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8/2/2019 Cs CA Us Rice Cimmyt 2008
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1
Soil Carbon Sequestration:Long-term Effect of Tillage and Rotations
Charles W. Riceand
Karina Fabrizzi
October 28-30, 2008
Kansas State University
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Energy supply
0
1
2
3
4
5
6
7
< 2 0
< 5 0
< 1 0 0 < 2
0 < 5
0 < 1
0 0
GtCO 2-eq
Transport Bui ld ings Industry Agricul ture Forestry Waste
Non-OECD/EITEITOECD
World total
US$/tCO 2-eq
Global economic mitigation potential fordifferent sectors at different carbon prices
IPCC, 2007
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Agriculture
A large proportion of the mitigation potential of agriculture(excluding bioenergy) arises from soil C sequestration,which has strong synergies with sustainable agriculture andgenerally reduces vulnerability to climate change.
Agricultural practices collectively can make a significantcontribution 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
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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 inMexico
Agroforestry Improved
managementof trees andcropland
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Agricultural Management Strategiesfor C Sequestration
Enhance C Inputs Reduce C losses Crop Management Tillage
Crop Selection Fallow Management
Crop Rotations
Develop Agricultural Management Programs that:
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Soil Microbial Activity
Soil Organic Matter (C)
CO2
Harvestable Yield
Sunlight
Climate Soils Management
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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, mulchtillage 0.24-0.40
Increasing amount of cropresidue return
High residue crops, applicationsof manure and biosolids, erosioncontrol, irrigation, integrated pestmanagement, precisionagriculture
Use of winter cover crops 0.1-0.3
Summer fallow elimination 0.1-0.3Fertilizer 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
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Soil C stocks after 18 years
0 20 40 60 80 100 120
0-60
30-60
15-30
5-15
0-5NTCT
9
*
*
*
Nicoloso et al., 2008
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Tillage effects on soil organic C bydepth, 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 **
10Huggins et al., 2007
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E
A
Change in management
Years of cultivation
S O C l e v e l s
( M g
C h a - 1 )
O
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Soil C sequestration rates for 15 years(Mg C/ha/y)
Depth Fertilizer NTilled
Fertilizer NNo-till
Manure NTilled
Manure NNo-till
cm0-5 0.161 0.351 0.393 1.182
0-15 0.254 0.497 0.792 1.4020-30 0.336 0.717 0.839 1.3870-60 0.146 1.325 0.733 1.141
12
NT > Tilled, but tilled had some increase Added C (manure) is less conserved in tilled
What is baseline? Nicoloso et al., 2008
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E
D
C
A Change in management
Years of cultivation
S O C l e v e l s
( M g
C h a - 1 )
O
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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/y0-5 0.187 0.450 0.190 0.468 0.789
0-15 0.182 0.371 0.243 0.402 0.6100-30 0.174 0.311 0.381 0.417 0.5480-60 -0.443 -0.191 1.179 0.961 0.408
14Nicoloso et al., 2008
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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
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16
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
S O C u s
i n g
N T o r
R T ( M g
C h a -
1 ) a t 0 - 3
0 c m
Ashland RT Ashland NTParsons NT Tribune RTParsons RT Tribune NT
Hays NT Hays RT
SOC NT = 1.14x - 4.90R2 = 0.76
SOC RT =1.08x - 3.14R2 = 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
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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
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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
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Physical Protection
Chemical
Microbial compositionand activity
Substratequality
Plantcharacteristics
H2O
Temperature
ClayBiological
factors
Organics
Clay
Organic C
CO2
O2
Disturbance
Conservation of Soil Carbon
H
i e r a r c
h y o
f i m p o r t a n c e
Mineralogy
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Fungal Role (18:2w6 biomarker) Significant tillage X residue
interaction (p
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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
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YMollisol = 1.48 SOC - 8.2R2 = 0.9245
YVertisol = 1.56 SOC - 2.83R2 = 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)
A m o u n
t o
f m a c r o a g g r e g a t e s
( g 1 0 0 g
- 1 s
o i l )
Fabrizzi, 2006
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SoilOrganicCarbon
MicrobialActivity
NutrientCycling
SoilStructure
SoilBiodiversity
WaterErosion
&
Availability
GaseousEmissions
Plant GrowthYield
EnvironmentalServices
Sustainability
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No-Tillage Cropping SystemsConservation 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
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Summary Soil C sequestration
Need to examine the system Less disturbance Organic C inputs
No-tillage must be combined with residues Residue removal in no-till may be worst than tillage
with residue
Agricultural soil C sequestration Keeps land in production in some cases In many cases increases profitability for the farmer Provides other environmental benefits to society
Soil and Water quality (less runoff, less erosion) May help adapt to climate change as well as mitigate
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Websiteswww. soilcarboncenter.k-state.edu/
K-State Research and Extension
Chuck RicePhone: 785-532-7217
Cell: [email protected]
http://soilcarboncenter.k-state.edu/http://soilcarboncenter.k-state.edu/http://soilcarboncenter.k-state.edu/http://soilcarboncenter.k-state.edu/8/2/2019 Cs CA Us Rice Cimmyt 2008
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Treatment Scenario Rate(Mg C/ha/y)
State
Eliminatesummerfallow
3-year system4-year systemContinuouscropping
0.0730.1170.229
EasternColorado
NT (corn) NT 150 N Fert 0.80 NEKansas
Rotations CT - NT wheatCT - NT sorghum
CTsorg/NTwheatto NT sorg/wheat
0.7640.605
0.624
SC KS
CRP 0.80 NE