Namiko Gibu1, Daisuke Kasai2, Takumi Ikawa1, Emiko Akiyama1, Masao Fukuda1. 1. Department of Bioengineering, Nagaoka University of Technology, Nagaoka 940-2188, Japan 2. Department of Bioengineering, Nagaoka University of Technology, Nagaoka 940-2188, Japan. dkasai1@vos.nagaokaut.ac.jp.
Abstract
Gram-positive actinomycete Rhodococcus jostii RHA1 is able to grow on C10 to C19 n-alkanes as a sole source of carbon and energy. To clarify, the n-alkane utilization pathway-a cluster of 5 genes (alkBrubA1A2BalkU) which appeared to be involved in n-alkane degradation-was identified and the transcriptional regulation of these genes was characterized. Reverse transcription-PCR analyses revealed that these genes constituted an operon and were transcribed in the presence of n-alkane. Inactivation of alkB led to the absence of the ability to utilize n-undecane. The alkB mutation resulted in reduction of growth rates on C10 and C12 n-alkanes; however, growths on C13 to C19 n-alkanes were not affected by this mutation. These results suggested that alkB was essential for the utilization of C10 to C12 n-alkanes. Inactivation of alkU showed the constitutive expression of alkB. Purified AlkU is able to bind to the putative promoter region of alkB, suggesting that AlkU played a role in repression of the transcription of alk operon. The results of this study indicated that alkB was involved in the medium-chain n-alkanes degradation of strain RHA1 and the transcription of alk operon was negatively regulated by alkU-encoded regulator. This report is important to understand the n-alkane degradation pathway of R. jostii, including the transcriptional regulation of alk gene cluster.
Gram-positive actinomyceteRhodococcus jostii RHA1 is able to grow on C10 to C19 n-alkanes as a sole source of carbon and energy. To clarify, the n-alkane utilization pathway-a cluster of 5 genes (alkBrubA1A2BalkU) which appeared to be involved in n-alkane degradation-was identified and the transcriptional regulation of these genes was characterized. Reverse transcription-PCR analyses revealed that these genes constituted an operon and were transcribed in the presence of n-alkane. Inactivation of alkB led to the absence of the ability to utilize n-undecane. The alkB mutation resulted in reduction of growth rates on C10 and C12 n-alkanes; however, growths on C13 to C19 n-alkanes were not affected by this mutation. These results suggested that alkB was essential for the utilization of C10 to C12 n-alkanes. Inactivation of alkU showed the constitutive expression of alkB. Purified AlkU is able to bind to the putative promoter region of alkB, suggesting that AlkU played a role in repression of the transcription of alk operon. The results of this study indicated that alkB was involved in the medium-chain n-alkanes degradation of strain RHA1 and the transcription of alk operon was negatively regulated by alkU-encoded regulator. This report is important to understand the n-alkane degradation pathway of R. jostii, including the transcriptional regulation of alk gene cluster.
Alkanes constitute up to 50% of crude oil and are commonly found in oil-contaminated environments [1]. Various microorganisms, both aerobic and anaerobic, utilize alkanes as a sole carbon and energy source [2,3]. Aerobic degradation of n-alkane is usually initiated by the alkane hydroxylase, which converts alkanes to alkanols [4,5,6]. The resulting alkanols are oxidized by the sequential reactions of alcohol and aldehyde dehydrogenases to yield the corresponding fatty acids, which are further metabolized by β-oxidation after conjugation of coenzyme A by an acyl CoA synthetase (Figure 1) [2,3,7]. The alkane-hydroxylation mechanism of Pseudomonas putida GPo1 has been characterized in detail, and consists of three subunits: an integral-membrane non-heme di-iron monooxygenase encoded by alkB; a rubredoxin encoded by duplicated genes, alkF and alkG; and a rubredoxin reductase encoded by alkT [8]. These genes are distributed in two different loci of the OCT plasmid in the strain GPo1 [8]. Their transcription is regulated by LuxR/UhpA-like transcriptional regulator encoded by alkS [8]. In the case of Acinetobacter baylyi ADP1, a three-component alkane hydroxylase containing alkane 1-monooxygenase encoded by alkM, a rubredoxin encoded by rubA, and a rubredoxin reductase encoded by rubB, which is similar to the GPo1 enzyme, catalyzes terminal alkane oxidation [9,10]. Transcription of alkM depends strictly on AraC/XylS-like transcriptional activator encoded by alkR and is induced by alkanes of various chain lengths [11].
Figure 1
Aerobic pathways for the n-alkane degradation by terminal oxidation. Abbreviations: AMO, n-alkane 1-monooxygenase; RU, rubredoxin; RUR, rubredoxin reductase; AD, alcohol dehydrogenase; ALD, aldehyde dehydrogenase; ACS, acyl-CoA synthetase; ox, oxidized; and red, reduced.
Other types of alkane-hydroxylation mechanism have also been reported. A flavin-binding monooxygenase encoded by almA is responsible for oxidation of C32 and C36 n-alkanes in Acinetobacter sp. DSM17874 [12]. In Geobacillus thermodenitrificans NG80-2, a soluble monomeric monooxygenase encoded by ladA, is involved in oxidation of C15 to C36 n-alkanes [13]. CYP153-family cytochrome P450 monooxygenases have been reported to catalyze terminal n-alkane oxidation in Acinetobacter sp. EB104, Mycobacterium sp. HXN-1500, and Alcanivorax dieselolei B-5 [5,14,15].Mycolic acid-containing actinomycetes, including Rhodococcus, have been increasingly recognized as candidates for the biodegradation of hydrocarbons because of their capacity to degrade a wide range of organic compounds and to produce biosurfactants, hydrophobic cell surface, and ubiquity and robustness in the environment [16]. Recently, alkB homologs, which codes for alkane 1-monooxygenase, have been characterized in actinomycetes, including Rhodococcus opacus B-4 [17], Rhodococcus ruber SP2B [18], Rhodococcus sp. BCP1 [19], Rhodococcus sp. TMP2 [20], Rhodococcus sp. NRRL B-16531 [21], Rhodococcus erythropolis Q15 [21], Gordonia sp. SoCg [22,23], and Nocardioides sp. CF8 [4]. However, little is known about the catabolic operon structure and regulatory mechanism of n-alkane degradation genes in actinomycetes. In this study, n-alkane degradation genes in Rhodococcus jostii RHA1 were examined. Strain RHA1 was isolated from a lindane-contaminated soil, and it co-metabolizes polychlorinated biphenyls with biphenyl via the biphenyl metabolic pathway [24,25]. It utilizes a wide range of hydrocarbons—such as aromatic compounds, propane, and steroids—as a sole source of carbon and energy [26,27,28,29]. In this study, we found that RHA1 utilized C10 to C19 n-alkanes, and characterized the operon structure and transcriptional regulation of n-alkane degradation genes in RHA1.
2. Materials and Methods
2.1. Bacterial Strains, Plasmids, and Culture Conditions
The bacterial strains and plasmids used in this study are listed in Table 1. Rhodococcus jostii RHA1 and its mutant derivatives were routinely grown at 30 °C in Luria-Bertani (LB) medium, 0.2× LB medium, or W minimal salt medium [30] containing 10 or 20 mM n-alkanes (C9 to C30) or 20 mM pyruvate. In solid cultures on W minimal medium agar, n-alkanes (C5 to C13) were supplemented as vapor. Escherichia coli strains were grown in LB medium at 37 °C. For cultures of cells carrying antibiotic resistance markers, the media for E. coli transformants were supplemented with 100 mg of ampicillin/liter or 25 mg of kanamycin/liter.
RK2 tra regulon, λ pir, host for pir-dependent plasmids
[32]
BL21(DE3)
F−ompT hsdSB(rB-mB-) gal dcm (DE3); T7 RNA polymerase gene under the control of the lacUV5 promoter
[33]
Plasmids
pT7Blue
Cloning vector; T7 promoter, Ap r
Novagen
pBluescript II KS(+)
Cloning vector; Ap r
[34]
pK19mobsacB
oriT sacB Km r
[35]
pK4
Rhodococcus-E. coli shuttle vector, Km r
[36]
pET16b
Expression vector, N-terminal His10 tag, Ap r T7 promoter
Novagen
pTALKBL
pT7Blue with a 917-bp PCR fragment generated by alkBL_F/R primer pair
This study
pTALKBR
pT7Blue with a 723-bp PCR fragment generated by alkBR_F/R primer pair
This study
pTALKBLR
pTALKBR with a 733-bp EcoRI-SacI fragment of pTALKBL
This study
pABSmobsacB
pK19mobsacB with a 1.5-kb EcoRI-HindIII fragment of pTALKBLR
This study
pTALKBD
pT7Blue with a 967-bp PCR fragment generated by alkBD_F/R primer pair
This study
pT7BL
pT7Blue with a 0.8-kb EcoRI-BamHI fragment of pTALKBL
This study
pT7B
pT7BL with a 0.7-kb BamHI-HindIII fragment of pTALKBD
This study
pK4ALKB
pK4 with a 1.5-kb EcoRI fragment of pT7B
This study
pTUPU
pT7Blue with a 761-bp PCR fragment generated by UPalkU_F/R primer pair
This study
pTDWU
pT7Blue with a 792-bp PCR fragment generated by DWalkU_F/R primer pair
This study
pKU
pK19mobsacB with a 1.6-kb HindIII fragment carrying part of alkU
This study
pETALKU
pET16b with a 0.7-kb PCR amplified fragment carrying of alkU
This study
a Abbreviations; Ap r and Km r, resistance to ampicillin and kanamycin, respectively.
2.2. DNA Manipulations, Nucleotide Sequencing, and Sequence Analysis
Total DNA isolation and electroporation were performed as described in a previous study [37]. DNA sequencing was performed by the Eurofins sequencing service (Eurofins Genomics, Tokyo, Japan). Analysis of nucleotide sequences and homology searches were carried out as previously described [38]. The genome sequence of RHA1, whose accession numbers are NC_008268, NC_008269, NC_008270, and NC_008271, was used to find n-alkane catabolic genes at the RHA1 genome database (http://www.rhodococcus.ca/index.jsp).
2.3. Construction of Disruption Mutants
The alkB and alkU genes were separately disrupted using the sacB counterselection system essentially as described previously [29,35,39]. Oligonucleotides that amplified flanking regions of each gene were listed in Table 2. Disruption of the genes was examined by PCR analysis. Disruption of the genes was confirmed by diagnostic PCR using specific primer sets and subsequently by DNA sequencing of the PCR amplified regions flanking the deletions.
Table 2
Primer sequences used in this study.
Primer
Sequence (5′ to 3′) a
alkB_F
TGACGACGTCGAATATCAGC
alkB_R
CCTGAATGATCAGGAACGG
alkBrubB_F
GAGCATTCACAACGATGTGC
alkBrubB_R
ACAGGAAGTCCTTCGACACC
rubA2B_F
GTACCGATTTCAAGCTCTACC
rubA2B_R
CACATCCGATGAGACCTCC
rubBalkU_F
ACGGTCGAAGTTGGAGTGC
rubBalkU_R
CTTTGTAGATCGTCTGCCTGC
alkU_F
CGAGCGACAGAGTCGATACC
alkU_R
ATGAAACTCAAGGCGAGCC
alkBL_F
ACAGGTGAAGCTACCAGCG
alkBL_R
GTGAGAGCTTCTGGACTTTCC
alkBR_F
CTTCGGTGAGAGCTTCTGG
alkBR_R
AAGCTTGTCGTCGGGCACATCG (HindIII)
alkBD_F
AACAGCTCGAGAACGACAGG
alkBD_R
GAATTCCATCACCGAACTCCGC (EcoRI)
UPalkU_F
AAGCTTTGTCCTCGCTCGACGTGAGC (HindIII)
UPalkU_R
GGATCCATTGTCGGCCAGGGACGTTCG (BamHI)
DWalkU_F
GGATCCAACGGTCGTGGGTGAACTCG (BamHI)
DWalkU_R
AAGCTTAGGAACTGATCTACGCCAACC (HindIII)
HISalkU_F
TCGAAGGTCGTCATAGCAGACGACCGCACCGCAGACGACCGCACC
HISalkU_R
GGATCCTCGAGCATAAAGTACTCACGGGTGAAGTACTCACGGGTG
a Engineered restriction sites are underlined, and the corresponding restriction enzymes are shown in parentheses.
2.4. Growth Curves on n-Alkanes
RHA1 and its mutant derivatives were grown in 10 mL of 0.2× LB medium for 36 h at 30 °C. Cells were harvested and washed three times with W medium and suspended in the same medium. Afterwards, the bacterial suspension was inoculated in 50 mL of W medium supplemented with 10 or 20 mM n-alkanes. The cells were incubated at 30 °C under shaking conditions and at each time point 1-mL aliquots were sampled and centrifuged at 5000× g and the pellet was dried to a constant weight.
2.5. Resting Cell Assay
RHA1 and DAB were grown on 0.2× LB or W minimal medium containing 20 mM pyruvate or 10 mM n-alkanes to give an OD600 of 1.0. The cells were collected by centrifugation, washed twice with 2 mL of W medium, and resuspended in a same medium to give an OD600 of 1.0. One milliliter of cell suspension was preincubated for 5 min at 30 °C and was incubated in a sealed 4.5-mL glass vial with shaking at 30 °C after the addition of 1 mM of n-alkanes. Control cells were inactivated by being autoclaved at 121 °C for 15 min prior to the addition of substrate. To stop the reaction 0.1 mL of 6 N HCl was added to the mix and 1 mM of phenanthrene was added as an internal standard. After the addition of NaCl to saturation, 3 mL of ethyl acetate was added to the mixture, which was then mixed on a vortex mixer for 1 min. The supernatant was recovered, dehydrated with sodium sulfate, evaporated, and dissolved in 150 μL of ethyl acetate. One microliter of extract was analyzed by gas chromatography-mass spectrometry (GC-MS; model 5971A; Agilent Technologies Co., Palo Alto, CA, USA), equipped with an Ultra-2 capillary column (50 m by 0.2 mm; Agilent Technologies) as described previously [25].
2.6. RNA Isolation
RHA1 and alkU-deficient mutant (DAU) were grown at 30 °C in 100 mL of W medium containing 10 mM n-undecane or 20 mM pyruvate. The resulting cells were harvested by centrifugation, washed with RNA protect bacterial reagent (QIAGEN, Germantown, MD, USA), and stored at −80 °C. Total RNA extraction from frozen cells was performed as described previously [40]. Purified RNA was then treated with RNase-free DNase I (Takara Bio Inc., Otsu, Japan) to remove contaminating DNA.
2.7. Reverse Transcription (RT)-PCR and Quantitative RT-PCR (qRT-PCR)
Single-stranded cDNA was synthesized from 1.0 µg of total RNA utilizing ReverTra Ace reverse transcriptase (Toyobo, Osaka, Japan) with random primers (Invitrogen, Carlsbad, CA, USA) in a 20-µL reaction mixture. PCR amplification was performed using 2.0 µL of the cDNA mixture, specific primers (Table 2), and Ex Taq DNA polymerase (Takara Bio Inc.) under the following conditions: 95 °C for 30 s and 30 cycles of 95 °C for 30 s, 60 °C for 60 s, and 72 °C for 60 s. A control without reverse transcriptase was used for each reaction to verify the absence of genomic DNA contamination. Samples from the PCR were electrophoresed on a 2.0% agarose gel and visualized with ethidium bromide.The amount of each transcript was measured using StepOne Plus real-time PCR system (Life Technologies, Carlsbad, CA, USA). Each primer set was designed using Primer Express version 3.0 software (Life Technologies). For qRT-PCR, 100 ng of cDNA sample, 100 nmol of each primer (Table 2), and 10 μL Fast SYBR Green PCR Master Mix (Life Technologies) were mixed in a final volume of 20 μL. The qRT-PCR was carried out using the following conditions: 95 °C for 20 sec and 40 cycles of 95 °C for 3 sec and 60 °C for 30 sec. The fluorescence signal from SYBR Green I intercalating into double-stranded DNA was detected during each annealing step. The copy number of each gene was determined based on the standard curve of the target gene, which was estimated by the results of qRT-PCR performed using 10-fold serial dilutions of each standard sample. To normalize the amount of RNA in each sample, 16S rRNA was used as an internal standard. Each measurement was carried out in triplicate, and the means and standard deviations were calculated.
2.8. Purification of His-Tagged alkU
The coding region of alkU was amplified by PCR using the specific primer pair (Table 2). The amplified fragment was cloned into NdeI-BamHI-digested pET16b by using In-Fusion cloning strategy [41]. The cells of E. coli BL21 (DE3) harboring the resultant plasmid (pETALKU) were grown at 30 °C. Expression of the gene was induced by adding 0.5 mM isopropyl-β-D-thiogalactopyranoside when the absorbance at 600 nm (A600) of the culture reached 0.5. After 4-h induction, the cells were harvested by centrifugation at 5000× g at 4 °C for 10 min and were resuspended in 50 mM Tris-HCl buffer (pH 7.5). The cells were then disrupted by an ultrasonic disintegrator (UD-201; Tomy Seiko Co., Tokyo, Japan) and centrifuged at 15,000× g at 4 °C for 15 min, to generate crude cell extract.To remove nucleic acids, streptomycin sulfate was added to the crude extracts to a final concentration of 1%. The lysate was kept on ice for 10 min and centrifuged at 15,000× g for 15 min. The supernatant was applied to a Ni Sepharose 6 Fast Flow column (GE Healthcare, Buckinghamshire, UK) previously equilibrated with buffer A consisting of 50 mM Tris-HCl (pH 7.5), 500 mM NaCl, and 100 mM imidazole. Proteins were allowed to bind for 1 min at 4 °C while rotating, followed by washing five times in 5 mL of buffer A. His-tagged proteins were eluted with 5 mL of buffer B consisting of 50 mM Tris-HCl (pH 7.5), 500 mM NaCl, and 500 mM imidazole, and the fractions were pooled and concentrated.
DNA fragments containing the upstream region of alkB were prepared by PCR with the specific primer pairs (Table 2). The 3′ ends of the probe fragments were labeled with DIG-11-ddUTP using the second-generation DIG gel shift kit (Roche), according to the manufacturer’s instructions. Binding reaction was performed at 20 °C for 20 min in a 10-μL reaction mixture containing 50 ng of the purified his-tagged AlkU (His-AlkU), 1 nM DIG-labeled probe, 1 μg of poly[d(I-C)], 0.1 μg of poly-L-lysine, 20 mM HEPES (pH 7.6), 1 mM EDTA, 10 mM (NH4)2SO4, 1 mM dithiothreitol, 0.2% (w/v) Tween 20, and 30 mM KCl. Gel electrophoresis and the detection of signals were performed as described previously [42].
3. Results
3.1. Growth of RHA1 on n-Alkanes
To determine growth characteristics of RHA1 on n-alkanes, RHA1 was grown in liquid W minimal medium containing 10 mM n-alkanes ranging in length from C9 to C30 and on W mediumagar supplemented with C5 to C13 as vapor. RHA1 grew on C11 to C19 n-alkanes in liquid medium (Table 3). It did not grow on C9, C10, C20, and C30 n-alkanes in liquid medium. On agar medium, it grew on n-decane in addition to C11 to C13n-alkanes. It did not grow on C5 to C9 n-alkanes on agar medium. Based on these results, we concluded that RHA1 utilized C10 to C19 n-alkanes as a sole source of carbon and energy.
Table 3
Growth of R. jostii RHA1 and DAB on n-alkanes.
Media
Strains
n-Alkanes a
C5
C6
C7
C8
C9
C10
C11
C12
C13
C14
C15
C16
C17
C18
C19
C20
C30
Liquid
RHA1
ND
ND
ND
ND
−
−
+
+
+
+
+
+
+
+
+
−
−
DAB
ND
ND
ND
ND
ND
−
−
±
+
+
+
+
+
+
+
−
−
Solid
RHA1
−
−
−
−
−
+
+
+
+
ND
ND
ND
ND
ND
ND
ND
ND
DAB
ND
ND
ND
ND
ND
±
−
±
+
ND
ND
ND
ND
ND
ND
ND
ND
ND, not determined. “+”, “–” and “± indicate significant, weak, and no growth, respectively.
3.2. The alk Gene Cluster of Strain RHA1
A BLASTp homology search using the amino acid sequence of alkane 1-monooxygenase (AlkB) from R. opacus B-4 (YP_002779449) as a query indicated that its closest ortholog is ro02534 in the genome database of RHA1. Hence, ro02534 was named as alkB. The region downstream of ro02534 contained orthologs of genes involved in n-alkane catabolism. Based on the amino acid sequence similarities, ro02535, ro02536, and ro02537 encode a couple of rubredoxins and a rubredoxin reductase, responsible for electron transfer in alkane hydroxylase [43], and were named as rubA1, rubA2, and rubB, respectively (Figure 2A). The ro02538 gene located next to rubB showed similarity to a putative TetR-type transcriptional regulator, and was named as alkU.
Figure 2
Organization and RT-PCR analysis of the alk gene cluster in RHA1. (A) Open arrows indicate the sizes, locations, and transcriptional directions of ORF. Boldfaced bars below the gene cluster diagram indicate the locations of the amplified RT-PCR products shown in panel B. Abbreviations for restriction enzymes: Ba, BamHI; EI, EcoRI; EV, EcoRV; Sm, SmaI; and Xh, XhoI. (B) Total RNA used for cDNA synthesis was isolated from RHA1 cells grown on n-undecane (upper panel), n-hexadecane (middle panel), and pyruvate (lower panel). Agarose gel electrophoresis of RT-PCR assays with primers targeting alkB (expected size, 831 bp), alkB-rubA1-rubA2-rubB (expected size, 1039 bp), rubA2-rubB (expected size, 671 bp), rubB-alkU (expected size, 766 bp), and alkU (expected size, 510 bp) are shown. Positions of amplified regions and primer sequences are indicated in panel A and Table 2, respectively. Lane M, molecular weight markers; Lanes + and −, RT-PCR with and without RT, respectively; lane G, control PCR with the RHA1 genomic DNA.
To examine operon structure of the alk gene cluster, RT-PCR analysis was performed with total RNA prepared from RHA1 cells grown on either n-undecane or pyruvate. Amplification products with the expected sizes of the segments alkB, alkB-rubB, rubA2-rubB, rubB-alkU, and alkU were detected using RNA prepared from the cells grown on n-undecane (Figure 2B). Based on these results, alkB, rubA1, rubA2, rubB, and alkU might be included in the same transcriptional unit. No amplification products were detected when RNA from pyruvate-grown cells was used, suggesting that transcription of these genes is induced after growth on n-undecane.
3.3. Disruption of alkB in RHA1
In order to evaluate the role of alkB in n-alkane utilization of RHA1, alkB was inactivated by gene replacement technique with the alkB disruption plasmid, pABSmobsacB. The degradation activities of the resting cells of RHA1 and the resulting mutant, DAB, toward n-undecane were determined by GC-MS. As shown in Figure 3A, DAB almost completely lost the activity to degrade n-undecane under the assay conditions used. To determine if this deficiency was caused by the disruption of alkB, a plasmid, pK4ALKB, containing an intact alkB was introduced into DAB to complement the mutation. Complementation with alkB restored these degradation activities to a level approximately equal to that of the wild-type strain (Figure 3A). Based on this result, we concluded that alkB was essential for degradation of n-undecane. In contrast, n-hexadecane degradation activity of DAB was almost the same as that of RHA1 (Figure 3B), suggesting that alkB was not essential for the utilization of n-hexadecane, and other gene(s) were involved in this degradation. However, the cells of DAB harboring pK4ALKB showed a higher activity than that of the wild-type strain. It is therefore probable that the alkB product has the ability to degrade n-hexadecane.
Figure 3
Degradation of n-undecane (A) and n-hexadecane (B) by RHA1, DAB, and DAB harboring pK4ALKB. 1 mM of each n-alkanes was incubated with the resting cells of RHA1 (open diamonds), DAB (open squares), DAB harboring pK4ALKB (open circles), and autoclaved cells of RHA1 (closed diamonds). The degradation activities were determined by GC-MS analysis. Each value is the average ± standard deviation of three independent experiments.
To estimate the level of participation of alkB in the growth of RHA1 on n-alkane, the growth ability of DAB was compared to that of RHA1. The capacity of DAB to grow in both liquid and solid media containing n-undecane was completely lost (Figure 4 and Table 3). When the alkB mutation was complemented by the introduction of the corresponding gene in trans, the growth deficiency was restored. When DAB was grown in n-dodecane and n-decane, the growths decreased (Table 3). These results indicated that alkB is fundamentally engaged in the utilization of C10 to C12 n-alkanes. On the other hand, disruption of alkB did not affect the growth on n-alkane from C13 to C20 (Table 3), suggesting that other gene(s) were involved in the n-alkanes utilization.
Figure 4
Growth of RHA1 and its mutant derivatives on n-undecane (A), n-dodecane (B), n-hexadecane (C), and n-decane (D). (A–C) RHA1 (diamonds), DAB (squares), DAB harboring pK4ALKB (circles) were grown in W medium containing 10 mM of each n-alkanes. Each value is the average ± standard deviation of three independent experiments. (D) Growth of RHA1 (left) and DAB (right) on n-decane after 5 days of incubation. (E) Growth of RHA1 (diamonds) and DAU (triangle) on 20 mM n-undecane.
3.4. Transcriptional Regulation of alk Operon
The alkU gene product (AlkU) is similar in sequence to putative transcriptional regulators belonging to the TetR family from Rhodococcus sp. Q15 (AAK97457) and R. opacus B-4 (BAH50508). To confirm that alkU gene product played a role in the transcriptional regulation of the alk operon, alkU was disrupted by homologous recombination. The growth ability on n-undecane of the resulting mutant strain DAU was slightly higher than that of the wild-type strain (Figure 4E). The results suggest that AlkU negatively regulated the transcription of alk genes and was responsible for the induction of these genes.To examine AlkU function, the level of transcription of alkB in strain DAU was examined by quantitative RT-PCR. When the RHA1 cells grew on pyruvate, mRNAs of alkB was not detected in our analytical condition (Figure 5). On the other hand, the transcription was significantly increased in the cells grown on n-undecane, indicating that the transcription of the alk genes was induced during n-undecane utilization. In contrast, DAU cells showed constitutive expression of alkB (Figure 5). The results suggest that AlkU was essential for the transcriptional regulation of alk operon as a repressor.
Figure 5
qRT-PCR analysis of the expression of alkB in RHA1 and DAU. The cells of RHA1 and DAU were grown in W medium containing 10 mM n-undecane (C11) or 20 mM pyruvate (PYR). Values for each mRNA expression were normalized to 16S rRNA gene expression. The data are mean values ± standard deviations for three independent experiments. N.D.: Not detected.
His-tag fused alkU was expressed in E. coli BL21 (DE3) cells to produce His-tagged AlkU (His-AlkU). SDS-PAGE analysis revealed the expression of a 25.3-kDa protein, consistent with the deduced amino acid sequence (Figure 6). Purified His-AlkU was used in electrophoretic mobility shift assays (EMSAs) with DNA probes containing the upstream region of alkB (Figure 7A). His-AlkU bound this DNA region (Figure 7B), indicating that the direct binding of AlkU with the promoter region of the alk operon.
Figure 6
SDS-PAGE analysis of protein fraction. Lanes: 1, molecular-weight markers; 2, Crude cell extract of E. coli BL21 (DE3) harboring pETALKU (10 µg of protein); 3, Elution fraction including His-AlkU (2 µg of protein).
Figure 7
Binding of His-AlkU to the upstream region of alkB. (A) Schematic diagrams of the upstream region of alkB. Black boxes revealed the region of DNA probe used in EMSAs. Underlines indicate a putative -10 and -35 sequences. Open box indicates start codon of alkB. Putative IR sequences are shown on top of nucleotide sequences. (B) EMSAs of the binding of purified His-AlkU (50 ng) to the DNA probe. The positions of the free probe and His-AlkU-DNA complex are shown by F and CP, respectively. + and − indicate presence and absence of His-AlkU, respectively.
4. Discussion
In this study, we identified and characterized the alkB gene and its transcriptional regulation in R. jostii RHA1, which could grow on n-alkanes ranging in length from C10 to C19 as the sole source of carbon and energy. Though RHA1 grows on propane [29], this strain is unable to utilize C5 to C9 n-alkanes. Similar observations have been reported for R. opacus B-4 and Rhodococcus sp. BCP1, which are unable to grow on C5 to C6 and C8 to C11 n-alkanes, respectively [17,19]. These observations may indicate that the hydroxylases for C5 to C9 n-alkanes degradation are absent in RHA1.In the deduced amino acid sequence of alkB, the conserved eight-histidine motif thought to be required for catalytic activity of non-heme di-iron integral membrane alkane hydroxylases was detected [44,45]. Kyte-Doolittle hydropathy analysis of the amino acid sequence deduced from AlkB of RHA1 showed similarity to those of other Rhodococcus strains and P. putida GPo1 [46], suggesting that AlkB of RHA1 was membrane bound (data not shown). AlkB of GPo1 oxidizes n-alkanes limited to C13 and has a bulky amino acid-like tryptophan at position 55 [47]. On the other hand, alkane 1-monooxygenase from Rhodococcus sp. strain NRRL B-16531, R. erythropolis Q15, and Mycobacterium tuberculosis H37Rv, with valine or leucine residue at the corresponding position, were shown to oxidize n-alkanes up to at least C16 [21,47]. Since leucine residue was found at the position of AlkB from RHA1, and the n-hexadecane degradation activity increased by introduction of alkB on a multicopy-number plasmid, this enzyme might be responsible for the long-chain n-alkane degradation. However, the growth on n-alkanes from C13 to C19 was not affected by deletion of alkB, whereas the alkB transcription was observed during the growth with n-hexadecane. It is suggested that alkB is a minor contributor to C13 to C19 n-alkanes utilization, and unidentified gene(s) played a major role in the degradation of these n-alkanes.AlkM from Acinetobacter sp. strain ADP1 oxidizes C12 to C18 n-alkanes [11]. Acinetobacter sp. strain M-1 was shown to possess two alkane monooxygenases encoded by alkMa and alkMb, involved in the degradation of up to C16 and C30 n-alkanes, respectively [48]. In addition, AlmA from Acinetobacter sp. strain DSM 17874 [12], LadA from G. thermodenitrificans NG80-2 [13], and cytochrome P450 monooxygenases [5,14,15] were reported to be involved in long-chain n-alkane degradation. In silico mining of the RHA1 genome database revealed the genes encoding for five AlmA homologs, a LadA homolog, and 31 putative cytochrome P450 monooxygenases. According to the deduced amino acid sequence similarity, some of these genes seemed to be responsible for C13 to C19n-alkane utilization in RHA1.The organization of alk genes is similar to that of the genes from several Rhodococcus strains [17,19,21], demonstrating that the gene clusters appear to have a common ancestral origin. RT-PCR analysis revealed that alkB, rubA1, rubA2, rubB, and alkU are transcribed as an operon (Figure 2B). The transcripts of these genes were observed in cells growing on both n-undecane and n-hexadecane, suggesting that the transcription of the alk operon was induced by these n-alkanes or their metabolites. In qRT-PCR analysis revealed the transcriptional induction of alk operon during the growth on n-undecane (Figure 5). The operon was constitutively transcribed in the absence of alkU. Furthermore, the EMSA revealed that AlkU bound the upstream region of alkB (Figure 7). These results strongly suggested that alkU codes for a repressor of the alk operon. In several Gram-negative bacteria, the transcriptions of the alk genes are under the control of a LuxR-type transcriptional regulator, AlkS binding the inverted repeat (IR) sequences located in directly upstream of the -35 region of alkB and alkS promoters [8,49,50]. In contrast, AlkU belongs to the TetR family of transcriptional regulators that regulate the transcription of genes for antibiotic resistance, antibiotic biosynthesis, catabolic pathway, and biofilm formation in Gram-negative and Gram-positive bacteria [51]. TetR-type transcriptional regulators are known to act both as a repressor and an activator [51,52]. TetR, which is involved in the transcriptional repression of tetracycline resistance gene, tetA, is known to act as a homodimer and binds the palindromic operator overlapping with the tetA and tetR promoters [53,54]. Furthermore, LuxR of Vibrio harveyi activates and represses the transcription of quorum-sensing genes by binding palindromic sequences located upstream or downstream of the promoter regions [52]. In the case of the alkB promoter region of Rhodococcus strains—including RHA1, BCP1, and B-4—two IR sequences, IR1 (GATTTacAAATC) and IR2 (ACAAATcTtcAtATTTGT), are well conserved [17,19], suggesting that AlkU may recognize to the IR sequences, in order to control the transcription of the alk operon. Since two different AlkU-DNA complexes were observed, AlkU may interact with multiple binding sites in the promoter in the same manner as other TetR family proteins [55]. The IR2 sequence is located immediately upstream of a putative -35 (TAGACC) sequence. Therefore, the transcription of alk genes appeared to be inhibited by the AlkU binding to the promoter region. It has been reported that the transcription of alkB of BCP1 and B-4 is also activated in the presence of n-alkanes [17,19]. The transcriptional regulation of the alk genes from these Rhodococcus stains was similar to that from RHA1.In this study, we identified the alk operon involved in the medium-chain n-alkanes degradation of strain RHA1. According to the mutant analysis of alkB, the gene is required for the growth on C10 to C12 n-alkanes. The alkU gene encodes a transcriptional repressor of alk operon, and n-alkanes act as inducers. It is necessary to identify the long-chain n-alkane oxidation genes in order to gain a better understanding of n-alkane degradation by this strain.
Authors: Ludmila Martínková; Bronislava Uhnáková; Miroslav Pátek; Jan Nesvera; Vladimír Kren Journal: Environ Int Date: 2008-09-11 Impact factor: 9.621