Previous Article | Next Article 
Journal of Bacteriology, August 1998, p. 3823-3827, Vol. 180, No. 15
0021-9193/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Purification and Characterization of EDTA
Monooxygenase from the EDTA-Degrading Bacterium BNC1
Jason W.
Payne,1,2
Harvey
Bolton Jr.,2
James A.
Campbell,3 and
Luying
Xun1,2,*
Department of Microbiology, Washington State
University, Pullman, Washington 99164-4233,1 and
Environmental Microbiology Group2 and
Advanced Organic Analytical Methods
Group,3 Pacific Northwest National
Laboratory, Richland, Washington 99352
Received 23 December 1997/Accepted 26 May 1998
 |
ABSTRACT |
The synthetic chelating agent EDTA can mobilize radionuclides and
heavy metals in the environment. Biodegradation of EDTA should reduce
this mobilization. Although several bacteria have been reported to
mineralize EDTA, little is known about the biochemistry of EDTA
degradation. Understanding the biochemistry will facilitate the removal
of EDTA from the environment. EDTA-degrading activities were detected
in cell extracts of bacterium BNC1 when flavin mononucleotide (FMN),
NADH, and O2 were present. The degradative enzyme system was separated into two different enzymes, EDTA monooxygenase and an FMN
reductase. EDTA monooxygenase oxidized EDTA to glyoxylate and
ethylenediaminetriacetate (ED3A), with the coconsumption of FMNH2 and O2. The FMN reductase provided EDTA
monooxygenase with FMNH2 by reducing FMN with NADH. The FMN
reductase was successfully substituted in the assay mixture by other
FMN reductases. EDTA monooxygenase was purified to greater than 95%
homogeneity and had a single polypeptide with a molecular weight of
45,000. The enzyme oxidized both EDTA complexed with various metal ions
and uncomplexed EDTA. The optimal conditions for activity were pH 7.8 and 35°C. Kms were 34.1 µM for uncomplexed
EDTA and 8.5 µM for MgEDTA2
; this difference in
Km indicates that the enzyme has greater affinity for MgEDTA2
. The enzyme also catalyzed the
release of glyoxylate from nitrilotriacetate and
diethylenetriaminepentaacetate. EDTA monooxygenase belongs to a small
group of FMNH2-utilizing monooxygenases that attack carbon-nitrogen, carbon-sulfur, and carbon-carbon double bonds.
 |
INTRODUCTION |
Synthetic chelating agents have a
wide variety of uses, from household cleaners, water treatment, and
pulp and paper bleaching to rubber and metal processing (2, 23,
30). About 70% of the chelating agents used worldwide are
aminopolycarboxylic acids, primarily EDTA,
diethylenetriaminepentaacetate (DTPA), and nitrilotriacetate (NTA),
with annual production about 372 million lb in the United States,
western Europe, and Japan in 1994 (30). EDTA is the most
commonly used chelating agent. In the environment, EDTA has some
undesirable environmental consequences such as the remobilization of
radionuclides and heavy metals from soils and sediments (6, 9,
24). The mobilized radionuclides and toxic heavy metals can cause
direct health problems or can be accumulated by plants and then
transferred to human beings through the food chain. EDTA is
recalcitrant in soils (25, 34, 35) and sediments (3, 34, 35). Photodegradation of FeEDTA plays a major role in the
fate of EDTA in surface waters (13, 14). Other species, such
as CuEDTA, ZnEDTA, and NiEDTA, are not degraded by sunlight, whereas
CoEDTA is only slightly sensitive (20, 26).
To date, only two microorganisms have been reported to degrade EDTA.
The gram-negative bacterium BNC1 was isolated from sewage receiving
EDTA-containing wastewater effluents (27); an
Agrobacterium sp. growing on Fe(III)EDTA has also been
isolated (18). However, little is known about the
biochemistry of EDTA degradation by these microorganisms. To facilitate
bioremediation of EDTA and reduce the mobility of heavy metals in the
groundwater, the biochemistry of EDTA degradation by bacterium BNC1 was
studied. We report here the purification and characterization of EDTA
monooxygenase (EDTA-Mo), which catalyzed the first step of EDTA
degradation by bacterium BNC1.
(A preliminary account of this work was presented at the 96th General
Meeting of the American Society for Microbiology
[28].)
 |
MATERIALS AND METHODS |
Bacterium and culture conditions.
The EDTA-degrading
bacterium BNC1 was kindly provided by Bernd Nörtemann (Technical
University of Braunschweig, Braunschweig, Germany). BNC1 was cultured
with Na2EDTA · 2H2O (0.3 g/liter) and
potassium acetate (0.25 g/liter) in a mineral medium (27). Large quantities of cells were obtained by culturing BNC1 in a 50-liter
carboy containing 30 liters of the medium bubbled with sterile air for
2.5 days at 24°C. Toward the end of log phase, cells were harvested
by concentrating the culture to 2 liters in a hollow fiber filtration
unit (model DC10L system; Amicon, Beverly, Mass.) and then centrifuged
at 17,000 × g for 15 min at 4°C. The cells were
stored at
20°C for a maximum of 3 days.
Enzyme assays.
EDTA-Mo activity was assayed by measuring the
production of glyoxylate. A standard assay mixture contained 20 mM
HEPES buffer (pH 7.8), 10 µM flavin mononucleotide (FMN), 2 mM NADH,
500 µM Na2EDTA (or other chelator), 500 µM
MgCl2, 0.2 U of NAD(P)H:FMN oxidoreductase from
Photobacterium fischeri (Boehringer Mannheim Co.,
Indianapolis, Ind.), 30 U of catalase (from bovine liver; Sigma), and
an appropriate amount of EDTA-Mo preparation in a total volume of 250 µl. The NAD(P)H:FMN oxidoreductase generated FMNH2 by
reducing FMN with NADH and was added in excess to ensure sufficient
amounts of FMNH2 for EDTA-Mo. The reaction was initiated by
adding NADH. A stock solution of 100 mM NADH was prepared in 10 mM Tris
base (pH >13). The assay was stopped by adding 100 µl of 0.1 N HCl.
The glyoxylate produced was detected by
phenylhydrazine-K3Fe(CN)6 as previously
described (37). The aqueous speciation of EDTA among its
free acid and complexed forms (e.g., H2EDTA2
and MgEDTA2
) was calculated with an aqueous
speciation-solubility model MINTEQA2 (1, 31) as previously
described (39).
Purification steps.
All operations were performed at 6°C.
All buffers except those used for the hydroxyapatite column contained 1 mM dithiothreitol. The levels of ammonium sulfate saturation were those
at 25°C.
(i) Extraction of cells.
About 15 g of frozen cells was
thawed at room temperature and suspended in 30 ml of 20 mM Tris buffer
(pH 8.0) containing 2.5 mM EDTA. The protease inhibitor
phenylmethylsulfonyl fluoride was freshly prepared in absolute ethanol
at a concentration of 30 mM and added to the cell suspension to a final
concentration of 0.5 mM. The slurry was passed through a French
pressure cell (model FA-030; Aminco, Urbana, Ill.) three times at 260 MPa. The product was centrifuged at 17,000 × g for 15 min. The supernatant was saved, and the pellet was discarded.
(ii) Protamine sulfate treatment.
A 2% solution of
protamine sulfate in 20 mM Tris buffer (pH 8.0) was added to the
supernatant slowly to 0.05% with stirring. After 5 min, the mixture
was centrifuged at 17,000 × g for 15 min, and the
supernatant was saved.
(iii) Ammonium sulfate fractionation.
Solid ammonium sulfate
was added to the supernatant to 33% saturation with constant stirring.
The pH of the solution was not adjusted. After 10 min of stirring, the
mixture was centrifuged at 17,000 × g for 15 min. The
precipitate was discarded. Additional solid ammonium sulfate was added
to the supernatant to 70% saturation with constant stirring. After 10 min of stirring, the mixture was centrifuged at 17,000 × g for 15 min. The precipitate was saved, and the supernatant
was discarded.
(iv) Ultracentrifugation.
The precipitate was suspended in
an equal volume of 25 mM potassium phosphate (KPi) buffer (pH 7.0). The
suspension was dialyzed against 1 liter of the same buffer for 2.5 h. The dialyzed sample was centrifuged at 331,000 × g
for 40 min, and the supernatant was saved.
(v) Dye chromatography.
The supernatant was loaded onto a
25-ml Cibacron Blue 3GA agarose (Sigma) column (1.5 by 14 cm)
previously equilibrated with 25 mM KPi buffer (pH 7.0). A maximum of
150 mg of total protein was loaded per run. After the proteins were
loaded, the column was washed with 80 ml of the equilibrating buffer
and then washed with 80 ml of 1 M NaCl in 25 mM KPi buffer (pH 7.0).
Most proteins did not bind to the column and washed off with the
starting buffer. Both EDTA-Mo and an FMN reductase were eluted with the
1 M NaCl solution. The eluent containing the enzymes was concentrated
to 1 ml with a Centriprep-10 (Millipore). The sample was desalted to 25 mM KPi (pH 7.0) with a Centriprep-10.
(vi) MonoQ chromatography.
The sample from the dye column in
25 mM KPi (pH 7.0) was injected onto a MonoQ HR 5/5 column (Pharmacia)
equilibrated with the same buffer. Proteins were eluted with a step and
linear gradient of NaCl (percentages of 1 M NaCl in the same buffer:
0%, 4 ml; 0 to 15%, 20-ml linear gradient; 100%, 6 ml; and 0%, 3 ml) by a fast protein liquid chromatography (FPLC) system (Pharmacia). EDTA-Mo was eluted associated with a major peak around 80 mM NaCl. The
fractions containing the enzyme activity were pooled and concentrated to less than 1 ml with a Centriprep-10. The FMN reductase was not bound
to the column and was separated from EDTA-Mo by this step.
(vii) Hydroxyapatite chromatography.
The buffer for EDTA-Mo
was changed to 8 mM KPi (pH 6.6) with a Centriprep-10. The sample was
injected onto a Bio-Scale CHT2-I hydroxyapatite column (Bio-Rad,
Hercules, Calif.) equilibrated with the same buffer. Proteins were
eluted with a step and linear gradient of KPi (pH 6.6) (concentrations
of KPi: 8 mM, 4 ml; 50 mM, 5 ml; 50 to 250 mM, 20-ml linear gradient;
and 500 mM, 8 ml) by FPLC. EDTA-Mo was eluted as a major peak around
165 mM KPi, concentrated to 1 ml with a Centriprep-10, and stored at
80°C.
Analytical methods.
Sodium dodecyl sulfate-polyacrylamide
gel electrophoresis (SDS-PAGE) was done by the method of Laemmli
(17). Gels were stained for proteins with Coomassie
brilliant blue R-250. Protein concentrations were determined by a
protein dye reagent (4), with bovine serum albumin as the
standard. Gel filtration chromatography was used to estimate the native
molecular weight of the enzyme. Purified enzyme was injected onto a
Superose 12 column (Pharmacia) equilibrated with 25 mM KPi (pH 7.0)
containing 150 mM NaCl. The enzyme was eluted with the same buffer by
FPLC. The EDTA-Mo was eluted off the column as a single peak with a
retention volume of 12.5 ml. Gel filtration standards were purchased
from Bio-Rad. The nitrogen-containing moiety of enzymatic end product
from NTA was derivatized by 9-fluorenylmethylchloroformate (7) and then determined by a high-performance liquid
chromatography (HPLC) system (Waters). The N-terminal amino acid
sequence of the purified protein was determined on an ABI 470 protein
sequencer at the Department of Biochemistry and Biophysics, Washington
State University, as previously described (38).
Oxygen consumption.
Oxygen consumption by FMNH2
and by EDTA-Mo was determined in a closed reaction vessel (0.6-ml total
volume) fitted with a Clarke-type oxygen electrode (Instech, Plymouth
Meeting, Pa.). The electrode was calibrated by
N-methylphynazonium methosulfate and NADH (29).
The reaction was in 20 mM HEPES buffer (pH 7.8)-10 µM FMN-500 µM
Na2EDTA-500 µM MgCl2. Two sets of
experiments were carried out. The first set contained 0.8 U of
NAD(P)H:FMN oxidoreductase only. The second set contained 0.8 U of
NAD(P)H:FMN oxidoreductase and 580 µg of EDTA-Mo from the MonoQ
column. In both cases, NADH was added in a 2.5-µl volume to a final
concentration of 198 µM to initiate O2 consumption. When
O2 consumption stopped, 90 U of catalase was added to
release O2 from H2O2. For the
reaction containing EDTA-Mo, the glyoxylate produced was also
quantified.
pH and temperature optima.
The EDTA-Mo activities were
measured at various pH values within the range of 6.6 to 8.4 with 20 mM
HEPES buffer. The enzyme assay was performed as described above except
that the reaction was stopped by heating at 90°C for 5 min instead of
acidification. The temperature optima for the enzyme activity were
determined in a similar way at pH 7.7. The reaction mixture without
NADH was incubated at the corresponding temperature for 5 min, and then
NADH was added to the mixture to start the reaction. The reaction was
terminated by acidification.
Product determination by mass spectroscopy.
A 5-ml aliquot
of the reaction mixture was lyophilized with an LPH LOCK (LABCONCO) for
approximately 12 h. The dried material was transferred to a
Reactivial (VWR Scientific); 2 ml of 12% BF3-methanol
(Aldrich) was added, and the sample was heated to 100°C for 1 h.
The solution was cooled, and 2 ml of chloroform was added. The entire
solution was then quenched in a vial containing 10 ml of 0.4 M
KH2PO4 (pH 9.5). The vial was vortexed, and the aqueous and chloroform layers were allowed to separate. The chloroform layer, containing the derivatized organics, was retained, and the
aqueous layer was discarded. The chloroform solution was then analyzed
by gas chromatography-mass spectrometry (GC-MS) (5, 10).
A model 5890 gas chromatograph (Hewlett-Packard) equipped with a fused
silica column (DB-5, 30 m by 0.25 mm [inside diameter], 0.25-µm film thickness; J & W Scientific) was interfaced to a model
5970 mass selective detector (Hewlett-Packard). The oven temperature
was programmed in the following manner: 50°C for 1 min, 8°C/min to
260°C, and hold at 260°C for 10 min. The mass selective detector
was tuned with perfluorotributylamine. In these studies, the detector
was scanned from 50 to 600 and operated in the electron impact mode (70 eV). The source temperature was 200°C, the injector port temperature
was 250°C, and the interfaces were at 250°C.
 |
RESULTS |
Identification of EDTA degradation in cell extracts.
Cell
extracts of BNC1 cultured with EDTA and acetate in a mineral medium
were able to degrade EDTA to glyoxylate in the presence of NADH, FMN,
and O2. Flavin adenine dinucleotide (FAD) and riboflavin could not replace FMN. The effects of temperature and pH on glyoxylate production by cell extracts were determined. Optimal reaction rates
were achieved at 35°C and pH 7.7. The rates of glyoxylate formation
were also affected by the metal cation complexed by EDTA in the assay.
Dialyzed cell extracts were able to release glyoxylate from EDTA
complexed with any of the cations tested (Mg2+,
Mn2+, Ni2+, Co2+, Zn2+,
Fe2+, Ca2+, Cu2+, Cr2+,
Sn2+, Ba2+, Cd2+, Sr2+,
Pd2+, Al3+, Cr3+, K+,
or Na+). MgEDTA2
was found to be the best
substrate, having a rate nearly twice that of uncomplexed EDTA. For
this reason, MgCl2 was used in the assay.
Enzyme purification.
EDTA-Mo was purified by monitoring
glyoxylate production from EDTA in reaction mixtures following each
purification step. In the cell extract, there was an FMN reductase that
was later separated from EDTA-Mo on a MonoQ column. After the
separation, the FMN reductase could be substituted by an NADH:FMN
oxidoreductase of Chelatobacter heintzii (38) or
an NAD(P)H:FMN oxidoreductase of P. fischeri (36)
to generate FMNH2 for EDTA-Mo. Because its activity can be
replaced by other NADH:FMN oxidoreductases, we purified EDTA-Mo with
the NAD(P)H:FMN oxidoreductase of P. fischeri to supply
FMNH2. The results of a typical purification of EDTA-Mo are
summarized in Table 1.
Enzyme properties and activities.
EDTA-Mo was apparently
purified to homogeneity as indicated by SDS-PAGE analysis, revealing a
single 45-kDa band (Fig. 1). The native
EDTA-Mo was estimated to be a monomer by gel filtration chromatography.
The N-terminal sequences of EDTA-Mo was determined to be MNKVLMYL.

View larger version (44K):
[in this window]
[in a new window]
|
FIG. 1.
SDS-PAGE of purified EDTA-Mo. Lane 1, low-range
molecular weight standards (Bio-Rad); lane 2, 1 µg of EDTA-Mo.
|
|
EDTA-Mo produced glyoxylate from EDTA, NTA, and DTPA, with the
coconsumption of FMNH
2 and O
2.
FMNH
2 was generated by an FMN
reductase with NADH as the
reductant in the assay system. In the
reaction mixture, O
2
consumption was observed even with NAD(P)H:FMN
oxidoreductase alone.
When 198 µM NADH was added to the reaction
mixture in a closed
vessel, 225 µM O
2 was consumed in 12 min.
The consumed
O
2 was quantitatively converted to
H
2O
2 since 116
µM O
2 was released
when catalase was added. When the reaction
mixture also contained
EDTA-Mo, 192 µM glyoxylate was produced
and 197 µM O
2
was consumed in 4 min. Only 10 µM O
2 was converted
to
H
2O
2 since only 5 µM O
2 was
released when catalase was added.
The end product with the nitrogen moiety from NTA was identified as
iminodiacetate by HPLC analysis. The enzyme did not release
glyoxylate
from commercial iminodiacetate (Sigma). The end product
with the
nitrogen moiety from EDTA was not detected by the HPLC
method and was
analyzed by GC-MS. The total ion chromatogram is
shown in Fig.
2A. On the basis of the mass spectrum of
the component
at the retention time of 24.1 min, it was identified as
the methyl
ester of the lactam of ethylenediaminetriacetate (ED3A)
(Fig.
2B). ED3A forms an internal amino carboxylic ester bond to yield
the lactam of ED3A during derivatization before GC-MS analysis
(
10). The compound at the retention time of 26.7 min was
identified
as the methyl ester of EDTA by its mass spectrum (data not
shown).
Neither unsymmetric nor symmetric ethylendiaminediacetate
(EDDA)
was detected. The first peak in Fig.
2A was caused by HEPES used
as a buffer for the enzymatic assay. The nitrogen-containing end
product from DTPA was not identified because the enzyme did not
produce
enough of it for GC-MS analysis.

View larger version (20K):
[in this window]
[in a new window]
|
FIG. 2.
GC-MS analysis of the end products of EDTA degradation
by EDTA-Mo. (A) Total ion chromatogram of the sample; (B) mass spectrum
of lactam ED3A.
|
|
The effects of temperature and pH on EDTA-Mo activity were determined.
The optimal temperature for EDTA-Mo activity was 35°C,
with 75, 93, and 96% of the optimal activity retained at 25, 30,
and 40°C,
respectively. The optimal pH was 7.7 in 20 mM HEPES
buffer; the
activities were 75, 83, and 70% of the optimum at
pH 6.9, 7.3, and
8.1, respectively. The best activity was obtained
in 20 mM HEPES buffer
(pH 7.7) at 35°C.
Kinetic analysis.
The kinetic parameters were determined for
EDTA-Mo with an excess of NAD(P)H:FMN oxidoreductase of P. fischeri to generate FMNH2. Km
and Vmax values were determined for EDTA-Mo from
Lineweaver-Burke plots of initial reaction rates. The degradation of
EDTA or MgEDTA2
was measured based on the formation of
glyoxylate. In the assay mixture without Mg2+, EDTA did not
associate with Na+ and was present as uncomplexed EDTA in
the forms of 94% HEDTA3
and 6% H2EDTA2
.
For uncomplexed EDTA, Km was 34.1 µM,
Vmax was 3.7 µM mg
1
min
1, kcat was 2.8 s
1, and
kcat/Km was 0.08 µM
1 s
1. When equimolar Mg2+
and EDTA were added to the reaction mixture, 98.8% of the EDTA was
present as MgEDTA2
. For MgEDTA2
,
Km was 8.5 µM, Vmax was
4.7 µM mg
1 min
1,
kcat was 3.6 s
1, and
kcat/Km was 0.43 µM
1 s
1. The difference in
kcat/Km for the two
substrates (MgEDTA2
5.3 times higher) was primarily due
to the difference in the Km, indicating that the
enzyme has a greater affinity for the chelate when it is complexed with
Mg2+.
 |
DISCUSSION |
This is the first report that EDTA-Mo has been identified,
purified, and characterized. When supplied with FMNH2, the
enzyme appears to break the N-C bond in EDTA, NTA, and DTPA, with one oxygen atom appearing in glyoxylate. The enzyme was able to degrade EDTA, NTA, and DTPA with a variety of metal cations. With cell extracts, the highest rate was found when Mg2+ was added.
The purified enzyme showed similar preferences for MgEDTA2
and free EDTA. Kinetic analyses indicate that the
enzyme has a higher affinity for MgEDTA2
. This finding
coincides with Mg2+ being the most abundant intracellular
cation in several tested microorganisms (12), with
MgEDTA2
the likely form of EDTA in the cytoplasm of BNC1.
HPLC, GC-MS, and colorimetric analyses showed that EDTA was oxidized to
glyoxylate and ED3A, and NTA was oxidized to glyoxylate and
iminodiacetate by EDTA-Mo (Fig. 3). Upon
examination of the structures of NTA and ED3A, we wondered whether
EDTA-Mo could also degrade ED3A to EDDA. However, GC-MS analysis did
not detect any trace of either symmetric or unsymmetric EDDA. We are
currently cloning the gene encoding EDTA-Mo by using a DNA probe
generated from the N-terminal amino acid sequence. Successful
production of a functional EDTA-Mo in an expression host will allow us
to confirm the identities of enzyme end products from EDTA and NTA as
well as to accumulate enough end products from DTPA for identification. Characterization of the gene sequence will reveal the relationships among related enzymes, especially between EDTA-Mo and NTA monooxygenase (NTA-Mo).
The stoichiometry of EDTA oxidation by EDTA-Mo was studied. One
molecule of FMN was reduced to one FMNH2 by NAD(P)H:FMN
oxidoreductase at the expense of one NADH. Then one FMNH2
reacted with one O2 chemically to generate one
H2O2. When catalase was added, one O2 was produced from two H2O2. When
EDTA-Mo was also present in the reaction mixture, the enzyme consumed
one O2 and one FMNH2 to oxidized EDTA and
produced one glyoxylate. It took 12 min to complete O2
consumption in the absence of EDTA-Mo but only 4 min in the presence of
EDTA-Mo. Ninety-five percent of FMNH2 generated by
NAD(P)H:FMN oxidoreductase was used by EDTA-Mo to oxidize EDTA, and
only 5% reacted with O2 to produce
H2O2. Although the concentrations of EDTA and
ED3A were not determined, the conversion of EDTA to ED3A was determined
by GC-MS analysis. On the basis of these data, the reaction catalyzed
by EDTA-Mo is proposed (Fig. 3).
When the kinetic parameters for EDTA oxidation were determined, excess
NAD(P)H:FMN oxidoreductase was added in the reaction mixture. Under
such conditions, a substantial amount of H2O2
was produced. Catalase was added to the reaction mixture to prevent the
buildup of H2O2. This practice provided
sufficient amount of FMNH2 to EDTA-Mo. When O2
consumption was studied, excess EDTA-Mo was added to effectively
utilize FMNH2 so that the formation of H2O2 was minimized. Because of
FMNH2 is highly reactive with O2, we could not
use O2 as the limiting factor in the reaction mixture and
thus could not determine its kinetic parameters.
There are similarities and differences between EDTA-Mo of BNC1 and
NTA-Mo (formerly component A) of C. heintzii (37,
38). Both enzymes require FMNH2 and O2 as
cosubstrates, and both are single polypeptides of about 50 kDa. EDTA-Mo
oxidizes EDTA to ED3A and glyoxylate, and oxidizes NTA to
iminodiacetate and glyoxylate. NTA-Mo oxidizes NTA to iminodiacetate
and glyoxylate (37, 38). NTA-Mo degrades only specific
metal-NTA complexes (37, 39), while EDTA-Mo degrades EDTA,
NTA, and DTPA in the absence or presence of metal cations. NTA-Mo does
not degrade EDTA or DTPA.
Flavin-dependent monooxygenases are ubiquitous. FAD and FMN are
normally prosthetic groups, not cosubstrates, and they are reduced by
the monooxygenases themselves with NADH or NADPH as the reductant
(8, 32). EDTA-Mo uses FMNH2 directly. Since the
enzyme does not appear to contain any chromophores and does not require
any specific transitional metal cofactors, the activated oxygen species
is likely a C(4a)-flavin hydroperoxide as proposed for other
flavin-dependent monooxygenases (15, 22). Thus, FMNH2 acts as both reductant and prosthetic group for
EDTA-Mo. An endogenous FMN reductase supplied EDTA-Mo with
FMNH2. Since the reductase was replaced by two other FMN
reductases, it is unlikely that there is any direct protein-protein
interactions between the reductase and oxygenase. These data suggest
that EDTA-Mo belongs to a small group of monooxygenases that utilize
FMNH2 as both reductant and prosthetic group. Bacterial
luciferase of P. fischeri was the first
FMNH2-utilizing monooxygenase studied (36).
Recently, pristinamycin IIA synthase of Streptomyces
pristinaespiralis (33), NTA-Mo of C. heintzii (38), and two monooxygenases involved in
desulfurization of dibenzothiophene by Rhodococcus sp.
strain IGTS8 (11, 19) have been characterized and shown to
use FMNH2 as the cosubstrate. EDTA-Mo appears to be the
sixth member of this group. These FMNH2-dependent
monooxygenases appear to attack carbon-nitrogen, carbon-sulfur,
carbon-carbon, or carbon-oxygen double bonds.
 |
ACKNOWLEDGMENTS |
This research was supported by the Microbial Biotechnology
Initiative at Pacific Northwest National Laboratory. It was also partially supported by the Subsurface Science Program, Office of Health
and Environmental Research, U.S. Department of Energy (DOE). The
support of Frank Wobber is greatly appreciated. Pacific Northwest
National Laboratory is operated for the DOE by Battelle Memorial
Institute under contract DE-AC06-76RLO 1830.
 |
ADDENDUM |
During review of the manuscript, Witschel et al. reported the
identification and characterization of a similar EDTA-degrading enzyme
from a different bacterial isolate (37a).
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Microbiology, Washington State University, Pullman, WA 99163-4233. Phone: (509) 335-2787. Fax: (509) 335-1907. E-mail:
xun{at}mail.wsu.edu.
 |
REFERENCES |
| 1.
|
Allison, J. D.,
D. S. Brown, and K. J. Novo-Gradac.
1991.
MinteqA2/ProdefA2, a geochemical assessment model for environmental systems: version 3.0 users manual. EPA/600/3-91/021.
Environmental Protection Agency, Athens, Ga.
|
| 2.
|
Avers, J. A.
1970.
Decontamination of nuclear reactors and equipment.
The Ronald Ress Co., New York, N.Y.
|
| 3.
|
Bolton, H., Jr.,
S. W. Li,
D. J. Workman, and D. C. Girvin.
1993.
Biodegradation of synthetic chelates in subsurface sediments from the Southeast coastal plain.
J. Environ. Qual.
22:125-132.
[Abstract/Free Full Text] |
| 4.
|
Bradford, M. M.
1976.
A rapid and sensitive method for the quantitation of microgram quantities of protein using the principle of protein-dye binding.
Anal. Biochem.
72:248-254[Medline].
|
| 5.
|
Campbell, J. A.
1994.
Flammable gas safety program. Analytical methods development: FY 1993 Progress Report. PNL-9062.
Pacific Northwest National Laboratory, Richland, Wash.
|
| 6.
|
Cleveland, J. M., and T. F. Rees.
1981.
Characterization of plutonium in Maxey Flats radioactive trench leachates.
Science
200:1506-1509.
|
| 7.
|
Einarsson, S.
1985.
Selective determination of secondary amino acids using precolumn derivatization with 9-fluorenylmethylchloroformate and reversed-phase high-performance liquid chromatography.
J. Chromatogr.
348:213-220.
|
| 8.
|
Flashner, M. S., and V. Massey.
1974.
Flavoprotein monooxygenases, p. 245-283.
In
O. Hayaishi (ed.), Molecular mechanisms of oxygen activation. Academic Press, Inc., New York, N.Y.
|
| 9.
|
Gardiner, J.
1976.
Complexation of trace metals by ethylenediaminetetraacetic acid (EDTA) in natural waters.
Water. Res.
10:507-514.
|
| 10.
|
Grant, K. E.,
G. M. Mong,
R. B. Lucke, and J. A. Campbell.
1996.
Quantitative determination of chelators and their degradation products in mixed hazardous wastes from tank 241-SY-101 using derivatization GC/MS.
J. Radioanal. Nucl. Chem.
211:383-402.
|
| 11.
|
Gray, K. A.,
O. S. Pogrebinsky,
G. T. Mrachko,
L. Xi,
D. J. Monticello, and C. H. Squires.
1996.
Molecular mechanisms of biocatalytic desulfurization of fossil fuels.
Nat. Biotechnol.
14:1705-1709[Medline].
|
| 12.
|
Hughes, M. N., and R. K. Poole.
1989.
Metals and microorganisms.
Chapman and Hall, New York, N.Y.
|
| 13.
|
Kari, F. G., and W. Giger.
1995.
Modeling the photochemical degradation of ethylenediaminetetraacetate (EDTA) in the River Glatt.
Environ. Sci. Technol.
29:2814-2827.
|
| 14.
|
Kari, F. G.,
S. U. Hilger, and S. Canonica.
1995.
Determination of the reaction quantum yield for the photochemical degradation of Fe(III)EDTA implications for the environmental fate of EDTA in surface waters.
Environ. Sci. Technol.
29:1008-1017.
|
| 15.
|
Kemal, C.,
T. W. Chan, and T. C. Bruice.
1977.
Reaction of 3O2 with dihydroflavins. 1. N3,5-dimethyl-1,5-dihydroluminflavin and 1,5-dihydroisoalloxazines.
J. Am. Chem. Soc.
99:7272-7286[Medline].
|
| 16.
|
Knobel, H.,
T. Egli, and J. R. Van Der Meer.
1996.
Cloning and characterization of the genes encoding nitrilotriacetate monooxygenase of Chelatobacter heintzii ATCC 29600.
J. Bacteriol.
178:6123-6132[Abstract/Free Full Text].
|
| 17.
|
Laemmli, U. K.
1970.
Cleavage of structural proteins during the assembly of the head of bacteriophage T4.
Nature (London)
227:680-685[Medline].
|
| 18.
|
Lauff, J. J.,
D. B. Steele,
L. A. Coogan, and J. M. Breitfeller.
1990.
Degradation of the ferric chelate of EDTA by a pure culture of an Agrobacterium sp.
Appl. Environ. Microbiol.
56:3346-3353[Abstract/Free Full Text].
|
| 19.
|
Lei, B., and S.-C. Tu.
1996.
Gene overexpression, purification, and identification of a desulfurization enzyme from Rhodococcus sp. strain IGTS8 as a sulfide/sulfoxide monooxygenase.
J. Bacteriol.
178:5699-5705[Abstract/Free Full Text].
|
| 20.
|
Lockhart, H. B., and R. V. Blakeley.
1975.
Aerobic photodegradation of Fe(III)-(ethylenedinitrilo)tetraacetate (ferric EDTA). Implications for natural waters.
Environ. Sci. Technol.
9:1035-1038.
|
| 21.
|
Martell, A. E., and R. M. Smith.
1974.
Critical stability constants, vol. 1. Amino acids.
Plenum Press, New York, N.Y.
|
| 22.
|
Massey, V.
1994.
Activation of molecular oxygen by flavins and flavoproteins.
J. Biol. Chem.
269:22549-22562.
|
| 23.
|
McFadden, K. M.
1980.
Organic components of nuclear wastes and their potential for altering radionuclide distribution when released to soil.
National Technical Information Service, Springfield, Va.
|
| 24.
|
Means, J. L.,
D. A. Crerar, and J. O. Duguid.
1978.
Migration of radioactive wastes: radionuclide mobilization by complexing agents.
Science
200:1477-1481[Abstract/Free Full Text].
|
| 25.
|
Means, J. L.,
T. Kucak, and D. A. Crerar.
1980.
Relative degradation of NTA, EDTA and DTPA and environmental implications.
Environ. Pollut. Ser. B
1:45-60.
|
| 26.
|
Natarajan, P., and J. F. Endicott.
1973.
Photoredox behavior of transition metal-ethylenediaminetetraacetate complexes. A comparison of some group VIII metals.
J. Phys. Chem.
77:2049-2054.
|
| 27.
|
Nörtemann, B.
1992.
Total degradation of EDTA by mixed cultures and a bacterial isolate.
Appl. Environ. Microbiol.
58:671-676[Abstract/Free Full Text].
|
| 28.
|
Payne, J. W.,
H. Bolton, Jr., and L. Xun.
1996.
Purification of a component of EDTA monooxygenase from EDTA degrading bacterium, BNC1, abstr. Q-275, p. 433.
In
Abstracts of the 96th General Meeting of the American Society for Microbiology 1996. American Society for Microbiology, Washington, D.C.
|
| 29.
|
Robinson, J., and J. M. Cooper.
1970.
Method of determining oxygen concentrations in biological media, suitable for calibration of oxygen electrode.
Anal. Biochem.
33:390-399[Medline].
|
| 30.
|
Sisto, J. D.,
M. Jackel, and M. Ishikawa.
1996.
Chelating agents, p. 515.5000 A.
In
Chemical economics handbook. SRI Consulting, Menlo Park, Calif.
|
| 31.
|
Smith, R. M., and A. E. Martell.
1987.
Critical stability constants, enthalpies and entropies for the formation of metal complexes of aminocarboxylic acids and carboxilic acids.
Sci. Total Environ.
64:125-147.
|
| 32.
|
Testa, B.
1995.
The nature and functioning of cytochromes P450 and flavin-containing-monooxygenases, p. 70-121.
In
B. Testa, and J. Caldwell (ed.), The metabolism of drugs and other xenobiotics: biochemistry of redox reactions. Academic Press Inc., San Diego, Calif.
|
| 33.
|
Thibaut, D.,
N. Ratet,
D. Bisch,
D. Faucher,
L. Debussche, and F. Blanche.
1995.
Purification of the two enzyme system catalyzing the oxidation of the D-proline residue of pristinamycin IIB during the last step of pristinamycin IIA biosynthesis.
J. Bacteriol.
177:5199-5205[Abstract/Free Full Text].
|
| 34.
|
Tiedje, J. M.
1975.
Microbial degradation of ethylenediaminetetraacetate in soils and sediments.
Appl. Environ. Microbiol.
30:327-329[Abstract/Free Full Text].
|
| 35.
|
Tiedje, J. M.
1977.
Influence of environmental parameters on EDTA biodegradation in soils and sediments.
J. Environ. Qual.
6:21-26.
[Abstract/Free Full Text] |
| 36.
|
Tu, S.-C., and H. I. X. Mager.
1995.
Biochemistry of bacterial bioluminescence.
Photochem. Photobiol.
62:615-624[Medline].
|
| 37.
|
Uetz, T.,
R. Schneider,
M. Snozzi, and T. Egli.
1992.
Purification and characterization of a two-component monooxygenase that hydroxylates nitrilotriacetate from "Chelatobacter" strain ATCC 29600.
J. Bacteriol.
174:1179-1188[Abstract/Free Full Text].
|
| 37a.
|
Witschel, M.,
S. Nagel, and T. Egli.
1997.
Identification and characterization of the two-enzyme system catalyzing oxidation of EDTA in the EDTA-degrading bacterial strain DSM 9103.
J. Bacteriol.
179:6937-6943[Abstract/Free Full Text].
|
| 38.
|
Xu, Y.,
M. W. Mortimer,
T. S. Fisher,
M. L. Kahn,
F. J. Brockman, and L. Xun.
1997.
Cloning, sequencing, and analysis of a gene cluster from Chelatobacter heintzii ATCC 29600 encoding nitrilotriacetate monooxygenase and NADH:flavin mononucleotide oxidoreductase.
J. Bacteriol.
179:1112-1116[Abstract/Free Full Text].
|
| 39.
|
Xun, L.,
R. B. Reeder,
A. E. Plymale,
D. C. Girvin, and H. Bolton, Jr.
1996.
Degradation of metal-nitrilotriacetate (NTA) complexes by NTA monooxygenase.
Environ. Sci. Technol.
30:1753-1755.
|
Journal of Bacteriology, August 1998, p. 3823-3827, Vol. 180, No. 15
0021-9193/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
Lee, J.-K., Zhao, H.
(2007). Identification and Characterization of the Flavin:NADH Reductase (PrnF) Involved in a Novel Two-Component Arylamine Oxygenase. J. Bacteriol.
189: 8556-8563
[Abstract]
[Full Text]
-
Weir, K. M., Sutherland, T. D., Horne, I., Russell, R. J., Oakeshott, J. G.
(2006). A Single Monooxygenase, Ese, Is Involved in the Metabolism of the Organochlorides Endosulfan and Endosulfate in an Arthrobacter sp.. Appl. Environ. Microbiol.
72: 3524-3530
[Abstract]
[Full Text]
-
Perez-Mendoza, D., Sepulveda, E., Pando, V., Munoz, S., Nogales, J., Olivares, J., Soto, M. J., Herrera-Cervera, J. A., Romero, D., Brom, S., Sanjuan, J.
(2005). Identification of the rctA Gene, Which Is Required for Repression of Conjugative Transfer of Rhizobial Symbiotic Megaplasmids. J. Bacteriol.
187: 7341-7350
[Abstract]
[Full Text]
-
Bohuslavek, J., Payne, J. W., Liu, Y., Bolton, H. Jr., Xun, L.
(2001). Cloning, Sequencing, and Characterization of a Gene Cluster Involved in EDTA Degradation from the Bacterium BNC1. Appl. Environ. Microbiol.
67: 688-695
[Abstract]
[Full Text]
-
Liu, Y., Louie, T. M., Payne, J., Bohuslavek, J., Bolton, H. Jr., Xun, L.
(2001). Identification, Purification, and Characterization of Iminodiacetate Oxidase from the EDTA-Degrading Bacterium BNC1. Appl. Environ. Microbiol.
67: 696-701
[Abstract]
[Full Text]
-
Xun, L., Sandvik, E. R.
(2000). Characterization of 4-Hydroxyphenylacetate 3-Hydroxylase (HpaB) of Escherichia coli as a Reduced Flavin Adenine Dinucleotide-Utilizing Monooxygenase. Appl. Environ. Microbiol.
66: 481-486
[Abstract]
[Full Text]
-
Galán, B., Díaz, E., Prieto, M. A., García, J. L.
(2000). Functional Analysis of the Small Component of the 4-Hydroxyphenylacetate 3-Monooxygenase of Escherichia coli W: a Prototype of a New Flavin:NAD(P)H Reductase Subfamily. J. Bacteriol.
182: 627-636
[Abstract]
[Full Text]