1 / 81

Genesis of the use of RothC to model soil organic carbon

Genesis of the use of RothC to model soil organic carbon. Outline. Composition of soil organic carbon – isolating biologically important fractions Methodology for quantifying C allocation to fractions Why attempt to understand allocation to fractions? Modelling soil carbon with RothC

diallo
Télécharger la présentation

Genesis of the use of RothC to model soil organic carbon

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Genesis of the use of RothC to model soil organic carbon

  2. Outline • Composition of soil organic carbon – isolating biologically important fractions • Methodology for quantifying C allocation to fractions • Why attempt to understand allocation to fractions? • Modelling soil carbon with RothC • Substitution of conceptual with measureable C pools in RothC • MIR prediction of soil carbon fractions CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  3. Crop residues on the soil surface (SPR) • Buried crop residues (>2 mm) (BPR) • Particulate organic matter (2 mm – 0.05 mm) (POC) • Humus (<0.05 mm) (HumC) Extent of decomposition increases Rate of decomposition decreases C/N/P ratio decreases (become nutrient rich) • Resistant organic matter (ROC) Dominated by charcoal with variable properties Composition of soil organic matter CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  4. Biologically significant soil organic fractions Particulate material (POC) Humus (HumC) Charcoal (ROC) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  5. Quadrat collection Surface plant residue carbon Soil sieved to >2mm Soil sieved to <2mm Na saturate, disperse, sieve <53 µm Density fractionation >53 µm fraction <53 µm fraction Buried plant residue carbon Density fractionation Humus + recalcitrant Particulate organic carbon HF treatment, UV-PO, & NMR Recalcitrant Charcoal C Quantifying SOC allocation of SOC to fractions Total soil organic carbon Humus = <53µm - Recalcitrant CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  6. 25 20 15 10 5 0 Variation in amount of C associated with soil organic fractions Surface plant residue C (SPR) Buried plant residue C (BPR) (Mg C/ha) Organic carbon in 0-10 cm layer Particulate organic carbon (POC) Humus C (HumC) Recalcitrant C (ROC - charcoal) Average for Hamilton (long term pasture) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  7. Variation in amount of C associated with soil organic fractions 30 SPR 25 BPR POC 20 HumC ROC 15 Organic C in 0-10 cm layer (Mg C/ha) 10 5 0 0P 1P 8P 11P 22P 32P W2PF Arboretum Pulse/wheat Strat (MedN) Strat (HighN) Canola/wheat Perm Pasture NoTill (MedN) NoTill (HighN) Pasture/wheat Hamilton Hart Yass Urrbrae Waikerie Pasture Cropped Pasture Mix Mix CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  8. Total soil organic C 30 Conversion to permanent pasture 25 20 Soil organic carbon (g C kg-1 soil) 15 10 5 10 y 18 y 0 10 20 30 50 0 40 70 60 15 33 43 Years Changes in total soil organic carbon with time Initiate wheat/fallow CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  9. Initiate wheat/fallow TOC 30 Humus C POC Conversion to permanent pasture 25 ROC 20 Soil organic carbon (g C kg-1 soil) 15 ~30% less humus C 10 5 10 y 18 y ~800% more POC 0 10 20 30 50 0 40 70 60 15 33 43 Years Importance of allocating C to soil organic fractions CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  10. Initiate wheat/fallow TOC Humus Conversion to wheat/fallow POC ROC 10 y 18 y 9 y 52 Vulnerability of soil carbon content to variations in management practices 30 25 Conversion to pasture 20 Soil organic carbon (g C kg-1 soil) 15 10 5 0 10 20 30 50 0 40 70 60 43 15 33 Years CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  11. 10 g Char-C kg-1soil 2.5 g Char-C kg-1soil Active C Active C Inert C Inert C Importance of quantifying allocation of C to soil organic fractions Soil 2 20 g SOC kg-1 soil Soil 1 20 g SOC kg-1 soil 25 25 20 20 15 Soil Organic Carbon (g C kg-1 soil) Soil Organic Carbon (g C kg-1 soil) 15 10 10 5 5 0 0 Time Time CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  12. Quadrat collection Surface plant residue carbon Soil sieved to >2mm Soil sieved to <2mm Na saturate, disperse, sieve <53 µm Density fractionation >53 µm fraction <53 µm fraction Buried plant residue carbon Density fractionation Humus + recalcitrant Particulate organic carbon HF treatment, UV-PO, & NMR Recalcitrant Charcoal C Summary SOC fractions Total soil organic carbon Humus = <53µm - Recalcitrant CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  13. DPM RPM CO2 Decomposition CO2 Decomposition BIO BIO HUM Decomposition HUM IOM Fire RothC Model (Version 26.3) Plant Inputs Original configuration – monthly time step CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  14. Roth C data requirements • Monthly climate data: rainfall (mm), open pan evaporation (mm), average monthly air temperature (°C) • Soil clay content (% soil OD mass) • Soil cover (vegetated or bare) • Monthly plant residue additions (t C ha-1) • Decomposability of plant residue additions • Monthly manure additions (t C ha-1) • Soil depth (cm) • Initial amount of C contained in each pool CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  15. RothC model structure – partitioning residue inputs into decomposable and resistant material • All plant material entering the soil is partitioned into DPM and RPM via DPM/RPM ratio CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  16. Values of k for each SOC fraction (y-1) BioF BioS DPM RPM Hum 0.66 0.66 10 0.15 0.02 RothC model structure – amount of each type of carbon decomposed • The amount of carbon associated with each pool that decomposes follows an exponential decay a = the rate modifying factor for temperature b = the plant retainment rate modifying factor c = the rate modifying factor for soil water k = the annual decomposition rate constant for a type of carbon t = 0.0833, since k is based on a yearly decomposition rate. CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  17. Plant retainment modifying factor (b) b = 0.6 if soil is vegetated b = 1.0 if soil is bare RothC model structure – calculation of rate constant modifying factors • Temperature modifying factor (a) tm= average monthly temperature CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  18. Saturation Upper Limit Water present in the soil (mm) Total porosity TSMD Lower Limit Dry RothC model structure – calculation of rate constant modifying factors • Soil water modifying factor – calculated based on top soil moisture deficit (TSMD) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  19. Calculation of accumulated TSMD over each time step under the constraint that the accumulated TSMD can only vary between 0 and MaxTSMD RothC model structure – calculation of rate constant modifying factors • Calculation of maximum TSMD CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  20. RothC model structure – calculation of rate constant modifying factors • Calculation of the rate modifying factor (c) if TSMDacc < 0.444 MaxTSMD then c=1.0 otherwise, 1.0 c 0.2 MaxTSMD 0.444 MaxTSMD CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  21. Values of k for each SOC fraction (y-1) BioF BioS DPM RPM Hum 0.66 0.66 10 0.15 0.02 RothC model structure – amount of each type of carbon decomposed • The amount of carbon associated with each pool that decomposes follows an exponential decay a = the rate modifying factor for temperature b = the plant retainment rate modifying factor c = the rate modifying factor for soil water k = the annual decomposition rate constant for a type of carbon t = 0.0833, since k is based on a yearly decomposition rate. CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  22. DPM RPM CO2 Decomposition CO2 Decomposition BIO BIO HUM Decomposition HUM IOM Fire RothC Model (Version 26.3) Plant Inputs CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  23. RothC model structure – partitioning of decomposition products • Fraction decomposing organic matter that goes to CO2, humus and biomass • Partitioning to CO2 is defined by clay content Biomass + Humus partitioning 46% Bio 54% Hum CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  24. RothC output under constant inputs and climate – to define equilibrium SOC CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  25. DPM RPM CO2 Decomposition CO2 Decomposition BIO BIO HUM Decomposition HUM IOM Fire Modelling the measurable Plant Inputs RPM = POC IOM = ROC (Charcoal C) HUM = TOC – (POC + ROC) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  26. Requirements for calibration CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  27. Calibration Sites Verification Sites Brigalow Tarlee 0 350 700 Kilometres Model calibration and verification sites CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  28. Brigalow calibration site: influence of modifying RPM decomposition constant (k) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  29. 60 50 40 Measured 40 30 Soil C (t/ha) Soil C (t/ha) 20 20 DPM 10 RPM 0 0 1970 1980 1990 2000 1988 1990 1992 1994 1996 1998 HUM Year Year IOM Modeled BIO Soil POC Salmon Gums - wheat/ 3 pasture Salmon Gums – wheat/wheat HUM 50 50 CHAR 40 40 30 30 TOC Soil C (t/ha) Soil C (t/ha) 20 20 10 10 0 0 1979 1983 1987 1991 1979 1983 1987 1991 Year Year Model Verification: (sites with archived soil samples) Wagga – wheat/pasture Tamworth – wheat/fallow CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  30. Is this result due poor model performance or poor pairing of the sites? Did the sites start off similar or were there significant initial differences in soil/plant/environmental properties? 50 Kindon - pasture 15 y Dunkerry South - crop 40 30 30 Soil C (t/ha) 20 20 Soil C (t/ha) 10 10 0 1986 1991 1996 2001 0 Year 1967 1977 1987 1997 DPM Year RPM Measured Modeled HUM IOM POC CHAR BIO HUM TOC Soil Model verification: (paired sites) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  31. Quadrat collection Surface plant residue carbon Soil sieved to >2mm Soil sieved to <2mm Na saturate, disperse, sieve <53 µm Density fractionation >53 µm fraction <53 µm fraction Buried plant residue carbon Density fractionation Humus + recalcitrant Particulate organic carbon HF treatment, UV-PO, & NMR Recalcitrant Charcoal C Quantifying SOC allocation of SOC to fractions Total soil organic carbon Humus = <53µm - Recalcitrant CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  32. Fourier Transform Infrared Spectrum 4 3 Intensity 2 1 5000 4500 4000 3500 3000 2500 2000 1500 1000 500 Frequency (cm-1) Predicting total organic carbon and its allocation to SOC fractions using MIR • Dependence on soil chemical properties • Prediction of allocation of carbon to fractions via calibration and PLS CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  33. Prediction of total organic carbon (TOC) 177 Australian soils (all states) from varying depths within the 0-50 cm layer n = 177 Range: 0.8 – 62.0 g C/kg R2 = 0.94 MIR predicted TOC (g C/kg soil) Measured TOC (g C/kg soil) Janik et al. 2007 Aust J Soil Res 45 73-81 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  34. Tasmanian soils project CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  35. MIR prediction of particulate organic carbon 141 Australian soils (all states) from varying depths within the 0-50 cm layer n = 141 Range: 0.2 – 16.8 g C/kg R2 = 0.71 MIR predicted POC (g C/kg soil) Variability in crop residue type exits Measured POC (g C/kg soil) Janik et al. 2007 Aust J Soil Res 45 73-81 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  36. MIR prediction of charcoal C 121 Australian soils (all states) from varying depths within the 0-50 cm layer n = 121 Range: 0.0 – 11.3 g C/kg R2 = 0.86 MIR predicted Char C (g/kg) Measured Char C (g/kg) Janik et al. 2007 Aust J Soil Res 45 73-81 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  37. Summary • Methodologies exist to quantify biologically significant pools of carbon • Understanding the dynamics of the pools allows accurate interpretation of potential changes • Substitution of measureable fractions for conceptual pools in models is possible • Rapid methods for predicting soil carbon allocation to pools exist CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  38. CSIRO Land and Water Jeff Baldock Research Scientist Phone: +61 8 8303 8537 Email: jeff.baldock@csiro.au Web:http://www.clw.csiro.au/staff/BaldockJ/ Acknowledgements Jan Skjemstad, Kris Broos, Evelyn Krull, Ryan Farquharson, Steve Szarvas, Leonie Spouncer, Athina Massis Thank you Contact UsPhone: 1300 363 400 or +61 3 9545 2176Email: Enquiries@csiro.au Web: www.csiro.au

  39. Measured 70 DPM 60 RPM HUM 50 IOM Modeled 0-30 cm Soil C (t/ha) 40 BIO Soil 30 POC 20 HUM CHAR 10 TOC 0 1982 1987 1992 1997 Year Model Calibration Brigalow South ws64 (RPM 0.15) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  40. Defining soil C dynamics at Roseworthy, SA under continuous wheat production Equilibrium conditions (model for 500 years) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  41. Changes in soil C for different levels of average grain yield CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  42. Changes in soil C for different levels of average grain yield Shift yield from 4 to 8 T grain/ha = 1.0 %C increase over 20 years Shift yield from 4 to 6 T grain/ha = 0.4 %C increase over 20 years CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  43. Composition of methodologically defined SOC fractions Particulate organic carbon (POC) • Fragments of plant residues >53 µm (living and dead) • Molecules sorbed to mineral particles >53 µm • Large pieces of charcoal Humus (HUM-C) • Fragments <53 µm • Molecules sorbed to particles <53 µm Recalcitrant (ROC) • Materials <53 µm that survive photo-oxidation • Dominated by material with a charcoal-like chemical structure • NMR to quantify char-C CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  44. TOC Inert OC W F 200 W F 35 35 35 35 35 P P F W 35 35 35 35 200 34 34 34 34 32 P P F W 34 34 34 33 33 33 33 P P F W 31 31 31 180 33 33 33 32 32 32 32 30 30 30 P P F W 32 32 31 31 31 31 Perm. Past. 29 29 29 180 30 30 30 30 Contour bank 160 29 29 29 29 W O O(g) F 27 27 27 28 W O O(g) F 26 26 26 26 26 26 160 27 27 27 27 W O O(g) F 25 25 25 25 25 25 140 26 W O O(g) F 24 24 24 24 24 24 25 B Pe W 23 23 23 23 23 23 ) 24 140 B Pe W 22 22 22 22 22 22 m ( 23 B Pe W 21 21 21 21 21 21 120 y 0.50 r 22 ) a W P P 20 20 20 20 20 20 m 2.40 d 21 ( n W P P 19 19 19 19 19 19 120 u y r 20 o W P P a 0.45 B 100 d 19 W W n 17 17 17 17 17 17 n r u 2.00 18 e 18 18 18 o W W P P P P P 16 16 16 16 16 16 18 18 18 h B 100 t 17 0.40 r W W P P P P P 15 15 15 15 15 15 n o r 80 16 N e W W P P P P P 14 14 14 14 14 14 h t 15 W W P P P P P r 13 13 13 1.60 13 13 13 o 0.35 14 80 N W W P P P P P 12 12 12 12 12 12 13 W W P P P P P 11 11 11 60 11 11 11 12 0.30 W O F 10 10 10 10 10 10 1.20 11 W O F 9 9 9 9 9 9 60 10 W O F 8 8 8 8 8 8 40 0.25 9 W O(g) F 7 7 7 7 7 7 0.80 8 W O(g) F 6 6 6 6 6 6 40 7 W O(g) F 5 5 5 5 5 5 0.20 20 6 W Pe 4 4 4 4 4 4 5 W Pe 3 3 3 0.40 3 3 3 4 0.15 20 Perm. Past 2 2 2 2 2 2 3 Perm. Past 1 1 1 1 1 1 0 0 0 2 0.10 0.00 1 0 0 25 50 75 100 0 25 50 75 100 Western Boundary (m) Western Boundary (m) Spatial variation in soil charcoal and carbon contents (0-10 cm layer) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  45. Predicting soil organic carbon contents • Clearing of Brigalow bushland CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  46. Options for increasing soil carbon content • Principal: increase inputs of carbon to the soil • Maximise capture of CO2 by photosynthesis and addition of carbon to soil • Options • Maximise water use efficiency (kg total dry matter/mm water) • Maximise stubble retention • Introduction of perennial vegetation • Alternative crops - lower harvest index • Alternative pasture species – increased below ground allocation • Addition of offsite organic materials – diversion of waste streams • Green manure crops – legume based for N supply CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  47. Options for increasing soil carbon content • Constraints • Soil type – protection and storage of carbon • Local environmental conditions • Dryland conditions – amount and distribution of rainfall • Irrigation – maximise water use efficiency • Economic considerations – alterations to existing systems must remain profitable • Social • Options need to be tailored to local conditions and farm business situation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  48. Defining inputs of organic carbon to soil – dryland conditions • Availability of water – amount and distribution of rainfall imposes constraints on productivity and options CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  49. Reactive surfaces Depth Bulk density Defining factors Potential sequestration Limiting factors Rainfall Temperature Light Attainable sequestration Soil management Plant species/crop selection Residue management Soil and nutrient losses Inefficient water and nutrient use Disrupted biology/disease Reducing factors Soil carbon sequestration situation Actual sequestration SOCactual SOCpotential SOCattainable Stable soil organic carbon (e.g. t1/2³ 10 years) Evaluating potential C sequestration in soil Optimise input and reduce losses Add external sources of carbon CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

  50. $$ for C sequestration – fact or fiction • There is no doubt that soils could hold more carbon • Challenge – increase soil C while maintaining economic viability • Options • Perennial vegetation • Regions with summer rainfall • Portions of paddocks that give negative returns • Reduce stocking, rotational grazing, green manure • Optimise farm management to achieve 100% of water limited potential yield • External sources of carbon • Under current C trading prices • Difficult to justify managing for soil C on the basis of C trading alone • Do it for all the other benefits enhanced soil carbon gives CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008

More Related