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University of Groningen Novel Dehalogenase Mechanism for 2,3-Dichloro-1-Propanol Utilization in Pseudomonas putida Strain MC4 Arif, Muhammad Ilan; Samin, Ghufrana; van Leeuwen, Jan G. E.; Oppentocht, Jantina; Janssen, Dick Published in: Applied and Environmental Microbiology DOI: 10.1128/AEM.00760-12 IMPORTANT NOTE: You are advised to consult the publisher's version (publisher's PDF) if you wish to cite from it. Please check the document version below. Document Version Publisher's PDF, also known as Version of record Publication date: 2012 Link to publication in University of Groningen/UMCG research database Citation for published version (APA): Arif, M. I., Samin, G., van Leeuwen, J. G. E., Oppentocht, J., & Janssen, D. B. (2012). Novel Dehalogenase Mechanism for 2,3-Dichloro-1-Propanol Utilization in Pseudomonas putida Strain MC4. Applied and Environmental Microbiology, 78(17), 6128-6136. DOI: 10.1128/AEM.00760-12 Copyright Other than for strictly personal use, it is not permitted to download or to forward/distribute the text or part of it without the consent of the author(s) and/or copyright holder(s), unless the work is under an open content license (like Creative Commons). Take-down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. Downloaded from the University of Groningen/UMCG research database (Pure): http://www.rug.nl/research/portal. For technical reasons the number of authors shown on this cover page is limited to 10 maximum. Download date: 11-02-2018 Novel Dehalogenase Mechanism for 2,3-Dichloro-1-Propanol Utilization in Pseudomonas putida Strain MC4 Muhammad Irfan Arif, Ghufrana Samin,* Jan G. E. van Leeuwen , Jantien Oppentocht, and Dick B. Janssen Department of Biochemistry, Groningen Biomolecular Sciences and Biotechnology Institute, University of Groningen, Groningen, Netherlands A Pseudomonas putida strain (MC4) that can utilize 2,3-dichloro-1-propanol (DCP) and several aliphatic haloacids and haloal- Downloaded from cohols as sole carbon and energy source for growth was isolated from contaminated soil. Degradation of DCP was found to start with oxidation and concomitant dehalogenation catalyzed by a 72-kDa monomeric protein (DppA) that was isolated from cell lysate. The dppA gene was cloned from a cosmid library and appeared to encode a protein equipped with a signal peptide and that possessed high similarity to quinohemoprotein alcohol dehydrogenases (ADHs), particularly ADH IIB and ADH IIG from Pseudomonas putida HK. This novel dehalogenating dehydrogenase has a broad substrate range, encompassing a number of ؊1 1 nonhalogenated alcohols and haloalcohols. With DCP, DppA exhibited a kcat of 17 s . H nuclear magnetic resonance experi- ments indicated that DCP oxidation by DppA in the presence of 2,6-dichlorophenolindophenol (DCPIP) and potassium ferri- http://aem.asm.org/ cyanide [K 3Fe(CN)6] yielded 2-chloroacrolein, which was oxidized to 2-chloroacrylic acid. ichloropropanols are widely used in the chemical industry, nicotinamide cofactor binding site. They catalyze the intramolec- Dparticularly as intermediates for epichlorohydrin produc- ular displacement of a halogen by the vicinal hydroxyl group, tion. The classical epichlorohydrin manufacturing process pro- yielding an epoxide, a halide ion, and a proton ( 52 ). At least six ceeds via hydrochlorination of allylchloride, which yields both different halohydrin dehalogenases have been found so far: two 2,3-dichloro-1-propanol and 1,3-dichloro-2-propanol (30 ). Be- enzymes from Corynebacterium sp. strain N-1074 (HheA and cause of the increasing availability of glycerol as a side product HheB) (57 ) and homologs in Arthrobacter sp. strain AD2 on September 27, 2012 by University of Groningen from biodiesel synthesis, this classical process is being replaced (HheBAD2) ( 52 ), Agrobacterium sp. strain NHG3 (DehB) (20 ), Ar- with the use of glycerol as a renewable feedstock for epichlorohy- throbacter erithii H10a (DehA) (5), and Agrobacterium radiobacter drin manufacture, again via chlorination to the same dichloropro- strain AD1 (HheC) (51 ). The structures are known, and the cata- panols or via 1-chloro-2,3-propanediol ( 6). Epichlorohydrin itself lytic mechanism is well understood ( 11 , 12 , 21 ). The halohydrin as well as the production intermediates 2,3-dichloropropanol dehalogenases have a preference for substrates with the halogen (DCP) and 1,3-dichloropropanol are mutagenic, genotoxic, and group on a terminal (primary) carbon atom, which can be ex- carcinogenic, and therefore their release and the possibility of hu- plained by analysis of X-ray structures ( 11 , 21 ). However, impor- man exposure are of significant concern ( 38 ). DCP also occurs as tant compounds, such as 2-chloro-1-propanol and DCP, are not a contaminant in cellulose and starch hydrolysates, soy sauce, and easily converted. The potential importance of DCP as an interme- baked foods (27 ). diate in the degradation of 1,2,3-trichloropropane prompted us to Microorganisms that metabolize dichloropropanols are of in- search for new pathways of DCP metabolism ( 9). terest in view of their role in the removal of these compounds from A well-established mechanism for the conversion of alcohols is waste streams and contaminated environments (14 ), from food oxidative conversion by alcohol dehydrogenases (ADHs). Many and pulp products, and also carbohydrate hydrolysates (55 ) and ADHs are NAD- or NADP-dependent enzymes ( 34 ). Oxidation of because dichloropropanols occur as intermediates in a catabolic alcohols by oxidases, which generates hydrogen peroxide, is also pathway for degradation of the emerging priority contaminant possible. A special class of alcohol dehydrogenases is formed by 1,2,3-trichloropropane (8). Of the dichloropropanols, 2,3-di- the periplasmic quinoprotein ADHs, which contain a quinoid co- chloro-1-propanol is chemically more stable and more difficult to factor, such as pyrroloquinoline quinone (PQQ), and Ca 2ϩ. A degrade than 1,3-dichloropropanol (14 ). Furthermore, microor- quinoprotein methanol dehydrogenase has been found to be re- ganisms that convert dichloropropanols can be used in the prep- sponsible for 2-chloroethanol oxidation in the 1,2-dichloroethane aration of enantiopure building blocks for the pharmaceutical in- catabolic pathway (26 ). PQQ-dependent ADHs have been discov- dustry (27 , 30 ). Several bacterial strains are known to grow on ered in a wide variety of bacteria, including Acetobacter, Glucono- dichloropropanols, such as Pseudomonas sp. strain OS-K-29 (30 ), Alcaligenes sp. strain DS-K-S38 (29 ), Mycobacterium sp. strain GP1 (40 ), Agrobacterium sp. strain NHG3 (14 , 20 ), and Arthrobac- Received 7 March 2012 Accepted 14 June 2012 ter sp. strain AD2 (51 ). Published ahead of print 29 June 2012 During the microbial conversion of vicinal haloalcohols, deha- Address correspondence to Dick B. Janssen, [email protected]. logenation is usually the first step, and this reaction can be cata- * Permanent address: Ghufrana Samin, Department of Chemistry, University of lyzed by haloalcohol dehalogenases ( 24 ). These enzymes, also Engineering and Technology Lahore, Faisalabad Campus, Faisalabad, Pakistan. called halohydrin dehalogenases, are composed of 2 to 4 subunits Supplemental material for this article may be found at http://aem.asm.org/. of molecular masses between 28 and 35 kDa and are phylogeneti- Copyright © 2012, American Society for Microbiology. All Rights Reserved. cally related to the short-chain dehydrogenase reductase super- doi:10.1128/AEM.00760-12 family (SDR proteins) (54 ), even though they do not possess a 6128 aem.asm.org Applied and Environmental Microbiology p. 6128–6136 September 2012 Volume 78 Number 17 Quinohemoprotein Dehydrogenase/Dehalogenase bacter, Pseudomonas, and Comamonas strains (1, 2, 4, 19 , 47 ). Enzyme characterization. For molecular weight determination of na- Some of these enzymes contain heme as a secondary prosthetic tive enzyme, purified dehydrogenase (DppA) was analyzed by gel filtra- group and are known as quinohemoproteins ( 4). The periplasmic tion (see the supplemental material). The purity and molecular weight of quinohemoproteins transfer electrons to the membrane-bound the protein were determined by SDS-PAGE (12% gel) analysis. Heme bacterial respiratory chain (4, 34 ). staining of the SDS-PAGE gels was done by using the method of Francis In this paper we show that such a quinohemoprotein alcohol and Becker (15 ). To determine heme c concentrations, we measured difference spectra dehydrogenase may act as DCP dehalogenase. We started with the of reduced and oxidized pyridine hemochrome according to a published isolation of a DCP-degrading organism from a site polluted with protocol (53a). chlorinated compounds. We report the properties of this new Enzyme assays. All enzyme assays were performed at 25°C. The dehy- DCP-utilizing bacterium, analyze the gene encoding the quinohe- drogenase (DppA) activity toward DCP in cell extracts was measured by Downloaded from moprotein alcohol dehydrogenase, and propose a pathway for following the reduction of the electron acceptor DCPIP with PMS as an DCP metabolism. intermediate electron carrier. The reaction mixture (1 ml) contained 50 mM potassium phosphate, pH 7.4, 35 M 2,6-DCPIP, 5 mM DCP, and MATERIALS AND METHODS cell extract. After addition of 1.6 mM PMS, the absorbance was monitored at 600 nm. The absorption coefficient of DCPIP at 600 nm is 21.0 mM Ϫ1 Chemicals, reagents and enzymes. All chemicals were obtained from Alfa cm Ϫ1 (16 ). Aesar, Sigma-Aldrich, and Acros Organics. Oxidase test discs were ob- For routine measurements, the enzyme activity was measured by fol- tained from Fluka. Plasmid DNA was isolated with the Qiagen plasmid lowing the reduction of potassium ferricyanide, K 3Fe(CN)6, at 420 nm in isolation kit. Enzymes used for cloning were either from Roche or New http://aem.asm.org/ a 1-ml reaction mixture consisting of 50 mM Tris-SO , pH 8.0, 5 mM England BioLabs. The PCR master mix for screening was purchased from 4 DCP, and 1 mM potassium ferricyanide (extinction coefficient, 1 mM Ϫ1 Promega. cm Ϫ1 at 420 nm [ 22 ]).