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25th International Meeting on Organic Geochemistry IMOG 2011

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O-39<br />

The fate of terrestrial organic matter in the Yangtze river- East<br />

China sea system and its implicati<strong>on</strong>s for the use of terrestrial<br />

organic proxies<br />

Chun Zhu 1 , Thomas Wagner 2 , Helen Talbot 2 , Johan Weijers 1,3 , Richard Pancost 1<br />

1 <strong>Organic</strong> <strong>Geochemistry</strong> Unit, Bristol Biogeochemistry Research Centre, School of Chemistry, University of<br />

Bristol, Bristol, United Kingdom, 2 School of Civil Engineering and Geosciences, Newcastle University,<br />

Newcastle, United Kingdom, 3 Utrecht University, department of Earth Sciences – <strong>Geochemistry</strong>, Utrecht,<br />

Netherlands (corresp<strong>on</strong>ding author:czhu@uni-bremen.de)<br />

Burial of organic carb<strong>on</strong> (OC) in marine<br />

sediments represents the 2 nd largest sink of<br />

atmospheric CO2 over geological time scales.<br />

Although c<strong>on</strong>tinental shelves receive massive OC<br />

inputs, their role in OC accumulati<strong>on</strong> vs. degradati<strong>on</strong><br />

is still under debate. The Yangtze River-dominated<br />

East China Sea (YR-ECS; Fig. 1) is characterized by<br />

massive terrestrial inputs (the YR is the world‘s 4 th<br />

largest river in terms of sediment discharge) <strong>on</strong>to a<br />

well-ventilated, shallow (500 km)<br />

c<strong>on</strong>tinental shelf, distinct from most narrow shelves in<br />

the world. We examine the unique role of the ECS <strong>on</strong><br />

the fate of terrestrial organic matter (TOM) and its<br />

implicati<strong>on</strong>s for the use of terrestrial biomarkers.<br />

Highly degraded soil OM and organic pollutants<br />

dominate the YR sediments. Such OM is degraded<br />

effectively in the estuary, particularly in the turbidity<br />

maximum z<strong>on</strong>e, where an enhanced bacterial activity,<br />

including the bloom of methane oxidizing bacteria, is<br />

also recorded by higher c<strong>on</strong>centrati<strong>on</strong>s and structural<br />

diversity of bacteriohopanepolyols (BHPs). Although<br />

TOM has been extensively degraded in the watershed<br />

and estuary, degradati<strong>on</strong> of TOM clearly c<strong>on</strong>tinues<br />

al<strong>on</strong>g the coast and across the shelf, which is driven<br />

by c<strong>on</strong>stant coastal currents and intermittent bottom<br />

currents. Due to str<strong>on</strong>g winnowing, few riverdischarged<br />

sediments are accumulated <strong>on</strong> the open<br />

shelf whereas relict sands deposited during the low<br />

sea level stands occur widely <strong>on</strong> the seafloor. Those<br />

sands c<strong>on</strong>tain a persistent amount of relict OC (ca.<br />

0.1%), which appears to be δ 13 C-depleted (ca. -24‰)<br />

but terrestrial biomarker-absent. Relict OC <strong>on</strong> the<br />

sandy open ECS shelf accounts for ~170% of the<br />

particulate OC annually discharged by the YR. Given<br />

the globally wide occurrence of relict sands, a<br />

persistent amount of relict OC may complicate the<br />

modern TOM budget <strong>on</strong> c<strong>on</strong>tinental shelves.<br />

The behaviour of novel soil bacterial biomarkers<br />

including BHPs and GDGTs (glycerol dialkyl glycerol<br />

tetraethers) in the YR-ECS system was examined.<br />

BHP distributi<strong>on</strong> from the watershed to the shelf edge<br />

indicates a fundamental difference in hopanoidproducing<br />

communities between soils (source) and<br />

sediments (sink). The Rsoil index, based <strong>on</strong> the ratio of<br />

soil-marker BHPs vs. bacteriohopanetetraol, is<br />

proposed as a new approach to track soil OM<br />

distributi<strong>on</strong> in marine sediments. This index displays a<br />

str<strong>on</strong>g correlati<strong>on</strong> (R 2 =0.75) with the BIT index and<br />

moderate correlati<strong>on</strong>s with land plant biomarkerderived<br />

proxies in this setting. Branched GDGT-based<br />

proxies for soil pH and air temperature do not reflect<br />

the actual catchment envir<strong>on</strong>mental c<strong>on</strong>diti<strong>on</strong>s due to<br />

their extensive degradati<strong>on</strong> in the estuary and in-situ<br />

producti<strong>on</strong> <strong>on</strong> the well-ventilated ECS.<br />

Finally, the fidelity of a range of proxies for TOM<br />

input is examined. All proxies showed similar land-sea<br />

trends; however, two factors impact their applicability<br />

significantly: 1) the distinct reactivity, with a<br />

decreasing degradability order: soil-marker BHPs > αamyrin<br />

> β-amyrin > taraxerol > lignin > HMW nalkanols<br />

> HMW n-alkanes, and similarly, the Rsoil<br />

changing faster than the BIT which changes faster<br />

than δ 13 Corg; 2) the str<strong>on</strong>g regi<strong>on</strong>al variati<strong>on</strong>s in<br />

marine biomarker distributi<strong>on</strong>s, which complicate the<br />

normalizati<strong>on</strong> of terrestrial signals. We thus suggest<br />

using a multi-proxy approach, c<strong>on</strong>sidering the nature<br />

of biomarkers and the depositi<strong>on</strong>al settings, when<br />

rec<strong>on</strong>structing OC supply <strong>on</strong> c<strong>on</strong>tinental shelves.<br />

Fig.1. Sampling sites of surface sediment (0-5 cm) in<br />

the YR-ECS system<br />

99

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