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World’s Soil Resources

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where the drainage in the 1960’s of areas previously classified as peatland caused the SOC content to fall to 7.5<br />

percent (Panagos et al., 2013). Without further adjustments of SOC stock estimates to take account of local<br />

changes in the factors that influence SOC, no clear timestamp can be attached to the global estimates. This<br />

lack of a clear timestamp of SOC stocks is of consequence when estimating temporal changes in SOC stocks.<br />

Estimates of changes in SOC stock therefore concentrate on modelling variations in SOC from changes in land<br />

use and cover.<br />

6.2.3 | Spatial distribution of SOC<br />

Different methods of combining point data from soil profiles with soil spatial layers and ancillary ecological<br />

data can be applied to derive spatial estimates of SOC stocks (Kern, 1994). SOC density and stock estimates<br />

from soil profile data were combined with spatial data of major ecosystems by Post et al. (1982). The total SOC<br />

stocks for all life zones to a depth of 1 m was 1 395 Pg of SOC. A combination of soil profile data with ancillary<br />

information on climate, vegetation and land use was used by Jobbágy and Jackson (2000) to estimate SOC<br />

stocks in 11 biomes. The estimates for the biomes were further divided into increments of 1 m soil depth and<br />

of 20 cm for the first meter. The distribution of SOC stocks by ecological regions has also been presented, for<br />

example by Amundson (2001), who used life zones as the study unit. Eglin et al. (2010) used the SOC stock<br />

estimates to a depth of 3 m from Jobbágy and Jackson (2000) and modified SOC stocks in permafrost areas<br />

(Tarnocai et al., 2009). These SOC stock estimates were combined with estimates provided by the IPCC (IPCC,<br />

2000) of C in vegetation to derive estimates of C in soil and biomass for 10 biomes, with an explicit class for<br />

peatlands. A step towards adding a temporal dimension to spatial SOC stock estimates, assessing historical<br />

and future trends, was made possible by the availability of SOC models. Combining the models with historic<br />

land use and climate data has allowed estimation of SOC stocks with a timestamp and with regional variations<br />

(Eglin et al., 2010; Schmidt et al., 2011).<br />

Carré et al. (2010) produced estimates of SOC stocks and density using climate data, IPCC methodology and<br />

the Harmonized World <strong>Soil</strong> Database. The results by IPCC Climate Region are presented in Table 6.1.<br />

Status of the <strong>World’s</strong> <strong>Soil</strong> <strong>Resources</strong> | Main Report Global soil status, processes and trends<br />

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