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25th International Meeting on Organic Geochemistry IMOG 2011

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P-040<br />

Evoluti<strong>on</strong> of organic matter in lignite-c<strong>on</strong>taining sediments<br />

under different envir<strong>on</strong>mental c<strong>on</strong>diti<strong>on</strong>s. Analytical pyrolysis<br />

(Py-GC/MS) proxy<br />

José A. G<strong>on</strong>zález-Pérez 1 , Abad Chabbi 2 , Cornelia Rumpel 3 , José Mª de la Rosa 4 ,<br />

Francisco J. G<strong>on</strong>zález-Vila 1<br />

1 IRNAS-CSIC, Seville, Spain, 2 INRA-UEFE, Lusignan, France, 3 INRA-BIOEMCO, Thivernal-Grign<strong>on</strong>, France,<br />

4 ITN, Sacavém, Portugal (corresp<strong>on</strong>ding author:jag@irnase.csic.es)<br />

Mine soils and sediments in Lusatian open-cast lignite<br />

mining district (Germany) c<strong>on</strong>tain a mixture of lignite<br />

and recent organic matter. <strong>Organic</strong> matter (OM)<br />

characterizati<strong>on</strong> and its transformati<strong>on</strong> in mine soils<br />

and sediments is essential to understand ecosystem<br />

functi<strong>on</strong>ing in this regi<strong>on</strong>. For this study analytical<br />

pyrolysis (Py-GC/MS) was used as a geochemical<br />

proxy to complement previous studies d<strong>on</strong>e at a<br />

rehabilitated site for soil development 45 years ago<br />

and directed to m<strong>on</strong>itor the different C sources (lignite<br />

or plant derived) in soils and sediments and its degree<br />

of degradati<strong>on</strong> in c<strong>on</strong>trasting envir<strong>on</strong>ments (Chabbi et<br />

al., 2006, 2007).<br />

Representative vegetati<strong>on</strong> and organic carb<strong>on</strong> (OC)<br />

rich soil/sediment fracti<strong>on</strong> (humus fracti<strong>on</strong> separated<br />

by flotati<strong>on</strong>) from lake sediments were sampled at two<br />

depths (0-5 and 5-10 cm) in three plots al<strong>on</strong>g a<br />

transect covering: an 1) upland forest soil, 2) partially<br />

submerged sediment at the land–water interface and<br />

3) c<strong>on</strong>stantly submerged sediment.<br />

The analysis of plant (lipds, isoprenoids,<br />

methoxyphenols & carbohydrates) and possible lignite<br />

(alkyl-napththalenes, alkyl-benzenes & PAHs)<br />

biomarkers released after pyrolysis (500 ºC) supports<br />

previous findings in the area using different proxies.<br />

The c<strong>on</strong>diti<strong>on</strong>s in the submerged sediment favors OM<br />

protecti<strong>on</strong> and the accumulati<strong>on</strong> of decomposing plant<br />

material, whereas a more intense OM degradati<strong>on</strong><br />

process seems to be occurring in the land–water<br />

interface area that is characterized by fluctuating<br />

water levels. In additi<strong>on</strong>, the presence of organic<br />

sulfur compounds (OSC); a well resolved series of<br />

alkyl-thiophenes (6 to 24 C) with marked dominance<br />

of even C number molecules, indicate the possible<br />

occurrence of particular mechanisms of C<br />

preservati<strong>on</strong> in this extreme anoxic S rich<br />

envir<strong>on</strong>ment i.e. via sulfur ―quenching‖ with plant<br />

derived lipids during early diagenesis (Sinninghe-<br />

Damsté et al. 1989; Sinninghe-Damsté & de Leeuw,<br />

1990) in the submerged sediments of rehabilited<br />

lakes.<br />

References:<br />

Chabbi A., Rumpel C., Kögel-Knabner I. (2007) Org.<br />

Geochem. 38: 835–844;<br />

Chabbi A., Rumpel C., Grootes P.M., Mariotti A. Hüttl<br />

R.F. (2006) Org. Geochem. 37: 740–753<br />

Sinninghe-Damsté J.S.; de Leeuw J.W. (1990) Org.<br />

Geochem. 16: 1077–1101<br />

Sinninghe Damsté J.S., Rijpstra W.I.C., Kock-van<br />

Dalen A.C., de Leeuw J.W., Schenck P.A. (1989)<br />

Geochim. Cosmochim. Acta: 53, 1343–1355.<br />

187

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