Naklang et al. Plant&Soil (1999)
Whitbread et al. Plant&Soil (1999)
Whitbread et al. Ag.Eco.Env(2003)
CT CL Lability CMI
(mg/g)
Forest 23.0 4.6 0.25 100
Paddy 3.5 0.4 0.14 9
Methodology
Shrubs surrounding field supplied the leaf litters of varying qualities.
Ubon Ratchathani Rice Research Centre (URRC) DoA
Methodology
• Assessment of decomposition characteristics
• Cumulative C release from leaf litters as determined by the
perfusion technique over 60 days
0
10
20
30
40
50
60
70
0 10 20 30 40 50 60
Days
ResidueCrelease(%)
C. cajan
S.saman
P. taxodifolius
A. auriculiformis
5%l.s.d.
12
23
25
19
C:N
Lefroy et al. (1995)
Methodology
Separation of Labile Fractions of Soil Carbon
• Total carbon (CT) by catalytic combustion
• Labile carbon (CL) by oxidation with 333mM KMnO4
(Blair et al. 1995)
Results Figure: Labile carbon (mg/g)
Results Figure: Total carbon (mg/g)
Results Figure: Grain yield 1992-2000
Results Grain yield 1992-2000
1992 1993 1994 1995 1996 1997 1998 1999 2000
Low N:P:K 1167 1207 1441 1318 1834 1604 1748 1413 1846
High N:P:K 1431 1455 1806 1558 2109 1953 2074 1633 2218
significance *** *** *** *** ** *** *** ** ***
Straw - 1241 1266 1598 1419 1896 1761 1861 1477 1935
Straw + 1356 1395 1649 1456 2046 1796 1961 1569 2129
significance ns * ns ns * ns ns ns *
* p≤0.05, ** p≤0.01, *** p≤0.001
Results Figure: Apparent recovery of S
Conclusions
• The hypothesis, ‘will repeated applications of low as compared to
high ‘quality’ leaf litters lead to higher C sequestration’ was not
proven.
• Lower and higher quality litters resulted in similar small increases
in soil organic C and in other indicators (yield).
• Apparent recovery of S was sig. higher with intermediate ‘quality
residues’ an indication of better synchrony in release of S.
• Small and repeated leaf litter applications did significantly increase
overall productivity and sustainability of a low input paddy system.
• Results are therefore very significant for low input systems.
The reality of managing soil as one component of the farm.
• Decisions made by farm households are made in context of many factors.
• While the maintenance of soil is the basis of sustainability, short term
considerations dominate decisions.
• Small and repeated leaf
litter applications may be
practical at small scale
with ‘trees on bunds’.
• Large scale – Zero Till,
residue retention,
rotations, living mulch,
etc. all require
mechanisation to be
practical

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Soil C sequestration in low-input farming systems of semi-arid tropics - does litter quality matter

  • 1. Sequestering soil carbon in the low input farming systems of the semi-arid tropics – does litter quality matter? Anthony Whitbread Rod Lefroy Graeme Blair Yothin Konboon (Late) Kunnika Naklang (Late)
  • 2. Introduction • Limited evidence from the drylands that soil C in arable systems can be ‘sequestered’ under normal management. • Apart from the aims of mitigation, managing soil C has many other benefits (soil structure, nutrient supply capacity, ‘soil health’) which may not payoff for several years. • Long term trials and multiple measures of systems performance are needed to assess a change in the system. • In low input systems, plant residues can be used to manage soil fertility but few examples of residue ‘quality’ being a factor. • Simple proxies of quality (Palm et al. AGEE, 2001) are available. • The hypothesis tested in this paper: “Will repeated applications of low as compared to high ‘quality’ leaf litters lead to higher C sequestration?”
  • 3. Methodology • This paper presents a unique long term application of leaf litters with varying qualities to a rice system: • Rainfed tropical rice system in north-east Thailand (URRC) • Paddy field experiments (9 seasons) Split plot design • Measured -nutrient dynamics, SOM dynamics and crop yields. 4 leaf litters+ no-leaf litter control × 2 fertiliser rates × ± rice stubble Naklang et al. Plant&Soil (1999) Whitbread et al. Plant&Soil (1999) Whitbread et al. Ag.Eco.Env(2003) CT CL Lability CMI (mg/g) Forest 23.0 4.6 0.25 100 Paddy 3.5 0.4 0.14 9
  • 4. Methodology Shrubs surrounding field supplied the leaf litters of varying qualities. Ubon Ratchathani Rice Research Centre (URRC) DoA
  • 5. Methodology • Assessment of decomposition characteristics • Cumulative C release from leaf litters as determined by the perfusion technique over 60 days 0 10 20 30 40 50 60 70 0 10 20 30 40 50 60 Days ResidueCrelease(%) C. cajan S.saman P. taxodifolius A. auriculiformis 5%l.s.d. 12 23 25 19 C:N Lefroy et al. (1995)
  • 6. Methodology Separation of Labile Fractions of Soil Carbon • Total carbon (CT) by catalytic combustion • Labile carbon (CL) by oxidation with 333mM KMnO4 (Blair et al. 1995)
  • 7. Results Figure: Labile carbon (mg/g)
  • 8. Results Figure: Total carbon (mg/g)
  • 9. Results Figure: Grain yield 1992-2000
  • 10. Results Grain yield 1992-2000 1992 1993 1994 1995 1996 1997 1998 1999 2000 Low N:P:K 1167 1207 1441 1318 1834 1604 1748 1413 1846 High N:P:K 1431 1455 1806 1558 2109 1953 2074 1633 2218 significance *** *** *** *** ** *** *** ** *** Straw - 1241 1266 1598 1419 1896 1761 1861 1477 1935 Straw + 1356 1395 1649 1456 2046 1796 1961 1569 2129 significance ns * ns ns * ns ns ns * * p≤0.05, ** p≤0.01, *** p≤0.001
  • 11. Results Figure: Apparent recovery of S
  • 12. Conclusions • The hypothesis, ‘will repeated applications of low as compared to high ‘quality’ leaf litters lead to higher C sequestration’ was not proven. • Lower and higher quality litters resulted in similar small increases in soil organic C and in other indicators (yield). • Apparent recovery of S was sig. higher with intermediate ‘quality residues’ an indication of better synchrony in release of S. • Small and repeated leaf litter applications did significantly increase overall productivity and sustainability of a low input paddy system. • Results are therefore very significant for low input systems.
  • 13. The reality of managing soil as one component of the farm. • Decisions made by farm households are made in context of many factors. • While the maintenance of soil is the basis of sustainability, short term considerations dominate decisions. • Small and repeated leaf litter applications may be practical at small scale with ‘trees on bunds’. • Large scale – Zero Till, residue retention, rotations, living mulch, etc. all require mechanisation to be practical