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25th International Meeting on Organic Geochemistry IMOG 2011

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P-492<br />

Investigating the microbial populati<strong>on</strong>s c<strong>on</strong>trolling the<br />

producti<strong>on</strong> and oxidati<strong>on</strong> of methane in water-saturated mineral<br />

soils<br />

Katie Lim 1 , Peter Maxfield 1 , Edward Hornibrook 2 , Richard Pancost 1 , Richard Evershed 1<br />

1 <strong>Organic</strong> <strong>Geochemistry</strong> Unit, School of Chemistry, University of Bristol, Bristol, United Kingdom,<br />

2 Department of Earth Sciences, University of Bristol, Bristol, United Kingdom (corresp<strong>on</strong>ding<br />

author:k.lim@bristol.ac.uk)<br />

There is significant c<strong>on</strong>cern regarding the projected<br />

emissi<strong>on</strong>s of the prominent greenhouse gas methane<br />

(CH4) from known sources, e.g. wetlands, and the<br />

potential impact <strong>on</strong> future climate change. In c<strong>on</strong>trast,<br />

mineral soils are generally regarded as CH4 sinks,<br />

due to the presence of high abundances of<br />

methanotrophic populati<strong>on</strong>s able to c<strong>on</strong>sume ambient<br />

levels of CH4. However, the flux of CH4 from certain<br />

mineral soils is a delicate balance between the<br />

simultaneous producti<strong>on</strong> and oxidati<strong>on</strong> carried out by<br />

methanogenic archaea and methanotrophic bacteria<br />

they c<strong>on</strong>tain. For example, mineral soils experiencing<br />

regular water saturati<strong>on</strong>, although not always fully<br />

anoxic, may host methanogenic communities and act<br />

as CH4 sources (Teh et al., 2005). It has become a<br />

c<strong>on</strong>cern that in such mineral soils, termed ‗transiti<strong>on</strong>al<br />

soils‘, internal CH4 producti<strong>on</strong> may be significantly<br />

underestimated, and that a ‗tipping-point‘ may occur<br />

where marginal increases in water-c<strong>on</strong>tent may<br />

increase their capacity to act as a net CH4 source.<br />

The aim of this research was to investigate CH4<br />

cycling in transiti<strong>on</strong>al soils susceptible to frequent<br />

seas<strong>on</strong>al water-logging using a combinati<strong>on</strong> of CH4<br />

flux measurements, 13 C-stable isotope probing and<br />

biomarker analyses. A major aim was to develop new<br />

methods for m<strong>on</strong>itoring C flow between methanogenic<br />

and methanotrophic microbes. Methanotrophic activity<br />

is based up<strong>on</strong> phospholipid fatty acid (PLFA) profiling<br />

in combinati<strong>on</strong> with 13 C-stable isotopic probing (SIP;<br />

Maxfield et al., 2006), c<strong>on</strong>firming a dominance of<br />

18:1�7 producing high affinity bacteria. In order to<br />

assess methanogenic archaeal communities we<br />

developed the use of archaeol, determined using gas<br />

chromatography/mass spectrometry (GC/MS), as a<br />

proxy for in situ methanogenesis. This holds particular<br />

potential, as evidenced by the vertical distributi<strong>on</strong> of<br />

archaeol in both free, phospholipid- and glycolipidbound<br />

forms, in mineral soils (see Fig. 1). These<br />

results show for the first time in UK mineral soils an<br />

increased populati<strong>on</strong> of methanogenic archaea at<br />

depth due to the increase in anoxia induced by<br />

increased water c<strong>on</strong>tent. Significantly, >90% of the<br />

total archaeol was present in ‗bound‘ glycolipid and<br />

phospholipid forms, indicating an origin from the living<br />

archaeal biomass. The link to methanogenesis was<br />

c<strong>on</strong>firmed through increased CH4 producti<strong>on</strong> rates.<br />

We are now using these techniques to assess the<br />

true ‗sink‘/‗source‘ capacity of mineral soils subjected<br />

to frequent water saturati<strong>on</strong> as basis for further<br />

predicting trends in emissi<strong>on</strong>s related to greenhouse<br />

gas driven climate change.<br />

Depth / cm<br />

0<br />

2<br />

4<br />

6<br />

8<br />

10<br />

12<br />

14<br />

C<strong>on</strong>centrati<strong>on</strong> / µg g -1 dry wt.<br />

0.00 0.05 0.10 0.15<br />

Free archaeol<br />

Phospholipid bound archaeol<br />

Glycolipid bound archaeol<br />

Figure 1. Vertical distributi<strong>on</strong> of free and bound<br />

archaeol detected using GC/MS in a mineral soil.<br />

References<br />

[1] Maxfield, P. J., Hornibrook, E. R. C. and<br />

Evershed, R. P., 2006. Applied and<br />

Envir<strong>on</strong>mental Microbiology 72 (6), 3901-<br />

3907.<br />

[2] Teh, Y. A., Silver, W. L. and C<strong>on</strong>rad, M. E.,<br />

2005. Global Change Biology 11 (8), 1283-<br />

1297.<br />

615

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