Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2014 Oct 28:5:571.
doi: 10.3389/fmicb.2014.00571. eCollection 2014.

Modeling adaptation of carbon use efficiency in microbial communities

Affiliations

Modeling adaptation of carbon use efficiency in microbial communities

Steven D Allison. Front Microbiol. .

Abstract

In new microbial-biogeochemical models, microbial carbon use efficiency (CUE) is often assumed to decline with increasing temperature. Under this assumption, soil carbon losses under warming are small because microbial biomass declines. Yet there is also empirical evidence that CUE may adapt (i.e., become less sensitive) to warming, thereby mitigating negative effects on microbial biomass. To analyze potential mechanisms of CUE adaptation, I used two theoretical models to implement a tradeoff between microbial uptake rate and CUE. This rate-yield tradeoff is based on thermodynamic principles and suggests that microbes with greater investment in resource acquisition should have lower CUE. Microbial communities or individuals could adapt to warming by reducing investment in enzymes and uptake machinery. Consistent with this idea, a simple analytical model predicted that adaptation can offset 50% of the warming-induced decline in CUE. To assess the ecosystem implications of the rate-yield tradeoff, I quantified CUE adaptation in a spatially-structured simulation model with 100 microbial taxa and 12 soil carbon substrates. This model predicted much lower CUE adaptation, likely due to additional physiological and ecological constraints on microbes. In particular, specific resource acquisition traits are needed to maintain stoichiometric balance, and taxa with high CUE and low enzyme investment rely on low-yield, high-enzyme neighbors to catalyze substrate degradation. In contrast to published microbial models, simulations with greater CUE adaptation also showed greater carbon storage under warming. This pattern occurred because microbial communities with stronger CUE adaptation produced fewer degradative enzymes, despite increases in biomass. Thus, the rate-yield tradeoff prevents CUE adaptation from driving ecosystem carbon loss under climate warming.

Keywords: bacteria; climate change; fungi; rate-yield tradeoff; soil carbon; temperature; theoretical model.

PubMed Disclaimer

Figures

Figure 1
Figure 1
Relative growth rate as a function of intrinsic carbon use efficiency (CUE) at different temperatures from the analytical model under the (A) high tradeoff (mU = −0.4) and (B) low tradeoff (mU = −0.2) scenarios.
Figure 2
Figure 2
Mean ± SE (A) intrinsic carbon use efficiency (CUE), (B) total substrate carbon, and (C) total microbial biomass carbon under high and low tradeoff scenarios at 15 vs. 20°C in the DEMENT model. Significant differences between temperatures are noted with an asterisk (P < 0.01, paired t-test).
Figure 3
Figure 3
Relationship between change in intrinsic carbon use efficiency (CUE) with 5°C warming (20°C minus 15°C) and change in (A) microbial biomass carbon or (B) substrate carbon. Linear regression statistics are given for the combined high and low tradeoff scenarios in the DEMENT model.
Figure 4
Figure 4
Substrate dynamics (A,D), microbial dynamics (B,E), and mean microbial abundance vs. the number of enzymes possessed by each taxon (C,F) in a selected pair of high tradeoff DEMENT simulations at 15°C (A–C) and 20°C (D–F). Line colors in (B,E) correspond to the number of enzymes shown in (C,F).

References

    1. Allison S. D. (2006). Soil minerals and humic acids alter enzyme stability: implications for ecosystem processes. Biogeochemistry 81, 361–373. 10.1007/s10533-006-9046-2 - DOI
    1. Allison S. D. (2012). A trait-based approach for modelling microbial litter decomposition. Ecol. Lett. 15, 1058–1070. 10.1111/j.1461-0248.2012.01807.x - DOI - PubMed
    1. Allison S. D., Lu Y., Weihe C., Goulden M. L., Martiny A. C., Treseder K. K., et al. . (2013). Microbial abundance and composition influence litter decomposition response to environmental change. Ecology 94, 714–725. 10.1890/12-1243.1 - DOI - PubMed
    1. Allison S. D., Wallenstein M. D., Bradford M. A. (2010). Soil-carbon response to warming dependent on microbial physiology. Nat. Geosci. 3, 336–340. 10.1038/ngeo846 - DOI
    1. Apple J. K., Del Giorgio P. A., Kemp W. M. (2006). Temperature regulation of bacterial production, respiration, and growth efficiency in a temperate salt-marsh estuary. Aquat. Microb. Ecol. 43, 243–254. 10.3354/ame043243 - DOI