Utilization of fluorescent microspheres and a green fluorescent protein-marked strain for assessment of microbiological contamination of permafrost and ground ice core samples from the Canadian High Arctic.

Fluorescent microspheres were applied in a novel fashion during subsurface drilling of permafrost and ground ice in the Canadian High Arctic to monitor the exogenous microbiological contamination of core samples obtained during the drilling process. Prior to each drill run, a concentrated fluorescent microsphere (0.5-microm diameter) solution was applied to the interior surfaces of the drill bit, core catcher, and core tube and allowed to dry. Macroscopic examination in the field demonstrated reliable transfer of the microspheres to core samples, while detailed microscopic examination revealed penetration levels of less than 1 cm from the core exterior. To monitor for microbial contamination during downstream processing of the permafrost and ground ice cores, a Pseudomonas strain expressing the green fluorescent protein (GFP) was painted on the core exterior prior to processing. Contamination of the processed core interiors with the GFP-expressing strain was not detected by culturing the samples or by PCR to detect the gfp marker gene. These methodologies were quick, were easy to apply, and should help to monitor the exogenous microbiological contamination of pristine permafrost and ground ice samples for downstream culture-dependent and culture-independent microbial analyses.

Purification of the NADP+:F420 oxidoreductase of Methanosphaera stadtmanae.

Methanosphaera stadtmanae (DSM 3091) is a methanogen that requires H2 and CH3OH for methanogenesis. The organism does not possess an F420-dependent hydrogenase and only low levels of F420. It does however possess NADP+:F420 oxidoreductase activity. The NADP+:F420 oxidoreductase, the enzyme which catalyses the electron transfer between NADP+ and F420 in this organism, was purified and characterized. NAD+, NADH, FMN, and FAD could not be used as electron acceptors. Optimal pH for F420 reduction was 6.0, and 8.5 for NADP+ reduction. During the purification process, it was noted that precipitation with (NH4)2SO4 increased total activity 16-fold but reduced the stability of the enzyme. However, recombination of cell-free extracts with resuspended 65-90% (NH4)2SO4 pellet returned activity to near cell-free extract levels. Neither high salt or protease inhibitors were effective in stabilizing the activity of the partially purified enzyme. The purified enzyme from M. stadtmanae possessed a molecular weight of 148 kDa as determined by gel filtration chromatography and native-PAGE, consisting of alpha, beta, and gamma subunits of 60, 50, and 45 kDa, respectively, using SDS-PAGE. The Km values were 370 microM for NADP+, 142 microM for NADPH, 62.5 microM for F420, and 7.7 microM for F420H2. These values were different from the Km values observed in the cell-free extract.