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Applied and Environmental Microbiology, October 2001, p. 4583-4587, Vol. 67, No. 10
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.10.4583-4587.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Reduction of Technetium(VII) by
Desulfovibrio fructosovorans Is Mediated by the
Nickel-Iron Hydrogenase
Gilles
De Luca,1
Pascale
de
Philip,2,3
Zorah
Dermoun,2,3
Marc
Rousset,2 and
André
Verméglio1,*
CEA Cadarache, DSV/DEVM/Laboratoire de
Bioénergétique Cellulaire, 13108 Saint
Paul-Lez-Durance,1 Laboratoire de
Bioénergétique et Ingénierie des Protéines, UPR
9036-CNRS, 13402 Marseille Cedex 20,2 and
Université de Provence 3, 13331 Marseille Cedex
3,3 France
Received 10 April 2001/Accepted 12 July 2001
 |
ABSTRACT |
Resting cells of the sulfate-reducing bacterium
Desulfovibrio fructosovorans grown in the absence of
sulfate had a very high Tc(VII)-reducing activity, which led to the
formation of an insoluble black precipitate. The involvement of a
periplasmic hydrogenase in Tc(VII) reduction was indicated (i) by the
requirement for hydrogen as an electron donor, (ii) by the tolerance of
this activity to oxygen, and (iii) by the inhibition of this activity
by Cu(II). Moreover, a mutant carrying a deletion in the
nickel-iron hydrogenase operon showed a dramatic decrease in the rate
of Tc(VII) reduction. The restoration of Tc(VII) reduction by
complementation of this mutation with nickel-iron hydrogenase genes
demonstrated the specific involvement of the periplasmic nickel-iron
hydrogenase in the mechanism in vivo. The Tc(VII)-reducing activity was
also observed with cell extracts in the presence of hydrogen. Under
these conditions, Tc(VII) was reduced enzymatically to soluble Tc(V) or
precipitated to an insoluble black precipitate, depending on the
chemical nature of the buffer used. The purified nickel-iron
hydrogenase performed Tc(VII) reduction and precipitation at high
rates. These series of genetic and biochemical approaches demonstrated
that the periplasmic nickel-iron hydrogenase of sulfate-reducing
bacteria functions as a Tc(VII) reductase. The role of cytochrome
c3 in the mechanism is also discussed.
 |
INTRODUCTION |
Technetium
(99Tc) is a fission product of
235U formed during the generation of nuclear
power. The solubility and mobility of Tc are highly dependent upon its
redox state. Under oxic conditions, Tc is present in its most stable
form, the pertechnetate anion [Tc(VII)O4
]. This form,
which is highly soluble and mobile in the environment, can enter the
food chain as a sulfate analogue (2, 20, 34). These
properties, coupled with its long half-life (2.13 × 105 years), make contamination by Tc one of the
major factors in the long-term impact of the nuclear fuel cycle. One
approach to remove 99Tc from aqueous solution is
to reduce the pertechnetate form Tc(VII) into the insoluble,
low-valence form Tc(IV). This can be achieved by abiotic
(5) or biotic (19, 20) processes.
Abiotic reduction involves electron transfer between Fe(II)-containing
minerals and Tc(VII) (3). The most efficient mineral appears to be magnetite, particularly when it is anodically polarized (5). Biotic precipitation of pertechnetate, probably its
reduction into a low-valence, insoluble Tc oxide, has been reported for several species of bacteria during the past few years. These include species such as Geobacter metallireducens (14),
Geobacter sulfurreducens (17),
Escherichia coli (13), Desulfovibrio
desulfuricans (16), Shewanella
putrefaciens (33), and Deinococcus
radiodurans (9). Both indirect (chemical) and direct
(enzymatic) reduction processes have been observed, depending on the
bacterial growth conditions. Chemical processes have been clearly
demonstrated in the case of the sulfate-reducing bacterium D. desulfuricans and in the case of the metal-reducing bacterium
G. sulfurreducens (15, 17). Cultures of
D. desulfuricans supplied with sulfate and lactate as
electron acceptor and donor, respectively, precipitated Tc
extracellularly as an insoluble sulfide. In this case, the Tc sulfide
results from the chemical reaction between H2S,
formed during reduction of sulfate, and
TcO4
(19). A
chemical reduction of Tc(VII) by the Fe(II) is also observed during
reduction of Fe(III) by G. sulfurreducens (17). In addition, enzymatic reduction of Tc(VII) has been reported for
different bacterial species. There are several lines of evidence indicating that this process involves hydrogenase, an enzyme which reversibly catalyzes the splitting of molecular hydrogen into protons
and electrons. Indeed, hydrogen is an effective electron donor for
Tc(VII) reduction for E. coli, D. desulfuricans,
and S. putrefaciens (13, 15, 16, 33).
Similarly, in the case of G. sulfurreducens, Tc(VII)
reduction has an exclusive requirement for hydrogen as the electron
donor, unlike the reduction of Fe(III), which can be coupled to the
oxidation of different organic electron donors (17). The
most convincing evidence has come from the work of Lloyd et al.
(13), who showed that mutants of E. coli defective in the synthesis of transcription factor FNR, of molybdenum cofactor, or of formate dehydrogenase H were unable to reduce Tc(VII),
indicating a role for the formate-hydrogenlyase complex in the reduction.
Desulfovibrio fructosovorans (24) is a
sulfate-reducing bacterium amenable to molecular biological
study. Three different hydrogenases have been identified in this
bacterium: [NiFe] and [Fe] hydrogenases (1, 10, 27),
localized in the periplasm, and a heterotetrameric NADP-reducing [Fe]
hydrogenase, localized in the cytoplasm (4, 21, 22). In
the present work, we have combined physiological, genetic, and
biochemical approaches to determine, at the molecular level, the exact
roles of these different hydrogenases in Tc(VII) reduction and precipitation.
 |
MATERIALS AND METHODS |
Growth of organisms and preparation of extracts.
The
wild-type strain D. fructosovorans DSM 3604 (24), D. fructosovorans strain MR400 carrying a
deletion in the nickel-iron hydrogenase operon (26), or
strain MR400 complemented with the nickel-iron hydrogenase genes
(28) was grown for 72 h at 37°C in stoppered 100-ml
bottles supplemented, when required, with kanamycin and gentamicin (50 µg/ml) in a minimal medium defined by Widdel and Pfennig
(32). For Tc(VII) reduction assay, the strains were
subcultured three times in a medium containing 20 mM fructose as an
electron donor and 20 mM fumarate as an electron acceptor.
D. fructosovorans cells grown to an optical density at 600 nm of 1.0 (20 g [wet weight]) were collected by centrifugation at
2,000 × g, washed twice with Tris-HCl (10 mM, pH 7.6),
and stored at
80°C before use. Unless otherwise noted, all
operations were performed under air at 4°C. Freshly thawed cells were
passed twice in a French pressure cell at 1,000 lb/in2
pressure in the presence of a few crystals of DNase. Cell debris were removed by centrifugation at 4,000 × g for 30 min, and the supernatant (crude extract) was then centrifuged at
120,000 × g for 1 h. The resulting soluble
fraction was used for purification and for Tc(VII) reduction.
Tc(VII) reduction by resting cell suspensions or purified
proteins.
Bacteria grown for 72 h at 37°C were transferred
anaerobically in a centrifuge tube stoppered with a rubber septum (Suba
seal no. 37; Aldrich) and washed four times in 50 mM Tris-HCl buffer (pH 8.0). The bacterial pellet was resuspended anaerobically in either
Tris-HCl (20 mM, pH 8.0 or 8.5), MES (morpholineethanesulfonic acid)
(20 mM, pH 5.5), MOPS (morpholinepropanesulfonic acid) (20 mM, pH 6.5 or 7.5), or citrate-sodium phosphate buffer (20 mM, pH 4.5) to a
concentration of about 0.5 mg of cells (dry weight) per ml. Aliquots
(1.9 ml) of the washed cell suspension were transferred under nitrogen
to 10-ml serum bottles sealed with butyl rubber stoppers. Electron
donors (fructose, fumarate, lactate, pyruvate, or formate) were added
from concentrated stock solutions to a final concentration of 10 mM.
For these experiments, all of the bottles were depleted of oxygen by
three cycles of vacuum-nitrogen and then flushed under nitrogen for 10 min. When hydrogen was supplied as an electron donor for metal
reduction, the gas was flushed into the headspace of the bottles for 20 min with resting cell suspensions or for 180 min with soluble extracts
or purified proteins in order to activate the nickel-iron hydrogenase,
as described by Fernandez et al. (6) and Hatchikian et al.
(10). A solution (100 µl) of ammonium pertechnetate
(NH4TcO4) (Amersham Life
Science Products, Orsay, France, and NEN Life Science Products, Paris, France), deaerated by flushing with argon 10 min before use, was added to a final concentration of 1 mM for cell suspensions. Concentrations of 250 µM to 6 mM were used for
Km and
Vmax determination, and a
concentration of 0.5 mM was used for reduction by soluble extracts or
by purified proteins.
Measurements of Tc.
Total Tc in solution was assayed by
autoradiography with a STORM 840 PhosphorImager (Molecular Dynamics) as
described by Lloyd and Macaskie (14). Tc uptake was
expressed as the percentage or the concentration of Tc remaining
in solution after centrifugation in an Eppendorf 5415C centrifuge
(14,000 rpm, 20 min) in comparison with total Tc. Tc(VII)
(Rf = 0.7) was also separated from
reduced, nonmobile [Tc(V); Rf = 0.0] and
mobile [mainly Tc(IV); Rf = 0.9] soluble
Tc species using paper chromatography (29) prior to autoradiography and quantification using a PhosphorImager. In most
experiments, concentrations of Tc were also quantified using a Packard
1900 TR analyzer. Each sample (10 µl) was added to a glass
scintillation vial with 10 ml of Ultima Gold or Insta-Gel-Plus scintillation fluid (Packard Instrument S. A., Rungis, France). Disintegration counts per minute were recorded at between 20 and 250 keV for 5 min.
Purification of cytochrome c3 and
[NiFe] hydrogenase.
Pure cytochrome
c3 and [NiFe] hydrogenase were
obtained in four steps, and all operations were performed at pH 7.6. In
the first step, the soluble fraction was loaded on a DEAE-Sepharose (Pharmacia) column. This column retains all of the hydrogenase but not
the cytochrome c3. The fraction
containing cytochrome c3 was
subsequently loaded on an SP-Sepharose (Pharmacia) column equilibrated
with Tris-HCl (10 mM, pH 7.6) and eluted at 200 mM NaCl. The eluted
fraction was then concentrated in a 15-ml Centriprep YM-10 (Centrifugal
Filter Device; Amicon) and filtered through a Sephacryl S-200
high-resolution column (Pharmacia). Finally, cytochrome was loaded on a
hydroxylapatite (Bio-Rad) column and eluted at 200 mM potassium
phosphate (pH 7.6). Purified cytochrome exhibited a broad single band
of 16.5 kDa in sodium dodecyl sulfate-15% polyacrylamide gel
electrophoresis and a purity index
(A553reduced
A570reduced/A280oxidized)
of 3.02.
The hydrogenase fraction was eluted from the first DEAE-Sepharose
column with 100 mM NaCl. This fraction was subsequently loaded on a
Q-Sepharose (Pharmacia) column equilibrated with Tris-HCl (10 mM, pH
7.6) and eluted at 320 mM NaCl. The eluted fraction was then
concentrated in a 50-ml ultrafiltration cell with a PM 30 membrane
(Amicon) and filtered through a Sephacryl S-200 high-resolution column
(Pharmacia). Finally, hydrogenase was loaded on a hydroxylapatite (Bio-Rad) column and eluted at 180 mM potassium phosphate (pH 7.6). The
hydrogenase was judged to be homogeneous by the following criteria: (i)
native polyacrylamide gel electrophoresis giving a single band of
protein which catalyzed the hydrogen-dependent reduction of methyl
viologen, (ii) the presence of two single bands at 29 and 60 kDa after
sodium dodecyl sulfate-polyacrylamide gel electrophoresis, and (iii) an
absorbance ratio
(A400/A280) equal to 0.28.
Analytical procedures.
Protein concentrations were measured
with a bicinchoninic acid assay kit (Pierce) by the method of Smith et
al. (30), using bovine serum albumin as a standard. Sodium
dodecyl sulfate-polyacrylamide gel electrophoresis was carried out by
the method of Laemmli (11). The hydrogen uptake activity
was visualized in the gel after native 7.5% polyacrylamide gel
electrophoresis as previously described (4). UV-visible
spectra of the pure nickel-iron hydrogenase and the cytochrome
c3 were recorded on a Varian
spectrophotometer. The hydrogen uptake activity was measured
spectrophotometrically by monitoring the reduction of methyl viologen
(6) at 30°C in a tightly closed quartz cuvette filled
with 1 ml of reaction buffer (50 mM Tris-HCl [pH 8], 1 mM methyl
viologen) bubbled for 20 min with H2. The
proton-deuterium (H-D) exchange reaction was measured in whole-cell
suspensions by a mass spectrometric method as described previously
(31). Production of H2 and HD was
used to calculate the exchange activity.
 |
RESULTS |
Microbial reduction of technetium: physiology and kinetic
parameters.
In order to study exclusively the enzymatic
contribution to Tc(VII) reduction by sulfate-reducing bacteria,
chemical Tc(VII) reduction was prevented by growing D. fructosovorans in a mineral medium in the absence of sulfate.
Cells grown under these conditions had a greyish color with no black
precipitate of iron sulfide. These conditions were preferred to those
used by Lloyd et al. (15) for D. desulfuricans,
which did not completely abolish the formation of iron sulfide in the
case of D. fructosovorans (data not shown).
After 2 h of incubation under hydrogen, approximately 92% of the
Tc(VII) (1 mM) present was reduced by a resting cell suspension of
D. fructosovorans to an insoluble black precipitate (Fig.
1A), as observed in the case of S. putrefaciens (33). On the other hand, only a minor
reduction (13%) occurred after 24 h when hydrogen was replaced by
nitrogen (Fig. 1A and Table 1). Tc(VII)
reduction occurred between pH 5.5 and 8.0 (Fig. 1B) and between 10 and
40°C (data not shown). The highest rate was observed at pH 5.5 and between 30 and 40°C, where an apparent
Km of 2 mM and a maximal velocity of 7 mmol of Tc(VII) reduced per g (dry weight) of bacteria per h were
determined using a Lineweaver-Burk plot.

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FIG. 1.
(A) Tc(VII) reduction and precipitation by resting cells
of D. fructosovorans supplied with hydrogen (closed
circles) as an electron donor. Control cultures with nitrogen (open
circles) contained no added electron donor. The cells were incubated
for 24 h at 23°C and pH 8.0. (B) Effect of pH on Tc(VII)
reduction by D. fructosovorans. Hydrogen was supplied as
the electron donor, and the cells were incubated at room temperature
(23°C) and pH 4.5 (open circles), 5.5 (closed triangles), 6.5 (open
squares), 7.5 (open triangles), 8.0 (closed circles), or 8.5 (inverted
closed triangles).
|
|
Several compounds, such as fructose, lactate, pyruvate, fumarate, and
formate, which are efficient electron donors for sulfate reduction in
D. fructosovorans (24) were tested for Tc(VII) reduction (Table 1). Only hydrogen appeared to be an efficient electron
donor for Tc(VII) reduction (Table 1), suggesting the involvement of a
hydrogenase in this process.
Inhibitors and genetic determinants.
The Tc(VII) reduction
activity of D. fructosovorans was not inhibited by exposure
of the cells to air, which indicated oxygen tolerance of the enzyme
(Fig. 2). Moreover, this activity was irreversibly inhibited by a 10-min preincubation of the cells with 0.5 mM CuCl2, a specific inhibitor of the periplasmic
hydrogen uptake activity in vivo (8) (Fig. 2). These
results excluded a possible role of NADP-reducing hydrogenase in the
reduction mechanism, as this enzyme is cytoplasmic and oxygen sensitive (4, 22). To investigate the role of the [NiFe]
hydrogenase, which is periplasmic and oxygen tolerant and is the major
hydrogenase produced by D. fructosovorans (10),
Tc(VII) reduction by strain MR400, which carries a specific deletion of
the structural genes of this hydrogenase (26), was
studied. This deletion strain showed a dramatic decrease in the rate of
reduction (Fig. 2): only 20% of the Tc(VII) was reduced in 3 h,
although iron-only hydrogenase activity still represented about 16% of
the wild-type level in both the hydrogen uptake and deuterium-hydrogen
exchange activities (data not shown). Moreover, the complementation of strain MR400 by the nickel-iron hydrogenase genes carried on a multicopy plasmid (28) restored hydrogenase activity
(hydrogen uptake and deuterium exchange) (data not shown) and Tc(VII)
reductase activity (Fig. 2) to wild-type levels. These results
demonstrated the essential role of the nickel-iron hydrogenase in the
in vivo reduction of Tc(VII) by the sulfate-reducing bacterium D. fructosovorans.

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FIG. 2.
Effect of hydrogenase inhibitors or hydrogenase contents
on Tc(VII) reduction in D. fructosovorans. Cells were
incubated at 23°C and pH 5.5 with hydrogen supplied as an electron
donor. Open circles, wild-type strain (control); closed circles,
wild-type strain after preincubation with air; closed squares,
wild-type strain after preincubation with 0.5 mM CuCl2;
closed triangles, mutant MR400 with the nickel-iron hydrogenase genes
deleted; open triangles, complemented mutant MR400.
|
|
Reduction and precipitation of Tc(VII) by soluble extracts and
purified proteins.
In order to provide biochemical evidence of the
involvement of the [NiFe] hydrogenase and possibly other
electron carriers in the biological reduction of Tc(VII),
this activity was tested in different fractions: (i) crude
extract (soluble and membranes proteins) and (ii) soluble fraction
(supernatant from centrifugation at 120,000 × g)
suspended in MOPS (20 mM, pH 6.5). In both cases, 85% of the Tc(VII)
was reduced and precipitated as shown by the appearance of brownish
particles after 18 h of incubation in the presence of hydrogen. No
reduction or precipitation occurred when hydrogen was omitted. This
experiment demonstrates that reduction of Tc(VII) is performed in vitro
by soluble proteins. This further shows that the precipitation of
reduced forms of Tc does not necessitate the presence of membranes as
nucleation sites. On the other hand, the precipitation process is
highly dependent on the buffer used. Indeed, when Tris-HCl (50 mM, pH
8.0) was used, 80% of the Tc(VII) (Rf = 0.7) was reduced to Tc(V) (Rf = 0) in the
first 24 h as shown by paper chromatography (Fig.
3) (29), but no
precipitation occurred. This result indicates that Tc(VII) reduction
mediated by the soluble fraction is not obligately followed by
precipitation. The precipitation process seems to be dependent mainly
on the chemical nature of the buffer used and the pH. This behavior is different from that observed in vivo, where the precipitation of Tc is
independent of the buffer used (Fig. 1B).

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FIG. 3.
Chromatograms of Tc(VII) reduction by soluble fractions
of D. fructosovorans at pH 8.0. Soluble proteins were
incubated at 23°C and pH 8.0 (20 mM Tris-HCl) with hydrogen as an
electron donor and 0.5 mM Tc(VII). Tc(VII),
Rf = 0.7; Tc(V),
Rf = 0.0.
|
|
To identify the proteins and enzymes involved in Tc(VII)
reduction in vitro, we have tested the involvement of the purified [NiFe] hydrogenase and its physiological electron acceptor (12, 25), cytochrome c3, in this
process. Pure hydrogenase at a high concentration (3.9 µM) exhibited
a high Tc(VII)-reducing activity [95% of Tc(VII) reduced in 2 h]
(Table 2). Diluted hydrogenase (0.4 µM)
reduced Tc(VII) more slowly, and 95% of the Tc(VII) was reduced only
after 18 h. Preincubation with Cu(II) inhibited 85% of this
activity. This value corresponded to the level of inhibition of methyl
viologen reduction observed with Desulfovibrio gigas [NiFe] hydrogenase (7). On the other hand, purified
cytochrome c3 alone (0.4 µM) did not
precipitate or reduce Tc(VII) with hydrogen. In the presence of both
[NiFe] hydrogenase and cytochrome c3
at low concentrations, reduction of Tc(VII) occurred in less than 1 h (Table 2).
The high reducing activity observed under such conditions may be
related to the reactivation of the hydrogenase in the presence of
cytochrome c3 (6).
Indeed, the addition of the oxidative agent Tc(VII)
(TcO4
/TcO2,
E'o = +0.748 V) may have induced some
inactivation of the hydrogenase, which is more readily reactivated in
the presence of its physiological electron acceptor, cytochrome
c3 (6).
 |
DISCUSSION |
In the present work, we report that D. fructosovorans
reduces Tc(VII) and removes it efficiently from solution. The
reduction process occurs at wide ranges of temperature (10 to 40°C)
and pH (5.5 to 8.0). The optimum pH (around pH 5.5) probably reflects the best affinity of hydrogenase for
TcO4
. Reduction of Tc(VII)
with increasing Tc concentrations gave an apparent
Km of 2 mM, which is slightly higher than
but consistent with the Km of 0.5 mM
determined by Lloyd et al. (18) with E. coli
and D. desulfuricans supplied with formate as an electron donor. At a high concentration of
TcO4
(6 mM), D. fructosovorans exhibits the highest rate of reduction described so
far, i.e., 7 mmol of Tc reduced per g (dry weight) of bacteria per h.
The corresponding values for E. coli and D. desulfuricans were 12.5 and 800 µmol of Tc reduced per g (dry weight) of bacteria per h, respectively (18). The high
efficiency of the Tc(VII)-reducing activity of D. fructosovorans within wide ranges of pH and temperature makes this
bacterium a good candidate for the removal of this radionuclide from
solution in a bioremediation process.
The Tc(VII)-reducing activity of D. fructosovorans requires
the presence of hydrogen as an electron donor, whereas organic electron
donors such as lactate, pyruvate, fumarate, fructose, and formate are
inefficient (Table 1). The essential role of the nickel-iron
hydrogenase in the process of reduction of Tc(VII) was further proved
by genetic and biochemical studies. This role is supported by (i) in
vivo and in vitro inhibition of the activity by Cu(II), (ii) oxygen
tolerance of the activity, (iii) the dramatic decrease of Tc(VII)
reduction in a mutant lacking [NiFe] hydrogenase structural genes,
and (iv) demonstration of direct reduction by purified [NiFe]
hydrogenase. This is the first report which demonstrates the reduction
and removal of Tc(VII) from solution with purified nickel-iron
hydrogenase. Reduction of Tc(VII) at the expense of molecular hydrogen
is the most efficient and most widespread mechanism in the bacteria
tested so far. Even though alternative electron donors can be used by
several species, such as E. coli (13), S. putrefaciens (14, 33), and D. desulfuricans (16), the oxidation of these
organic substrates often leads to the production of hydrogen or
formate. Therefore, hydrogenase (alone or in a formate-hydrogenlyase
complex) appears to be the major component involved in enzymatic
Tc(VII) reduction.
In addition to the ability to reduce Tc(VII), selenite- and
chromate-reducing activities have been reported for the [Fe]
hydrogenase of Clostridium pasteurianum (35)
and the [Fe] hydrogenase of sulfate-reducing bacteria
(23), respectively. Metal reductase activity of
hydrogenases therefore appears to be a widespread property.
 |
ACKNOWLEDGMENTS |
We gratefully acknowledge Bernard Dimon and Patrick Carrier for
the mass spectrometric measurements and Jean-Pierre
Bélaïch for his support and helpful discussions.
Marc Rousset is Laboratoire de Recherche Conventionné avec le CEA
no. 25V.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: CEA Cadarache,
DSV/DEVM/LBC, 13108 Saint Paul-Lez-Durance, France. Phone: 33 (0)4.42.25.46.30. Fax: 33 (0)4.42.25.47.01. E-mail:
avermeglio{at}cea.fr.
 |
REFERENCES |
| 1.
|
Casalot, L.,
C. E. Hatchikian,
N. Forget,
P. de Philip,
Z. Dermoun,
J. P. Bélaïch, and M. Rousset.
1998.
Molecular study and partial characterization of iron-only hydrogenase in Desulfovibrio fructosovorans.
Anaerobe
4:45-55.
|
| 2.
|
Cataldo, D. A.,
T. R. Garland,
R. E. Wildung,
R. E. Wildung, and R. J. Fellows.
1989.
Comparative metabolic behaviour and interrelationships of Tc and S in soybean plants.
Heath Physics
57:281-288.
|
| 3.
|
Cui, D., and T. E. Ericksen.
1996.
Reduction of pertechnetate in solution by heterogeneous electron transfer from Fe(II)-containing geological material.
Environ. Sci. Technol.
30:2263-2269[CrossRef].
|
| 4.
|
De Luca, G.,
P. de Philip,
M. Rousset,
J. P. Bélaïch, and Z. Dermoun.
1998.
The NADP-reducing hydrogenase of Desulfovibrio fructosovorans: evidence for a native complex with hydrogen-dependent methyl viologen activity.
Biochem. Biophys. Res. Commun.
248:591-596[CrossRef][Medline].
|
| 5.
|
Farell, J.,
W. D. Bostick,
R. J. Jarabek, and J. N. Fiedor.
1999.
Electrosorption and reduction by anodically polarized magnetite.
Environ. Sci. Technol.
33:1244-1249[CrossRef].
|
| 6.
|
Fernandez, V. M.,
C. E. Hatchikian, and R. Cammack.
1985.
Properties and reactivation of two different deactivated forms of Desulfovibrio gigas hydrogenase.
Biochim. Biophys. Acta
832:69-79.
|
| 7.
|
Fernandez, V. M.,
M. L. Rua,
P. Reyes,
R. Cammack, and C. E. Hatchikian.
1989.
Inhibition of Desulfovibrio gigas hydrogenase with copper salts and other metal ions.
Eur. J. Biochem.
185:449-454[Medline].
|
| 8.
|
Fitz, R. M., and H. Cypionka.
1991.
Generation of a proton gradient in Desulfovibrio vulgaris.
Arch. Microbiol.
155:444-448.
|
| 9.
|
Fredrickson, J. K.,
H. M. Kostandarithes,
S. W. Li,
A. E. Plymale, and M. J. Maly.
2000.
Reduction of Fe(III), Cr(VI), U(VI), and Tc(VII) by Deinococcus radiodurans R1.
Appl. Environ. Microbiol.
66:2006-2011[Abstract/Free Full Text].
|
| 10.
|
Hatchikian, C. E.,
A. S. Traore,
V. M. Fernandez, and R. Cammack.
1990.
Characterization of the nickel-iron periplasmic hydrogenase from Desulfovibrio fructosovorans.
Eur. J. Biochem.
187:635-643[Medline].
|
| 11.
|
Laemmli, U. K.
1970.
Cleavage of structural proteins during the assembly of the head of bacteriophage T4.
Nature
227:680-685[CrossRef][Medline].
|
| 12.
|
LeGall, J.,
W. J. Payne,
L. Chen,
M. Y. Liu, and A. V. Xavier.
1994.
Localization and specificity of cytochromes and other electron transfer proteins from sulfate-reducing bacteria.
Biochimie
76:655-665[Medline].
|
| 13.
|
Lloyd, J. R.,
J. A. Cole, and L. E. Macaskie.
1997.
Reduction and removal of heptavalent technetium from solution by Escherichia coli.
J. Bacteriol.
179:2014-2021[Abstract/Free Full Text].
|
| 14.
|
Lloyd, J. R., and L. E. Macaskie.
1996.
A novel phosphorimager-based technique for monitoring the microbial reduction of technetium.
Appl. Environ. Microbiol.
62:578-583[Abstract].
|
| 15.
|
Lloyd, J. R.,
H.-F. Nolting,
V. A. Solé,
K. Bosecker, and L. E. Macaskie.
1998.
Technetium reduction and precipitation by sulfate-reducing bacteria.
Geomicrobiol. J.
15:43-56.
|
| 16.
|
Lloyd, J. R.,
J. Ridley,
T. Khizniak,
N. N. Lyalikova, and L. E. Macaskie.
1999.
Reduction of technetium by Desulfovibrio desulfuricans: biocatalyst characterization and use in a flowthrough bioreactor.
Appl. Environ. Microbiol.
65:2691-2696[Abstract/Free Full Text].
|
| 17.
|
Lloyd, J. R.,
V. A. Sole,
C. V. Van Praagh, and D. R. Lovley.
2000.
Direct and Fe(II)-mediated reduction of technetium by Fe(III)-reducing bacteria.
Appl. Environ. Microbiol.
66:3743-3749[Abstract/Free Full Text].
|
| 18.
|
Lloyd, J. R.,
G. H. Thomas,
J. A. Finlay,
J. A. Cole, and L. E. Macaskie.
1999.
Microbial reduction of technetium by Escherichia coli and Desulfovibrio desulfuricans: enhancement via the use of high-activity strains and effect of process parameters.
Biotechnol. Bioeng.
66:122-130[CrossRef][Medline].
|
| 19.
|
Lovley, D. R.
1993.
Dissimilatory metal reduction.
Annu. Rev. Microbiol.
47:263-290[CrossRef][Medline].
|
| 20.
|
Macaskie, L. E.
1991.
The application of biotechnology to the treatment of wastes produced from the nuclear fuel cycle: biodegradation and bioaccumulation as a means of treating radionuclide-containing streams.
Crit. Rev. Biotechnol.
11:41-112[Medline].
|
| 21.
|
Malki, S.,
G. De Luca,
M. L. Fardeau,
M. Rousset,
J. P. Bélaïch, and Z. Dermoun.
1997.
Physiological characteristics and growth behaviour of single and double hydrogenase mutants of Desulfovibrio fructosovorans.
Arch. Microbiol.
167:38-45[CrossRef][Medline].
|
| 22.
|
Malki, S.,
I. Saimmaime,
G. De Luca,
M. Rousset,
Z. Dermoun, and J. P. Bélaïch.
1995.
Characterization of an operon encoding a NADP-reducing hydrogenase in Desulfovibrio fructosovorans.
J. Bacteriol.
177:2628-2636[Abstract/Free Full Text].
|
| 23.
|
Michel, C.,
M. Brugna,
C. Aubert,
A. Bernadac, and M. Bruschi.
2001.
Enzymatic reduction of chromate: comparative studies using sulfate-reducing bacteria. Key role of polyheme cytochromes c and hydrogenases.
Appl. Microbiol. Biotechnol.
55:95-100[CrossRef][Medline].
|
| 24.
|
Ollivier, B.,
R. Cord-Ruwisch,
E. C. Hatchikian, and J.-L. Garcia.
1988.
Characterization of Desulfovibrio fructosovorans sp. nov.
Arch. Microbiol.
150:26-31[CrossRef].
|
| 25.
|
Peck, H. D., Jr.
1993.
Bioenergetic strategies of the sulfate-reducing bacteria, p. 41-76.
In
J. M. Odom, and R. Singleton (ed.), Sulfate-reducing bacteria: contemporary perspectives. Springer-Verlag, New York, N.Y.
|
| 26.
|
Rousset, M.,
Z. Dermoun,
M. Chippaux, and J. P. Bélaïch.
1991.
Marker exchange mutagenesis of the hydN genes in Desulfovibrio fructosovorans.
Mol. Microbiol.
5:1735-1740[CrossRef][Medline].
|
| 27.
|
Rousset, M.,
Z. Dermoun,
C. E. Hatchikian, and J. P. Bélaïch.
1990.
Cloning and sequencing of the locus encoding the large and small subunit genes of the periplasmic [NiFe] hydrogenase from Desulfovibrio fructosovorans.
Gene
94:95-101[CrossRef][Medline].
|
| 28.
|
Rousset, M.,
Y. Montet,
B. Guigliarelli,
N. Forget,
M. Asso,
P. Bertrand,
J. C. Fontecilla-Camps, and C. E. Hatchikian.
1998.
[3Fe-4S] to [4Fe-4S] cluster conversion in Desulfovibrio fructosovorans [NiFe] hydrogenase by site-directed mutagenesis.
Proc. Natl. Acad. Sci. USA
95:11625-11630[Abstract/Free Full Text].
|
| 29.
|
Shukla, S. K.
1966.
Ion exchange paper chromatography of Tc(IV), Tc(V) and Tc(VII) in hydrochloric acid.
J. Chromatogr.
21:92-97[CrossRef][Medline].
|
| 30.
|
Smith, P. K.,
R. I. Krohn,
G. T. Hermanson,
A. K. Mallia,
F. H. Gartner,
M. D. Provenzano,
E. K. Fujimoto,
N. M. Goeke,
B. J. Olson, and D. C. Klenk.
1985.
Measurement of protein using bicinchoninic acid.
Anal. Biochem.
150:76-85[CrossRef][Medline].
|
| 31.
|
Vignais, P. M.,
B. Dimon,
N. A. Zorin,
A. Colbeau, and S. Elsen.
1997.
HupUV proteins of Rhodobacter capsulatus can bind H2: evidence from the H-D exchange reaction.
J. Bacteriol.
179:290-292[Abstract/Free Full Text].
|
| 32.
|
Widdel, F., and N. Pfennig.
1984.
Dissimilatory sulfate- or sulfur-reducing bacteria, p. 663-679.
In
N. R. Krieg, and J. G. Holt (ed.), Bergey's manual of systematic bacteriology, 9th ed. Williams & Wilkins, Baltimore, Md.
|
| 33.
|
Wildung, R. E.,
Y. A. Gorby,
K. M. Krupka,
N. J. Hess,
S. W. Li,
A. E. Plymale,
J. P. McKinley, and J. K. Fredrikson.
2000.
Effect of electron donor and solution chemistry on products of dissimilatory reduction of technetium by Shewanella putrefaciens.
Appl. Environ. Microbiol.
66:2451-2460[Abstract/Free Full Text].
|
| 34.
|
Wildung, R. E.,
K. M. McFadden, and T. R. Garland.
1979.
Technetium sources and behaviour in the environment.
J. Environ. Qual.
8:156-161[Abstract/Free Full Text].
|
| 35.
|
Yanke, L. J.,
R. D. Bryant, and E. J. Laishley.
1995.
Hydrogenase I of Clostridium pasteurianum functions as a novel selenite reductase.
Anaerobe
1:61-67.
|
Applied and Environmental Microbiology, October 2001, p. 4583-4587, Vol. 67, No. 10
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.10.4583-4587.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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