Please wait a minute...
Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front.Environ.Sci.Eng.    2014, Vol. 8 Issue (4) : 539-546    https://doi.org/10.1007/s11783-013-0616-y
RESEARCH ARTICLE
Multistep conversion of cresols by phenol hydroxylase and 2,3-dihydroxy-biphenyl 1,2-dioxygenase
Shengnan SHI1,Fang MA1,*(),Tieheng SUN1,Ang LI1,Jiti ZHOU2,Yuanyuan QU2,*()
1. State Key Laboratory of Urban Water Resource and Environment, School of Municipal and Environmental Engineering, Harbin Institute of Technology, Harbin 150090, China
2. Key Laboratory of Industrial Ecology and Environmental Engineering (Ministry of Education), School of Environmental Science and Technology, Dalian University of Technology, Dalian 116024, China
 Download: PDF(899 KB)   HTML
 Export: BibTeX | EndNote | Reference Manager | ProCite | RefWorks
Abstract

A multistep conversion system composed of phenol hydroxylase (PHIND) and 2,3-dihydroxy-biphenyl 1,2-dioxygenase (BphCLA-4) was used to synthesize methylcatechols and semialdehydes from o- and m-cresol for the first time. Docking studies displayed by PyMOL predicted that cresols and methylcatechols could be theoretically transformed by this multistep conversion system. High performance liquid chromatography mass spectrometry (HPLC-MS) analysis also indicated that the products formed from multistep conversion were the corresponding 3-methylcatechol, 4-methylcatechol, 2-hydroxy-3-methyl-6-oxohexa-2,4-dienoic acid (2-hydroxy-3-methyl-ODA) and 2-hydroxy-5-methyl-6-oxohexa-2,4-dienoic acid (2-hydroxy-5-methyl-ODA). The optimal cell concentrations of the recombinant E. coli strain BL21 (DE3) expressing phenol hydroxylase (PHIND) and 2,3-dihydroxy-biphenyl 1,2-dioxygenase (BphCLA-4) and pH for the multistep conversion of o- and m-cresol were 4.0 (g·L-1 cell dry weight) and pH 8.0, respectively. For the first step conversion, the formation rate of 3-methylcatechol (0.29 μmol·L-1·min-1·mg-1 cell dry weight) from o-cresol was similarly with that of methylcatechols (0.28 μmol·L-1·min-1·mg-1 cell dry weight) from m-cresol by strain PHIND. For the second step conversion, strain BphCLA-4 showed higher formation rate (0.83 μmol·L-1·min-1·mg-1 cell dry weight) for 2-hydroxy-3-methyl-ODA and 2-hydroxy-5-methyl-ODA from m-cresol, which was 1.1-fold higher than that for 2-hydroxy-3-methyl-ODA (0.77 μmol·L-1·min-1·mg-1cell dry weight) from o-cresol. The present study suggested the potential application of the multistep conversion system for the production of chemical synthons and high-value products.

Keywords multistep conversion      cresols      phenol hydroxylase      2      3-dihydroxybiphenyl 1      2-dioxygenase      methylcatechols     
Corresponding Author(s): Fang MA   
Issue Date: 11 June 2014
 Cite this article:   
Shengnan SHI,Fang MA,Tieheng SUN, et al. Multistep conversion of cresols by phenol hydroxylase and 2,3-dihydroxy-biphenyl 1,2-dioxygenase[J]. Front.Environ.Sci.Eng., 2014, 8(4): 539-546.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-013-0616-y
https://academic.hep.com.cn/fese/EN/Y2014/V8/I4/539
Fig.1  Interactions between PHIND and BphCLA-4 component with o- and m-cresol, and methylcatechols, respectively. Red spheres represent for diiron. (a) o-cresol; (b) m-cresol; (c) 3-methylcatechol; (d) 4-methylcatechol
Fig.2  Mass spectra of products formed from multistep conversion by strains PHIND and BphCLA-4. (a) products of o-cresol multistep conversion; (b) products of m-cresol multistep conversion
Fig.3  Effect of strain concentration on multistep conversion. The first step conversion (a): 3-methylcatechol (?) formed from o-cresol, 3-methylcatechol (◆) formed from m-cresol and 4-methylcatechol (?) formed from m-cresol; The second step conversion (b): 2-hydroxy-3-methyl-ODA (n) formed from 3-methylcatechol, 2-hydroxy-3-methyl-ODA (?) formed from 3-methylcatechol and 2-hydroxy-5-methyl-ODA (●) formed from 4-methylcatechol
Fig.4  Time course of o- and m-cresol multistep conversion. The first step conversion was on the left side, the second step conversion was on the right. (a) concentration of o-cresol (n), 3-methylcatechol (l), 2-hydroxy-3-methyl-ODA (π); (b) concentration of m-cresol (?), 3-methylcatechol (l), 4-methylcatechol (u), 2-hydroxy-3-methyl-ODA (π) 2-hydroxy-5-methyl-ODA (?)
Fig.5  Effect of pH on multistep conversion. (a) 3-methylcatechol (n) formed from o-cresol, 3-methylcatechol (?) formed from m-cresol and 4-methylcatechol (●) formed from m-cresol; (b) 2-hydroxy-3-methyl-ODA (?) formed from 3-methylcatechol, 2-hydroxy-3-methyl-ODA (◆) formed from 3-methylcatechol and 2-hydroxy-5-methyl-ODA (?) formed from 4-methylcatechol
Fig.6  Effect of glucose concentrations on the first step conversion: 3-methylcatechol (n) formed from o-cresol, 3-methylcatechol (?) formed from m-cresol and 4-methylcatechol (●) formed from m-cresol
1 MüllerJ A, GalushkoA S, KapplerA, SchinkB. Anaerobic degradation of m-cresol by Desulfobacterium cetonicum is initiated by formation of 3-hydroxybenzylsuccinate. Archives of Microbiology, 1999, 172(5): 287-294
doi: 10.1007/s002030050782 pmid: 10550470
2 LondryK L, FedorakP M, SuflitaJ M. Anaerobic degradation of m-Cresol by a sulfate-reducing bacterium. Applied and Environmental Microbiology, 1997, 63(8): 3170-3175
pmid: 16535673
3 TallurP N, MegadiV B, KamanavalliC M, NinnekarH Z. Biodegradation of p-cresol by Bacillus sp. strain PHN 1. Current Microbiology, 2006, 53(6): 529-533
doi: 10.1007/s00284-006-0309-x pmid: 17106800
4 KnackmussH J. Biochemistry and practical implications of organohalide degradation. In: KlugM J, ReddyC A, eds. Current Perspectives in Microbial. Washington, D C: American Society for Microbiology, 1984, 687-693
5 DagleyS, GibsonD T. The bacterial degradation of catechol. The Biochemical Journal, 1965, 95(2): 466-474
pmid: 14340096
6 CoulombelL, NolanL C, NikodinovicJ, DoyleE M, O’ConnorK E. Biotransformation of 4-halophenols to 4-halocatechols using Escherichia coli expressing 4-hydroxyphenylacetate 3-hydroxylase. Applied Microbiology and Biotechnology, 2011, 89(6): 1867-1875
doi: 10.1007/s00253-010-2969-5 pmid: 21057945
7 QuY Y, ShiS N, QiaoM, KongC L, ZhouH, ZhangX W, ZhouJ T. Multistep conversion of para-substituted phenols by phenol hydroxylase and 2,3-dihydroxy-biphenyl 1,2-dioxygenase. Applied Biochemistry and Biotechnology, 2013, 169(7): 2064-2075.
doi: 10.1007/s12010-013-0112-7 pmid: 19140028
8 TaoY, FishmanA, BentleyW E, WoodT K. Oxidation of benzene to phenol, catechol, and 1,2,3-trihydroxybenzene by toluene 4-monooxygenase of Pseudomonas mendocina KR1 and toluene 3-monooxygenase of Ralstonia pickettii PKO1. Applied and Environmental Microbiology, 2004, 70(7): 3814-3820
doi: 10.1128/AEM.70.7.3814-3820.2004 pmid: 15240250
9 RobertsS J, MorrisJ C, DobsonR C J, GerrardJ A. The preparation of (S)-aspartate semi-aldehyde appropriate for use in biochemical studies. Bioorganic & Medicinal Chemistry Letters, 2003, 13(2): 265-267
doi: 10.1016/S0960-894X(02)00923-X pmid: 12482436
10 ParalesR E, BruceN C, SchmidA, WackettL P. Biodegradation, biotransformation, and biocatalysis (b3). Applied and Environmental Microbiology, 2002, 68(10): 4699-4709
doi: 10.1128/AEM.68.10.4699-4709.2002 pmid: 12324310
11 GarikipatiS V, McIverA M, PeeplesT L. Whole-cell biocatalysis for 1-naphthol production in liquid-liquid biphasic systems. Applied and Environmental Microbiology, 2009, 75(20): 6545-6552
doi: 10.1128/AEM.00434-09 pmid: 19700554
12 PollardD J, WoodleyJ M. Biocatalysis for pharmaceutical intermediates: the future is now. Trends in Biotechnology, 2007, 25(2): 66-73
doi: 10.1016/j.tibtech.2006.12.005 pmid: 17184862
13 SchmidA, DordickJ S, HauerB, KienerA, WubboltsM, WitholtB. Industrial biocatalysis today and tomorrow. Nature, 2001, 409(6817): 258-268
doi: 10.1038/35051736 pmid: 11196655
14 AzeradR. Editorial overview: better enzyme for green chemistry. Current Opinion in Biotechnology, 2001, 12(6): 533-534
doi: 10.1016/S0958-1669(01)00259-2
15 StraathofA J J, PankeS, SchmidA. The production of fine chemicals by biotransformations. Current Opinion in Biotechnology, 2002, 13(6): 548-556
doi: 10.1016/S0958-1669(02)00360-9 pmid: 12482513
16 SelinheimoE, GasparettiC, MattinenM L, SteffensenC L, BuchertJ, KruusK. Comparison of substrate specificity of tyrosinases from Trichoderma reesei and Agaricus bisporus. Enzyme and Microbial Technology, 2009, 44(1): 1-10
doi: 10.1016/j.enzmictec.2008.09.013
17 SazinskyM H, DuntenP W, McCormickM S, DiDonatoA, LippardS J. X-ray structure of a hydroxylase-regulatory protein complex from a hydrocarbon-oxidizing multicomponent monooxygenase, Pseudomonas sp. OX1 phenol hydroxylase. Biochemistry, 2006, 45(51): 15392-15404
doi: 10.1021/bi0618969 pmid: 17176061
18 EltisL D, HofmannB, HechtH J, LünsdorfH, TimmisK N. Purification and crystallization of 2,3-dihydroxybiphenyl 1,2-dioxygenase. The Journal of Biological Chemistry, 1993, 268(4): 2727-2732
pmid: 8428946
19 WuZ L, PodustL M, GuengerichF P. Expansion of substrate specificity of cytochrome P450 2A6 by random and site-directed mutagenesis. The Journal of Biological Chemistry, 2005, 280(49): 41090-41100
doi: 10.1074/jbc.M508182200 pmid: 16215230
20 MorrisG M, Lim-WilbyM. Molecular docking. Methods in Molecular Biology (Clifton, N.J.), 2008, 443(1064-3745): 365-382
doi: 10.1007/978-1-59745-177-2_19 pmid: 18446297
21 MaF, ShiS N, SunT H, LiA, ZhouJ T, QuY Y. Biotransformation of benzene and toluene to catechols by phenol hydroxylase from Arthrobacter sp. W1. Applied Microbiology and Biotechnology, 2013, 97(11): 5097-5103
doi: 10.1007/s00253-012-4301-z pmid: 22854893
22 CarliellC M, BarclayS J, NaidooN, BuckleyC A, MulhollandD A, SeniorE. Microbial decolorization of a reactive azo dye under anaerobic conditions. Water SA, 1995, 21(1): 61-69
[1] Shiguan Yang, Xinrui Fan, Ji Liu, Wei Zhao, Bin Hu, Qiang Lu. Mechanism insight into the formation of H2S from thiophene pyrolysis: A theoretical study[J]. Front. Environ. Sci. Eng., 2021, 15(6): 120-.
[2] Chengjie Xue, Juan Wu, Kuang Wang, Yunqiang Yi, Zhanqiang Fang, Wen Cheng, Jianzhang Fang. Effects of different types of biochar on the properties and reactivity of nano zero-valent iron in soil remediation[J]. Front. Environ. Sci. Eng., 2021, 15(5): 101-.
[3] Guowen Hu, Zeqi Zhang, Xuan Zhang, Tianrong Li. Size and shape effects of MnFe2O4 nanoparticles as catalysts for reductive degradation of dye pollutants[J]. Front. Environ. Sci. Eng., 2021, 15(5): 108-.
[4] Mengqing Ge, Tao Lin, Kemei Zhou, Hong Chen, Hang Xu, Hui Tao, Wei Chen. Characteristics and removal mechanism of the precursors of N-chloro-2,2-dichloroacetamide in a drinking water treatment process at Taihu Lake[J]. Front. Environ. Sci. Eng., 2021, 15(5): 93-.
[5] Ruijie Li, Mengmeng Zhou, Shilong He, Tingting Pan, Jing Liu, Jiabao Zhu. Deciphering the effect of sodium dodecylbenzene sulfonate on up-flow anaerobic sludge blanket treatment of synthetic sulfate-containing wastewater[J]. Front. Environ. Sci. Eng., 2021, 15(5): 91-.
[6] Yueqi Jiang, Jia Xing, Shuxiao Wang, Xing Chang, Shuchang Liu, Aijun Shi, Baoxian Liu, Shovan Kumar Sahu. Understand the local and regional contributions on air pollution from the view of human health impacts[J]. Front. Environ. Sci. Eng., 2021, 15(5): 88-.
[7] Tianyi Li, Chengwu Zhang, Jingyi Zhang, Song Yan, Chuanyu Qin. Remediation of 2,4-dichlorophenol-contaminated groundwater using nano-sized CaO2 in a two-dimensional scale tank[J]. Front. Environ. Sci. Eng., 2021, 15(5): 87-.
[8] Xinzheng Li, Zhiming Li, Zhihui Xing, Zhimin Song, Bei Ye, Zhengming Wang, Qianyuan Wu. UV-LED/P25-based photocatalysis for effective degradation of isothiazolone biocide[J]. Front. Environ. Sci. Eng., 2021, 15(5): 85-.
[9] Aifang Gao, Junyi Wang, Jianfei Luo, Aiguo Li, Kaiyu Chen, Pengfei Wang, Yiyi Wang, Jingyi Li, Jianlin Hu, Hongliang Zhang. Temporal variation of PM2.5-associated health effects in Shijiazhuang, Hebei[J]. Front. Environ. Sci. Eng., 2021, 15(5): 82-.
[10] Haoran Feng, Min Liu, Wei Zeng, Ying Chen. Optimization of the O3/H2O2 process with response surface methodology for pretreatment of mother liquor of gas field wastewater[J]. Front. Environ. Sci. Eng., 2021, 15(4): 78-.
[11] Ting Wang, Renxian Zhou. PM-support interfacial effect and oxygen mobility in Pt, Pd or Rh-loaded (Ce,Zr,La)O2 catalysts[J]. Front. Environ. Sci. Eng., 2021, 15(4): 76-.
[12] Boyi Cheng, Yi Wang, Yumei Hua, Kate V. Heal. The performance of nitrate-reducing Fe(II) oxidation processes under variable initial Fe/N ratios: The fate of nitrogen and iron species[J]. Front. Environ. Sci. Eng., 2021, 15(4): 73-.
[13] Chenchen Li, Lijie Yan, Yiming Li, Dan Zhang, Mutai Bao, Limei Dong. TiO2@palygorskite composite for the efficient remediation of oil spills via a dispersion-photodegradation synergy[J]. Front. Environ. Sci. Eng., 2021, 15(4): 72-.
[14] Lina Gan, Kezhi Li, Hejingying Niu, Yue Peng, Jianjun Chen, Yuandong Huang, Junhua Li. Simultaneous removal of NOx and chlorobenzene on V2O5/TiO2 granular catalyst: Kinetic study and performance prediction[J]. Front. Environ. Sci. Eng., 2021, 15(4): 70-.
[15] Tianhao Xi, Xiaodan Li, Qihui Zhang, Ning Liu, Shu Niu, Zhaojun Dong, Cong Lyu. Enhanced catalytic oxidation of 2,4-dichlorophenol via singlet oxygen dominated peroxymonosulfate activation on CoOOH@Bi2O3 composite[J]. Front. Environ. Sci. Eng., 2021, 15(4): 55-.
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed