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.1997 Aug 5;94(16):8284-91.
doi: 10.1073/pnas.94.16.8284.

Potential responses of soil organic carbon to global environmental change

Affiliations

Potential responses of soil organic carbon to global environmental change

S E Trumbore. Proc Natl Acad Sci U S A..

Abstract

Recent improvements in our understanding of the dynamics of soil carbon have shown that 20-40% of the approximately 1,500 Pg of C stored as organic matter in the upper meter of soils has turnover times of centuries or less. This fast-cycling organic matter is largely comprised of undecomposed plant material and hydrolyzable components associated with mineral surfaces. Turnover times of fast-cycling carbon vary with climate and vegetation, and range from <20 years at low latitudes to >60 years at high latitudes. The amount and turnover time of C in passive soil carbon pools (organic matter strongly stabilized on mineral surfaces with turnover times of millennia and longer) depend on factors like soil maturity and mineralogy, which, in turn, reflect long-term climate conditions. Transient sources or sinks in terrestrial carbon pools result from the time lag between photosynthetic uptake of CO2 by plants and the subsequent return of C to the atmosphere through plant, heterotrophic, and microbial respiration. Differential responses of primary production and respiration to climate change or ecosystem fertilization have the potential to cause significant interrannual to decadal imbalances in terrestrial C storage and release. Rates of carbon storage and release in recently disturbed ecosystems can be much larger than rates in more mature ecosystems. Changes in disturbance frequency and regime resulting from future climate change may be more important than equilibrium responses in determining the carbon balance of terrestrial ecosystems.

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Figures

Figure 1
Figure 1
Conceptual model of SOM dynamics used in this paper (after ref. 40).
Figure 2
Figure 2
(Left) Change in Δ14C in atmospheric CO2 and in two homogeneous C pools with turnover times of 5, 10, 50, and 70 years. (Right) Effect of passive organic matter on Δ(Δ14C) values in bulk SOM. Failure to account for 10% of the carbon in a passive fraction that does not change in14C content between 1959 and 1992 will result in an underestimate of the increase in fast-cycling Δ14C and therefore of turnover time in that fraction. Thus it is important to assess whether passive components such as charcoal are present in presumed fast-cycling pools (such as low-density carbon).
Figure 3
Figure 3
Increases in Δ14C between 1959 (1964 for lowest elevation site) and 1992 for (a) low density (<2.0 g/cm3), (b) hydrolyzable (>2.0 g/cm3), and (c) nonhydrolyzable (>2.0 g/cm3) portions of SOM from an elevation transect in the Sierra Nevada (3). The fraction of organic matter with the fastest turnover time will have the highest pre-196314C values and show the largest increase in14C between 1959 and 1992 (a) while the fraction with slowest turnover has lowest initial14C values and shows little increase in14C over the past 30 years (c).
Figure 4
Figure 4
Turnover times for fast-cycling fractions for a number of sites plotted against mean annual temperature: (a) low-density C in the Sierra Nevada transect (3); combined active plus slow C from the Hawaii temperature transect (5); low-density C from a mature seasonal tropical forest in eastern Amazonia (60); (b) using low-density plus hydrolyzable carbon for Sierra and Brazil sites. All data represent approximately the upper 20 cm of soil. Also shown are predicted turnover time-temperature relationships estimated from thecentury model and from the literature review of Kirschbaum (51). Thecentury curve is based on model results reported in Schimelet al. (12) assuming the temperature dependence reported in that paper, and combining pools assuming 5% of the C to 0–20 cm is contained microbial biomass pool, 20% in the detrital pool, and 50% in the slow pool.
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References

    1. Jenny H. Factors of Soil Formation. New York: McGraw–Hill; 1941.
    1. Jenny H. The Soil Resource: Origin and Behavior. New York: Springer; 1980.
    1. Trumbore S E, Chadwick O A, Amundson R. Science. 1996;272:393–396.
    1. Vitousek P M, Turner D R, Kitayama K. Ecology. 1995;11:189–203.
    1. Townsend A R, Vitousek P M, Trumbore S E. Ecology. 1995;11:721–733.

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