Previous Article | Next Article ![]()
Applied and Environmental Microbiology, December 2006, p. 7922-7924, Vol. 72, No. 12
0099-2240/06/$08.00+0 doi:10.1128/AEM.00819-06
Copyright © 2006, American Society for Microbiology. All Rights Reserved.
| SHORT REPORT |
,
Radioecology Section, National Research Institute of Fisheries Science, Fisheries Research Agency, 2-12-4 Fukuura, Kanazawa, Yokohama, Kanagawa 236-8648, Japan
Received 7 April 2006/ Accepted 10 October 2006
|
|
|---|
|
|
|---|
We attempted to isolate Tc-accumulating bacteria from marine samples (seawater, sediments, seaweeds, plankton, annelids, crustaceans, and fish) collected by the research vessel Soyo-maru of the National Research Institute of Fisheries Science. One hundred microliters of sample suspended in sterilized seawater was spread on modified PPES-II medium plates supplemented with 4.8 pmol of 99Tc as NH499TcO4 (Eckert & Ziegler, California) (11). Figure 1 shows an example of sterilized filter paper replicated from the 99Tc-supplemented PPES plates and the image of a storage phosphor screen (SPS) (Amersham Biosciences) exposed by the filter paper. The SPS was scanned with Storm860 (Amersham Biosciences) and analyzed by using ImageJ 1.33u software (NIH). Colonies accumulating 99Tc were detected as black spots on the image of SPS (Fig. 1B). About 5% of all colonies which grew on 99Tc spread plates had the ability to accumulate Tc. Five strains out of 231 colonies were able to remove Tc from the liquid culture medium. One typical strain (Tc-202), which displayed satisfactory growth and removal, was selected and used for the following studies. Tc-202 was isolated from the surface of drifting brown seaweed. Though the biochemical features of Tc-202 differed from those of the other Halomonas strains (see Table S1 in the supplemental material), the molecular phylogenetic analysis using the 16S rRNA gene sequences assigned Tc-202 to the genus Halomonas (see Fig. S1 in the supplemental material). Figure 1C shows the time course of cell growth for Tc-202 and the amount of Tc removed from solution. The optical density at 600 nm of the culture of Tc-202 increased from 0.1 (at the initial time) to 3.0 within 24 h (Fig. 1C, right axis). The amount of Tc precipitated with Tc-202 cells by centrifugation increased with cell growth and reached 55% of the total Tc added to the culture medium (Fig. 1C, left axis, at 72 h of incubation) in stationary phase. Although the status of Tc-202 shifted to extinction phase after 72 h, the amount of Tc removed from the medium hardly changed.
![]() View larger version (59K): [in a new window] |
FIG. 1. Screening of Tc-accumulating microorganisms. (A) Filter paper with colonies transferred from a plate supplemented with 4.8 pmol of 99Tc at 15°C for 48 h. (B) Autoradiogram of the filter paper exposed to SPS for 48 h in a lead shield. Arrows indicate the colony of Tc-202. (C) Time course of growth and Tc removal by Tc-202. A cell suspension (optical density at 600 nm [O.D.600] = 0.1) was prepared with the medium containing 0.16 µM of NH499TcO4 and incubated at 15°C with shaking at 120 rpm. At each period, cell density was measured and 99Tc radioactivity of the supernatant after centrifugation at 12,000 x g for 5 min was measured with a liquid scintillation counter. Values are means ± standard deviations for four independent experiments.
|
![]() View larger version (24K): [in a new window] |
FIG. 2. Removal of Tc from solution by Tc-202 and other strains of Halomonas. Cell density was adjusted at 0.1 at the start of the experiment with modified PPES medium containing 0.16 µM of 99Tc. After incubation at 15°C for 24 h, cells and insoluble Tc were removed from solution by centrifugation prior to measurement of the percentage of Tc remaining in the supernatant with a liquid scintillation counter. The control was incubation without bacteria. Values are means ± standard deviations for four independent experiments.
|
Paper chromatography analysis indicated the Tc(V) band (Rf value = 0.0) was detected in the precipitate fraction of Tc-202 (Fig. 3, lane 1). However, no band representing other reduced Tc species, such as Tc(IV) (Rf = 0.9), was detected. No band was detected in the fractions of the control without bacteria or in those of the type strains of Halomonas (data not shown).
![]() View larger version (59K): [in a new window] |
FIG. 3. Chromatogram of Tc removed by Tc-202 cultured in medium containing 1.6 µM of 99Tc. After incubation at 15°C for 24 h, cells and insoluble Tc were collected from solution by centrifugation at 12,000 x g for 5 min. The cell pellet was spotted on 3MM filter paper and developed using 1 N HCl. The filter paper was exposed to SPS for 48 h. Lane 1, Tc-202 incubated with 99Tc(VII); lane 2, Tc(V) standard; lane 3, Tc(VII) standard. Tc(V) was prepared by reduction of Tc(VII). Tc(V) and Tc(VII) represent Rf values of 0.0 and 0.7, respectively.
|
Boiled cells of Tc-202 failed to remove Tc from the culture medium (data not shown). Therefore, it was predicted that some proteins are involved in the process of Tc removal by Tc-202. Previous studies have revealed that reduction of Tc by Escherichia coli and Desulfovibrio fructosovorans is mediated by hydrogenase (4, 8). Tc reduction by these bacteria was completely inhibited by 0.5 mM Cu(II) ion. In contrast, Tc removal by Tc-202 was stimulated by the presence of the Cu(II) ion (see Fig. S2B in the supplemental material). Thus, the removal process of Tc-202 is considered to be carried out by a different kind of hydrogenase or to progress through a different mechanism from that of E. coli and D. fructosovorans.
In conclusion, Tc-202, identified as a Halomonas sp., has the ability to remove Tc from solutions over a broad pH range under aerobic conditions. The removal ability of Tc-202 is less than those of microorganisms previously described (4, 6-10, 13, 16). However, considering the various kinds of waste and environmental conditions, aerobic and broad-pH-range conditions for removal by the Tc-202 strain are considered to be beneficial for practical use. The Tc-202 strain is anticipated to be able to play an important role in development of new methods for removal of Tc from contaminated areas and wastes.
Published ahead of print on 20 October 2006. ![]()
Supplemental material for this article may be found at http://aem.asm.org/. ![]()
|
|
|---|
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Copyright © 2009 by the American Society for Microbiology. For an alternate route to Journals.ASM.org, visit: http://intl-journals.asm.org | More Info»