Biotransformation of dioxins by assembling RW1 upper pathway gene cassettes in Escherichia coli

##plugins.themes.bootstrap3.article.main##

THAMER Y. MUTTER
https://orcid.org/0000-0002-7631-954X
GERBEN J. ZYLSTRA
https://orcid.org/0000-0003-0419-1353
XING HUANG

Abstract

Abstract. Mutter TY, Zylstra GJ, Huang X. 2023. Biotransformation of dioxins by assembling RW1 upper pathway gene cassettes in Escherichia coli. Biodiversitas 24: 3648-3656. Rhizorhabdus wittichii RW1 (formerly known as Sphingomonas) is one of the few bacterial strains known to grow and metabolize dibenzofuran and dibenzo-p-dioxin as a carbon source. The rare ability of strain RW1 to transform both substrates suggests the involvement of unidentified genes. Its genome sequence showed that RW1 has an extreme redundancy of ring cleavage dioxygenases and hydrolases. RW1 genes were assembled on an expression vector to provide additional experimental evidence that both substrates are metabolized in RW1 by two different sets of hydrolases. Three different combinations of the ring cleavage dioxygenase gene (dbfB2) with three hydrolases (dxnB1, dxnB2, and dxnB3) were cloned on an expression vector (pET30a) in Escherichia coli BL21 (DE3), and the enzymes' roles were tested against DD and DF transformation. The results of the heterologous expression in E. coli showed that DbfB2 can transform both intermediates 2,2?,3-trihydroxybiphenyl (THD) and 2,2?,3-trihydroxybiphenyl ether (THDE) from DF and DD, respectively. The two hydrolases DxnB1 and DxnB2 are involved only in transforming the DF intermediate 2-hydroxy-6-oxo-6-(2-hydroxyphenyl)-hexa-2,4-dienoate (2OH-HOPDA) into salicylate. The newly identified hydrolase DxnB3 is involved only in transforming 2-hydroxy-6-oxo-6-(2-hydroxyphenoxy)-hexa-2,4-dienoate (2OH-O-HOPDA) into catechol in the DD pathway. The study clarifies and answers the question regarding the rare ability of other organisms that can degrade dibenzofuran but can’t degrade dibenzo-p-dioxin. The results showed that the hydrolases involved in DD degradation differ from those involved in DF degradation, as previously known that the same hydrolases are involved in the two pathways. All genes are assembled on one cassette for the first time, which has never been done previously.

##plugins.themes.bootstrap3.article.details##

References
Asimakoula S, Marinakos O, Tsagogiannis E, Koukkou AI. 2023. Phenol Degradation by Pseudarthrobacter phenanthrenivorans Sphe3. Microorganisms 11(2), p.524. DOI: 10.3390/microorganisms11020524.
Bünz PV, Falchetto R, Cook AM. 1993. Purification of two isofunctional hydrolases (EC 3.7. 1.8) in the degradative pathway for dibenzofuran in Sphingomonas sp. strain RW1. Biodegradation 4(3), pp.171-178. DOI: 10.1007/BF00695119.
Knutsen HK, Alexander J, Barregård L, Bignami M, Brüschweiler B, Ceccatelli S, Cottrill B, Dinovi M, Edler L, Grasl?Kraupp B. 2018. Risk for animal and human health related to the presence of dioxins and dioxin?like PCBs in feed and food. EFSA J 16(11), p.e05333. DOI: doi.org/10.2903/j.efsa.2018.5333.
Faisal RM. 2019. Understanding the role of Dibenzofuran 4, 4a dioxygenase reveals a silent pathway for biphenyl degradation in Sphingomonas wittichii RW1 and helps in engineering dioxin degrading strains. [Dissertation]. Rutgers University-School of Graduate Studies, New Jersey. [USA]. DOI: 10.7282/t3-cct8-q279
Green MR, Sambrook J. 2012. Molecular cloning. A Laboratory Manual 4th ed. Cold Spring Harbor Laboratory Press:, New York, USA.
Happe B, Eltis LD, Poth H, Hedderich R, Timmis KN. 1993. Characterization of 2, 2', 3-trihydroxybiphenyl dioxygenase, an extradiol dioxygenase from the dibenzofuran-and dibenzo-p-dioxin-degrading bacterium Sphingomonas sp. strain RW1. J Bacteriol 175(22), pp.7313-7320. DOI: 10.1128/jb.175.22.7313-7320.1993
Hashimoto S, Takazawa Y, Ieda T, Omagari R, Nakajima D, Nakamura S, Suzuki N. 2022. Application of rapid air sampling and non-targeted analysis using thermal desorption comprehensive two-dimensional gas chromatography/time-of-flight mass spectrometry to accidental fire. Chemosphere 303, p.135021. DOI: 10.1016/j.chemosphere.2022.135021
Hassan HA, d´ Enza M, Armengaud J, Pieper DH. 2022. Biochemical and genetic characterization comparison of four extradiol dioxygenases in Rhizorhabdus wittichii RW1. Appl Microbiol Biotechnol 106(17), pp.5539-5550. DOI: 10.1007/s00253-022-12099-3
Jia X, He Y, Jiang D, Liu C, Lu W. 2019. Construction and analysis of an engineered Escherichia coli-Pseudomonas aeruginosa co-culture consortium for phenanthrene bioremoval. Biochem Eng J 148, pp.214-223. DOI: 10.1016/j.bej.2019.05.010
Kohler HP, Schmid A, van der Maarel M. 1993. Metabolism of 2, 2'-dihydroxybiphenyl by Pseudomonas sp. strain HBP1: production and consumption of 2, 2', 3-trihydroxybiphenyl. J bacteriol 175(6), pp.1621-1628. DOI: 10.1128/jb.175.6.1621-1628.1993
Li J, Dong H, Sun J, Nie J, Zhang S, Tang J, Chen Z. 2016. Composition profiles and health risk of PCDD/F in outdoor air and fly ash from municipal solid waste incineration and adjacent villages in East China. Sci Total Environ 571, pp.876-882. DOI: 10.1016/j.scitotenv.2016.07.069
Mutter TY, Zylstra GJ. 2021. Separate upper pathway ring cleavage dioxygenases are required for growth of Sphingomonas wittichii strain RW1 on dibenzofuran and dibenzo-p-dioxin. Appl Environ Microbiol 87(11), pp.e02464-20. DOI: 10.1128/AEM.02464-20
Mutter TY, Zylstra GJ. 2021. Differential Roles of Three Different Upper Pathway meta Ring Cleavage Product Hydrolases in the Degradation of Dibenzo-p-Dioxin and Dibenzofuran by Sphingomonas wittichii Strain RW1. Appl Environ Microbiol 87(22), pp.e01067-21. DOI: 10.1128/AEM.01067-21
Omori T, Ishigooka H, Minoda Y. 1986. Purification and some properties of 2-hydroxy-6-oxo-6-phenylhexa-2, 4-dienoic acid (HOPDA) reducing enzyme from Pseudomonas cruciviae S93B1 involved in the degradation of biphenyl. Agric Biol Chem 50(6), pp.1513-1518. DOI: 10.1080/00021369.1986.10867594
Prajwal S, Murari SK. 2022. Current State, Challenges, and Perspectives on Microbial Degradation of Dioxin and Furan. Enzymes for Pollutant Degradation pp.247-267. DOI: 10.1007/978-981-16-4574-7_13
Saibu S, Adebusoye SA, Oyetibo GO, Rodrigues DF. 2020. Aerobic degradation of dichlorinated dibenzo-p-dioxin and dichlorinated dibenzofuran by bacteria strains obtained from tropical contaminated soil. Biodegradation 31, pp.123-137. DOI: 10.1007/s10532-020-09898-8
Van den Berg M, Birnbaum LS, Denison M, De Vito M, Farland W, Feeley M, Fiedler H, Hakansson H, Hanberg A, Haws L, Rose M. 2006. The 2005 World Health Organization reevaluation of human and mammalian toxic equivalency factors for dioxins and dioxin-like compounds. Toxicol Sci 93(2), pp.223-241. DOI: 10.1093/toxsci/kfl055
Wang B, Xu J, Gao J, Fu X, Han H, Li Z, Wang L, Tian Y, Peng R, Yao Q. 2019. Construction of an Escherichia coli strain to degrade phenol completely with two modified metabolic modules. J Hazard Mater 373, pp.29-38. DOI: 10.1016/j.jhazmat.2019.03.055
Wittich RM, Wilkes HEINZ, Sinnwell VOLKER, Francke W, Fortnagel P. 1992. Metabolism of dibenzo-p-dioxin by Sphingomonas sp. strain RW1. Appl Environ Microbiol 58(3), pp.1005-1010. DOI: 10.1128/aem.58.3.1005-1010.1992