Abstract

Soil microbial C:N:P stoichiometry and microbial maintenance respiration (i.e. metabolic quotient, qCO2) were monitored along a nutrient gradient in soils from a 52-year space-for-time chronosequence of reclaimed agricultural land after brown-coal mining. Land reclamation produced loess soils of initially low (0.2%) SOC. Consecutive agricultural land management led to a gradual recovery of SOC contents. Our data revealed sudden shifts in microbial stoichiometry and metabolic quotient with increasing SOC at a critical value of 1% SOC. As SOC increased, accrual rate of C into microbial biomass decreased, whereas microbial N increased. Simultaneously, metabolic quotient strongly decreased with increasing SOC until the same critical value of 1% SOC and remained at a constant low thereafter. The microbial fractions of the soil in samples containing < 1% SOC were out of stoichiometric equilibrium and were inefficient at immobilising C due to high maintenance respiration. Increasing SOC above the threshold value shifted the soil microbes towards a new equilibrium where N became growth limiting, leading to a more efficient acquisition of C. The shift in microbial N accrual was preluded by high variation in microbial biomass N in soils containing 0.5–0.9% SOC indicative of a regime shift between microbial stoichiometric equilibria. Our data may help in establishing a quantitative framework for SOC targets that, along with agricultural intensification, may better support feedback mechanisms for a sustainable accrual of C in soils.

Highlights

  • Chronosequences of post-mining areas are ideal model systems to study soil processes related to the formation of soil organic matter (SOM) over time, because these soils, typically being reclaimed over decades from the same carbon-poor overburden substrates, form a succession of soil development with almost identical starting conditions and well-defined dates of origin (Bartuska and Frouz 2015; Dworschak and Rose 2014; Walker et al 2010)

  • After 10 years, the accumulation of soil organic C (SOC) and microbial biomass ceased in the arable soils, but continued to increase in the margin soils (Fig. S1a-e)

  • Plotting the ratios of soil C:N versus microbial biomass C:N (MB-C:N) with the soil C:N calculated either from SOC and total N (SOC:Ntot) or from the extractable C and N (Cext:) (Fig. 1a, b) showed slopes strongly deviating from the 1:1 line

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Summary

Introduction

Chronosequences of post-mining areas are ideal model systems to study soil processes related to the formation of soil organic matter (SOM) over time, because these soils, typically being reclaimed over decades from the same carbon-poor overburden substrates, form a succession of soil development with almost identical starting conditions and well-defined dates of origin (Bartuska and Frouz 2015; Dworschak and Rose 2014; Walker et al 2010). Soil microorganisms can respond to such a stoichiometric imbalance by either adjusting their stoichiometry to match the resource (plasticity) or by maintaining a fixed stoichiometry (homeostasis) (Spohn 2016). Both require adaptations on the individual level, e.g. by expelling or storing nutrients (Manzoni and Porporato 2009) and adjusting exoenzyme production (Allison and Vitousek 2005; Sinsabaugh et al 2009), and/or on the community level through shifts in community composition to species that are better adapted to the constraints of the resource (Ma et al 2019; ZechmeisterBoltenstern et al 2015). A consensus on the stoichiometric plasticity of soil microbial biomass and a good mechanistic understanding of the factors driving the relationship between soil and microbial stoichiometry have not yet been reached (Cleveland and Liptzin 2007; Ehlers et al 2010; Fanin et al 2017; 2013; Hartman and Richardson 2013; Li et al 2012; Xue et al 2019)

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