Peatlands Geomicrobiology

Iron Cycling in an Acidic Fen

The Schlöppnerbrunnen Fen on a sunny summer day.
Image
Dr. Marco Reiche collecting a core from the small diameter peat corer.
Syringes attached to the rhizome samplers to collect groundwater at 5 cm intervals between 0 and 40 cm below the surface.

Peatlands have waterlogged soils with acidic conditions and a peat forming vegetation. High water levels have led to an imbalance between net primary production and decomposition which results in the storage of large carbon pools. Therefore, peatlands have a great impact on global carbon cycling. With the prospect of global climate change and the consequent predicted decreases in annual precipitation in most European regions, lower water levels might turn peatlands into sources of CH4 and CO2. The aeration of the upper peat layers (0-40 cm) renews the pool of electron acceptors like nitrate, Fe(III) and sulfate, making them available again for the oxidative processes leading to the release of CO2. The cycling of carbon is also greatly influenced by the turnover of acetate, an important intermediate in the anaerobic degradation of organic matter. Investigating peatland biogeochemistry and microbiology under altered water level conditions is therefore of great importance. Additionally, the dynamics of soil processes under extreme meteorological boundary conditions are studied within this project as a joint effort with researchers from the University of Bayreuth.

Our study site, the Schlöppnerbrunnen fen, (pH 4.8) is located in the Fichtelgebirge (northern Bavaria, Germany). It is part of the Lehstenbach Catchment, has an area of 0.8 ha, and has a the peat layer from 40 to 70 cm thick. The soil is Histosol build on granite bedrock. The fen receives high amounts of iron(II) via groundwater flow (up to 160 µM). This Fe(II) is oxidized in oxygenated surface layers to Fe(III) oxides, which are then available as an alternative electron acceptor for the oxidation of organic matter. The formation of an oxic- anoxic interface with a putative cycling of Fe has been observed due to the abundance of both Fe(II) oxidizers and Fe(III) reducers.

Click here to see this field site on a map >>

In our previous work we investigated the impact of drying and rewetting of peat soil. We determined the effect of altering the water table on mineralization processes like Fe(II) and CO2 formation rates, as well as enzymatic activities (Reiche et al., 2009). Our research also aimed to compare microbial Fe(III)-reduction and methanogenesis (Reiche et al., 2008) and to characterize the fen microbial communities. In particular, we were interested in characterizing microaerophilic Fe(II)-oxidizing bacteria (FeOB) and we successfully isolated an acid-tolerant FeOB, which competes with chemical oxidation at pH 4.0-5.5 (Lüdecke et al. 2010).

In our ongoing research, we are investigating how peatland FeOB can be important to carbon cycling by providing biogenic Fe(III) for Fe(III)-reducing bacteria, thereby suppressing methanogenesis. In addition, to better understand iron cycling we need to determine whether soluble Fe(III)-complexes, i.e., colloidal or chelated Fe(III), play a role as intermediates and facilitate the oxidation of Fe(II). We are working with Dr. Martial Taillefert (GA Tech) to measurements of Fe(III)-complexes with voltammetric techniques to determine how oxidized Fe is transported from oxic to anoxic zones, driving the iron cycle.

In the work of Anke Hädrich, the fate of acetate during the anaerobic oxidation of organic matter is being investigated. The sources and sinks of acetate were illuminated by a combination of porewater analysis, microcosm studies, stable isotope analysis (in collaboration with Dr. Verena Heuer), and microbial populations involved in acetogenesis were characterized by targeting the fhs functional gene.

Additional methods used in this project include anoxic microcosm experiments, gas chromatography, HPLC, dialyses chambers, FeS probes (to demonstrate the stability of anoxic conditions), cultivation and enrichment methods (microaerophilic Fe(II) oxidizers, Fe(III) reducers), microscopic methods (EDX, REM), XRD, Raman spectroscopy, Mössbauer spectroscopy, and photometric measurements.

Photos

Follow this link for more photos of the Schloeppnerbrunnen Fen site.
This temporary rainwater-exclusion roof was used in conjunction with an experiment to determine the effects of a drying event on geochemical processes in the fen.
This is a dialysis chamber for sampling porewater to determine geochemistry at high depth resolution.
Preparing equipment to make voltammetric depth measurements in the fen.
A large diameter peat core. This fen is somewhat atypical in that the peat only extends down 50 cm or so below the surface.
Measuring Fe gradients in microaerophilic Fe(II) oxidizer cultures using voltammetric techniques.
Measuring Fe gradients in the fen using voltammetric techniques.

Peer-Reviewed Publications

2012

  • Hädrich, A., Heuer, V.B., Herrmann, M., Hinrichs, K.-U. und K. Küsel. (2012). Origin and fate of acetate in an acidic fen. FEMS Microbiol., Accepted, published online ahead of print on 09 March 2012; DOI: 10.1111/j.1574-6941.2012.01352.x.

2010

  • Reiche, M.; Gleixner, G. & Küsel, K. 2010. Effect of peat quality on microbial greenhouse gas formation in an acidic fen. Biogeosciences 7(1): 187-198.
  • Lüdecke, C., Reiche, M., Eusterhues, K., Nietzsche, S., Küsel, K. 2010. Acid-tolerant microaerophilic Fe(II)-oxidizing bacteria promote Fe(III)-accumulation in a fen. Environmental Microbiology 12 (10): 2814–2825.

2009

  • Reiche, M.; Hädrich, A.; Lischeid, G. & Küsel, K. 2009. Impact of manipulated drought and heavy rainfall events on peat mineralization processes and source-sink functions of an acidic fen. J. Geophys. Res. 114: G02021.

2008

  • Küsel, K.; Blöthe, M.; Schulz, D.; Reiche, M. & Drake, H. L. 2008. Microbial reduction of iron and porewater biogeochemistry in acidic peatlands. Biogeosciences 5:1537-1549
  • Reiche, M.; Torburg, G. & Küsel, K. 2008. Competition of Fe(III) reduction and methanogenesis in an acidic fen. FEMS Microbiol. Ecol. 65: 88–101

2007

  • Schmalenberger, A., Drake, H. L., and Küsel, K. 2007. High unique diversity of sulfate-reducing prokaryotes in a depth gradient in an acidic fen. Environ. Microbiol. 9: 1317-1328.

2006

  • Alewell, C., Paul, S., Lischeid, G., Küsel, K., and Gehre, M. 2006. Characterizing the redox status in three different forested wetlands with biogeochemical data. Environ. Sci. Technol. 40: 7609-7615.
  • Paul, S., Küsel, K., and Alewell, C. 2006. Reduction processes in forest wetlands: tracking down heterogeneity of source/sink functions with a combination of methods. Soil Biol. Biochem. 38: 1028-1039.

2004

  • Küsel, K., and Alewell, C. 2004. Riparian zones in a forested catchment: hot spots for microbial reductive processes. In: Matzner, E. (ed.), Biogeochemistry of two German forested catchments in a changing environment, Ecol. Stud. 172: 377-395, Springer-Verlag.
  • Loy, A., Küsel, K., Lehner, A., Klein, M., Drake, H. L., and Wagner, M. 2004. Microarray and functional gene analyses of sulfate-reducing prokaryotes in low sulfate, acidic fens reveal co-occurrence of recognized genera and novel lineages. Appl. Environ. Microbiol. 70:6998-7009.

2003

  • Horn, M. A., Matthies, C., Küsel, K., Schramm, A., and Drake, H. L. 2003. Hydrogenotrophic methanogenesis by moderately acid-tolerant methanogens of a methane-emitting acidic peat. Appl. Environ. Microbiol. 69:74-83.

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