1 soil carbon sequestration: long-term effect of tillage and rotations charles w. rice and karina...
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Soil Carbon Sequestration: Long-term Effect of Tillage and Rotations
Charles W. Riceand
Karina Fabrizzi
October 28-30, 2008
Kansas State University
Energy supply
0
1
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3
4
5
6
7GtCO2-eq
Transport Buildings Industry Agriculture Forestry Waste
Non-OECD/EI TEITOECDWorld total
US$/tCO2-eq
Global economic mitigation potential for
different sectors at different carbon prices
IPCC, 2007
Agriculture
• A large proportion of the mitigation potential of agriculture (excluding bioenergy) arises from soil C sequestration, which has strong synergies with sustainable agriculture and generally reduces vulnerability to climate change.
• Agricultural practices collectively can make a significant contribution at low cost – By increasing soil carbon sinks, – By reducing GHG emissions, – By contributing biomass feedstocks for energy use
IPCC Fourth Assessment Report, Working Group III, 2007
Agriculture• Cropland
– Reduced tillage– Rotations– Cover crops– Fertility management– Erosion control– Irrigation management
• Rice paddies– Irrigation– Chemical and organic fertilizer– Plant residue management
No-till seeding in USA
Rice fields in The Philippines
Maize / coffee fields in Mexico
• Agroforestry
– Improved managementof trees and cropland
Agricultural Management Strategies for C Sequestration
Enhance C Inputs Reduce C losses
Crop Management Tillage
Crop Selection Fallow Management
Crop Rotations
Develop Agricultural Management Programs that:
Soil Microbial ActivitySoil Microbial Activity
Soil Organic Matter (C)Soil Organic Matter (C)
CO2CO2
Harvestable Yield
Harvestable Yield
SunlightSunlight
ClimateClimate
SoilsSoils ManagementManagement
Potential C sequestration in U.S
Lal et al., 1999, Post et al.,2004
Strategies Management practices Mg C ha-1 yr-1
Decreasing tillage intensity Reduced tillage, no-tillage, mulch tillage
0.24-0.40
Increasing amount of crop residue return
High residue crops, applications of manure and biosolids, erosion control, irrigation, integrated pest management, precision agriculture
Use of winter cover crops 0.1-0.3
Summer fallow elimination 0.1-0.3
Fertilizer management 0.05-0.15
Perennial vegetation CRP 0.3-0.7
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Corn production in NE Kansas
• Continuous corn• 168 kg N/ha• Tillage Systems
– No-tillage– Conservation tillage (Chisel-disk)
• 15 year analysis
Soil C stocks after 18 years
0 20 40 60 80 100 120
0-60
30-60
15-30
5-15
0-5NTCT
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*
*
*
Nicoloso et al., 2008
Tillage effects on soil organic C by depth, Minnesota: 14 y continuous corn
Mg C/ha/cmDepth No-till Plow
0.7.5 4.49 3.89 **
7.5-15 4.94 4.66
15-30 3.51 3.17
30-45 2.45 1.48 **
0-45 (Mg/ha) 160 133 **
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Huggins et al., 2007
E
A
Change in management
Years of cultivation
SO
C le
vels
(M
g C
ha
-1)
O
Soil C sequestration rates for 15 years(Mg C/ha/y)
Depth Fertilizer NTilled
Fertilizer NNo-till
Manure NTilled
Manure NNo-till
cm
0-5 0.161 0.351 0.393 1.182
0-15 0.254 0.497 0.792 1.402
0-30 0.336 0.717 0.839 1.387
0-60 0.146 1.325 0.733 1.141
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• NT > Tilled, but tilled had some increase• Added C (manure) is less conserved in tilled• What is baseline? Nicoloso et al., 2008
E
D
C
AChange in management
Years of cultivation
SO
C le
vels
(M
g C
ha
-1)
O
Net effect of NT for 15 yearsNT (0-15y) –T (0-15y)
Depth No N0.5
Fertilizer N Fertilizer N0.5
Manure N Manure N
cm Mg/ha/y
0-5 0.187 0.450 0.190 0.468 0.789
0-15 0.182 0.371 0.243 0.402 0.610
0-30 0.174 0.311 0.381 0.417 0.548
0-60 -0.443 -0.191 1.179 0.961 0.408
14Nicoloso et al., 2008
Carbon sequestration rate (C rate) expressed in equivalent mass (Mg C/ha/y) to a 30 cm depth except for Hayes (15 cm)
Location Rotation Duration CT RT NT
Hayes Wheat-Sorg-F 37 y 0.008 0.020 0.055
Parson Sorg-Soy 20 y 0.234 0.370 0.420
Ashland Average 29 y 0.269 0.346 0.384
Tribune Wheat-Sorg-F 15 y -0.570 -0.503 -0.392
15Fabrizzi, 2006
04/19/23
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30
35
40
45
50
55
60
30 35 40 45 50 55 60
SOC using CT (Mg C ha-1) at 0-30 cm
SO
C u
sin
g N
T o
r R
T (
Mg
C h
a-1
) at
0-3
0 cm
Ashland RT Ashland NT
Parsons NT Tribune RT
Parsons RT Tribune NT
Hays NT Hays RT
SOCNT = 1.14x - 4.90 R2 = 0.76
SOCRT =1.08x - 3.14 R2 = 0.67
1:1 Line
Intergovernmental Panel on Climate Change (IPCC): 1.1 for CT to NT West and Post (2002): 1.16 for CT to NT
Fabrizzi, 2006
Carbon sequestration rate (C rate) expressed in equivalent mass (Mg C/ha/y) to a 15 cm depth as a function of N rate (kg N/ha/y)
located Hayes, Kansas, USA
Rotation Duration 0 N 22 N 45 N 67 N
Wheat-Sorg-F 37 y 0.007 0.012 0.035 0.057
17Fabrizzi, 2006
Carbon sequestration rate (C rate) expressed in equivalent mass (Mg C/ha/y) to a 30 cm depth for Manhattan, KS USA
Rotation
Continuous Soybean 0.066
Continuous Sorghum 0.292
Continuous Wheat 0.487
Soybean - Wheat 0.510
Soybean - Sorghum 0.311
18Fabrizzi, 2006
Physical Protection
Chemical
Microbial composition and activity
Substrate
quality
Plant
characteristics
H2O
Temperature
Clay
Biological
factors
Organics
Clay
Organic C
CO2
O2
Disturbance
Conservation of Soil Carbon
Hie
rarc
hy
of
imp
ort
an
ce
Mineralogy
• Fungal Role (18:2w6 biomarker)
• Significant tillage X residue interaction (p<0.05)
0
0.02
0.04
0.06
0.08
CT + No R CT + Residue NT + No R NT + Residue
c*
a
b
c
Mo
le F
rac
tio
n
Frey et al. (1999) found greater fungal networks optically in NT as compared to CT for the same soil.White and Rice, 2007
Plant C
SOM SOM
CO2 CO2
FungiFungi
Micro-aggregates
No-Till = Lower disturbance
Soil MacroaggregateSoil Macroaggregate
Tillage = Higher disturbance
Plant C
SOM SOM
CO2 CO2
FungiFungi
Micro-aggregates
No-Till = Lower disturbance
Soil MacroaggregateSoil Macroaggregate
Tillage = Higher disturbance
Plant C
SOM SOM
CO2 CO2
FungiFungi
Micro-aggregates
No-Till = Lower disturbance
Soil MacroaggregateSoil Macroaggregate
Tillage = Higher disturbance
White and Rice, 2007
YMollisol = 1.48 SOC - 8.2
R2 = 0.9245
YVertisol= 1.56 SOC - 2.83
R2 = 0.1292
YOxisol= 0.58 SOC - 6.9
R2 = 0.3344
0
10
20
30
40
50
60
70
80
0 10 20 30 40 50 60 70
SOC (g C kg-1)
Am
ou
nt
of
ma
cro
ag
gre
ga
tes
(g 1
00
g-1
so
il)
Fabrizzi, 2006
Soil
Organic
Carbon
MicrobialActivity
Nutrient
Cycling
Soil
Structure
Soil
Biodiversity
WaterErosion
&
Availability
Gaseous Gaseous EmissionsEmissions
Plant Growth
Yield
Environmental Environmental ServicesServices
SustainabilitySustainability
No-Tillage Cropping SystemsNo-Tillage Cropping Systems
Conservation AgricultureConservation Agriculture
•Restores soil carbon
•Conserves moisture
•Saves fuel
•Saves labor
•Lowers machinery costs
•Reduces erosion
•Improved soil fertility
•Controls weed
•Planting on the best date
•Improves wildlife habitat
SummarySummary• Soil C sequestrationSoil C sequestration
– Need to examine the systemNeed to examine the system• Less disturbanceLess disturbance• Organic C inputsOrganic C inputs
– No-tillage must be combined with residuesNo-tillage must be combined with residues• Residue removal in no-till may be worst than tillage Residue removal in no-till may be worst than tillage
with residuewith residue
• Agricultural soil C sequestrationAgricultural soil C sequestration– Keeps land in production in some casesKeeps land in production in some cases– In many cases increases profitability for the farmerIn many cases increases profitability for the farmer– Provides other environmental benefits to societyProvides other environmental benefits to society
• Soil and Water quality (less runoff, less erosion)Soil and Water quality (less runoff, less erosion)– May help adapt to climate change as well as mitigateMay help adapt to climate change as well as mitigate
• Websiteswww.soilcarboncenter.k-state.edu/
K-State Research and ExtensionK-State Research and Extension
Chuck Rice
Phone: 785-532-7217
Cell: 785-587-7215 [email protected]
04/19/23
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Treatment Scenario Rate
(Mg C/ha/y)
State
Eliminate summer fallow
3-year system
4-year system Continuous cropping
0.073
0.117
0.229
Eastern Colorado
NT (corn) NT 150 N Fert 0.80 NE Kansas
Rotations CT - NT wheat
CT - NT sorghum
CTsorg/NTwheat to NT sorg/wheat
0.764
0.605
0.624
SC KS
CRP 0.80 NE