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25th International Meeting on Organic Geochemistry IMOG 2011

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P-423<br />

Effects of l<strong>on</strong>g-term climatic manipulati<strong>on</strong>s <strong>on</strong> microbial<br />

communities in European shrublands<br />

Shar<strong>on</strong> Mas<strong>on</strong> 1 , Chiara Cerli 1 , Andrew Smith 2 , Albert Tietema 1<br />

1 University of Amsterdam, Amsterdam, Netherlands, 2 Centre for Ecology and Hydrology, Bangor, United<br />

Kingdom (corresp<strong>on</strong>ding author:s.l.mas<strong>on</strong>@uva.nl)<br />

Soil microbial communities are key regulators of soil<br />

organic matter (SOM) dynamics. Therefore, shifts in<br />

microbial community compositi<strong>on</strong> in resp<strong>on</strong>se to<br />

envir<strong>on</strong>mental change may significantly affect key<br />

ecosystem processes, such as nutrient cycling and<br />

soil organic carb<strong>on</strong> (SOC) turnover. Previous studies<br />

have shown significant, yet c<strong>on</strong>trasting microbial<br />

resp<strong>on</strong>se to increased soil temperature and altered<br />

precipitati<strong>on</strong> patterns [1, 2 & 3], highlighting the need<br />

for a greater understanding of how different<br />

ecosystems resp<strong>on</strong>d to such changes.<br />

Climate change effects <strong>on</strong> European shrublands have<br />

been investigated for more than 10 years during the<br />

EU-funded projects of CLIMOOR (1998-2000),<br />

VULCAN (2001-2004) and INCREASE (2009-2012),<br />

with c<strong>on</strong>tinued measurements at many sites in the<br />

intervening years. A network of 6 large scale field<br />

experiments simulate realistic levels of climatic<br />

change in 20 m 2 plots, that are superimposed across<br />

a natural temperature and precipitati<strong>on</strong> gradient (Fig.<br />

1). Each site has 9 experimental plots; 3 x c<strong>on</strong>trol, 3<br />

x warming and 3 x drought. Warming treatment is<br />

achieved by covering plots with a reflective curtain at<br />

night to prevent heat loss (increases soil temperature<br />

by 0.4-1.2 ºC), whilst drought treatment is simulated<br />

by covering plots with a transparent cover for 1-2<br />

m<strong>on</strong>ths during the growing seas<strong>on</strong> (Fig. 2). How the<br />

different sites resp<strong>on</strong>d to climatic manipulati<strong>on</strong> is most<br />

intriguing, with findings indicating that the effect of<br />

warming might be seen across all sites, whilst the<br />

effect of drought could be more significant in Northern<br />

as opposed to the drier Southern European soils [4].<br />

Significant effects <strong>on</strong> soil processes have been found<br />

but a greater understanding of molecular level<br />

resp<strong>on</strong>se is still required. In this study we assess and<br />

report changes in phospholipid fatty acid (PLFA)<br />

profiles to determine how microbial communities are<br />

affected by climatic manipulati<strong>on</strong>s imposed across<br />

experimental sites. Soil samples were collected from<br />

plots in The Netherlands, Denmark, Italy, Hungary<br />

and Wales (UK) in November 2009 and analysed for<br />

PLFA c<strong>on</strong>tent and compositi<strong>on</strong> using a modificati<strong>on</strong> of<br />

the method outlined in [5]. We hypothesised that<br />

warming would increase fungal:bacterial ratios, whilst<br />

drought would reduce fungal community compositi<strong>on</strong>.<br />

An initial assessment of outside plot samples showed<br />

variati<strong>on</strong> between sites in both total active microbial<br />

biomass and fungal:bacterial ratios due to natural<br />

differences between ecosystems. Linking these<br />

findings with further molecular geochemical<br />

assessment and investigati<strong>on</strong> of microbial activity will<br />

in future be critical to our overall understanding of the<br />

shrubland ecosystem resp<strong>on</strong>se to climate change.<br />

Fig. 1. Locati<strong>on</strong> of infrastructures, showing natural gradients<br />

in temperature and precipitati<strong>on</strong> (left).<br />

Fig. 2. Climate manipulati<strong>on</strong> techniques (right).<br />

References<br />

[1] Feng, X. J., Simps<strong>on</strong>, A. J., Wils<strong>on</strong>, K. P., Williams, D. D.<br />

and Simps<strong>on</strong>, M. J. (2008) Nature Geosci. 1, 836-839.<br />

[2] Frey, S.D., Drijber, R., Melillo, J. (2008) Soil Biol.<br />

Biochem. 40, 2904-2907.<br />

[3] Toberman, H., Freeman, C., Evans, C., Fenner, N. and<br />

Artz, R. R. E. (2008) FEMS Microbiol. Ecol. 66, 426-436.<br />

[4] Sowerby, A., Emmett, B., Beier, C., Tietema, A.,<br />

Penuelas, J., Estiarte, M., van Meeteren, M.J.M., Hughes,<br />

S., Freeman, C. (2006) Soil Biol. Biochem. 37, 1805-1813.<br />

[5] Elvert, M., Boetius, A., Knittel, K., Jorgensen, B. B. (2003)<br />

Geomicrobiol J. 20, 403-419.<br />

549

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