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Applied and Environmental Microbiology, April 2002, p. 1803-1807, Vol. 68, No. 4
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.4.1803-1807.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Cloning and Characterization of linR, Involved in Regulation of the Downstream Pathway for
-Hexachlorocyclohexane Degradation in Sphingomonas paucimobilis UT26
Keisuke Miyauchi,1,2* Haeng-Seog Lee,1 Masao Fukuda,2 Masamichi Takagi,1 and Yuji Nagata1,3
Department of Biotechnology, The University of Tokyo, 1-1-1 Yayoi, Bunkyo-ku, Tokyo 113-8657,1
Department of Bioengineering, Kamitomioka, Nagaoka, Niigata 940-2188,2
Graduate School of Life Sciences, Tohoku University, Katahira, Sendai 980-8577, Japan3
Received 5 October 2001/
Accepted 9 January 2002

ABSTRACT
In
Sphingomonas paucimobilis UT26, LinD and LinE activities,
which are responsible for the degradation of

-hexachlorocyclohexane,
are inducibly expressed in the presence of their substrates,
2,5-dichlorohydroquinone (2,5-DCHQ) and chlorohydroquinone (CHQ).
The nucleotide sequence of the 1-kb upstream region of the
linE gene was determined, and an open reading frame (ORF) was found
in divergent orientation from
linE. Because the putative protein
product of the ORF showed similarity to the LysR-type transcriptional
regulator (LTTR) family, we named it
linR. The fragment containing
the putative LTTR recognition sequence (a palindromic TN
11A
sequence), which exists immediately upstream of
linE, was ligated
with the reporter gene
lacZ and was inserted into the plasmid
expressing LinR under the control of the
lac promoter. When
the resultant plasmid was introduced into
Escherichia coli,
the LacZ activity rose in the presence of 2,5-DCHQ and CHQ.
RNA slot blot analysis for the total RNAs of UT26 and UT102,
which has an insertional mutation in
linR, revealed that the
expression of the
linD and
linE genes was induced in the presence
of 2,5-DCHQ, CHQ, and hydroquinone in UT26 but not in UT102.
These results indicated that the
linR gene is directly involved
in the inducible expression of the
linD and
linE genes.

INTRODUCTION

-Hexachlorocyclohexane (

-HCH; also called

-BHC or lindane) is
a haloorganic insecticide which has been used worldwide.
Sphingomonas paucimobilis UT26 can utilize

-HCH as a sole source of carbon
and energy (
4). The degradation pathway of

-HCH in UT26 consists
of upstream and downstream pathways, which are shown in Fig.
1 (
11). In the upstream pathway,

-HCH is transformed to 2,5-dichlorohydroquinone
(2,5-DCHQ), which is further degraded in the downstream pathway.
In the previous studies, we isolated five genes (
linA,
linB,
linC,
linD, and
linE) involved in these pathways and characterized
their protein products (
3,
7,
8,
12,
13). The
linA,
linB, and
linC genes, for the upstream pathway, exist separately on the
UT26 genome and are constitutively expressed (
4,
12,
13). On
the other hand, the
linD and
linE genes, for the downstream
pathway, are located near each other and are inducibly expressed
in the presence of their substrates (
7,
8). They may constitute
an operon (
7). LinE is a novel
meta-cleavage dioxygenase which
cleaves aromatic rings with two hydroxy groups at
para positions.
We also demonstrated that PcpA from a pentachlorophenol-degrading
bacterium,
Sphingomonas chlorophenolica ATCC 39723, has activity
similar to that of LinE (
14). These results directly demonstrated
a new type of ring cleavage pathway for aromatic compounds,
the "hydroquinone (HQ) pathway." Although reports of the HQ
pathway have been limited, we consider it one of the major degradation
pathways for aromatic compounds whose regulation system for
gene expression has been established. However, the regulation
system for the genes of the HQ pathway in UT26 is still unknown.
In this study, we cloned and characterized a regulatory gene
encoding a transcriptional regulator for
linD and
linE.

MATERIALS AND METHODS
Bacterial strains, plasmids, and culture conditions.
The bacterial strains and plasmids used in this study are listed
in Table
1.
Sphingomonas strains and
Escherichia coli were grown
on Luria broth (
6). The cultures were incubated at 30°C
for
Sphingomonas strains and at 37°C for
E. coli. Antibiotics
were used at final concentrations of 50 µg/ml for ampicillin
and kanamycin and 25 µg/ml for nalidixic acid.
Isolation of DNA.
Plasmid DNA of
E. coli was isolated by the alkaline lysis method
of Maniatis et al. (
6). Total DNAs from
Sphingomonas strains
were isolated as described previously (
9).
Southern blot analysis.
Southern blot analysis was performed with the ECL (enhanced chemiluminescence) gene detection system (Amersham, Arlington Heights, Ill.) according to the protocol provided.
Nucleotide sequence determination.
The nucleotide sequences of a 1.0-kb PstI-SmaI fragment of plasmid pLR1 and the fragments amplified by PCR were determined by the dideoxy chain termination method with the LI-COR (Lincoln, Neb.) model 4000L DNA-sequencing system.
Construction of plasmids for promoter activity assay.
Various lengths of the region upstream of linE followed by the 5' end of the linE gene were amplified by PCR and fused to the lacZ gene in the same frame on the plasmid pMC1403 (18) to form plasmids pMEU1, pMEU2, and pMEU3. The primers used to amplify the region upstream of linE are LEUP-1 (5'-GCCGAATTCTCGTGCAGCGGCGCTGA-3'), LEUP-2 (5'-GCGGGATCCAGTTGCATCATGATCGCTC-3'), LEUP-3 (5'-GCCGAATTCTATATTCACAATCTG-3'), and LEUP-4 (5'-GCCGAATTCTATGAAGGTCCGC-3'). To amplify the fragments for pMEU1, pMEU2, and pMEU3, primers LEUP-4, LEUP-3, and LEUP-2, respectively, were used in combination with LEUP-1. The resultant plasmids can express the LinE-LacZ fusion protein if the upstream region has promoter activity. To form pMEU1R, pMEU2R, and pMEU3R, the PvuII-PvuII fragment containing Plac-linR was isolated from pLR1 and inserted into the BalI site of each plasmid. To make the BalI sites easily digested, each plasmid was purified from E. coli JM110 (dcm mutant).
ß-Galactosidase assay.
E. coli harboring each plasmid was incubated with isopropyl-ß-D-thiogalactopyranoside (1 mM). The culture was divided, and each substrate was added (10 µM final concentration). After incubation for 2 h, the cells were harvested and resuspended in 1 ml of Z buffer (60 mM Na2HPO4, 40 mM NaH2PO4, 10 mM KCl, 1 mM MgSO4, 50 mM 2-mercaptoethanol). The cells were disrupted by sonication (Sonifier 250; Branson, Danbury, Conn.) and centrifuged at 12,000 x g. The supernatant was used for the measurement of ß-galactosidase activity. The ß-galactosidase activity of the cell extract was measured as follows. One hundred microliters of 13.3 mM o-nitrophenyl-ß-D-galactopyranoside was added to 400 µl of cell extract. After incubation at 30°C, 250 µl of Na2CO3 solution (1 M) was added to stop the reaction, and the absorbance at 420 nm was measured. The protein concentration of the cell extract was determined by using a protein assay kit (Bio-Rad Laboratories, Richmond, Calif.) with bovine serum albumin as a standard. One unit of ß-galactosidase activity was defined as the amount of enzyme that would hydrolyze 1 nmol of o-nitrophenyl-ß-D-galactopyranoside in 1 min at 30°C.
RNA slot blot analysis.
Total RNAs of UT26 and UT102 were isolated as described previously (8). 2,5-DCHQ, chlorohydroquinone (CHQ), and HQ were used as inducers at final concentrations of 10 µM. Six micrograms of each RNA was blotted onto the nylon membrane with a PR600 slot blot manifold (Amersham, Arlington Heights, Ill.). Northern blot hybridization was performed as described previously (8).
Nucleotide sequence accession number.
The nucleotide sequence data reported in this paper were registered in the DDBJ nucleotide sequence database under accession no. AB021863.

RESULTS AND DISCUSSION
Cloning and sequencing of the linR gene.
S. paucimobilis UT26 inducibly expresses LinD and LinE activities
in the presence of 2,5-DCHQ, substrate for LinD (
8) and CHQ,
substrate for both LinD and LinE (
7,
8). On the other hand,
UT102, which is one of the Tn
5-induced mutants of UT26, shows
faint LinD and LinE activities with or without their substrates
(
7,
10). It can be considered that this phenotype of UT102 is
caused by a mutation in a regulatory gene for the expression
of
linD and
linE. As UT102 has an insertional mutation other
than Tn
5 in the upstream region of the
linE gene (K. Miyauchi,
Y. Nagata, and M. Takagi, unpublished data), we determined the
nucleotide sequence of this region. The nucleotide sequence
of a 1.0-kb
PstI-
SmaI fragment was determined, and we found
an open reading frame (ORF) of 909 bp in this region (Fig.
2).
Because this ORF showed similarity to regulatory proteins (see
below) and UT102 has an insertion sequence in the N terminus
of the ORF (Fig.
2) (Miyauchi et al., unpublished), we designated
the ORF
linR. The
linR gene appears to be divergently transcribed
from
linE and to use GTG as a start codon. The G+C content of
the
linR gene is 61.3%, which is similar to those of other
lin genes (
7,
8,
12,
13) except for
linA (53.9%) (
3). The deduced
molecular mass of LinR is 33.6 kDa.
Homology search analysis of LinR.
A FASTA homology search revealed that LinR shows similarity
to LysR-type transcriptional regulators (LTTRs) (
16). The proteins
which showed high similarity to LinR are as follows: OhbR (29%
identity; 69% similarity), a LysR-like protein in an operon
for
ortho-halobenzoate degradation in
Pseudomonas aeruginosa strain JB2 (AF087482); NahR (31% identity; 68% similarity),
a regulatory protein for naphthalene degradation genes in plasmid
NAH7 of
Pseudomonas putida (J04233); NagR (32% identity; 66%
similarity), the regulator of the
nag operon in
Ralstonia sp.
strain U2 plasmid pWWU2 (AF036940-2); NahR (31% identity; 68%
similarity), a regulatory protein for naphthalene degradation
genes in
Pseudomonas stutzeri AN10 (AF039534-4); and SyrM1 (32%
identity; 66% similarity), a LysR-like protein in
Rhizobium sp. strain NGR234 (AE000091-2). The LTTR family is one of the
ubiquitous transcriptional regulators in prokaryotes (
16), and
the transcription of the genes responsible for the degradation
of aromatic compounds is often regulated by LTTRs (
2). Like
known LTTRs, LinR also contains a putative helix-turn-helix
structure (S
22VSAAARELDLPQPTASHGLARLRKALGDPL
52) at its N terminus,
which is proposed to be responsible for DNA binding. Like many
LTTRs, LinR does not have a glycine residue in the middle of
the helix-turn-helix (D
31 in LinR), which is conserved among
classic helix-turn-helix structures (
16), while OhbR, two NahRs,
and SyrM have it. In the immediate upstream region of the
linE gene, there is a consensus sequence for LTTR binding (A
TTCACAATCTGA
AT),
which is a palindromic TN
11A sequence (beginning and end underlined)
(
16) (Fig.
3).
In vivo analysis of the function of LinR.
To characterize the function of LinR in the expression of
linE,
we constructed the plasmids pMEU1R, pMEU2R, and pMEU3R (Fig.
3). We also constructed pMEU1, pMEU2, and pMEU3, which do not
have the
linR gene, as a control for each plasmid.
E. coli harboring
pMEU1, pMEU2, or pMEU3 showed only a faint LacZ activity under
every condition we tested (data not shown).
E. coli harboring
either pMEU1R or pMEU2R showed an increase in LacZ activity
in the presence of 2,5-DCHQ and CHQ (23- to 36-fold), while
E. coli harboring pMEU3R did not (Fig.
4). These results indicated
that the
linR gene and the palindromic TN
11A sequence which
is located upstream of
linE are necessary for the upregulation
of
linE expression. It also seemed that the TN
11A sequence is
required to repress the expression of the
linE gene when the
substrates are not present.
Substrate specificity of LinR.
The substrate specificity of LinR was studied with the
E. coli in vivo system described above. In addition to 2,5-DCHQ and
CHQ, only 2,6-DCHQ gave upregulation activity to
E. coli harboring
pMEU1R (Table
2). This result indicated that LinR specifically
recognizes mono- or di-CHQs among the substrates we tested.
RNA slot blot analysis.
To confirm the function of the
linR gene for the expression
of
linE and
linD, RNA slot blot analysis was performed with
total RNAs of UT26 and UT102, which is a
linR mutant. Figure
5 shows that
linD and
linE were inducibly expressed in the presence
of 2,5-DCHQ, CHQ, and HQ in UT26, while almost no expression
of
linD and
linE was observed in UT102 even in the presence
of these substrates. The
linA gene, which is constitutively
expressed regardless of the presence of the substrates (
4),
was used as a control. This result indicated that HQ worked
as an inducer for
linD and
linE expression in UT26 (Fig.
5)
in addition to 2,5-DCHQ and CHQ, while it did not in the
E. coli in vivo system (Fig.
4 and Table
2), suggesting a difference
between the permeabilities of HQ in
Sphingomonas and
E. coli.
The possibility that the intermetabolite of HQ works as an inducer
in UT26 could not be excluded. However, we can conclude that
CHQs are direct substrates of LinR at least, because
E. coli does not have activity for conversion of CHQs. Like LinR, the
inducer of NahR for the expression of naphthalene-degradative
genes is an aromatic compound, salicylate (
17), while that of
CatR for the expression of catechol-degradative genes is
cis,
cis-muconate,
which is the ring cleavage product of catechol (
15). The BenM
protein, which regulates the expression of the
ben operon in
Acinetobacter sp. strain ADP1, responds to both aromatic compounds
and ring cleavage products, i.e., benzoate and
cis,
cis-muconate
(
1). It would be very interesting to know why these substrates
are selected as the inducers for the regulation system of each
degradation pathway.
HQ pathway.
The results described above indicate that the
linR gene is necessary
for the inducible expression of
linE and
linD. Because (C)HQs
are specific substrates not only for LinD and LinE but also
for LinR (Fig.
4 and
5 and Table
2), the genes encoding these
three proteins seem to constitute a specific system for the
degradation of (C)HQs, while the gene expression of some dehalogenases
for xenobiotic haloalkanes is constitutive (
5). The existence
of a well-established degradation system strongly suggests that
the HQ pathway is one of the major pathways for the degradation
of aromatic compounds.
linD and
linE are considered to form
an operon for the following reasons, although we could not detect
the band corresponding to the predicted length for the putative
linE-
linD operon by Northern blot analysis (data not shown).
First, the
linD and
linE genes are located close to each other.
Second, the expression of
linD is induced simultaneously with
that of
linE (Fig.
5). Third, we could not identify an obvious
terminator sequence between the
linE and
linD genes. We are
trying to identify other genes which belong to this operon.

ACKNOWLEDGMENTS
This work was supported in part by a Grant-in-Aid for Scientific
Research from the Ministry of Education, Science, Sports, and
Culture of Japan.
This work was performed using the facilities of the Biotechnology Research Center, The University of Tokyo.

FOOTNOTES
* Corresponding author. Mailing address: Department of Bioengineering, Kamitomioka, Nagaoka, Niigata 940-2188, Japan. Phone: 81-258-47-9427. Fax: 81-258-47-9450. E-mail:
kmiya{at}vos.nagaokaut.ac.jp.


REFERENCES
1
- Collier, L. S., G. L. Gaines III, and E. L. Neidle. 1998. Regulation of benzoate degradation in Acinetobacter sp. strain ADP1 by BenM, a LysR-type transcriptional activator. J. Bacteriol. 180:2493-2501.[Abstract/Free Full Text]
2
- Diaz, E., and M. A. Prieto. 2000. Bacterial promoters triggering biodegradation of aromatic pollutants. Curr. Opin. Biotechnol. 11:467-475.[CrossRef][Medline]
3
- Imai, R., Y. Nagata, M. Fukuda, M. Takagi, and K. Yano. 1991. Molecular cloning of a Pseudomonas paucimobilis gene encoding a 17-kilodalton polypeptide that eliminates HCl molecules from
-hexachlorocyclohexane. J. Bacteriol. 173:6811-6819.[Abstract/Free Full Text]
4
- Imai, R., Y. Nagata, K. Senoo, H. Wada, M. Fukuda, M. Takagi, and K. Yano. 1989. Dehydrochlorination of
-hexachlorocyclohexane (
-BHC) by
-BHC-assimilating Pseudomonas paucimobilis. Agric. Biol. Chem. 53:2015-2017.
5
- Janssen, D. B., J. E. Oppentocht, and G. J. Poelarends. 2001. Microbial dehalogenation. Curr. Opin. Biotechnol. 12:254-258.[CrossRef][Medline]
6
- Maniatis, T., E. F. Fritsch, and J. Sambrook. 1982. Molecular cloning: a laboratory manual. Cold Spring Harbor Laboratory, Cold Spring Harbor, N.Y.
7
- Miyauchi, K., Y. Adachi, Y. Nagata, and M. Takagi. 1999. Cloning and sequencing of a novel meta-cleavage dioxygenase gene whose product is involved in degradation of
-hexachlorocyclohexane in Sphingomonas paucimobilis. J. Bacteriol. 181:6712-6719.[Abstract/Free Full Text]
8
- Miyauchi, K., S. K. Suh, Y. Nagata, and M. Takagi. 1998. Cloning and sequencing of a 2,5-dichlorohydroquinone reductive dehalogenase gene which is involved in the degradation of
-hexachlorocyclohexane in Sphingomonas paucimobilis. J. Bacteriol. 180:1354-1359.[Abstract/Free Full Text]
9
- Nagata, Y., R. Imai, A. Sakai, M. Fukuda, K. Yano, and M. Takagi. 1993. Isolation and characterization of Tn5-induced mutants of Pseudomonas paucimobilis UT26 defective in
-hexachlorocyclohexane dehydrochlorinase (LinA). Biosci. Biotech. Biochem. 57:703-709.[Medline]
10
- Nagata, Y., K. Miyauchi, S. K. Suh, A. Futamura, and M. Takagi. 1996. Isolation and characterization of Tn5-induced mutants of Sphingomonas paucimobilis defective in 2,5-dichlorohydroquinone degradation. Biosci. Biotech. Biochem. 60:689-691.
11
- Nagata, Y., K. Miyauchi, and M. Takagi. 1999. Complete analysis of genes and enzymes for
-hexachlorocyclohexane degradation in Sphingomonas paucimobilis UT26. J. Ind. Microbiol. Biotechnol. 23:380-390.[CrossRef][Medline]
12
- Nagata, Y., T. Nariya, R. Ohtomo, M. Fukuda, K. Yano, and M. Takagi. 1993. Cloning and sequencing of a dehalogenase gene encoding an enzyme with hydrolase activity involved in the degradation of
-hexachlorocyclohexane in Pseudomonas paucimobilis. J. Bacteriol. 175:6403-6410.[Abstract/Free Full Text]
13
- Nagata, Y., R. Ohtomo, K. Miyauchi, M. Fukuda, K. Yano, and M. Takagi. 1994. Cloning and sequencing of a 2,5-dichloro-2,5-cyclohexadiene-1,4-diol dehydrogenase gene involved in the degradation of
-hexachlorocyclohexane in Pseudomonas paucimobilis. J. Bacteriol. 176:3117-3125.[Abstract/Free Full Text]
14
- Ohtsubo, Y., K. Miyauchi, K. Kanda, T. Hatta, H. Kiyohara, T. Senda, Y. Nagata, Y. Mitsui, and M. Takagi. 1999. PcpA, which is involved in the degradation of pentachlorophenol in Sphingomonas chlorophenolica ATCC39723, is a novel type of ring-cleavage dioxygenase. FEBS Lett. 459:395-398.[CrossRef][Medline]
15
- Parsek, M. R., D. L. Shinabarger, R. K. Rothmel, and A. M. Chakrabarty. 1992. Roles of CatR and cis,cis-muconate in activation of the catBC operon, which is involved in benzoate degradation in Pseudomonas putida. J. Bacteriol. 174:7798-7806.[Abstract/Free Full Text]
16
- Schell, M. A. 1993. Molecular biology of the LysR family of transcriptional regulators. Annu. Rev. Microbiol. 47:597-626.[CrossRef][Medline]
17
- Schell, M. A. 1985. Transcriptional control of the nah and sal hydrocarbon-degradation operons by the nahR gene product. Gene 36:301-309.[CrossRef][Medline]
18
- Shapira, S. K., J. Chou, F. V. Richaud, and M. J. Casadaban. 1983. New versatile plasmid vectors for expression of hybrid proteins coded by a cloned gene fused to lacZ gene sequences encoding an enzymatically active carboxy-terminal portion of beta-galactosidase. Gene 25:71-82.[CrossRef][Medline]
19
- Viera, J., and J. Messing. 1987. Production of single-stranded plasmid DNA. Methods Enzymol. 153:3-11.[Medline]
Applied and Environmental Microbiology, April 2002, p. 1803-1807, Vol. 68, No. 4
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.4.1803-1807.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
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