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J Bacteriol, January 1998, p. 152-158, Vol. 180, No. 1
0021-9193/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
AtzC Is a New Member of the Amidohydrolase Protein
Superfamily and Is Homologous to Other Atrazine-Metabolizing
Enzymes
Michael J.
Sadowsky,1,2,3,4,*
Zhaokun
Tong,1,4
Mervyn
de Souza,3,4,5 and
Lawrence P.
Wackett3,4,5
Department of
Microbiology,1
Department of Soil,
Water, and Climate,2
Institute for
Advanced Studies in Biological Process
Technology,3
Center for Biodegradation
Research and Informatics,4 and
Department of Biochemistry,5 University
of Minnesota, St. Paul, Minnesota 55108
Received 15 August 1997/Accepted 23 October 1997
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ABSTRACT |
Pseudomonas sp. strain ADP metabolizes atrazine to
cyanuric acid via three plasmid-encoded enzymes, AtzA, AtzB, and AtzC. The first enzyme, AtzA, catalyzes the hydrolytic dechlorination of
atrazine, yielding hydroxyatrazine. The second enzyme, AtzB, catalyzes
hydroxyatrazine deamidation, yielding N-isopropylammelide. In this study, the third gene in the atrazine catabolic pathway, atzC, was cloned from a Pseudomonas sp. strain
ADP cosmid library as a 25-kb EcoRI DNA fragment in
Escherichia coli. The atzC gene was further
delimited by functional analysis following transposon Tn5
mutagenesis and subcloned as a 2.0-kb
EcoRI-AvaI fragment. An E. coli
strain containing this DNA fragment expressed
N-isopropylammelide isopropylamino hydrolase activity,
metabolizing N-isopropylammelide stoichiometrically to
cyanuric acid and N-isopropylamine. The 2.0-kb DNA fragment
was sequenced and found to contain a single open reading frame of 1,209 nucleotides, encoding a protein of 403 amino acids. AtzC showed modest
sequence identity of 29 and 25%, respectively, to cytosine deaminase
and dihydroorotase, both members of an amidohydrolase protein
superfamily. The sequence of AtzC was compared to that of E. coli cytosine deaminase in the regions containing the five
ligands to the catalytically important metal for the protein. Pairwise
comparison of the 35 amino acids showed 61% sequence identity and 85%
sequence similarity. AtzC is thus assigned to the amidohydrolase
protein family that includes cytosine deaminase, urease, adenine
deaminase, and phosphotriester hydrolase. Similar sequence comparisons
of the most highly conserved regions indicated that the AtzA and AtzB
proteins also belong to the same amidohydrolase family. Overall, the
data suggest that AtzA, AtzB, and AtzC diverged from a common ancestor
and, by random events, have been reconstituted onto an atrazine
catabolic plasmid.
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INTRODUCTION |
Despite several years of research,
little information concerning the genes involved in the metabolism of
atrazine and other s-triazine compounds is available. An
inducible set of genes that encode the enzymes for melamine
(1,3,5-triazine-2,4,6-triamine) metabolism was isolated from
Pseudomonas sp. strain NRRL B-12227 (15, 16).
While NRRL B-12227 did not degrade atrazine, it metabolized melamine
via six enzymatic steps to liberate six ammonia molecules. Three of the
genes involved in the melamine degradation pathway, trzB,
trzC, and trzD, have been cloned. Similar
degradative genes have been isolated from Pseudomonas sp.
strain NRRL B-12228 and Klebsiella pneumoniae 99 (15,
16). More recently, it has been shown that the genes encoding
ammelide aminohydrolase (trzC) and cyanuric acid
amidohydrolase (trzD) (from strain NRRLB 12227) are located
on a large IncI plasmid in K. pneumonia 99 (21).
Genes encoding atrazine degradation activity from
Rhodococcus sp. strains have been reported
(27-29). In Rhodococcus sp. strain TE1,
N dealkylation of atrazine is mediated by a single gene, atrA (33). Rhodococcus corallinus NRRL
B-15544R has the ability to dechlorinate the s-triazines
desethylsimazine and desethylatrazine (26). This strain,
however, does not metabolize atrazine or simazine. The gene responsible
for the dechlorination-deamination has been sequenced and is termed
trzA (35). A Rhodococcus cytochrome P-450 multicomponent monooxygenase system, encoded by the
thcBCD genes (34), catalyzes the N
dealkylation of atrazine to desethylsimazine and desethylatrazine
(27, 28). A recombinant Rhodococcus strain containing atrA and trzA catalyzes multiple steps
in atrazine metabolism but not the complete mineralization of atrazine
(35).
We recently used functional and transposon Tn5 mutagenesis
approaches to isolate and characterize gene regions encoding atrazine catabolism by Pseudomonas sp. strain ADP (2,
10-12). Pseudomonas sp. strain ADP (23)
uses atrazine as a sole source of nitrogen for growth and transforms
the ring and side-chain atoms to carbon dioxide. The first gene in the
degradation pathway, atzA, catalyzes atrazine dechlorination
to hydroxyatrazine (10), directly forming a nonphytotoxic
metabolite (2). The atzA gene was localized to a
21.5-kb EcoRI genomic DNA fragment, designated pMD1, and shown to encode atrazine degradation activity in Escherichia
coli DH5
. Atrazine degradation was demonstrated by a
zone-clearing assay on agar medium containing crystalline atrazine
(10). AtzA, a polypeptide of 473 amino acids, was purified
to homogeneity by a rapid purification procedure (11) and
found to be a homotetramer with a native molecular mass of about 245 kDa.
The second step in the atrazine catabolic pathway is encoded by
atzB (2). Transposon Tn5 mutagenesis
localized atzA and atzB to the same (21.5-kb)
genomic DNA fragment, pMD1, as atzA. The atzB
gene encodes a 481-amino-acid polypeptide that transforms hydroxyatrazine to N-isopropylammelide
[2,4-dihydroxy-6-(isopropylamino)-s-triazine] by the
hydrolytic removal of the N-ethyl group. The atzA
and atzB genes are separated by approximately 8.7 kb in
Pseudomonas sp. strain ADP (2, 12).
Transposons have been reported to be a significant factor affecting the
evolution of novel degradative pathways (4). While there
have been many reports of transposable elements that carry antibiotic
resistance determinants, a smaller number have described catabolic
transposons that specify metabolic pathways for the degradation of
organic compounds (36). We recently reported that the
Pseudomonas sp. strain ADP atzA gene was flanked
by DNA showing greater than 95% sequence identity to insertion
sequence IS1071 from Alcaligenes sp. strain BR60
and that the atzA and atzB genes are located on a
96-kb self-transmissible plasmid, pADP-1 (12). Moreover, six
atrazine-degrading microorganisms which were recently isolated from
geographically separated sites exposed to atrazine contain homologous
atrazine degradation genes (12). Taken together, these
results indicate that atrazine catabolism via hydroxyatrazine is
widespread and suggests a potential molecular mechanism for the global
dispersion of the atzA and atzB genes.
Protein sequence analyses have indicated that AtzA and AtzB are 41 and
25% homologous, respectively, to TrzA, a protein that catalyzes
hydrolytic deamination of the s-triazine substrates melamine
and 2-chloro-4,6-diamino-s-triazine, but not atrazine (2, 26). TrzA has very recently been identified as a member of a broad class of bacterial amidohydrolases that includes
dihydroorotase, cytosine deaminase, urease, and adenine deaminase
(18). AtzB is also an amidohydrolase, but its evolutionary
relationship with other proteins has not been described.
In this study, we used N-isopropylammelide to screen a
Pseudomonas sp. strain ADP gene library for the gene
encoding the degradation of the AtzB product. This gene,
atzC, is shown here to encode an enzyme catalyzing the
hydrolytic deamidation of N-isopropylammelide to cyanuric
acid and isopropylamine. Moreover, the gene sequence reveals that AtzC
is a new member of the broad family of amidohydrolases that includes
TrzA. Most surprisingly, AtzA, AtzB, and AtzC contain significant
sequence identity near or in the regions of the amidohydrolase consensus metal-binding amino acids. The data suggests that AtzA, AtzB,
and AtzC have all diverged from a common ancestor and have now been
assembled on a catabolic plasmid for the purpose of metabolizing the
herbicide atrazine.
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MATERIALS AND METHODS |
Chemicals.
Authentic samples of atrazine
(2-chloro-4-isopropylamino-6-isopropylamino-1,3,5-s-triazine)
and N-isopropylammelide
(2,4-dihydroxy-6-isopropylamino-s-triazine) were obtained
from Novartis Crop Protection, Greensboro, N.C. Cyanuric acid
(2,4,6-trihydroxy-1,3,5-s-triazine) and biuret
(imidocarbonic diamide) were obtained from Aldrich Chemical Co.,
Milwaukee, Wis.
Bacteria and growth conditions.
Atrazine-degrading
Pseudomonas sp. strain ADP was previously described
(23) and was grown at 37°C in minimal salt medium (10) or Luria-Bertani (LB) medium (32). E. coli DH5
(32) was used for all molecular
manipulations. E. coli(pLTD4) was grown in LB medium
supplemented with tetracycline (30 µg/ml), and E. coli
containing plasmid pTD2 or pTD2.5 was grown in LB medium containing
ampicillin (25 µg/ml).
Library screening.
A Pseudomonas sp. strain ADP
DNA library containing 2,000 clones was obtained as described
previously (10). E. coli colonies were grouped
into 20 sets of 100 clones each. Each set of 100 clones was grown as a
mixture in a single test tube with 5 ml of LB medium containing 50 µg
of N-isopropylammelide per ml. After 18 h of incubation
at 37°C, the mixed clones were screened by high-performance liquid
chromatography (HPLC) analysis for the disappearance of
N-isopropylammelide (see below). Positive mixtures were
further analyzed by dividing the 100 original clones into 10 subgroups
and repeating the HPLC screening procedure. Individual clones with
N-isopropylammelide-metabolizing ability were subsequently identified. One clone, pLTD4, was chosen for further analysis.
Plasmids and molecular manipulations.
Subcloning and plasmid
purification were performed as described previously (32).
Plasmid pLTD4 contains a 25-kb EcoRI genomic DNA fragment
from Pseudomonas sp. strain ADP cloned in cosmid pLAFR3
(10). A 2.7-kb EcoRI fragment from plasmid pLTD4
was subcloned into the EcoRI site of pUC18, generating
plasmid pTD2. Plasmid pTD2 was further subcloned as a 2.0-kb
EcoRI-AvaI fragment in pUC18, producing plasmid
pTD2.5.
DNA sequencing.
The DNA sequence of plasmid pTD2.5 was
obtained by use of custom synthesized primers (Gibco BRL, Gaithersberg,
Md.). The DNA sequence was generated by fluorescence sequencing with
the Applied Biosystems (Foster City, Calif.) Prism DyeDeoxy Terminator
cycle sequencing kit. Sequencing reaction mixtures were prepared with a
TempCycler II thermal cycler (Coy Laboratory Products, Inc., Ann Arbor,
Mich.), purified through Centri-Sep spin columns (Princeton Separations, Inc., Adelphia, N.J.), and analyzed on an Applied Biosystems model 373 DNA sequencer. DNA sequence data were compiled with the GeneWorks 2.45 software package (IntelliGenetics, Inc., Mountain View, Calif.).
Sequence analyses.
DNA and protein sequence analyses were
done with GCG sequence analysis software (version 8.1-Unix; Genetics
Computer Group, Madison, Wis.). Searches of protein and nucleic acid
sequence data banks were performed at the National Center for
Biotechnology Information by use of the BLAST and Blitz network
services. The codon preference and third-position GC bias of possible
coding regions were compared to a codon usage table for
Pseudomonas sp. genes (PSE.COD) by use of the GCG program
CODONPREFERENCE. Consensus patterns were found by use of the
ProfileScan subroutine of the GCG program, and amino acid sequences
were aligned manually.
Metabolic studies with resting cells.
E. coli DH5
cells containing pLTD4, pTD2, or pDT2.5 were grown overnight in LB
medium with the appropriate antibiotics and harvested by centrifugation
at 14,000 × g for 10 min. Cells were washed three
times in 50 mM sodium phosphate buffer (pH 7.2) and resuspended in the
same buffer to an A600 of 1.0. N-Isopropylammelide or isopropylamine was added to a final
concentration of 50 µg/ml or 1 mM, and cell suspensions were
incubated at 37°C for 12 h.
Analysis of N-isopropylammelide and metabolites.
N-Isopropylammelide and cyanuric acid were determined by
HPLC analysis. Samples of resting cell suspensions were prepared for
HPLC analysis by centrifugation at 14,000 × g for 10 min. Supernatant fractions were added to an equal volume of methanol and centrifuged at 14,000 × g for 10 min to remove
salts and other insoluble materials. HPLC analysis was performed as
described previously (14) with a Hewlett-Packard HP 1090 liquid chromatography system equipped with a photodiode array detector
and interfaced to an HP 79994A Chemstation.
N-Isopropylammelide and cyanuric acid were resolved by use
of an analytical Lichrosorb RP-18 reverse-phase HPLC column (Alltech
Associates, Deerfield, Ill.; 5-µm spherical packing; 250 by 4.6 µm). The isocratic mobile phase was 0.1 M potassium phosphate buffer
(pH 7) at a flow rate of 1.0 ml min
1. For all compounds,
spectral data for the column eluent were acquired at between 200 and
400 nm (12-nm bandwidth per channel) with a sampling frequency of 640 ms. Spectra were referenced against a signal at 550 nm and compared to
those obtained with authentic samples of N-isopropylammelide
and cyanuric acid. Concentrations of N-isopropylammelide and
cyanuric acid were quantified by integrating peak areas at 220 nm.
Under these conditions, N-isopropylammelide and cyanuric
acid eluted from the column at about 20 and 4 min, respectively.
Isopropylamine in supernatants from resting cell suspensions was
determined with 2,4-dinitrofluorobenzene as described by McIntire and
coworkers (25) and modified by Dubin (13).
Mass spectrometry.
The products of
N-isopropylammelide degradation by E. coli
DH5
(pLTD4) and E. coli DH5
(pTD2) were identified by
mass spectrometry analysis. A 100-ml culture of E. coli
DH5
(pLTD4) or DH5
(pTD2) was grown in LB medium containing
tetracycline (30 µg/ml) or ampicillin (25 µg/ml), respectively, for
24 h at 37°C. Resting cells were prepared as described above and
resuspended in 1 ml of 50 mM potassium phosphate buffer (pH 7.0)
amended with 50 µg of N-isopropylammelide per ml. Cells
were incubated, with shaking, at 37°C for 12 h. Cells were
removed by centrifugation, and the supernatant was subjected to HPLC
analysis as described above. Samples were collected from the targeted
peak and subjected to mass spectrometry analysis. Direct-insertion mass
spectrometry was performed by use of a glycerol matrix with a Kratos
(Ramsey, N.J.) mass spectrometer operated in the fast atom bombardment
mode with xenon.
Tn5 mutagenesis.
Tn5 mutagenesis of
plasmid pTD2.5 was done with
::Tn5 (
467 b221 rex::Tn5
cI857 Oam29 Pam80) as described by de
Bruijn and Lupski (8). Tn5 insertions in cloned
insert DNA were identified and mapped by restriction enzyme analysis
and by Southern hybridization. To determine whether Tn5
insertions in pTD2.5 affected N-isopropylammelide degradation activity, E. coli cells containing mutated
plasmids were grown in LB medium containing ampicillin (30 µg/ml),
and resting cells were cultured with 50 µg of
N-isopropylammelide per ml. N-Isopropylammelide
in the culture medium was determined by HPLC analysis as described
above.
Protein purification and electrophoresis.
E. coli
DH5
and E. coli DH5
(pLTD4) were grown overnight in LB
medium containing ampicillin (25 µg/ml), when required. Cultures were
centrifuged at 14,000 × g for 10 min at 4°C and
washed in 0.85% NaCl, and cell pellets were resuspended in 25 mM
morpholinepropanesulfonic acid (MOPS) buffer (pH 6.9) on ice. Cold cell
suspensions were broken by three consecutive freeze-thaw cycles,
followed by sonication with a Biosonik sonicator (Bronwill Scientific,
Rochester, N.Y.). Sonication was carried out three times at 80% probe
intensity with intermittent cooling on ice. The broken cell suspensions were centrifuged at 17,000 × g for 90 min at 4°C to
obtain crude cell extracts. The cell extracts from E. coli
DH5
and E. coli DH5
(pTD2.5) were separated by sodium
dodecyl sulfate-polyacrylamide gel electrophoresis (PAGE) with 7.5%
acrylamide and a MiniProtean II gel apparatus (Bio-Rad Laboratories,
Hercules, Calif.) as described previously (11, 22). The AtzC
protein was electroblotted onto a polyvinylidene difluoride membrane
and processed for N-terminal sequencing as described previously
(24).
Amino acid analysis.
The N-terminal amino acid sequence of
gel-purified AtzC was determined with an Applied Biosystems 477A
protein sequencer at the Microchemical Facility, Human Genetics
Institute, University of Minnesota.
Nucleotide sequence accession number.
The DNA sequence of
atzC and the protein sequence of AtzC have been submitted to
the GenBank Nucleotide Sequence Database under accession no. AF017572.
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RESULTS |
Cloning of genes involved in the degradation of
N-isopropylammelide.
A library of
Pseudomonas sp. strain ADP genomic DNA (10) in
E. coli DH5
was screened for the ability to degrade
N-isopropylammelide, the product of atrazine transformation
by the sequential action of AtzA and AtzB. HPLC analysis identified
four clones that degraded 50 µg of N-isopropylammelide per
ml within 12 h. One cosmid clone, pLTD4, was selected for further
study. pLTD4 contained a 25-kb DNA insert (Fig.
1) cloned in pLAFR3.

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FIG. 1.
Restriction map of the 25-kb Pseudomonas sp.
strain ADP genomic DNA fragment cloned in plasmid pLTD4 and containing
the atzC gene. Symbols: , mutations which disrupted the
ability of cells to convert N-isopropylammelide to cyanuric
acid and isopropylamine; , mutations not affecting the ability of
cells to degrade N-isopropylammelide. A 2.0-kb
EcoRI-AvaI fragment was subcloned into pUC18 to
produce plasmid pTD2.5. The direction of transcription is indicated by
the arrow.
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In order to localize the gene region involved in
N-isopropylammelide metabolism, restriction fragments were
subcloned into pUC18. A plasmid containing a 2.7-kb EcoRI
insert, pTD2, was obtained, and the insert was further subcloned as a
2.0-kb EcoRI-AvaI fragment in pUC18 to yield
pTD2.5. Clones containing either plasmid metabolized N-isopropylammelide, as determined by HPLC analysis.
Enzymatic activity in resting cell suspensions.
E. coli
clones containing pTD2 or pTD2.5 were evaluated for their ability to
degrade N-isopropylammelide. With the HPLC conditions used
in this study, N-isopropylammelide, which eluted at 20 min, was observed to decrease over time, with a concomitant increase in a
peak eluting at 4 min. Since authentic cyanuric acid also eluted at 4 min, our results suggested that the cloned DNA region encoded the
ability to degrade N-isopropylammelide to cyanuric acid, the
third step in the Pseudomonas sp. strain ADP atrazine degradation pathway (Fig. 2). The same
apparent product was also detected in culture supernatants of
Pseudomonas sp. strain ADP growing with
N-isopropylammelide (data not shown).

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FIG. 2.
Third enzymatic step in atrazine degradation by
Pseudomonas sp. strain ADP. The AtzC enzyme,
N-isopropylammelide isopropylaminohydrolase, transforms
N-isopropylammelide to cyanuric acid and isopropylamine via
a hydrolytic deamination reaction.
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The unknown metabolite was purified by HPLC and subjected to mass
spectrometry. Fast atom bombardment-mass spectrometry indicated that
the metabolite had a molecular weight of 129 with prominent ion
fragments having molecular weights of 86 and 70. Authentic cyanuric
acid gave the same mass spectrum (data not shown). Taken together,
these data showed that the N-isopropyl group of
N-isopropylammelide had been replaced by a hydroxyl group,
producing cyanuric acid. Based on this metabolite, the other product of
this reaction likely was isopropylamine. Isopropylamine was detected
(data not shown) in resting cell culture supernatants of E. coli(pLTD4) and E. coli(pTD2.5) by a colorimetric assay
with 2,4-dinitrofluorobenzene.
The reaction stoichiometry was investigated with both
Pseudomonas sp. strain ADP and E. coli clones
(Table 1) to confirm that
N-isopropylammelide was transformed to cyanuric acid and isopropylamine in a single physiologically relevant reaction catalyzed by AtzC. Within 12 h, Pseudomonas sp. strain ADP
completely degraded 1 mM N-isopropylammelide to 0.7 mM
cyanuric acid and 1.2 mM isopropylamine. The concentration of cyanuric
acid was less than 1 mM because it was further degraded by
Pseudomonas sp. strain ADP. The catabolism of exogenously
added isopropylamine by Pseudomonas sp. strain ADP was very
slow. Resting cells of the bacterium required 6 days to metabolize 1 mM
isopropylamine (data not shown). E. coli(pLTD4), however,
completely degraded 1 mM N-isopropylammelide to 1.0 mM cyanuric acid and 1.1 mM isopropylamine within 12 h and failed to
further metabolize cyanuric acid or isopropylamine. E. coli(pTD2) gave the same stoichiometry but metabolized
N-isopropylammelide more slowly. It transformed 0.5 mM
N-isopropylammelide to 0.5 mM cyanuric acid and 0.6 mM
isopropylamine within the 12-h incubation period.
Tn5 mutagenesis analysis.
Random Tn5
mutagenesis was used to more precisely delineate the region of pTD2.5
encoding the enzyme(s) metabolizing N-isopropylammelide. Tn5 insertion sites in 32 mutated plasmids were determined
by restriction enzyme analysis; the locations of the 15 unique
Tn5 insertions in pTD2.5 are shown in Fig. 1. Nine
transposon insertions abolished N-isopropylammelide
degradation activity. The Tn5 insertions in all other
regions of pTD2.5 did not affect N-isopropylammelide degradation. Results of this mutagenesis study indicated that the
region essential for N-isopropylammelide degradation was
limited to the central 1.2-kb region of pTD2.5.
DNA sequence analysis.
The 2.0-kb
EcoRI-AvaI fragment cloned in pTD2.5 was
sequenced in both directions. The DNA sequence is shown in Fig.
3. The sequenced region contained one
large open reading frame (ORF) beginning at base 438. Results of codon
usage and preference analyses and the Tn5 data indicated
that this ORF comprised the N-isopropylammelide degradation
gene. This gene, designated atzC, consisted of 1,209 nucleotides predicted to encode a protein of 403 amino acids, with a
calculated molecular weight of 44,938 and a pI of 5.3. A putative
ribosome binding site (AGGAGG) was identified 11 nucleotides upstream of the translation initiation codon (ATG). Two consecutive stop codons (TAA TAG) were located at the end of the coding region, beginning at nucleotide 1647.

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FIG. 3.
Sequence of the atzC gene. The DNA sequence
of atzC was determined with pTD2.5. The DNA sequence of the
2,093-nucleotide region was determined on both strands. The
atzC ORF is indicated by the arrow. The start codon of the
atzC ORF is underlined, a possible ribosome binding site
upstream of the start site is in boldface, and stop codons are
represented by asterisks. The translation of the atzC ORF is
shown below the first nucleic acid of each codon.
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Expression of the recombinant protein.
Protein extracts from
E. coli DH5
and E. coli DH5
(pLTD4) were
separated by denaturing PAGE. Figure 4
shows that relative to the E. coli control, E. coli(pLTD4) produced a unique, intensely stained protein band with
a molecular weight of approximately 44,000. This size is in close
agreement with the calculated molecular weight of AtzC (44,938), based
on translation of the 403-amino-acid ORF. The putative AtzC protein was
electroblotted onto polyvinylidene difluoride membranes and subjected
to N-terminal sequence analysis. The first 10 amino acids detected
(SKDFDLIIRN) were identical to those predicted by translation of the
atzC ORF, with the exception of the posttranslational
removal of the N-terminal methionine (Fig. 4).

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FIG. 4.
Denaturing PAGE of total cell protein from E. coli DH5 (lane 1) and E. coli DH5 (pLTD4) (lane
2). Molecular mass markers (in kilodaltons) are on the left. The first
10 amino acids detected by N-terminal sequence analysis of the
approximately 44,000-molecular-weight protein encoded by
atzC are shown on the right.
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Protein sequence analysis.
The amino acid sequence derived
from translation of the atzC ORF was compared with those of
other proteins in the SwissProt and PIR databases and those derived
from translation of genes in the GenBank and EMBL databases. AtzC had
less than 30% overall sequence identity with any known proteins. The
highest identities were observed with cytosine deaminase from E. coli (29%) and dihydroorotase from Bacillus subtilis
(25%). Moreover, AtzC had about 20% identity with the first two
enzymes in the atrazine degradation pathway, AtzA and AtzB.
A search for conserved sequence motifs, however, was more informative.
AtzC matches the first 5 residues of the N-terminal dihydroorotase
signature pattern (Prosite entry PS00482), simplified here as
D-X-H-X-H, and has significant similarity (79%) to dihydroorotase (PyrC) from B. subtilis in 13 residues adjacent to the
N-terminal side of this pattern. Moreover, multisequence alignment of
this 18-residue motif region indicated that AtzC clearly fits in with dihydroorotase and other metal-binding hydrolases acting largely on
nitrogenous heterocyclic ring substrates (Fig.
5A). E. coli AdeC, which
encodes adenine deaminase, and Dan, an
N-acyl-D-glutamate amidohydrolase from
Alcaligenes xylosoxidans, also match AtzC in 10 of 18 amino
acids. The conserved H-X-H region is proposed to provide ligands to a
zinc atom bound by dihydroorotase (3), suggesting a need for
functional conservation of this region of the protein. In all cases,
the conserved motif is found in a region near the N terminus of each
protein.

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FIG. 5.
Alignment of N-terminal (A) and C-terminal (B) deduced
amino acid sequences of Pseudomonas sp. strain ADP AtzA
(atrazine chlorohydrolase; U55933), AtzB (hydroxyatrazine
ethylaminohydrolase; U66917), and AtzC (N-isopropylammelide
isopropylaminohydrolase; AF017572); B. subtilis PyrC
(dihydroorotase; M59757); E. coli AdeC (adenine deaminase;
L10328); and A. xylosoxidans Dan
(N-acyl-D-glutamate amidohydolase; D45919). The
amino acids were numbered according to the N terminus of each protein
as reported in GenBank, and boxes indicate identical amino acids.
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The alignment in Fig. 5A also reveals a heretofore-unrecognized
homology among AtzC, AtzB, and AtzA, the first three proteins in the
atrazine degradation pathway of Pseudomonas sp. strain ADP.
All three proteins show significant identity or similarity in amino
acids upstream of the H-X-H motif, and all contain the conserved H-X-H
motif in similar regions. While AtzA shares 10 of 18 amino acids with
AtzC in the motif region, AtzB shares 5 of 18 amino acids with AtzC and
8 of 18 amino acids with AtzA. Moreover, AtzC also shares conserved
amino acids with AtzA (13 of 20) and AtzB (8 of 20) in the C termini of
the proteins (Fig. 5B). While the sequence relatedness of AtzB was the
least, AtzB showed its greatest overall sequence identity with proteins
in the amidohydrolase protein superfamily: s-triazine
hydrolase from Rhodococcus corallinus (25% identity) and
dihydroorotase from Lactobacillus leichmannii (22%
identity).
Origins of AtzC.
It is also instructive to compare the
atzA, -B and -C gene sequences and the
respective DNA sequences flanking each of their coding regions. First,
atzA and -B have mol% G+C contents of 58.3 and
64.1, respectively, within the range of moles percent G+C contents
found in total Pseudomonas sp. DNA (58 to 70%). In
contrast, the atzC gene has a 39.5 mol% G+C content, well
outside the range for total Pseudomonas sp. DNA.
Previous evidence indicated that atrazine catabolism by
Pseudomonas sp. strain ADP may have had recent evolutionary
origins (12). Part of the evidence was the non-operon-like
structure of the atzA, -B and -C genes
and the discovery of insertion element sequences flanking the
atzA gene (12). In this study, DNA sequence analysis revealed the presence of insertion sequence-like elements downstream of atzC between nucleotides 1836 and 2035 (Fig.
3). The IS-like sequence showed the greatest sequence identity with portions of IS1051 (73%) from Xanthomonas
campestris pv. dieffenbachiae (1), IS52
(69%) from Pseudomonas savastanoi subsp.
savastanoi (37), ISXW5 and
ISXW4 (73%) from Xanthomonas campestris pv. campestris (18a; GenBank), and tnpA (68%)
from plasmid pEST1226 (30). In total, the data suggest that
atzC is derived from an ancient family of amidohydrolases
and has been brought together with two other long-divergent members of
that family by recent evolutionary events.
 |
DISCUSSION |
Studies on the biochemistry and genetics of microbiologically
mediated atrazine degradation are proving useful for our understanding of how bacteria evolve catabolic pathways in response to new chemical inputs into the environment. For the last 40 years, more than 1 billion
pounds of atrazine has been applied to soils. This application has
provided selection pressure for the evolution of new pathways of
microbial atrazine metabolism.
In this paper, we describe the cloning, sequencing, and analysis of the
third gene in the atrazine degradation pathway of Pseudomonas sp. strain ADP. This gene, atzC,
encodes an enzyme, N-isopropylammelide
isopropylaminohydrolase, which transforms N-isopropylammelide to cyanuric acid and isopropylamine
(Fig. 2). The identities of these products were unequivocally
established by HPLC, mass spectrometry, and chemical analysis.
The cloning, expression in E. coli, and elucidation of the
reaction products of atzC revealed the overall metabolic
logic of atrazine catabolism by Pseudomonas sp. strain ADP.
Metabolism proceeds by a series of hydrolases that are unique in each
reaction and that catalyze dechlorination and the sequential hydrolytic removal of N-ethylamine and N-isopropylamine. The
resultant product of the three enzyme-catalyzed reactions is cyanuric
acid, a cyclic polyamide in its preferred tautomeric form which is
known to undergo hydrolytic ring opening (15), a reaction
similar to that catalyzed by dihydroorotase. Cyanuric acid, biuret, and
urea are known to undergo hydrolytic C---N bond cleavage reactions, and
the occurrence of these reactions in Pseudomonas sp. strain
ADP could explain previous observations that all three ring carbon
atoms from atrazine are liberated as CO2 (23).
Moreover, cyanuric acid and related compounds are readily catabolized
by many soil bacteria (5, 6, 17, 20) and by
Pseudomonas sp. strain ADP to carbon dioxide and ammonia
(23), providing evolutionary pressure for the
atzA, -B, and -C genes to allow
bacterial growth on atrazine.
While the first two genes encoding enzymes for atrazine catabolism in
Pseudomonas sp. strain ADP, atzA and
atzB, have been localized to the same 21.5-kb genomic DNA
fragment, cloned in plasmid pMD1 (2, 10, 11), the exact
location of the atzC gene is currently not known.
Preliminary data indicate that atzC is located at least 25 kb from atzA and atzB, since pLTD4 did not
hybridize to atzA or atzB or overlap with pMD1.
However, our recent data indicate that all three genes are located on a
96-kb self-transmissible plasmid, pADP-1, in Pseudomonas sp.
strain ADP (12).
The most surprising finding in this report is the placement of AtzA,
AtzB, and AtzC in an ancient class of amidohydrolases that are
distributed throughout three kingdoms of life: Eubacteria, Archaea, and Eukaryota. AtzA, AtzB, and AtzC are
each comprised of polypeptides of similar sizes. Moreover, they all
catalyze hydrolytic reactions with nitrogen heterocyclic ring
substrates, as does dihydroorotase (PyrC) and adenine deaminase (AdeC).
However, the sequence identity in pairwise comparisons among AtzA,
AtzB, and AtzC was only on the order of 20%, so the idea for even an ancient common evolutionary origin was initially missed. Examination of
the sequences in the region of the conserved motif for the dihydroorotase (PyrC) protein family, as defined in the ProfileScan database, indicated that the AtzA, AtzB, and AtzC protein sequences were reasonably well conserved in the critical N-terminal H-X-H region
proposed to contain metal-coordinating histidine residues in the
members of this family of proteins (Fig. 5). This proposition is
strengthened by the recent analysis of the amidohydrolase protein family, which includes dihydroorotase, adenine deaminase, ureases, cytosine deaminases, and s-triazine hydrolase
(18). This study established an amidohydrolase superfamily
of proteins containing over 70 members, some of which show sequence
identities in pairwise comparisons that are lower than those observed
in pairwise comparisons among AtzA, AtzB, and AtzC. However, analysis
of the sequences in the context of the known structures of adenine
deaminase, ureases, and phosphotriester hydrolase revealed that
sequence conservation is highest in the region of the
metal-coordinating amino acids. Moreover, based on comparisons to the
crystal structure and enzyme architecture of ureases and adenine
deaminase (18, 19), it is proposed that these proteins all
share a common fold.
One of the members of the amidohydrolase protein superfamily is
cytosine deaminase (CodA) from E. coli (7), and
its pairwise alignment with AtzC reveals how a selective alignment in
the regions of proposed metal ligands can show a striking homology
between proteins that might otherwise be missed by a comparison of the entire protein sequences. Figure 6 shows
a comparison of the AtzC sequence and the sequence of cytosine
deaminase (CodA) in the regions of the five amino acids that coordinate
the transition metal implicated in its catalytic activity. While the
overall sequence identity is 29%, the identity in the regions shown in Fig. 6 is 61% and the similarity is 85%. This high sequence
relatedness argues that these regions are critical in the functioning
of AtzC and hence have been conserved despite extensive evolutionary
divergence. The high degree of identity, the observation that the
common residues appear in nearly identical regions, and the fact that
the similarities are spread across five regions which are most
conserved across the entire amidohydrolase superfamily strongly argue
for divergent, rather than convergent, evolution.

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|
FIG. 6.
Pairwise alignment of amino acid sequences from AtzC and
E. coli cytosine deaminase (CodA; P25524) in the regions of
CodA indicated to be involved in active-site metal coordination. The
five metal-liganding amino acids of CodA are indicated with vertical
arrows. Amino acid numbers were determined by counting from the N
terminus of each protein.
|
|
A key mechanistic feature of the amidohydrolase superfamily is that
many of the enzymes contain mononuclear or binuclear metal centers that
are essential for catalytic activity. Cytosine deaminase, for example,
can bind zinc, manganese, iron, or cobalt and is maximally activated by
iron (31). The role of metals in the catalytic mechanisms of
AtzA, AtzB, or AtzC is largely uninvestigated. Previously, it was
reported that AtzA purified from a recombinant E. coli
strain contained only substoichiometric quantities of transition
metals. However, more recent experiments indicated that atrazine
hydrolysis by AtzA is strongly activated by iron(II) and cobalt(II)
salts (9). These data suggest a functional significance for
the H-X-H motif found in that protein (Fig. 5). The conservation of all
cytosine deaminase metal-binding amino acids in AtzC suggests that the
latter protein might use a metal ion catalytically. Further studies on
the purification and characterization of AtzC will resolve this
question.
 |
ACKNOWLEDGMENTS |
This work was supported in part by a grant from Novartis Crop
Protection, Inc., and by grant 94-34339-1122 from the United States-Israel Binational Agricultural Research and Development (BARD)
Fund.
We thank Janis Mcfarland and Steven Dumford of Novartis for providing
s-triazine compounds, William Koskinen, Tom Krick, and Eric
Eccleston for experimental assistance, and Lynda Ellis for helpful
critical comments about the manuscript.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Soil, Water and Climate, University of Minnesota, 439 Borlaug Hall,
1991 Upper Buford Circle, St. Paul, MN 55108. Phone: (612) 624-2706. Fax: (612) 625-2208. E-mail: Sadowsky{at}soils.umn.edu.
Manuscript 971250037 in the University of Minnesota Agricultural
Experiment Station series.
 |
REFERENCES |
| 1.
|
Berthier, Y.,
D. Thierry,
M. Lemattre, and J. L. Guesdon.
1994.
Isolation of an insertion sequence (IS1051) from Xanthomonas campestris pv. dieffenbachiae with potential use for strain identification and characterization.
Appl. Environ. Microbiol.
60:377-384[Abstract/Free Full Text].
|
| 2.
|
Boundy-Mills, K. L.,
M. L. de Souza,
R. T. Mandelbaum,
L. P. Wackett, and M. J. Sadowsky.
1997.
The atzB gene of Pseudomonas sp. strain ADP encodes the second enzyme of a novel atrazine degradation pathway.
Appl. Environ. Microbiol.
63:916-923[Abstract].
|
| 3.
|
Brown, D. C., and K. D. Collins.
1991.
Dihydroorotase from Escherichia coli: substitution of Co(II) for the active site Zn(II).
J. Biol. Chem.
266:1597-1604[Abstract/Free Full Text].
|
| 4.
|
Chakrabarty, A. M.
1996.
Microbial degradation of toxic chemicals: evolutionary insights and practical considerations.
ASM News
62:130-137.
|
| 5.
|
Cook, A. M.,
P. Bellstein,
H. Grossenbacher, and R. Hutter.
1985.
Ring cleavage and degradative pathway of cyanuric acid in bacteria.
Biochem. J.
231:25-30[Medline].
|
| 6.
|
Cook, A. M.
1987.
Biodegradation of s-triazine xenobiotics.
FEMS Microbiol. Rev.
46:93-116.
|
| 7.
|
Danielsen, S.,
M. Kilstrup,
K. Barilla,
B. Jochimsen, and J. Neuhard.
1992.
Characterization of the Escherichia coli codBA operon encoding cytosine permease and cytosine deaminase.
Mol. Microbiol.
6:1335-1344[Medline].
|
| 8.
|
de Bruijn, F. J., and J. R. Lupski.
1984.
The use of transposon Tn5 mutagenesis in the rapid generation of correlated physical and genetic maps of DNA segments cloned into multicopy plasmids.
Gene
27:131-149[Medline].
|
| 9.
| de Souza, M. L. Unpublished data.
|
| 10.
|
de Souza, M. L.,
L. P. Wackett,
K. L. Boundy-Mills,
R. T. Mandelbaum, and M. J. Sadowsky.
1995.
Cloning, characterization, and expression of a gene region from Pseudomonas sp. strain ADP involved in the dechlorination of atrazine.
Appl. Environ. Microbiol.
61:3373-3378[Abstract].
|
| 11.
|
de Souza, M. L.,
M. J. Sadowsky, and L. P. Wackett.
1996.
Atrazine chlorohydrolase from Pseudomonas sp. strain ADP: gene sequence, enzyme purification, and protein characterization.
J. Bacteriol.
178:4894-4900[Abstract/Free Full Text].
|
| 12.
|
de Souza, M. L.,
L. P. Wackett, and M. J. Sadowsky.
1997.
Highly homologous atrazine degradation genes widespread in recently isolated atrazine degrading organisms, abstr. Q-405, p. 522.
Abstracts of the 97th General Meeting of the American Society for Microbiology 1997
.
|
| 13.
|
Dubin, D. T.
1960.
The assay and characterization of amines by means of 2,4-dinitrofluorobenzene.
J. Biol. Chem.
235:783-786[Free Full Text].
|
| 14.
|
Eady, R. R.,
T. R. Jarman, and P. J. Large.
1971.
Microbial oxidation of amines.
Biochem. J.
125:449-459[Medline].
|
| 15.
|
Eaton, R. W., and J. S. Karns.
1991.
Cloning and comparison of the DNA encoding ammelide aminohydrolase and cyanuric acid amidohydrolase from three s-triazine-degrading bacterial strains.
J. Bacteriol.
173:1363-1366[Abstract/Free Full Text].
|
| 16.
|
Eaton, R. W., and J. S. Karns.
1991.
Cloning and analysis of s-triazine catabolic genes from Pseudomonas sp. strain NRRLB-12227.
J. Bacteriol.
173:1215-1222[Abstract/Free Full Text].
|
| 17.
|
Erickson, L. E., and K. H. Lee.
1989.
Degradation of atrazine and related s-triazines.
Crit. Rev. Environ. Control
19:1-14.
|
| 18.
|
Holm, L., and C. Sander.
1997.
An evolutionary treasure: unification of a broad set of amidohydrolases related to urease.
Proteins
28:72-82[Medline].
|
| 18a.
| Hsieh, Y., and J. Chen. Unpublished data.
|
| 19.
|
Jabri, E.,
M. B. Carr,
R. P. Hausinger, and P. A. Karplus.
1995.
The crystal structure of urease from Klebsiella aerogenes.
Science
268:998-1004[Abstract/Free Full Text].
|
| 20.
|
Jutzi, K.,
A. M. Cook, and R. Hutter.
1982.
The degradative pathway of the s-triazine melamine.
Biochem. J.
208:679-684[Medline].
|
| 21.
|
Karns, J. S., and R. W. Eaton.
1997.
Genes encoding s-triazine degradation are plasmid-borne in Klebsiella pneumoniae strain 99.
J. Agric. Food Chem.
45:1017-1022.
|
| 22.
|
Laemmli, U. K.
1970.
Cleavage of structural proteins during the assembly of the head of bacteriophage T4.
Nature (London)
227:680-685[Medline].
|
| 23.
|
Mandelbaum, R. T.,
D. L. Allan, and L. P. Wackett.
1995.
Isolation and characterization of a Pseudomonas sp. that mineralizes the s-triazine herbicide atrazine.
Appl. Environ. Microbiol.
61:1451-1457[Abstract].
|
| 24.
|
Matsudaira, P.
1987.
Sequence from picomole quantities of proteins electroblotted onto polyvinylidene difluoride membranes.
J. Biol. Chem.
262:10035-10038[Abstract/Free Full Text].
|
| 25.
|
McIntire, F. C.,
L. M. Clements, and M. Sproull.
1953.
1-Fluoro-2,4-dinitrobenzene as a quantitative reagent for primary and secondary amines.
Anal. Chem.
25:1757-1758.
|
| 26.
|
Mulbry, W. W.
1994.
Purification and characterization of an inducible S-triazine hydrolase from Rhodococcus corallinus NRRL B-15444R.
Appl. Environ. Microbiol.
60:613-618[Abstract/Free Full Text].
|
| 27.
|
Nagy, I.,
F. Compernolle,
K. Ghys,
J. Vanderleyden, and R. de Mot.
1995.
A single cytochrome P-450 system is involved in degradation of the herbicides EPTC (S-ethyldipropylthiocarbamate) and atrazine by Rhodococcus sp. strain NI86/21.
Appl. Environ. Microbiol.
61:2056-2060[Abstract].
|
| 28.
|
Nagy, I.,
G. Schoofs,
F. Compernolle,
P. Proost,
J. Vanderleyden, and R. Demot.
1995.
Degradation of the thiocarbamate herbicide EPTC (S-ethyl dipropylcarbamothioate) and biosafening by Rhodococcus sp. strain NI86/21 involve an inducible cytochrome P-450 system and aldehyde dehydrogenase.
J. Bacteriol.
177:676-687[Abstract/Free Full Text].
|
| 29.
|
Nagy, I.,
S. Verheijen,
A. De Schrijver,
J. Van Damme,
P. Proost,
G. Schoofs,
J. Vanderleyden, and R. De Mot.
1995.
Characterization of the Rhodococcus sp. NI86/21 gene encoding alcohol: N,N'-dimethyl-4-nitrosoaniline oxidoreductase inducible by atrazine and thiocarbamate herbicides.
Arch. Microbiol.
163:439-446[Medline].
|
| 30.
|
Nurk, A.,
L. Kasak, and M. Kivisaar.
1991.
Sequence of the gene (pheA) encoding phenol monooxygenase from Pseudomonas sp. EST1001: expression in Escherichia coli and Pseudomonas putida.
Gene
102:13-18[Medline].
|
| 31.
|
Porter, D. J., and E. A. Austin.
1993.
Cytosine deaminase: the role of divalent metal ions in catalysis.
J. Biol. Chem.
268:24005-24011[Abstract/Free Full Text].
|
| 32.
|
Sambrook, J.,
E. F. Fritsch, and T. Maniatis.
1989.
.
Molecular cloning: a laboratory manual, 2nd ed.
Cold Spring Harbor Laboratory Press, Cold Spring Harbor, N.Y.
|
| 33.
|
Shao, Z. Q., and R. Behki.
1995.
Cloning of the genes for degradation of the herbicides EPTC (S-ethyldipropylthiocarbamate) and atrazine from Rhodococcus sp. strain TE1.
Appl. Environ. Microbiol.
61:2061-2065[Abstract].
|
| 34.
|
Shao, Z. Q., and R. Behki.
1996.
Characterization of the expression of the thcB gene, coding for a pesticide-degrading cytochrome P-450 in Rhodococcus strains.
Appl. Environ. Microbiol.
62:403-407[Abstract].
|
| 35.
|
Shao, Z. Q.,
W. Sefens,
W. Mulbry, and R. M. Behki.
1995.
Cloning and expression of the s-triazine hydrolase gene (trzA) from Rhodococcus corallinus and development of Rhodococcus recombinant strains capable of dealkylating and dechlorinating the herbicide atrazine.
J. Bacteriol.
177:5748-5755[Abstract/Free Full Text].
|
| 36.
|
Wyndham, R. C.,
A. E. Cashore,
C. H. Nakatsu, and M. C. Peel.
1994.
Catabolic transposons.
Biodegradation
5:323-342[Medline].
|
| 37.
|
Yamada, T.,
P. Lee, and T. Kosuge.
1986.
Insertion sequence of Pseudomonas savastanoi: nucleotide sequence and homology with Agrobacterium tumefaciens transfer DNA.
Proc. Natl. Acad. Sci. USA
83:8263-8267[Abstract/Free Full Text].
|
J Bacteriol, January 1998, p. 152-158, Vol. 180, No. 1
0021-9193/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
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