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Kevin W. Mandernack

Publications and source records attributed to Kevin W. Mandernack.

3 recordsLinked to original sources

The relative contribution of methanotrophs to microbial communities and carbon cycling in soil overlying a coal-bed methane seep

Seepage of coal-bed methane (CBM) through soils is a potential source of atmospheric CH 4 and also a likely source of ancient (i.e. 14 C-dead) carbon to soil microbial communities. Natural abundance 13 C and 14 C compositions of bacterial membrane phospholipid fatty acids (PLFAs) and soil gas CO 2 and CH 4 were used to assess the incorporation of CBM-derived carbon into methanotrophs and other members of the soil microbial community. Concentrations of type I and type II methanotroph PLFA biomarkers (16:1ω8c and 18:1ω8c, respectively) were elevated in CBM-impacted soils compared with a control site. Comparison of PLFA and 16s rDNA data suggested type I and II methanotroph populations were well estimated and overestimated by their PLFA biomarkers, respectively. The δ 13 C values of PLFAs common in type I and II methanotrophs were as negative as −67‰ and consistent with the assimilation of CBM. PLFAs more indicative of nonmethanotrophic bacteria had δ 13 C values that were intermediate indicating assimilation of both plant- and CBM-derived carbon. Δ 14 C values of select PLFAs (−351 to −936‰) indicated similar patterns of CBM assimilation by methanotrophs and nonmethanotrophs and were used to estimate that 35–91% of carbon assimilated by nonmethanotrophs was derived from CBM depending on time of sampling and soil depth.

FEMS Microbiology Ecology

Microbial carbon cycling in oligotrophic regional aquifers near the Tono Uranium Mine, Japan as inferred from δ13C and Δ14C values of in situ phospholipid fatty acids and carbon sources

Microorganisms are ubiquitous in deep subsurface environments, but their role in the global carbon cycle is not well-understood. The natural abundance δ 13 C and Δ 14 C values of microbial membrane phospholipid fatty acids (PLFAs) were measured and used to assess the carbon sources of bacteria in sedimentary and granitic groundwaters sampled from three boreholes in the vicinity of the Tono Uranium Mine, Gifu, Japan. Sample storage experiments were performed and drill waters analyzed to characterize potential sources of microbial contamination. The most abundant PLFA structures in all waters sampled were 16:0, 16:1ω7 c , cy 17:0, and 18:1ω7 c . A PLFA biomarker for type II methanotrophs, 18:1ω8 c , comprised 3% and 18% of total PLFAs in anoxic sedimentary and granitic waters, respectively, sampled from the KNA-6 borehole. The presence of this biomarker was unexpected given that type II methanotrophs are considered obligate aerobes. However, a bacterium that grows aerobically with CH 4 as the sole energy source and which also produces 56% of its total PLFAs as 18:1ω8 c was isolated from both waters, providing additional evidence for the presence of type II methanotrophs. The Δ 14 C values determined for type II methanotroph PLFAs in the sedimentary (−861‰) and granite (−867‰) waters were very similar to the Δ 14 C values of dissolved inorganic carbon (DIC) in each water (∼−850‰). This suggests that type II methanotrophs ultimately derive all their carbon from inorganic sources, whether directly from DIC and/or from CH 4 produced by the reduction of DIC. In contrast, δ 13 C values of type II PLFAs in the sedimentary (−93‰) and granite (−60‰) waters indicate that these organisms use different carbon assimilation schemes in each environment despite very similar δ 13 C CH 4 "> δ13CCH4 values (∼−95‰) for each water. The δ 13 C PLFA values (−28‰ to −45‰) of non-methanotrophic bacteria in the KNA-6 LTL water do not clearly distinguish between heterotrophic and autotrophic metabolisms, but Δ 14 C PLFA values indicate that >65% of total bacteria filtered from the KNA-6 LTL water are heterotrophs. Ancient Δ 14 C values (∼−1000‰) of some PLFAs suggest that many heterotrophs utilize ancient organic matter, perhaps from lignite seams within the sedimentary rocks. The more negative range of δ 13 C PLFA values determined for the KNA-6 granitic water (−42‰ to −66‰) are likely the result of a microbial ecosystem dominated by chemolithoautotrophy, perhaps fuelled by abiogenic H 2 . Results of sample storage experiments showed substantial shifts in microbial community composition and δ 13 C PLFA values (as much as 5‰) during 2–4 days of dark, refrigerated, aseptic storage. However, water samples collected and immediately filtered back in the lab from freshly drilled MSB-2 borehole appeared to maintain the same relative relationships between δ 13 C PLFA values for sedimentary and granitic host rocks as observed for samples directly filtered under artesian flow from the KNA-6 borehole of the Tono Uranium Mine.

Tono Uranium Mine

The δ 15 N and δ 18 O values of N 2 O produced during the co-oxidation of ammonia by methanotrophic bacteria

In order to determine if the δ 15 N and δ 18 O values of N 2 O produced during co-oxidation of NH 4 + by methanotrophic (methane oxidizing) bacteria can be isotopically distinguished from N 2 O produced either by autotrophic nitrifying or denitrifying bacteria, we conducted laboratory incubation experiments with pure cultures of methanotrophic bacteria that were provided NH 4 Cl as an oxidation substrate. The N 2 O produced during NH 4 + oxidation by methanotrophic bacteria showed nitrogen isotope fractionation between NH 4 + and N 2 O ( ε N 2 O–NH 4 + ) of − 48 and − 55‰ for Methylomonas methanica and Methylosinus trichosporium , OB3b respectively. These large fractionations are similar to those previously measured for autotrophic nitrifying bacteria and consistent with N 2 O formation by multiple rate limiting steps that include NH 4 + oxidation by the methane monooxygenase enzyme and reduction of NO 2 − to N 2 O. Consequently, N 2 O formed by NH 4 + oxidation via methanotrophic or autotrophic nitrifying bacteria might generally be characterized by lower δ 15 N N 2 O values than that formed by denitrificaiton, although this also depends on the variability of δ 15 N of available nitrogen sources (e.g., NH 4 + , NO 3 − , NO 2 − ). Additional incubations with M. trichosporium OB3b at high and low CH 4 conditions in waters of different δ 18 O values revealed that 19–27% of the oxygen in N 2 O was derived from O 2 with the remainder from water. The biochemical mechanisms that could explain this amount of O 2 incorporation are discussed. The δ 18 O of N 2 O formed under high CH 4 conditions was ~ + 15‰ more positive than that formed under lower CH 4 conditions. This enrichment resulted in part from the incorporation of O 2 into N 2 O that was enriched in 18 O due to an isotope fractionation effect of − 16.1 ± 2.0‰ and − 17.5 ± 5.4‰ associated with O 2 consumption during the high and low methane concentration incubations, respectively. Therefore, N 2 O formed by NH 4 + oxidation via methanotrophic or autotrophic nitrifying bacteria can have very positive δ 18 O N 2 O values if the O 2 incorporated is previously enriched in 18 O from high rates of respiration. Nitrous oxide was collected from various depths in soils overlying a coal-bed methane seep where methanotrophic bacteria are naturally enriched. In one sampling when soil methane concentrations were very high, the δ 18 O VSMOW values of the N 2 O were highly enriched (+ 50‰), consistent with our laboratory experiments. Thus, soils overlying methane seeps could provide an 18 O-enriched source of atmospheric N 2 O.

Chemical Geology