Abstract

Lateral movements of soil organic C (SOC) influences Earth’s C budgets by transporting organic C across landscapes and by modifying soil-profile fluxes of CO2. We extended a previously presented model (Soil Organic C Erosion Replacement and Oxidation (SOrCERO)) and present SOrCERODe, a model with which we can project how erosion and subsequent deposition of eroded material can modify biosphere-atmosphere CO2 fluxes in watersheds. The model permits the user to quantify the degree to which eroding and depositional profiles experience a change in SOC oxidation and production as formerly deep horizons become increasingly shallow, and as depositional profiles are buried. To investigate the relative importance of erosion rate, evolving SOC depth distributions, and mineralization reactivity on modeled soil C fluxes, we examine two forests exhibiting distinct depth distributions of SOC content and reactivity, hydrologic regimes and land use. Model projections suggest that, at decadal to centennial timescales: 1) the quantity of SOC moving across a landscape depends on erosion rate and the degree to which SOC production and oxidation at the eroding profile are modified as deeper horizons become shallower, and determines the degree to which depositional profile SOC fluxes are modified; 2) erosional setting C sink strength increases with erosion rate, with some sink effects reaching more than 40% of original profile SOC content after 100 y of a relatively high erosion rate (i.e. 1 mm y-1); 3) even large amounts of deposited SOC may not promote a large depositional profile C sink in spite of large gains in autochthonous SOC post-deposition if oxidation of buried SOC is not limited; and 4) when modeled depositional settings receive a disproportionately large amount of SOC, simulations of strong C sink scenarios mimic observations of modest preservation of buried SOC and large SOC gains in surficial horizons, suggesting that C sink scenarios have merit in these forests. Our analyses illuminate the importance of cross-landscape linkages between upland and depositional environments for watershed-scale biosphere-atmosphere C fluxes, and emphasize the need for accurate representations and observations of time-varying depth distributions of SOC reactivity across evolving watersheds if we seek accurate projections of ecosystem C balances.

Highlights

  • Lateral movement of soil organic C (SOC) due to erosion can influence regional and global C budgets (Doetterl et al, 2016), a phenomenon of increasing importance given human acceleration of soil transport across the globe (Syvitski et al, 2005; Wilkinson and McElroy, 2007; Haff, 2010; Hook et al, 2012)

  • We investigate erosion-induced modifications to C inputs and losses in eroding and depositional profiles and associated watershed-scale C dynamics

  • We demonstrate the importance of eroded SOC retention in a terrestrial depositional setting vs. its escape via mineralization or transport to an aquatic system for estimating a watershed’s C balance

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Summary

Introduction

Lateral movement of soil organic C (SOC) due to erosion can influence regional and global C budgets (Doetterl et al, 2016), a phenomenon of increasing importance given human acceleration of soil transport across the globe (Syvitski et al, 2005; Wilkinson and McElroy, 2007; Haff, 2010; Hook et al, 2012). Soil erosion and subsequent deposition transports SOC, which locally depletes or augments profile SOC reservoirs, respectively. Erosion can alter regional and global C budgets by influencing fluxes of CO2 to and from the atmosphere (Stallard, 1998; Harden et al, 1999; Berhe et al, 2007; van Oost et al, 2007; Billings et al, 2010; Doetterl et al, 2015; Dialynas et al, 2016; Wang et al, 2017). Biosphere-atmosphere exchange of C can be influenced by erosion via SOC mineralization to CO2 during transport of eroded material, and by alteration of SOC production and mineralization rates in both eroding and depositional profiles. Mineralization of SOC to CO2 during transport of eroded material (Jacinthe and Lal, 2001; Jacinthe et al, 2002) is perhaps the most obvious way that erosion can influence atmospheric CO2. Difficulties with tracking the fate of eroded SOC make quantifying the eroded SOC that is lost as CO2 during transport a challenging problem (Hu and Kuhn, 2014)

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