Biotransformation of various alkanes using the Escherichia coli expressing an alkane hydroxylase system from Gordonia sp. TF6

Biotransformation using alkane-oxidizing bacteria or their alkane hydroxylase (AH) systems have been little studied at the molecular level. We have cloned and sequenced genes from Gordonia sp. TF6 encoding an AH system, alkB2 (alkane 1-monooxygenase), rubA3 (rubredoxin), rubA4 (rubredoxin), and rubB (rubredoxin reductase). When expressed in Escherichia coli, these genes allowed the construction of biotransformation systems for various alkanes. Normal alkanes with 5 to 13 carbons were good substrates for this biotransformation, and oxidized to their corresponding 1-alkanols. Surprisingly, cycloalkanes with 5 to 8 carbons were oxidized to their corresponding cycloalkanols as well. This is the first study to achieve biotransformation of alkanes using the E. coli expressing the minimum component genes of the AH system. Our biotransformation system has facilitated assays and analysis leading to improvement of AH systems, and has indicated a cycloalkane oxidation pathway in microorganisms for the first time.     

Rubredoxin reductase from Alcanivorax borkumensis: expression and characterization

Oil pollution is an environmental problem of increasing importance. Alcanivorax borkumensis, with a high potential for biotechnological applications, is a key marine hydrocarbonoclastic bacterium and plays a critical role in the bioremediation of oil-polluted marine systems. In oil degrading bacteria, the first step of alkane degradation is catalyzed by a monooxygenase. The reducing electrons are tunneled from NAD(P)H via rubredoxin, one of the most primitive metalloproteins, to the hydroxylase. Rubredoxin reductase is a flavoprotein catalyzing the reduction of rubredoxin. There are two rubredoxin genes, alkG and rubA, in A. borkumensis genome. In this work, the genes encoding rubredoxin reductase (ABO_0162, rubB) and AlkG(ABO_2708, alkG) were cloned and functionally overexpressed in E. coli. Our results demonstrate that RubB could reduce AlkG, therefore compensating for the absence of AlkT, also a rubredoxin reductase, missing in A. borkumensis SK2 genome. These results will increase our knowledge concerning biological alkane degradation and will lead us to design more efficient biotransformation and bioremediation systems.     

Production of a recombinant alkane hydroxylase (AlkB2) from <Emphasis Type="Italic">Alcanivorax</Emphasis><Emphasis Type="Italic">borkumensis</Emphasis>

Alcanivorax borkumensis is an oil-degrading marine bacterium. Its genome contains genes coding for three cytochrome P450s and two integral membrane alkane hydroxylases (AlkB1 & AlkB2), all assumed to perform hydroxylation of different linear or branched alkanes. Although, the sequence of alkB2 has been determined, the molecular characterization and the substrate specificity of AlkB2 require more precise investigation. In this study, AlkB2 from A. borkumensis SK2 was expressed in Escherichia coli to examine the functionality of AlkB2 as a hydroxylating enzyme. Furthermore, the activity of the enzyme in the presence of the accessory proteins, rubredoxin (RubA) and rubredoxin reductase (RubB), produced in E. coli BL21(DE3)plysS cells, was determined. Recombinant AlkB2 is produced in an active form and rubredoxin is the intermediate electron donor to AlkB2 and can replace AlkG function, when NADH is the prime electron donor.     

Differential expression of the components of the two alkane hydroxylases from Pseudomonas aeruginosa

Oxidation of n-alkanes in bacteria is normally initiated by an enzyme system formed by a membrane-bound alkane hydroxylase and two soluble proteins, rubredoxin and rubredoxin reductase. Pseudomonas aeruginosa strains PAO1 and RR1 contain genes encoding two alkane hydroxylases (alkB1 and alkB2), two rubredoxins (alkG1 and alkG2), and a rubredoxin reductase (alkT). We have localized the promoters for these genes and analyzed their expression under different conditions. The alkB1 and alkB2 genes were preferentially expressed at different moments of the growth phase; expression of alkB2 was highest during the early exponential phase, while alkB1 was induced at the late exponential phase, when the growth rate decreased. Both genes were induced by C(10) to C(22)/C(24) alkanes but not by their oxidation derivatives. However, the alkG1, alkG2, and alkT genes were expressed at constant levels in both the absence and presence of alkanes.     

A Toolkit to Enable Hydrocarbon Conversion in Aqueous Environments

This work puts forward a toolkit that enables the conversion of alkanes by Escherichia coli and presents a proof of principle of its applicability. The toolkit consists of multiple standard interchangeable parts (BioBricks)⁹ addressing the conversion of alkanes, regulation of gene expression and survival in toxic hydrocarbon-rich environments.A three-step pathway for alkane degradation was implemented in E. coli to enable the conversion of medium- and long-chain alkanes to their respective alkanols, alkanals and ultimately alkanoic-acids. The latter were metabolized via the native β-oxidation pathway. To facilitate the oxidation of medium-chain alkanes (C5-C13) and cycloalkanes (C5-C8), four genes (alkB2, rubA3, rubA4and rubB) of the alkane hydroxylase system from Gordonia sp. TF6^8,21 were transformed into E. coli. For the conversion of long-chain alkanes (C15-C36), theladA gene from Geobacillus thermodenitrificans was implemented. For the required further steps of the degradation process, ADH and ALDH (originating from G. thermodenitrificans) were introduced^10,11. The activity was measured by resting cell assays. For each oxidative step, enzyme activity was observed.To optimize the process efficiency, the expression was only induced under low glucose conditions: a substrate-regulated promoter, pCaiF, was used. pCaiF is present in E. coli K12 and regulates the expression of the genes involved in the degradation of non-glucose carbon sources.The last part of the toolkit - targeting survival - was implemented using solvent tolerance genes, PhPFDα and β, both from Pyrococcus horikoshii OT3. Organic solvents can induce cell stress and decreased survivability by negatively affecting protein folding. As chaperones, PhPFDα and β improve the protein folding process e.g. under the presence of alkanes. The expression of these genes led to an improved hydrocarbon tolerance shown by an increased growth rate (up to 50%) in the presences of 10% n-hexane in the culture medium were observed.Summarizing, the results indicate that the toolkit enables E. coli to convert and tolerate hydrocarbons in aqueous environments. As such, it represents an initial step towards a sustainable solution for oil-remediation using a synthetic biology approach.     

Marine hydrocarbonoclastic bacteria as whole‐cell biosensors for n‐alkanes

Whole‐cell biosensors offer potentially useful, cost‐effective systems for the in‐situ monitoring of seawater for hydrocarbons derived from accidental spills. The present work compares the performance of a biosensor system for the detection of alkanes in seawater, hosted in either Escherichia coli (commonly employed in whole‐cell biosensors but not optimized for alkane assimilation) or different marine bacteria specialized in assimilating alkanes. The sensor system was based on the Pseudomonas putida AlkS regulatory protein and the PalkB promoter fused to a gene encoding the green fluorescent protein. While the E. coli sensor provided the fastest response to pure alkanes (25‐fold induction after 2 h under the conditions used), a sensor based on Alcanivorax borkumensis was slower, requiring 3–4 h to reach similar induction values. However, the A. borkumensis sensor showed a fourfold lower detection threshold for octane (0.5 μM), and was also better at sensing the alkanes present in petrol. At petrol concentrations of 0.0125%, the A. borkumensis sensor rendered a sevenfold induction, while E. coli sensor showed no response. We discuss possible explanations to this behaviour in terms of the cellular adaptations to alkane uptake and the basal fluorescence produced by each bacterial strain, which was lowest for A. borkumensis.     

Identification of different alkane hydroxylase systems in Rhodococcus ruber strain SP2B,an hexane‐degrading actinomycete

Aims: To investigate the alkane‐hydroxylating system of isolate SP2B, closely related to Rhodococcus ruber DSM 43338^T and uncharacterized so far for its alkane degradation genes. Methods and Results: Although isolate SP2B and reference strain can grow on by‐products from hexane degradation, the type strain R. ruber was unable, unlike SP2B isolate, to use short‐chain alkanes, as assessed by gas chromatography. Using PCR with specific or degenerated primers, inverse PCR and Southern blot, two alkane hydroxylase encoding genes (alkB) were detected in both bacteria, which is in agreement with their alkane range. The first AlkB was related to Rhodococcus AlkB7 enzymes and contains a nonbulky residue at a specific position, suggesting it might be involved in medium‐ and long‐chain alkane oxidation. The second partial alkB gene potentially belongs to alkB5‐type, which was found in bacteria unable to use hexane. Moreover, a partial P450 cytochrome alkane hydroxylase, thought to be responsible for the hexane degradation, was detected only in the isolated strain. Conclusions: Rhodococcus ruber SP2B should prove to be a promising candidate for bioremediation studies of contaminated sites because of its large degradation range of alkanes. Significance and Impact of the Study: This is the first thorough study on R.ruber alkane degradation systems.     

Modulating the import of medium-chain alkanes in <Emphasis Type="Italic">E. coli</Emphasis> through tuned expression of FadL

Background

In recent years, there have been intensive efforts to develop synthetic microbial platforms for the production, biosensing and bio-remediation of fossil fuel constituents such as alkanes. Building predictable engineered systems for these applications will require the ability to tightly control and modulate the rate of import of alkanes into the host cell. The native components responsible for the import of alkanes within these systems have yet to be elucidated. To shed further insights on this, we used the AlkBGT alkane monooxygenase complex from Pseudomonas putida GPo1 as a reporter system for assessing alkane import in Escherichia coli. Two native E. coli transporters, FadL and OmpW, were evaluated for octane import given their proven functionality in the uptake of fatty acids along with their structural similarity to the P. putida GPo1 alkane importer, AlkL.

Results

Octane import was removed with deletion of fadL, but was restored by complementation with a fadL-encoding plasmid. Furthermore, tuned overexpression of FadL increased the rate of alkane import by up to 4.5- fold. A FadL deletion strain displayed a small but significant degree of tolerance toward hexane and octane relative to the wild type, while the responsiveness of the well-known alkane biosensor, AlkS, toward octane and decane was strongly reduced by 2.7- and 2.9-fold, respectively.

Conclusions

We unequivocally show for the first time that FadL serves as the major route for medium-chain alkane import in E. coli. The experimental approaches used within this study, which include an enzyme-based reporter system and a fluorescent alkane biosensor for quantification and real-time monitoring of alkane import, could be employed as part of an engineering toolkit for optimizing biological systems that depend on the uptake of alkanes. Thus, the findings will be particularly useful for biological applications such as bioremediation and biomanufacturing.

     

Functional characterization of genes involved in alkane oxidation by Pseudomonas aeruginosa

Most clinical isolates identified as Pseudomonas aeruginosa grow on long-chain n-alkanes, while environmental P. aeruginosa isolates often grow on medium- as well as long-chain n-alkanes. Heterologous expression showed that the two alkane hydroxylase homologs of P. aeruginosa PAO1 (AlkB1 and AlkB2) oxidize C₁₂-C₁₆ n-alkanes, while two rubredoxin (RubA1 and RubA2) and a rubredoxin reductase (RubB) homologs can replace their P. putida GPo1 counterparts in n-octane oxidation. The two long-chain alkane hydroxylase genes are present in all environmental and clinical isolates of P. aeruginosa strains tested in this study. This revised version was published online in August 2006 with corrections to the Cover Date.     

Functional analysis of alkane hydroxylases from gram-negative and gram-positive bacteria

We have cloned homologs of the Pseudomonas putida GPo1 alkane hydroxylase from Pseudomonas aeruginosa PAO1, Pseudomonas fluorescens CHA0, Alcanivorax borkumensis AP1, Mycobacterium tuberculosis H37Rv, and Prauserella rugosa NRRL B-2295. Sequence comparisons show that the level of protein sequence identity between the homologs is as low as 35%, and that the Pseudomonas alkane hydroxylases are as distantly related to each other as to the remaining alkane hydroxylases. Based on the observation that rubredoxin, an electron transfer component of the GPo1 alkane hydroxylase system, can be replaced by rubredoxins from other alkane hydroxylase systems, we have developed three recombinant host strains for the functional analysis of the novel alkane hydroxylase genes. Two hosts, Escherichia coli GEc137 and P. putida GPo12, were equipped with pGEc47 Delta B, which encodes all proteins necessary for growth on medium-chain-length alkanes (C(6) to C(12)), except a functional alkane hydroxylase. The third host was an alkB knockout derivative of P. fluorescens CHA0, which is no longer able to grow on C(12) to C(16) alkanes. All alkane hydroxylase homologs, except the Acinetobacter sp. ADP1 AlkM, allowed at least one of the three hosts to grow on n-alkanes.     

Identification of alkane monoxygenase genes inAcinetobacter venetianus VE-C3 and analysis of mutants impaired in diesel fuel degradation

Cells ofAcinetobacter venetianus strain VE-C3 are able to degrade diesel fuel oil by a complex mechanism requiring the formation of cell aggregates and their further adhesion to fuel oil drops. In this work the biodegradation process inA. venetianus was studied by a combination of genetic, molecular and physiological methods. PCR amplification, sequencing and Southern blot analysis ofalkM andrubA genes coding for the alkane hydroxylase and rubredoxin were carried out. Then, 22 Alk^? mutants impaired in diesel fuel degradation were obtained by nitrosoguanidine mutagenesis and characterised by i) growth on alkanes as sole carbon and energy sources, ii) modification of cell electrophoretic properties, and iii) analysis of plasmid content. Data obtained revealed that the genetic determinants for alkane degradation are located on both the chromosome and the two plasmids harboured by VE-C3 strain (pAV1 and pAV2, 11 Kbp and 15 kbp, respectively). This organization of genes coding for alkane monoxygenase complex seems to be similar to the arrangement found in Acinetobacter sp. strains ADP1 and M1, where genes are scattered through the chromosome but, as a novelty, that some genes involved in hydrocarbon degradation are plasmid borne also.     

Purified Penicillin Binding Proteins 1Bs from Escherichia coli Membrane Showing Activities of Both Peptidoglycan Polymerase and Peptidoglycan Crosslinking Enzyme

Our biotransformation using Escherichia coli expressing a cytochrome P450 (CYP) belonging to the CYP153A family from Acinetobacter sp. OC4 produced a great amount of 1-octanol (2,250 mg per liter) from n-octane after 24 h of incubation. This level of production is equivalent to the maximum level previously achieved in biotransformation experiments of alkanes. In addition, the initial production rate of 1-octanol was maintained throughout the entire incubation period. These results indicate that we have achieved the functional and stable expression of a CYP in E. coli for the first time. Further, our biotransformation system showed α,ω-diterminal oxidation activity of n-alkanes, and a large amount of 1,8-octanediol (722 mg per liter) was produced from 1-octanol after 24 h of incubation. This is the first report on the bioproduction of α,ω-alkanediols from n-alkanes or 1-alkanols.     

Biosynthesis of chain‐specific alkanes by metabolic engineering in Escherichia coli

Renewable energy is one of the key issues for sustainable development. Compared with alcohols and esters, alkanes—with the highest energy density—are a better liquid fuel. In this study, we focused on medium‐chain alkanes, the main compounds of jet fuels. To control the chain length of alkanes, a chain length specific thioesterase from Umbellularia californica, a fatty acyl‐CoA reductase Acinetobacter sp. M‐1 that prefers lauroyl‐CoA and myristoyl‐CoA, and a decarbonylase from Nostoc punctiforme were engineering into Escherichia coli cells. The combination of genes, which determines the chain length of products, was carefully designed to control the product spectrum. Undecane and tridecane were produced with a concentration of 2.21 ± 0.18 and 1.83 ± 0.12 mg?g^?1, respectively. A total of 4.01 ± 0.43 mg?g^?1 pentadecane was also detected in the final products. The results showed the feasibility to use microorganisms as cell factories for alkane production. The product spectrum revealed that the chosen genes played a key role in the production of chain length specific alkanes.     

Biochemical characterization of two haloalkane dehalogenases: DccA from Caulobacter crescentus and DsaA from Saccharomonospora azurea

Two putative haloalkane dehalogenases (HLDs) of the HLD‐I subfamily, DccA from Caulobacter crescentus and DsaA from Saccharomonospora azurea, have been identified based on sequence comparisons with functionally characterized HLD enzymes. The two genes were synthesized, functionally expressed in E. coli and shown to have activity toward a panel of haloalkane substrates. DsaA has a moderate activity level and a preference for long (greater than 3 carbons) brominated substrates, but little activity toward chlorinated alkanes. DccA shows high activity with both long brominated and chlorinated alkanes. The structure of DccA was determined by X‐ray crystallography and was refined to 1.5 Å resolution. The enzyme has a large and open binding pocket with two well‐defined access tunnels. A structural alignment of HLD‐I subfamily members suggests a possible basis for substrate specificity is due to access tunnel size.