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25th International Meeting on Organic Geochemistry IMOG 2011

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P-024<br />

The phenolic characterisati<strong>on</strong> of peat profiles al<strong>on</strong>g a vegetati<strong>on</strong><br />

successi<strong>on</strong> using 13C-labelled tetramethylamm<strong>on</strong>ium hydroxide<br />

(13C-TMAH) thermochemolysis<br />

Eleanor Swain, Geoffrey Abbott<br />

Newcastle University, Newcastle up<strong>on</strong> Tyne, United Kingdom (corresp<strong>on</strong>ding author:geoff.abbott@ncl.ac.uk)<br />

Northern peatlands cover an area of around 350 x10 6<br />

ha, and store approximately <strong>on</strong>e-third of global soil<br />

carb<strong>on</strong> (C) 1 . Peatland vegetati<strong>on</strong> varies in resp<strong>on</strong>se to<br />

external drivers including climate induced<br />

disturbance, due to differences in tissue biochemistry<br />

and changes in litter reactivity. These factors are<br />

poorly understood, but critical to understanding soil<br />

organic matter turnover in peatlands and its resp<strong>on</strong>se<br />

to a changing climate. This study aims to provide a<br />

detailed and comprehensive SOM characterisati<strong>on</strong> of<br />

a peatland using thermally assisted hydrolysis and<br />

methylati<strong>on</strong> (THM) in the presence of 13 C-TMAH.<br />

Peat profiles were sampled from Wark Forest, an<br />

afforested moorland site in northeast England. The<br />

site includes two soil profiles in an undisturbed open<br />

bog and four profiles in a bog margin. The bog margin<br />

comprised two pits am<strong>on</strong>gst Sitka spruce but not<br />

situated underneath the canopy, and two pits located<br />

directly under the canopy of Sitka spruce.<br />

Figure 1: Depth profile showing changes in total lignin<br />

products (Λ) (x10 -2 mg/100mg OC). SE = 4.<br />

The additi<strong>on</strong> of 13 C-TMAH allows the distincti<strong>on</strong><br />

between intact lignin, degraded lignin and n<strong>on</strong>-lignin<br />

phenols to be made 2 .<br />

This site was selected due to the absence of any<br />

recent human influence <strong>on</strong> the peat, to allow us to<br />

explore the effect of direct lignin and tannin inputs <strong>on</strong><br />

the geochemical and carb<strong>on</strong> c<strong>on</strong>tents of the peat<br />

down the profile.<br />

A high Sphagnum input is observed in the surface<br />

litter of the peat beneath the Sitka Spruce, indicating<br />

a current vegetati<strong>on</strong> cover of Sphagnum. The<br />

Sphagnum and lignin inputs (Figs.1 & 2 respectively)<br />

are very low in the deeper organic horiz<strong>on</strong>s,<br />

suggesting an increased SOM turnover.<br />

The phenolic compositi<strong>on</strong> of the SOM of the surface<br />

litter reflects the vegetati<strong>on</strong> input at all three sites.<br />

However, these molecular characteristics are lost with<br />

increasing depth. The open bog site with no<br />

Sphagnum at the surface had a significantly higher<br />

carb<strong>on</strong> storage compared to the bog margin sites<br />

(409 and 290 t C/ha respectively). This suggests that<br />

Sphagnum moss may not incorporate more carb<strong>on</strong><br />

than any other plant genus as previously thought 3 .<br />

Figure 2: Depth profile showing changes in total<br />

Sphagnum products (mg/100mg OC). SE = 2.<br />

[1] Gorham, E. (1991) Ecological Applicati<strong>on</strong>s 1(2)<br />

182-195; [2] Filley, T., Minard, R., and Hatcher, P.<br />

(1999) <strong>Organic</strong> <strong>Geochemistry</strong> 30(7) 607-621; [3]<br />

Clymo, R., and Hayward, P.(1982) in Bryophyte<br />

Ecology 229-289.<br />

172

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