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25th International Meeting on Organic Geochemistry IMOG 2011

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P-410<br />

Carb<strong>on</strong> cycling in lacustrine food webs<br />

J. Marieke Lammers 1 , Carsten J. Schubert 2 , Jack J. Middelburg 1 , Jaap S. Sinninghe<br />

Damsté 1,3 , Gert-Jan Reichart 1<br />

1 Universiteit Utrecht, Utrecht, Netherlands, 2 EAWAG, Kastanienbaum, Switzerland, 3 Netherlands Institute for<br />

Sea Research, Den Burg, Netherlands (corresp<strong>on</strong>ding author:M.Lammers@geo.uu.nl)<br />

Heterotrophs in freshwater systems rely <strong>on</strong> three<br />

major sources of carb<strong>on</strong>/energy: (1) local primary<br />

producti<strong>on</strong>, (2) terrestrial input from plants and soils<br />

and (3) methanotrophic biomass (depending <strong>on</strong> either<br />

locally produced or imported methane). The<br />

availability of these three energy sources has major<br />

c<strong>on</strong>sequences for food web functi<strong>on</strong>ing and structure,<br />

and determine the carb<strong>on</strong> fluxes within the lake and<br />

how much carb<strong>on</strong> is ultimately exported from the lake<br />

to rivers or the atmosphere. Terrestrial<br />

(allochth<strong>on</strong>ous) organic carb<strong>on</strong> is traditi<strong>on</strong>ally<br />

assumed to be aged and thus refractory, yet evidence<br />

indicates that it may fuel parts of the food web [1, 2],<br />

enhancing sec<strong>on</strong>dary producti<strong>on</strong> [1, 3]. So far, the<br />

sec<strong>on</strong>dary producers involved and relative<br />

c<strong>on</strong>tributi<strong>on</strong>s of in situ produced and allochth<strong>on</strong>ous<br />

organic matter to sec<strong>on</strong>dary productivity remains<br />

poorly quantified.<br />

Processing of terrestrial organic matter in lakes is<br />

highly variable through the year [3], and possibly<br />

depending <strong>on</strong> trophic level [1]. This research,<br />

therefore, focuses <strong>on</strong> identifying main organic carb<strong>on</strong><br />

fluxes and elucidating food web functi<strong>on</strong>ing in<br />

freshwater systems with variable trophic levels.<br />

Energy flow at higher food web levels can be studied<br />

using stable isotope analyses [4]. Two frequently<br />

used approaches, sampling primary producers or bulk<br />

particulate organic matter (POM), both have their<br />

inherent problems. Putative primary c<strong>on</strong>sumers may<br />

sometimes c<strong>on</strong>sume small heterotrophs and bulk<br />

POM comprises not <strong>on</strong>ly primary producers but also<br />

bacteria, small heterotrophs and detritus. Compound<br />

specific isotope analysis (CSIA) of lipid biomarkers<br />

allows including the microbial compartment of food<br />

webs [5].<br />

Two Swiss lakes are studied for food web<br />

structure and carb<strong>on</strong> flows. Lake Lucerne is a prealpine,<br />

oligotrophic lake with limited terrestrial input.<br />

Rotsee, a small eutrophic lake just north of Lucerne,<br />

has a major methane-based productivity. Samples for<br />

characterizing DIC, DOC and POM were collected at<br />

different water depths. Also, samples of soil<br />

surrounding Lake Lucerne were collected. DIC, DOC<br />

and POM c<strong>on</strong>centrati<strong>on</strong>s and carb<strong>on</strong> isotopic<br />

analyses of inflowing streams, lake water and<br />

outflowing streams are used to deduce whether the<br />

lakes are a net carb<strong>on</strong> source or sink. DOC is the<br />

main coupling between autotrophs and heterotrophic<br />

bacteria. It forms an important step in the food web<br />

and is therefore analyzed for bulk isotopic<br />

compositi<strong>on</strong>. POM is often used as a representative<br />

of phytoplankt<strong>on</strong> carb<strong>on</strong> and is therefore analyzed for<br />

bulk carb<strong>on</strong> and nitrogen isotopic compositi<strong>on</strong>. To<br />

differentiate between algal and bacterial classes,<br />

POM is also analyzed for biomarker presence and<br />

abundance and subsequently for CS-δ 13 C. As a first<br />

order approximati<strong>on</strong>, functi<strong>on</strong>al groups are assigned<br />

using analyses of phospholipid-derived fatty acids<br />

(PLFA). More specifically, other lipid biomarkers such<br />

as free fatty acids, sterols and hopanoids are used to<br />

identify and quantify algal and bacterial classes.<br />

Samples of soil surrounding Lake Lucerne are<br />

analyzed similarly to POM samples in order to obtain<br />

isotopic signature and compositi<strong>on</strong>al informati<strong>on</strong> <strong>on</strong><br />

allochth<strong>on</strong>ous material entering the lake.<br />

References<br />

[1] Cole et al. (2006) Ecology Letters 9: 558-568<br />

[2] Cole et al. (2007) Ecosystems 10: 171-184<br />

[3] Pace et al. (2004) Nature 427: 240-243<br />

[4] Peters<strong>on</strong> and Fry (1987) Annu. Rev. Ecol. Syst.<br />

18: 293-320<br />

[5] Middelburg et al. (2000) Limnol. Ocean. 45: 1224-<br />

1234<br />

538

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