Environmental relevance
The SCM view of the nature of soil organic matter—which excludes any secondary synthesis of ‘humic substances’—has implications for a range of disciplines that build on the science of organic matter properties and changes in soil (Fig. 1). This is all the more important as the ‘humic substances’ concept is very widely adopted outside the soil sciences, with the majority of publications focusing on ‘humic substances’ published in journals that do not explicitly cover soil science.
Soil carbon modelling
Soils contain more organic carbon than the atmosphere and vegetation combined1 and predictions of soil organic matter dynamics could there-fore greatly influence forecasts of global climate change. Major soil carbon models such as Century54 or RothC55 are built on the premise that soil organic matter can be divided into pools that have different turnover times. None of these models explicitly represents the characteristic pro-cesses of carbon transformation detailed in the SCM, such as adsorption and protection, desorption, and microbial activity. Although carbon movement between pools and their decomposition rates are modified by temperature, texture and moisture, the default turnover rates asso-ciated with individual carbon pools are justified by the combined influ-ence of physical protection and an inferred resistance to decomposition that is dependent on substrate quality (‘quality’ is here used in the sense of molecular composition of the organic matter). Particularly for the ‘slow’ and ‘passive’ pools, this inherent resistance to decomposition (recalcitrance) has been understood to be the result of ‘humification’, with the RothC model explicitly including ‘humus’ fractions55. Lack of mech-anistic representation of the decomposition process produces disagree-ment among models56 and between model predictions and observational data
The shortcomings become apparent when these models are applied to predict the global warming feedback of soil organic carbon miner-alization. Rising temperatures increase microbial activity and a warm-ing atmosphere may therefore lead to greater mineralization of soil organic carbon59. The resultant carbon dioxide emissions would then accelerate the greenhouse effect and thereby increase global temper-ature. Soil organic matter pools with slower turnover are thought to respond more sensitively to climate warming than those with fast turn over59–61. The underlying, so-called carbon–quality–temperature theory (CQT theory62) combines classical ‘humification’ theory, that is, the assumption that decomposition creates complex, recalcitrant compounds, with the Arrhenius theory that chemical reactions are faster at higher tem-peratures63. According to CQT theory, the decomposition of a complex substrate requires more enzymatic reactions and a higher total activation energy than a reaction metabolizing a simple carbon substrate, and as a result, would be more sensitive to rising temperatures than the decom-position of a simple carbon substrate. The CQT theory loses much of its explanatory potential for the carbon pools with slow turnover if the decomposition of organic matter is not creating complex and recalcitrant compounds.
Different organic compounds entering the soil have highly varying composition 64 and in isolation (for example, fresh litter) have differ-ent turnover and hence temperature responses as a function of their composition60 . However, this variation is so heavily influenced by environmental and biotic factors after they enter the soil ecosystem that the concept of relying on quality-dependent temperature responses is, in our opinion, obsolete. We propose that future research should concentrate to a much greater extent on the causes of any observed substrate prefer-ences, such as the absence of a decomposer with a matching catabolic toolbox or the lack of a critical resource for the decomposer.