Abstract

Abstract. In a context of global change, soil has been identified as a potential carbon (C) sink, depending on land-use strategies. To detect the trends in carbon stocks after the implementation of new agricultural practices, early indicators, which can highlight changes in short timescales, are required. This study proposes the combined use of stable isotope probing and chemometrics applied to solid-state 13C nuclear magnetic resonance (NMR) spectra to unveil the dynamics of the storage and mineralization of soil carbon (C) pools. We focused on light organic matter fractions isolated by density fractionation of soil water stable aggregates because they respond faster to changes in land use than the total soil organic matter (SOM). Samples were collected from an agricultural field experiment with grassland, continuous maize cropping, and ley grassland under temperate climate conditions. Our results indicated contrasting aggregate dynamics depending on land-use systems. Under our experimental conditions, grassland returns larger amounts of C as belowground inputs than maize cropping, evidencing a different distribution of light C fractions between aggregate classes. Coarse aboveground inputs from maize contributed mostly to larger macroaggregates. Land-use changes with the introduction of ley grassland provoked a decoupling of the storage and/or degradation processes after the grassland phase. The newly derived maize inputs were barely degraded during the first 3 years of maize cropping, whereas grassland-derived material was depleted. As a whole, results suggest large microbial proliferation as shown by 13C NMR under permanent grassland, then reduced within the first years after the land-use conversion, and finally restored. The study highlighted a fractal structure of the soil, determining a scattered spatial distribution of the cycles of storage and degradation of soil organic matter related to detritusphere dynamics. As a consequence, vegetal inputs from a new land use are creating new detritusphere microenvironments that may be disconnected from the dynamics of C cycle of the previous land use. The formation of those different and unconnected microenvironments may explain the observed legacy effect of the previous land use, since each microenvironment type contributes separately to the overall soil C cycle. The effects of the new land use on the soil C cycle are delayed until the different detritusphere microenvironments remain unconnected, and the ones from the previous land use represent the predominant microenvironment type. Increasing knowledge of the soil C dynamics at a fine scale will be helpful in refining the prediction models and land-use policies.

Highlights

  • Soil carbon (C) stocks represent the largest C pool of the terrestrial biosphere (Scharlemann et al, 2014) which is accumulated and released to the atmosphere and, to an extent, dependent on land-use and anthropogenic factors (Lal, 2004; Powlson et al, 2011)

  • The light fraction (LF)-C content under ley grassland decreased to levels comparable to those measured for bare fallow in which no vegetal inputs were returned to soil during the previous 9 years

  • Our findings indicate that C under ley grassland is subjected to two different and mostly independent mechanisms, namely the degradation regarding the grassland-derived LF carbon (LF-C) and the accumulation of new maizederived LF-C

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Summary

Introduction

Soil carbon (C) stocks represent the largest C pool of the terrestrial biosphere (Scharlemann et al, 2014) which is accumulated and released to the atmosphere and, to an extent, dependent on land-use and anthropogenic factors (Lal, 2004; Powlson et al, 2011). Agriculture is responsible for 20 % of the total GHG emissions, but the transformation of soil into a C sink with sustainable agricultural practices (Chenu et al, 2019) has been proposed as a promising mitigation strategy by researchers, international panels, and governments (IPCC, 2013; Lal, 2008; Minasny et al, 2017) These mitigation strategies need to be evaluated using adequate biomarkers that can decipher the stabilization and/or destabilization mechanisms and, in particular, the direction of the change in suitable land-use practices (Dignac et al, 2017; Wiesmeier et al, 2019) and refine the prediction models about C balance associated with land-use policies (Chenu et al, 2019). Solid-state 13C NMR analysis of chemically or physically isolated SOM pools has been used to evaluate the degradation status of SOM induced by land use (Rabbi et al, 2014) and agricultural management (Panettieri et al, 2013, 2014)

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