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25th International Meeting on Organic Geochemistry IMOG 2011

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P-513<br />

Anaerobic oxidati<strong>on</strong> of plant-derived 3-phenylpropanoids by the<br />

denitrifying bacterium ―Aromatoleum aromaticum‖ EbN1<br />

Heinz Wilkes 1 , Kathleen Trautwein 2,3 , Ralf Rabus 2,3<br />

1 Helmholtz Centre Potsdam GFZ German Research Centre for Geosciences, Potsdam, Germany, 2 Institute<br />

of Chemistry and Biology of the Marine Envir<strong>on</strong>ment (ICBM), University Oldenburg, Oldenburg, Germany,<br />

3 Max Planck Institute for Marine Microbiology, Bremen, Germany (corresp<strong>on</strong>ding author:wilkes@gfzpotsdam.de)<br />

Phenylalanine-derived 3-phenylpropanoids (e.g.<br />

cinnamic acid, p-coumaric acid, ferulic acid, sinapinic<br />

aicd) are widespread in nature. They represent the<br />

building blocks of lignin, which is the sec<strong>on</strong>d most<br />

abundant terrestrial biopolymer after cellulose,<br />

accounting for approx. 30% of the organic carb<strong>on</strong> in<br />

the terrestrial biosphere [1]. As comp<strong>on</strong>ents of<br />

sec<strong>on</strong>dary metabolites (anthocyanins, flav<strong>on</strong>oids or<br />

phytoalexins) 3-phenylpropanoids play also an<br />

important role in plant stress resp<strong>on</strong>ses [2]. Release<br />

of 3-phenylpropanoids into the envir<strong>on</strong>ment arises<br />

mainly from the biodegradati<strong>on</strong> of plant material. In<br />

accordance with the natural abundance, many<br />

microorganisms are able to utilize 3phenylpropanoids.<br />

Their metabolism has been<br />

studied in a variety of bacteria, and different<br />

degradati<strong>on</strong> pathways have been proposed to be<br />

employed by these bacteria.<br />

Here we present results of studies <strong>on</strong> the metabolism<br />

of 3-phenylpropanoids by the denitrifying bacterium<br />

―Aromatoleum aromaticum‖ EbN1 under aerobic and<br />

anaerobic c<strong>on</strong>diti<strong>on</strong>s based <strong>on</strong> identificati<strong>on</strong> of<br />

metabolites and differential protein profiling. Strain<br />

EbN1 was originally isolated with ethylbenzene from<br />

freshwater sediments and dem<strong>on</strong>strated to utilize a<br />

large variety of aromatic compounds under anoxic<br />

c<strong>on</strong>diti<strong>on</strong>s [3]. This includes p-ethylphenol which is<br />

oxidised via a degradati<strong>on</strong> pathway reminiscent of<br />

known anaerobic ethylbenzene degradati<strong>on</strong> in the<br />

same bacterium [4].<br />

The present study revealed that strain EbN1 is<br />

capable of utilizing cinnamyl alcohol, hydrocinnamic<br />

acid, cinnamic acid, 3-(4-hydroxyphenyl)propanoic<br />

acid, p-coumaric acid, m-coumaric acid, 3-(3,4dihydroxyphenyl)propanoic<br />

acid and caffeic acid<br />

under anoxic c<strong>on</strong>diti<strong>on</strong>s. GC-MS analysis of<br />

metabolites formed during growth with these<br />

substrates provided evidence for their degradati<strong>on</strong> via<br />

a �-oxidati<strong>on</strong> pathway as outlined for<br />

hydrocinnamic/cinnamic acid in Figure 1. 3-Hydroxy-<br />

3-phenylpropanoate was str<strong>on</strong>gly prevailing up<strong>on</strong><br />

growth with hydrocinnamate and cinnamate while the<br />

respective substrate as well as benzoate were<br />

present in small relative amounts <strong>on</strong>ly. This could<br />

indicate that the hydrati<strong>on</strong> of cinnamoyl-CoA takes<br />

place at a high rate while <strong>on</strong>e of the following steps<br />

required to form benzoyl-CoA from 3-hydroxy-3phenylpropanoyl-CoA<br />

might be rate limiting.<br />

Experiments performed to test the potential of strain<br />

EbN1 to co-metabolize 3-phenylpropanoids that do<br />

not support growth indicated a high substrate<br />

specificity of the involved enzymes. The capacity of<br />

strain EbN1 for lignin m<strong>on</strong>omer degradati<strong>on</strong> is of<br />

ecophysiological relevance, since it could potentially<br />

c<strong>on</strong>tribute to the formati<strong>on</strong> and fate of dissolved<br />

organic matter in freshwater and soil envir<strong>on</strong>ments.<br />

HO<br />

COO -<br />

COSCoA<br />

O<br />

COSCoA COSCoA<br />

COSCoA<br />

COSCoA<br />

+ Acetyl-CoA<br />

Fig. 1. Simplified pathway of oxidati<strong>on</strong> of<br />

hydrocinnamic and cinnamic acid to benzoic acid in<br />

strain EbN1.<br />

References<br />

[1] Boerjan, W., Ralph, J., Baucher, M., 2003. Annu Rev<br />

Plant Biol 54, 519-546.<br />

[2] Dix<strong>on</strong>, R.A., Paiva, N.L., 1995. The Plant Cell 7, 1085-<br />

1097.<br />

[3] Rabus, R., Widdel, F., 1995. Arch Microbiol 163, 96-103.<br />

[4] Wöhlbrand, L., Wilkes, H., Halder, T., Rabus, R., 2008. J<br />

Bacteriol 190, 5699-5709.<br />

634

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