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Dynamic of dissolved organic matter and trace elements in a steady state lake bottom layer : molecular size fractionation.

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HAL Id: insu-00189196

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Submitted on 20 Nov 2007

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Dynamic of dissolved organic matter and trace elements

in a steady state lake bottom layer : molecular size

fractionation.

Patrick Albéric, Didier Jezequel, Eric Viollier, Christian Défarge, Pascale

Gautret

To cite this version:

Patrick Albéric, Didier Jezequel, Eric Viollier, Christian Défarge, Pascale Gautret. Dynamic of dis-solved organic matter and trace elements in a steady state lake bottom layer : molecular size fraction-ation.. IMOG 2007, Sep 2007, Torquay, United Kingdom. pp.P78-MO. �insu-00189196�

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P78-MO

DYNAMIC OF DISSOLVED ORGANIC MATTER AND TRACE ELEMENTS IN A STEADY STATE LAKE BOTTOM LAYER: MOLECULAR SIZE FRACTIONATION

Patrick ALBERIC1, Didier JEZEQUEL2, Eric VIOLLIER2, Christian DEFARGE1and Pascale GAUTRET1

1. Institut des Sciences de la Terre d'Orléans (ISTO), UMR 6113 CNRS-Université d'Orléans, 45067 Orléans cedex2, France.

2. Laboratoire de Géochimie des eaux, UMR CNRS 7154 Université Paris 7 - Denis Diderot& Institut de Physique du Globe de Paris, 75251 Paris cedex 05, France.

Dissolved organic matter (DOM) in aquatic systems interacts with most processes including redox reactions, trace elements complexation, sorption and sedimentation. The complex nature of DOM in natural waters suggests that all the fractions constituting it do not contribute in the same way to its reactivity. The total stock of DOM can be split by various means like the difference in size of the molecules or the difference in affinity for adsorbent phases. The deep and stable layers of meromictic lakes are of a particular interest for the study of the mechanisms controlling the behaviour of chemical elements in natural systems. Quasi stationary conditions unroll and stratify the processes through a certain thickness of the water column. In the deep layer of the lake Pavin (Massif-Central, France), solutes dispersing from the water-sediment interface (92 meter depth) cross a succession of levels characterized by different physicochemical and microbiological conditions (redox conditions, interactions with neoformed or settling particles, bacterial metabolic types) before to reach the oxic layer around 60 meter depth (Viollier et al., 1995, 1997, Lehours et al., 2003). In the layer 70-90 m (monimolimnion), trace elements can be schematically divided into two groups; one disperses upwards with mostly no interaction with the medium (Li, Cs), while the other undergoes a strong recycling sedimentation (Ba, U, Mo, V, Sb, La) (Viollier et al., 1995; 1997). It was shown that many elements undergoing this recycling were associated (at 85 m depth) to organic fractions higher than 1 KD, hydrophobic enough to be adsorbed onto XAD-8 and XAD-4 resins (Albéric et al., 2000). The dissolved organic carbon profiles (Fig. 1) recently obtained by in-situ pumping and on-line tangential ultrafiltration of the anoxic water of the monimolimnion, demonstrate the contrasted dynamics of the different DOM fractions according to their size. Less than 1 KD DOM presents a dispersion profile similar to those of the first group trace elements (“no reactive”) while the fractions ranging between 1 to 10 KD and 10 KD to 0.45 µm conversely show profiles which testify to their reactivity in the deep layer of the lake. The ultrafiltration profiles carried out there have confirmed the essential role of the colloidal fractions on the recycling of certain elements like Mo and V (Thiam et al.,

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P78-MO

2007). Microscopic observations (SEM, cryo-SEM) of the colloidal fractions, suggests the interaction of iron phosphate in the processes of coagulation and scavenging of certain forms of DOM in the deep layer.

60 65 70 75 80 85 90 0 1 2 3 4 5 6 7 8 9 DOC (mg/L) D ep th (m ) 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 DOC (mM) total DOC < 10 KD DOC < 1 KD DOC

Figure 1. Depth profiles of dissolved organic carbon fractions in the monimolimnion of Lake Pavin.

REFERENCES

Albéric P., Viollier E., Jézéquel D., Grosbois C., Michard G. (2000). Interactions between trace elements and dissolved organic matter in the stagnant anoxic deep layer of a meromictic lake. Limnology and Oceanography 45: 1088-1096.

Lehours A.C., Bardot C., Debroas D., Fonty. G. (2003) Etude des communautés microbiennes de la zone anoxique d'un lac méromictique (lac Pavin): Approches moléculaires. Colloque SFM " Anaérobies 2003 " Marseille.

Viollier E., Jézéquel D., Michard G., Pèpe M. Sarazin G., Albéric P. (1995) Geochemical study of a crater lake (Pavin Lake, France): Trace-element behaviour in the monimolimnion. Chemical Geology 125: 61-72.

Viollier E., Michard G., Jézéquel D., Pèpe M., Sarazin G. (1997) Geochemical study of a crater lake: Lake Pavin, Puy-de-Dôme, France. Constraints afforded by the particulate matter distribution in element cycling within the lake. Chemical Geology 142: 225-241. Thiam A., Viollier E., Jézéquel D., Albéric P. (2007) Seasonal dynamics of molybdenum in a

Figure

Figure 1. Depth profiles of dissolved organic carbon fractions in the monimolimnion of Lake Pavin.

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