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Calculation of attainable SOC stocks and mineralization rates.
We obtained the annual SOC stock from the model for 86 years (simulation between 2014 and 2100). As 2000–2013
climate data was used, this estimation considers climate stability and does not take the role of climate change into
account.
RothC is a multiple pool model but the overall shape of the dynamic SOC curves for each pool is approximately
exponential. For grassland and agricultural classes, this approximation is a good fit for all periods simulated because the
C input from residues is constant, but for forest classes it is only true after maturity (i.e. when annual C residues are
constant).
In the transition period, dynamic SOC curves are approximately a fourth-degree polynomial. For grasslands, croplands
and mature forests, we used a simple two-parameter mass balance model for SOC dynamics to fit the annual SOC stocks
obtained by the application of RothC for each land class in each UHTU. The SOC balance is the difference between C
input and mineralization, described by
dSOC = K – α SOC
dt
where SOC is the SOC stock (t C/ha) at time t, K is the C input to soil at time t, and α is the C mineralization rate. C input
(parameter K) is a function of the LU. Therefore, K and α are time-invariant and vary with location (i.e. UHTU) and LU
class.
SOC MODELLING
Integrating between 0 and t, we obtain
SOCt = K (1 – eαt) + e –αt SOC0
α
SOC is limited by an upper bound, i.e. SOC reaches a maximum attainable equilibrium,
which is given by K/α.
The curve fitting procedure thus provides attainable SOC stocks and mineralization rates that are LU and site-specific

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SOC MODELLING.pptx

  • 1. Calculation of attainable SOC stocks and mineralization rates. We obtained the annual SOC stock from the model for 86 years (simulation between 2014 and 2100). As 2000–2013 climate data was used, this estimation considers climate stability and does not take the role of climate change into account. RothC is a multiple pool model but the overall shape of the dynamic SOC curves for each pool is approximately exponential. For grassland and agricultural classes, this approximation is a good fit for all periods simulated because the C input from residues is constant, but for forest classes it is only true after maturity (i.e. when annual C residues are constant). In the transition period, dynamic SOC curves are approximately a fourth-degree polynomial. For grasslands, croplands and mature forests, we used a simple two-parameter mass balance model for SOC dynamics to fit the annual SOC stocks obtained by the application of RothC for each land class in each UHTU. The SOC balance is the difference between C input and mineralization, described by dSOC = K – α SOC dt where SOC is the SOC stock (t C/ha) at time t, K is the C input to soil at time t, and α is the C mineralization rate. C input (parameter K) is a function of the LU. Therefore, K and α are time-invariant and vary with location (i.e. UHTU) and LU class. SOC MODELLING
  • 2.
  • 3.
  • 4. Integrating between 0 and t, we obtain SOCt = K (1 – eαt) + e –αt SOC0 α SOC is limited by an upper bound, i.e. SOC reaches a maximum attainable equilibrium, which is given by K/α. The curve fitting procedure thus provides attainable SOC stocks and mineralization rates that are LU and site-specific