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Presenter: Wayne Roper
Co-authors: Wayne Robarge, Deanna Osmond, Joshua Heitman
Department of Crop and Soil Sciences, NC State University
Using Low Organic Matter Soils to Compare
Conventional Soil Organic Carbon Measurements
Soil health and soil organic carbon
Soil health is โ€œthe capacity for soil to function as a ecosystem that sustains lifeโ€
Soil organic carbon (SOC) is a critical component of soil health
Stimulates microbial activity
SOC is derived from plant, animal, and microbial residues that are incorporated into soil
Animal manure Microbial biomass
CO2
& byproducts
Oxidant
Organic Carbon reactivity
As carbon compounds are degraded by biological or
chemical processes, CO2 is released
Glucose
Plant litter
Chemistry of soil organic carbon
Mass loss on ignition (LOI)
Automated dry combustion (ADC)
Walkley-Black (WB)
360ยฐC ๐‘” ๐‘†๐‘‚๐‘€ ร— 0.58
๐‘” ๐‘ ๐‘œ๐‘–๐‘™
SOC
Calculation
Thermal digestion
SOC oxidation
925ยฐC
Thermal
detection
Methods to measure soil organic carbon
Ceramic
crucible
Mass soil
with SOM
Muffle
furnace
SOC
oxidation
Mass soil
without SOM
Gas
chromatography
๐‘” ๐ถ
๐‘” ๐‘ ๐‘œ๐‘–๐‘™
SOC
Calculation
(๐‘š๐‘’๐‘ž ๐พ2 ๐ถ๐‘Ÿ2 ๐‘‚7 โˆ’ ๐‘š๐‘’๐‘ž ๐น๐‘’๐‘†๐‘‚4)(0.003)
๐‘” ๐‘ ๐‘œ๐‘–๐‘™
SOC
Calculation
~ 10 g
soil
~ 0.03 g
soil
~ 1 g
soil
Oxidant (K2Cr2O7)
Heat (H2SO4)
SOC
oxidation
Filter
solution
Titration
(FeSO4)
Do the methods lead to similar interpretations of SOC?
Assess the ability for different methods to differentiate among soils
Objective 1
Compare correlations among measurements of SOC from different methods
Objective 2
Study objectives
Experiment locations
Mountain
Mills River, NC
Began: 1990
Soil:
Delanco silt loam
Typical SOM (0-15 cm):
0.5-3% (5-30 g kg-1)
Treatment factors:
Organic management
Conventional management
No-till
Conventional tillage
Piedmont 1
Reidsville, NC
Began: 1984
Soil:
Toast coarse sandy loam
Typical SOM (0-15 cm):
0.5-3% (5-30 g kg-1)
Treatment factors:
No-till, chisel plow, disc plow,
moldboard plow
Piedmont 2
Reidsville, NC
Began: 1984
Soil:
Pacolet sandy loam
Typical SOM (0-15 cm):
0.5-2% (5-20 g kg-1)
Treatment factors:
No-till, disc plow
Coastal Plain
Goldsboro, NC
Began: 1999
Soil:
Wickham sandy loam
Typical SOM (0-15 cm):
0.5-2% (5-20 g kg-1)
Treatment factors:
Organic management
conventional management
No-till
Four long-term agronomic trials in North Carolina
Soils collected from
top 15 cm...
โ€ฆground up and forced
through a 2-mm meshโ€ฆ
Automated dry
combustion
Mass loss
on ignition
Walkley-Black
then processed using different methods
Soil preparation
ResultsResults
Method N Mean SD Minimum Maximum Range
โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“
WB 84 12.99 a 2.05 9.7 18.8 9.1
LOI 84 13.47 a 3.30 8.4 22.5 14.1
ADC 84 7.70 b 2.05 3.7 13.3 9.6
Letters after means indicate statistical grouping
โ€ข SOC mostly fit ranges expected for these soils (< 2% or < 20 g kg-1)
โ€ข ADC measured less SOC than LOI and WB
โ€ข LOI had the largest range and variability
Results โ€“ summary statistics
Summary statistics for soil organic carbon measurements
0
6
12
18
24
0 6 12 18 24
LOISOC(gkg-1)
ADC SOC (g kg-1)
r2 = 0.40
n = 84 Trial r2
ADC vs LOI Overall 0.40
Coastal Plain 0.62
Piedmont 1 0.33
Piedmont 2 0.81
Mountain 0.71
Results โ€“ correlations
Correlation between SOC measured by ADC and LOI
0
6
12
18
24
0 6 12 18 24
WBSOC(gkg-1)
LOI SOC (g kg-1)
r2 = 0.31
n = 84 Trial r2
LOI vs WB Overall 0.31
Coastal Plain 0.08
Piedmont 1 0.15
Piedmont 2 0.40
Mountain 0.33
Results โ€“ correlations
Correlation between SOC measured by LOI and WB
0
6
12
18
24
0 6 12 18 24
WBSOC(gkg-1)
ADC SOC (g kg-1)
r2 = 0.30
n = 84 Trial r2
ADC vs WB Overall 0.30
Coastal Plain 0.05
Piedmont 1 0.18
Piedmont 2 0.28
Mountain 0.59
Results โ€“ correlations
Correlation between SOC measured by ADC and WB
1. ADC reports less SOC than LOI and WB
2. Separating the data by location did not consistently improve correlations
3. The amount of SOC measured by one method is not predictive of SOC that
would be measured by another method
Objective 1
Compare correlations among measurements of SOC from different methods
RESULTS
Results โ€“ correlations
Automated dry
combustion
Mass loss
on ignition
Walkley-Black
Trial Treatment ADC LOI WB
โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“
Coastal
Plain
No-till Conventional 8.3 9.9 13.2 a
Conv. Tillage 9.0 9.9 10.7 b
Conv. Tillage organic 1 8.5 10.3 13.3 a
Conv. Tillage organic 2 9.0 11.9 11.9 ab
ADC: No differentiation
LOI: No differentiation
WB: + Organic with tillage
+ No-till
Results โ€“ agronomic management
Comparison of coastal plain treatments
Trial Treatment ADC LOI WB
โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“
Piedmont 1 No-till chemical 7.5 ab 12.6 bc 11.9
In-row subsoiling 9.5 a 16.9 a 14.0
Disk, spring 5.3 b 13.8 abc 14.3
Chisel, fall 7.9 ab 13.6 abc 12.4
Chisel, spring 8.1 ab 14.9 ab 13.7
Chisel, disk, fall 7.1 ab 12.3 bc 12.2
Chisel, disk, spring 6.5 ab 13.4 abc 12.1
Moldboard, fall 5.3 b 12.7 bc 10.9
Moldboard, spring 5.5 b 10.2 c 11.6
Piedmont 2 No-till chemical 7.1 11.6 11.6
Alternate year tillage 7.1 12.0 13.6
Disk, spring 6.7 11.6 12.7
Twice disking, spring 5.9 10.2 12.4
ADC: subsoiling > moldboard, disc
LOI: subsoiling > moldboard, chisel + disc
WB: no differentiation
ADC: no differentiation
LOI: no differentiation
WB: no differentiation
Results โ€“ agronomic management
Comparison of piedmont treatments
Trial Treatment ADC LOI WB
โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“
Mountain No-till Organic 12.3a 20.1 a 16.4 a
No-till Conv. 8.8b 16.3 b 14.6 ab
Conv. Tillage Organic 9.3b 17.3 ab 13.9 ab
Conv. Tillage 7.3b 15.3 b 12.7 b
Conv. Tillage Fallow 8.8b 16.4 b 15.0 ab ADC: + no-till organic
LOI: + no-till organic
WB: + no-till organic > conventional
Results โ€“ agronomic management
Comparison of mountain treatments
โ€ข Statistical differentiation of the effects of agronomic management practices
on SOC was not consistent among the methods when comparing results
within and across agronomic trials
Objective 2
Assess the ability for different methods to differentiate among soils
RESULTS
Results โ€“ correlations
โ€ข Interpretations of SOC content in these soils should be relative to a specific method and
should not be compared to different procedures.
Conclusions and implications
โ€ข Correlations between methods for measuring SOC are not predictive of each other
(for the low SOC soils used in the experiment)
โ€ข Differences in how agronomic management affects SOC content are not consistent among
conventional methods
Acknowlegements
Ph.D. committee:
Deanna Osmond & Joshua Heitman
Michael Wagger
Chris Reberg-Horton
Co-author:
Wayne Robarge
Soil analyses:
Environmental and Agricultural Testing Service
Dean Hesterberg soil chemistry laboratory
Assistance:
Adam Howard
Wesley Childres
Melissa Bell & Tomas Moreno
All research station personnel
Funding
Thank you
Questions?

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Using low organic matter soils to compare conventional soil organic carbon measurements

  • 1. Presenter: Wayne Roper Co-authors: Wayne Robarge, Deanna Osmond, Joshua Heitman Department of Crop and Soil Sciences, NC State University Using Low Organic Matter Soils to Compare Conventional Soil Organic Carbon Measurements
  • 2. Soil health and soil organic carbon Soil health is โ€œthe capacity for soil to function as a ecosystem that sustains lifeโ€ Soil organic carbon (SOC) is a critical component of soil health Stimulates microbial activity
  • 3. SOC is derived from plant, animal, and microbial residues that are incorporated into soil Animal manure Microbial biomass CO2 & byproducts Oxidant Organic Carbon reactivity As carbon compounds are degraded by biological or chemical processes, CO2 is released Glucose Plant litter Chemistry of soil organic carbon
  • 4. Mass loss on ignition (LOI) Automated dry combustion (ADC) Walkley-Black (WB) 360ยฐC ๐‘” ๐‘†๐‘‚๐‘€ ร— 0.58 ๐‘” ๐‘ ๐‘œ๐‘–๐‘™ SOC Calculation Thermal digestion SOC oxidation 925ยฐC Thermal detection Methods to measure soil organic carbon Ceramic crucible Mass soil with SOM Muffle furnace SOC oxidation Mass soil without SOM Gas chromatography ๐‘” ๐ถ ๐‘” ๐‘ ๐‘œ๐‘–๐‘™ SOC Calculation (๐‘š๐‘’๐‘ž ๐พ2 ๐ถ๐‘Ÿ2 ๐‘‚7 โˆ’ ๐‘š๐‘’๐‘ž ๐น๐‘’๐‘†๐‘‚4)(0.003) ๐‘” ๐‘ ๐‘œ๐‘–๐‘™ SOC Calculation ~ 10 g soil ~ 0.03 g soil ~ 1 g soil Oxidant (K2Cr2O7) Heat (H2SO4) SOC oxidation Filter solution Titration (FeSO4)
  • 5. Do the methods lead to similar interpretations of SOC? Assess the ability for different methods to differentiate among soils Objective 1 Compare correlations among measurements of SOC from different methods Objective 2 Study objectives
  • 6. Experiment locations Mountain Mills River, NC Began: 1990 Soil: Delanco silt loam Typical SOM (0-15 cm): 0.5-3% (5-30 g kg-1) Treatment factors: Organic management Conventional management No-till Conventional tillage Piedmont 1 Reidsville, NC Began: 1984 Soil: Toast coarse sandy loam Typical SOM (0-15 cm): 0.5-3% (5-30 g kg-1) Treatment factors: No-till, chisel plow, disc plow, moldboard plow Piedmont 2 Reidsville, NC Began: 1984 Soil: Pacolet sandy loam Typical SOM (0-15 cm): 0.5-2% (5-20 g kg-1) Treatment factors: No-till, disc plow Coastal Plain Goldsboro, NC Began: 1999 Soil: Wickham sandy loam Typical SOM (0-15 cm): 0.5-2% (5-20 g kg-1) Treatment factors: Organic management conventional management No-till Four long-term agronomic trials in North Carolina
  • 7. Soils collected from top 15 cm... โ€ฆground up and forced through a 2-mm meshโ€ฆ Automated dry combustion Mass loss on ignition Walkley-Black then processed using different methods Soil preparation
  • 9. Method N Mean SD Minimum Maximum Range โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ WB 84 12.99 a 2.05 9.7 18.8 9.1 LOI 84 13.47 a 3.30 8.4 22.5 14.1 ADC 84 7.70 b 2.05 3.7 13.3 9.6 Letters after means indicate statistical grouping โ€ข SOC mostly fit ranges expected for these soils (< 2% or < 20 g kg-1) โ€ข ADC measured less SOC than LOI and WB โ€ข LOI had the largest range and variability Results โ€“ summary statistics Summary statistics for soil organic carbon measurements
  • 10. 0 6 12 18 24 0 6 12 18 24 LOISOC(gkg-1) ADC SOC (g kg-1) r2 = 0.40 n = 84 Trial r2 ADC vs LOI Overall 0.40 Coastal Plain 0.62 Piedmont 1 0.33 Piedmont 2 0.81 Mountain 0.71 Results โ€“ correlations Correlation between SOC measured by ADC and LOI
  • 11. 0 6 12 18 24 0 6 12 18 24 WBSOC(gkg-1) LOI SOC (g kg-1) r2 = 0.31 n = 84 Trial r2 LOI vs WB Overall 0.31 Coastal Plain 0.08 Piedmont 1 0.15 Piedmont 2 0.40 Mountain 0.33 Results โ€“ correlations Correlation between SOC measured by LOI and WB
  • 12. 0 6 12 18 24 0 6 12 18 24 WBSOC(gkg-1) ADC SOC (g kg-1) r2 = 0.30 n = 84 Trial r2 ADC vs WB Overall 0.30 Coastal Plain 0.05 Piedmont 1 0.18 Piedmont 2 0.28 Mountain 0.59 Results โ€“ correlations Correlation between SOC measured by ADC and WB
  • 13. 1. ADC reports less SOC than LOI and WB 2. Separating the data by location did not consistently improve correlations 3. The amount of SOC measured by one method is not predictive of SOC that would be measured by another method Objective 1 Compare correlations among measurements of SOC from different methods RESULTS Results โ€“ correlations Automated dry combustion Mass loss on ignition Walkley-Black
  • 14. Trial Treatment ADC LOI WB โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ Coastal Plain No-till Conventional 8.3 9.9 13.2 a Conv. Tillage 9.0 9.9 10.7 b Conv. Tillage organic 1 8.5 10.3 13.3 a Conv. Tillage organic 2 9.0 11.9 11.9 ab ADC: No differentiation LOI: No differentiation WB: + Organic with tillage + No-till Results โ€“ agronomic management Comparison of coastal plain treatments
  • 15. Trial Treatment ADC LOI WB โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ Piedmont 1 No-till chemical 7.5 ab 12.6 bc 11.9 In-row subsoiling 9.5 a 16.9 a 14.0 Disk, spring 5.3 b 13.8 abc 14.3 Chisel, fall 7.9 ab 13.6 abc 12.4 Chisel, spring 8.1 ab 14.9 ab 13.7 Chisel, disk, fall 7.1 ab 12.3 bc 12.2 Chisel, disk, spring 6.5 ab 13.4 abc 12.1 Moldboard, fall 5.3 b 12.7 bc 10.9 Moldboard, spring 5.5 b 10.2 c 11.6 Piedmont 2 No-till chemical 7.1 11.6 11.6 Alternate year tillage 7.1 12.0 13.6 Disk, spring 6.7 11.6 12.7 Twice disking, spring 5.9 10.2 12.4 ADC: subsoiling > moldboard, disc LOI: subsoiling > moldboard, chisel + disc WB: no differentiation ADC: no differentiation LOI: no differentiation WB: no differentiation Results โ€“ agronomic management Comparison of piedmont treatments
  • 16. Trial Treatment ADC LOI WB โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ g C kg-1 โ€“โ€“โ€“โ€“โ€“โ€“โ€“โ€“ Mountain No-till Organic 12.3a 20.1 a 16.4 a No-till Conv. 8.8b 16.3 b 14.6 ab Conv. Tillage Organic 9.3b 17.3 ab 13.9 ab Conv. Tillage 7.3b 15.3 b 12.7 b Conv. Tillage Fallow 8.8b 16.4 b 15.0 ab ADC: + no-till organic LOI: + no-till organic WB: + no-till organic > conventional Results โ€“ agronomic management Comparison of mountain treatments
  • 17. โ€ข Statistical differentiation of the effects of agronomic management practices on SOC was not consistent among the methods when comparing results within and across agronomic trials Objective 2 Assess the ability for different methods to differentiate among soils RESULTS Results โ€“ correlations
  • 18. โ€ข Interpretations of SOC content in these soils should be relative to a specific method and should not be compared to different procedures. Conclusions and implications โ€ข Correlations between methods for measuring SOC are not predictive of each other (for the low SOC soils used in the experiment) โ€ข Differences in how agronomic management affects SOC content are not consistent among conventional methods
  • 19. Acknowlegements Ph.D. committee: Deanna Osmond & Joshua Heitman Michael Wagger Chris Reberg-Horton Co-author: Wayne Robarge Soil analyses: Environmental and Agricultural Testing Service Dean Hesterberg soil chemistry laboratory Assistance: Adam Howard Wesley Childres Melissa Bell & Tomas Moreno All research station personnel Funding