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Soil organic carbon management for
 global benefits : a review for STAP
   Gerard Govers, Roel Merckx, Kristof
      Van Oost, Bas van Wesemael
This presentation
• Some important principles and numbers
• Some ideas/visions on SOC management and
  SOC research
  – Maybe somewhat provocative from time to time
  – Open for discussion
How much SOC is there ?
A lot: about three times as much C in
   the soil than in the atmosphere
                              Source      0-1 m     0-2 m
             Batjes (1996)                1462-   2376-2456
                                          1548
             Kasting (1998)               1580
             Robert (2001)                1500      2456
             Jobbagy and Jackson (2000)   1502      1993
             Post et al. (1982)           1395
             Hiederer and Köchyl (2012)   1417




  • Topsoils contain 1400-1500 Pg (or Gt, billions of tonnes) of SOC
  • There is an additional 1000 Pg stored in deeper soil layers
What determines the amount of SOC
 in a soil : the kitchen sink analogy




 http://hotfile.wordpress.com/2008/10/09/mccain-and-palin-launch-kitchen-sink-strategy/
What happens if we vary (i) water input through
the tap and/or water evacuation (by opening or
              closing the drain) ?


           a                 b                c
Soil organic carbon is basically the same thing: just
 think of the tap discharge by C input rate and think of
the drain discharge as the respiration rate i.e the rate at
       which it is consumed and converted to CO2


              a                     b                     c
  I                     I                     I




                  R                 R                         R
How realistic is it to expect benefits
      from SOC management ?
• SOC reservoir is quite responsive to
  perturbance /management over timescales of
  decennia
Disturbances may be natural of
            human-induced
• Climate change:
  – warming increases respiration rates: SOC
  – Warming and atmosphering CO2 stimulate plant
    growth : SOC
• Disturbance by tillage: increases respiration
  rates: SOC
• Harvesting: reduces input: SOC
• Land use change: SOC or SOC
What would happen if we would be
   able to increase inputs by 1 % ?
• We would be able to store 0.5 Pg/y for a
  period of 30 yrs
• Human emissions: 9 Pg/yr
GEF focal areas
•   Biodiversity
•   Climate change
•   Land degradation
•   (International waters)
•   (Persistent organic pollutants)
Climate change
• Human impact = undeniable
• Historical release of SOC due to land use
  change has strongly contributed to warming
• Future of SOC stocks is unclear
  – Increased productivity of the biosphere may
    increase them: tap discharge increases
  – Increased temperature and reduction of soil
    moisture may decrease them: drain discharge
    increases
Final result
Things may even be worse




                   Falloon, 2011
Can management, within a given land
     use, make a difference ?
• Initial estimates: up to 1Pg C/y may be stored
  by implementing adequate land management
Is this a lot ?
• Yes, it is : if you would like to store that on
  cropland alone you can calculate the
  equivalent C sequestration rate.
   – We have about 15 million km² or 1.5 billion ha of
     cropland globally
   – Thus, you would need to sequester ca. 0.6 Mg
     C/(ha y)
What do numbers tell us ?
•   Conversion to no-tillage
•   Agroforestry
•   Grassland
•   Forests
•   Organic agriculture
No-tillage




•Temperate arable land: 0-1 Mg C/(ha yr), generally < 0.3
Mg C/(ha yr) but recent regional study found no
significant effects
•Tropical arable land: less data, 0.3-0.8 Mg C/(ha yr)
Agroforestry




0-1 Mg C/(ha yr), but many studies did not find significant
effects, effects sometimes overstated in literature, no
accounting for land use effects
Forests




Management may make a difference: potential
        effect is largely unknown
Grasslands




Ca. 0.3 Mg C/(ha yr), but very variable
Organic agriculture




•Reduces, on average yields (and therefore inputs)
•Significant gains in SOC are therefore unlikely, unless
respiration rates are decreased
What do numbers tell us ?
• Conversion to no-tillage
   – Temperate arable land: 0-1 Mg C/(ha yr), generally < 0.3 Mg C/(ha yr)
   – Tropical arable land: less data, 0.3-0.8 Mg C/(ha yr)
• Agroforestry
   – 0-1 Mg C/(ha yr), but many studies did not find significant effects,
     effects sometimes overstated in literature, no accounting for land use
     effects
• Grassland
   – Ca. 0.3 Mg C/(ha yr), but very variable
• Forests
   – Management may make a difference: potential effect is largely
     unknown
• Organic agriculture
   – Reduces, on average yields (and therefore inputs)
   – Significant gains in SOC are therefore unlikely, unless respiration rates
     are decreased
Also, we should be cautious with the
           data we have
                        response ratio vs depth
          3


      2.5


          2


      1.5


          1


      0.5


          0
    -10       10   30      50     70     90       110   130   150

 Response ratio (depth integrated SOC stock in alternatively managed or
 converted grassland vs. tradionally managed grassland) vs. sampling depth as
 calculated from the data compiled by (Conant et al., 2001). Note that the
 response ratio generally decreases with increasing sampling depth, an
 observation also made by (Manley et al., 2005)
Land degradation
• Consists of a complex interplay of different
  processes
  – Wind and water erosion
  – Compaction
  – Salinisation
• What will happen with SOC stocks when we
  reduce land degradation
Erosion : 4 subprocesses

What happens with exported C ?
                                       What happens at depositional sites ?




                                                    What happens at eroding sites ?


What happens during mobilisation and transport ?
Erosion is a small source of C for the soil
  (sink for the atmosphere, Van Oost et
     al., Science, 2007): why is that ?
• SOC is dynamically replaced at eroding sites
• Most of the SOC that is eroded is stored for
  longer time spans in depositional
  environments
• Erosion is not a major cause of SOC loss
Erosion also causes detrimental nutrient
losses, especially in low input agricultural areas




                                    Quinton et al., 2010
Other soil degradation processes
• General principle: if degration decreases
  primary productivity (plant growth) it will lead
  to a SOC loss
However, reclamation of degraded
     land is still (very) beneficial
• On degraded land, dynamic replacement is
  less important or even non-existing
• In strongly degraded environments erosion
  may therefore indeed be a source of C to the
  atmosphere, not a sink
SOC management: sparing or sharing ?




                     Phalan et al., 2011
Sparing vs. sharing
Sparing vs. sharing
                  SOC
What is the impact on SOC ?
• Sparing may be advantageous:
  – Non-disturbed biomes are high in SOC
  – Intensive agriculture can provide more C input into
    the soil, thereby maintaining SOC stocks (if properly
    managed)
  – Benefits of sparing will depend on species dynamics
    and type of wildlife-friendly farming adapted
  – Care should be taken in evaluating low-input
    agricultural systems: effects on yields should be
    accounted for
Are there other benefits ? SOC and soil
                health
• Biodiversity: not discussed here
• Soil quality
• Soil productivity
Soil quality: soil structure




        Jordan et al., 2010
Soil erosion
Soil quality: erosion




                Poesen and Torri, 1997
Crop yields: often a positive
relationship betweeen SOC and yield is
                 found




                               Lal, 2010
However….
• Relationship is not always causal: increased
  yield is often due to co-variation in nutrients
  available to plants


                                         Chemical fertilizers

                                           Manure

                                          Reference




                                        Edmeades, 2003
Do not reverse causality




SOC               YIELDS
Overall
• Conclusive evidence regarding positive causal
  effect of SOC on soil structure, soil life, soil
  erodibility
• Effects on yields is inconclusive: reported
  relationships are often to a large extent
  explainable by co-variations and causal effect
  may even be inverse
Where does all this this leave us ?
   Towards a vision on SOC
 management within the GEF
           context
SOC management requires an
 integrated, landscape scale approach
• Opting for low-intensity land use should
  account for disturbance of ‘virgin’ SOC stocks
  over larger areas (that does not mean that it
  always has to be negative !)
• Same holds for FYM-based systems: manure
  has to come from somewhere
• Other landscape functions (water
  provision, tourism, biodiversity) need to be
  accounted for
It is easier (and probably cheaper) to
         preserve than to restore.
• Preserving a stock has immediate benefits
• Managed systems only rarely meet SOC stocks
  found under undisturbed natural vegetation
  (exception: specific cases of grassland
  afforestation)
• Simple estimates: stopping deforestation is
  much cheaper than increasing stocks on
  arable land
Improving crop yields and restoring
soil fertility is a key component of SOC
                management
• Higher yields means that less land is necessary
  (although true sparing may demand further
  encouragement)
• Higher yields have a positive effect on SOC
  stocks on cropland
Target soils and environments correctly
What was happening ?
Paramo afforestation dramatically
      reduces water yield
Paramo afforestation reduces SOC
    stocks (Farley et al., 2004)
More gain is to be expected from the
afforestation of cropland (SOC stocks are
       low), Laganière et al., 2010
Afforesting, degraded, dry lands will
 have undoubtedly positive effects
Afforesting, degraded, dry lands will
 have undoubtedly positive effects
Set goals realistically
• The response time of SOC=decades
• The sequestration rates possible under
  alternative management systems may be
  lower than initially proposed
• Account for negative externalities when they
  are likely to occur (water yield, land
  use, biodiversity…)
Generate co-benefits
• SOC sequestration is not a commercially viable
  operation at present (one would need prices
  of ca. $ 100 USD/(ton C) for the conversion of
  cropland in developing countries to see
  significant effects.
• Co-benefits may be reduced labour, increased
  yields, biodiversity preservation, increased soil
  quality
Assess socio-economic conditions that
 may affect potential success of SOC
        management projects
• Do the farmers-land managers have access to
  all relevant information ?
• Are the relevant skills present ?
Assess the socio-economic implications
    (see also Stringer et al., 2012)
• What is the effect of pine forests on local
  communities in the Paramo ?
   – Where does the income generated by the wood go ?
   – Are they able to deal with reduced water yields ?
   – What is replacing their traditional activities in the
     Paramo ?
   – What will be the effect on the gender distribution of
     the workload ?
   – How will the arrival of the Iphone 12 in 2020 affect
     these results ?
Provide sufficient support
• SOC projects are long-term !
• Benefits are not immediately visible to the
  local population
Account for biophysical and socio-
         economic risks
Where is science in all this ?
• Do we know enough or do we need more ?
Over recent decennia we have gained
 much more insight in SOC dynamics
We often work with SOC pools
• SOC pools are reservoirs of SOC that have
  distinct physico-chemical characteristics
• Literature has convincingly shown that
  understanding and describing SOC dynamics is
  far more efficient when different SOC pools
  are considered
In some cases: clear implications for
           management

Chivenge et al., 2007, long-term study
on sandy and clayey soils
          - management should try to
increase SOC input on sandy soils
(coarse sand SOC most responsive and
important pool)
          - management should try to
reduce soil disturbance on clayey soils
to preserve fine sand (fine sand SOC in
aggregates is most important pool)
However, in general…
• Yet, while scientifically extremely rewarding, it
  remains unlikely that increased understanding
  will in the short run lead to a drastically
  improved predictive capacity or improved
  policy guidelines, reaching beyond what
  already can be achieved with the
  semi-empirical approach taken based on size
  and density separates in combination with
  SOM models en vogue. (R. Merckx, 2012)
Why is that ?
• The curse of environmental sciences:
  – Systems that are studied are intrinsically
    complicated, controlled by many factors and
    coupling is often non-linear and affected by
    feedbacks
  – Such systems may be better described with more
    complex models, but that does not lead to better
    predictions
Where do we need scientific progress
           the most ?
• Concept of SOC saturation appears critical
• How do we monitor SOC stocks ?
• What will be the effect of climate change on
  SOC stocks ?
Concept of soil saturation appears to
             be critical




                            Angers et al., 2011
Climatic effects on SOC stocks are still very
                 uncertain

• Makes it very difficult to assess future stocks
• Correctly understanding climate effects is also
  important if we want to disentangle effects of
  different drivers (climate
  (temperature, moisture, CO2) from
  management effects
The land is at present a
  strong sink (Le Quéré et
al., 2009): 30% of emissions
      absorbed on land
The world is getting greener




                    www.zef.de
How to assess SOC stocks ?
• Role of monitoring vs. modelling
• Role of high-throughput measurement
  techniques
0.1% of C = ca. 4 Mg C/ha




                      Saby et al., 2008
Conclusions
• SOC management for global benefits is
  important.
• SOC management needs careful
  considerations (spare or share…)
• SOC management could benefit tremendously
  from scientific progress in a number of key
  areas

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Gerard GOVERS, Roel MERCKX, Kristof VAN OOST, Bas VAN WESEMAEL "Soil organic carbon management for global benefits – A review for STAP"

  • 1. Soil organic carbon management for global benefits : a review for STAP Gerard Govers, Roel Merckx, Kristof Van Oost, Bas van Wesemael
  • 2. This presentation • Some important principles and numbers • Some ideas/visions on SOC management and SOC research – Maybe somewhat provocative from time to time – Open for discussion
  • 3. How much SOC is there ? A lot: about three times as much C in the soil than in the atmosphere Source 0-1 m 0-2 m Batjes (1996) 1462- 2376-2456 1548 Kasting (1998) 1580 Robert (2001) 1500 2456 Jobbagy and Jackson (2000) 1502 1993 Post et al. (1982) 1395 Hiederer and Köchyl (2012) 1417 • Topsoils contain 1400-1500 Pg (or Gt, billions of tonnes) of SOC • There is an additional 1000 Pg stored in deeper soil layers
  • 4. What determines the amount of SOC in a soil : the kitchen sink analogy http://hotfile.wordpress.com/2008/10/09/mccain-and-palin-launch-kitchen-sink-strategy/
  • 5. What happens if we vary (i) water input through the tap and/or water evacuation (by opening or closing the drain) ? a b c
  • 6. Soil organic carbon is basically the same thing: just think of the tap discharge by C input rate and think of the drain discharge as the respiration rate i.e the rate at which it is consumed and converted to CO2 a b c I I I R R R
  • 7. How realistic is it to expect benefits from SOC management ? • SOC reservoir is quite responsive to perturbance /management over timescales of decennia
  • 8. Disturbances may be natural of human-induced • Climate change: – warming increases respiration rates: SOC – Warming and atmosphering CO2 stimulate plant growth : SOC • Disturbance by tillage: increases respiration rates: SOC • Harvesting: reduces input: SOC • Land use change: SOC or SOC
  • 9. What would happen if we would be able to increase inputs by 1 % ? • We would be able to store 0.5 Pg/y for a period of 30 yrs • Human emissions: 9 Pg/yr
  • 10. GEF focal areas • Biodiversity • Climate change • Land degradation • (International waters) • (Persistent organic pollutants)
  • 11. Climate change • Human impact = undeniable • Historical release of SOC due to land use change has strongly contributed to warming • Future of SOC stocks is unclear – Increased productivity of the biosphere may increase them: tap discharge increases – Increased temperature and reduction of soil moisture may decrease them: drain discharge increases
  • 13. Things may even be worse Falloon, 2011
  • 14. Can management, within a given land use, make a difference ? • Initial estimates: up to 1Pg C/y may be stored by implementing adequate land management
  • 15. Is this a lot ? • Yes, it is : if you would like to store that on cropland alone you can calculate the equivalent C sequestration rate. – We have about 15 million km² or 1.5 billion ha of cropland globally – Thus, you would need to sequester ca. 0.6 Mg C/(ha y)
  • 16. What do numbers tell us ? • Conversion to no-tillage • Agroforestry • Grassland • Forests • Organic agriculture
  • 17. No-tillage •Temperate arable land: 0-1 Mg C/(ha yr), generally < 0.3 Mg C/(ha yr) but recent regional study found no significant effects •Tropical arable land: less data, 0.3-0.8 Mg C/(ha yr)
  • 18. Agroforestry 0-1 Mg C/(ha yr), but many studies did not find significant effects, effects sometimes overstated in literature, no accounting for land use effects
  • 19. Forests Management may make a difference: potential effect is largely unknown
  • 20. Grasslands Ca. 0.3 Mg C/(ha yr), but very variable
  • 21. Organic agriculture •Reduces, on average yields (and therefore inputs) •Significant gains in SOC are therefore unlikely, unless respiration rates are decreased
  • 22. What do numbers tell us ? • Conversion to no-tillage – Temperate arable land: 0-1 Mg C/(ha yr), generally < 0.3 Mg C/(ha yr) – Tropical arable land: less data, 0.3-0.8 Mg C/(ha yr) • Agroforestry – 0-1 Mg C/(ha yr), but many studies did not find significant effects, effects sometimes overstated in literature, no accounting for land use effects • Grassland – Ca. 0.3 Mg C/(ha yr), but very variable • Forests – Management may make a difference: potential effect is largely unknown • Organic agriculture – Reduces, on average yields (and therefore inputs) – Significant gains in SOC are therefore unlikely, unless respiration rates are decreased
  • 23. Also, we should be cautious with the data we have response ratio vs depth 3 2.5 2 1.5 1 0.5 0 -10 10 30 50 70 90 110 130 150 Response ratio (depth integrated SOC stock in alternatively managed or converted grassland vs. tradionally managed grassland) vs. sampling depth as calculated from the data compiled by (Conant et al., 2001). Note that the response ratio generally decreases with increasing sampling depth, an observation also made by (Manley et al., 2005)
  • 24. Land degradation • Consists of a complex interplay of different processes – Wind and water erosion – Compaction – Salinisation • What will happen with SOC stocks when we reduce land degradation
  • 25. Erosion : 4 subprocesses What happens with exported C ? What happens at depositional sites ? What happens at eroding sites ? What happens during mobilisation and transport ?
  • 26. Erosion is a small source of C for the soil (sink for the atmosphere, Van Oost et al., Science, 2007): why is that ? • SOC is dynamically replaced at eroding sites • Most of the SOC that is eroded is stored for longer time spans in depositional environments • Erosion is not a major cause of SOC loss
  • 27. Erosion also causes detrimental nutrient losses, especially in low input agricultural areas Quinton et al., 2010
  • 28. Other soil degradation processes • General principle: if degration decreases primary productivity (plant growth) it will lead to a SOC loss
  • 29. However, reclamation of degraded land is still (very) beneficial • On degraded land, dynamic replacement is less important or even non-existing • In strongly degraded environments erosion may therefore indeed be a source of C to the atmosphere, not a sink
  • 30. SOC management: sparing or sharing ? Phalan et al., 2011
  • 33. What is the impact on SOC ? • Sparing may be advantageous: – Non-disturbed biomes are high in SOC – Intensive agriculture can provide more C input into the soil, thereby maintaining SOC stocks (if properly managed) – Benefits of sparing will depend on species dynamics and type of wildlife-friendly farming adapted – Care should be taken in evaluating low-input agricultural systems: effects on yields should be accounted for
  • 34. Are there other benefits ? SOC and soil health • Biodiversity: not discussed here • Soil quality • Soil productivity
  • 35. Soil quality: soil structure Jordan et al., 2010
  • 37. Soil quality: erosion Poesen and Torri, 1997
  • 38. Crop yields: often a positive relationship betweeen SOC and yield is found Lal, 2010
  • 39. However…. • Relationship is not always causal: increased yield is often due to co-variation in nutrients available to plants Chemical fertilizers Manure Reference Edmeades, 2003
  • 40. Do not reverse causality SOC YIELDS
  • 41. Overall • Conclusive evidence regarding positive causal effect of SOC on soil structure, soil life, soil erodibility • Effects on yields is inconclusive: reported relationships are often to a large extent explainable by co-variations and causal effect may even be inverse
  • 42. Where does all this this leave us ? Towards a vision on SOC management within the GEF context
  • 43. SOC management requires an integrated, landscape scale approach • Opting for low-intensity land use should account for disturbance of ‘virgin’ SOC stocks over larger areas (that does not mean that it always has to be negative !) • Same holds for FYM-based systems: manure has to come from somewhere • Other landscape functions (water provision, tourism, biodiversity) need to be accounted for
  • 44. It is easier (and probably cheaper) to preserve than to restore. • Preserving a stock has immediate benefits • Managed systems only rarely meet SOC stocks found under undisturbed natural vegetation (exception: specific cases of grassland afforestation) • Simple estimates: stopping deforestation is much cheaper than increasing stocks on arable land
  • 45. Improving crop yields and restoring soil fertility is a key component of SOC management • Higher yields means that less land is necessary (although true sparing may demand further encouragement) • Higher yields have a positive effect on SOC stocks on cropland
  • 46. Target soils and environments correctly
  • 48. Paramo afforestation dramatically reduces water yield
  • 49. Paramo afforestation reduces SOC stocks (Farley et al., 2004)
  • 50. More gain is to be expected from the afforestation of cropland (SOC stocks are low), Laganière et al., 2010
  • 51. Afforesting, degraded, dry lands will have undoubtedly positive effects
  • 52. Afforesting, degraded, dry lands will have undoubtedly positive effects
  • 53. Set goals realistically • The response time of SOC=decades • The sequestration rates possible under alternative management systems may be lower than initially proposed • Account for negative externalities when they are likely to occur (water yield, land use, biodiversity…)
  • 54. Generate co-benefits • SOC sequestration is not a commercially viable operation at present (one would need prices of ca. $ 100 USD/(ton C) for the conversion of cropland in developing countries to see significant effects. • Co-benefits may be reduced labour, increased yields, biodiversity preservation, increased soil quality
  • 55. Assess socio-economic conditions that may affect potential success of SOC management projects • Do the farmers-land managers have access to all relevant information ? • Are the relevant skills present ?
  • 56. Assess the socio-economic implications (see also Stringer et al., 2012) • What is the effect of pine forests on local communities in the Paramo ? – Where does the income generated by the wood go ? – Are they able to deal with reduced water yields ? – What is replacing their traditional activities in the Paramo ? – What will be the effect on the gender distribution of the workload ? – How will the arrival of the Iphone 12 in 2020 affect these results ?
  • 57. Provide sufficient support • SOC projects are long-term ! • Benefits are not immediately visible to the local population
  • 58. Account for biophysical and socio- economic risks
  • 59. Where is science in all this ? • Do we know enough or do we need more ?
  • 60. Over recent decennia we have gained much more insight in SOC dynamics
  • 61. We often work with SOC pools • SOC pools are reservoirs of SOC that have distinct physico-chemical characteristics • Literature has convincingly shown that understanding and describing SOC dynamics is far more efficient when different SOC pools are considered
  • 62. In some cases: clear implications for management Chivenge et al., 2007, long-term study on sandy and clayey soils - management should try to increase SOC input on sandy soils (coarse sand SOC most responsive and important pool) - management should try to reduce soil disturbance on clayey soils to preserve fine sand (fine sand SOC in aggregates is most important pool)
  • 63. However, in general… • Yet, while scientifically extremely rewarding, it remains unlikely that increased understanding will in the short run lead to a drastically improved predictive capacity or improved policy guidelines, reaching beyond what already can be achieved with the semi-empirical approach taken based on size and density separates in combination with SOM models en vogue. (R. Merckx, 2012)
  • 64. Why is that ? • The curse of environmental sciences: – Systems that are studied are intrinsically complicated, controlled by many factors and coupling is often non-linear and affected by feedbacks – Such systems may be better described with more complex models, but that does not lead to better predictions
  • 65. Where do we need scientific progress the most ? • Concept of SOC saturation appears critical • How do we monitor SOC stocks ? • What will be the effect of climate change on SOC stocks ?
  • 66. Concept of soil saturation appears to be critical Angers et al., 2011
  • 67. Climatic effects on SOC stocks are still very uncertain • Makes it very difficult to assess future stocks • Correctly understanding climate effects is also important if we want to disentangle effects of different drivers (climate (temperature, moisture, CO2) from management effects
  • 68. The land is at present a strong sink (Le Quéré et al., 2009): 30% of emissions absorbed on land
  • 69. The world is getting greener www.zef.de
  • 70. How to assess SOC stocks ? • Role of monitoring vs. modelling • Role of high-throughput measurement techniques
  • 71. 0.1% of C = ca. 4 Mg C/ha Saby et al., 2008
  • 72. Conclusions • SOC management for global benefits is important. • SOC management needs careful considerations (spare or share…) • SOC management could benefit tremendously from scientific progress in a number of key areas