Acid Orange 7 degradation using methane as the sole carbon source and electron donor

Yanan Bai , Xiuning Wang , Fang Zhang , Raymond Jianxiong Zeng

Front. Environ. Sci. Eng. ›› 2022, Vol. 16 ›› Issue (3) : 34

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Front. Environ. Sci. Eng. ›› 2022, Vol. 16 ›› Issue (3) : 34 DOI: 10.1007/s11783-021-1468-5
RESEARCH ARTICLE
RESEARCH ARTICLE

Acid Orange 7 degradation using methane as the sole carbon source and electron donor

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Abstract

• AO7 degradation was coupled with anaerobic methane oxidation.

• Higher concentration of AO7 inhibited the degradation.

• The maximum removal rate of AO7 reached 280 mg/(L·d) in HfMBR.

• ANME-2d dominated the microbial community in both batch reactor and HfMBR.

• ANME-2d alone or synergistic with the partner bacteria played a significant role.

Azo dyes are widely applied in the textile industry but are not entirely consumed during the dyeing process and can thus be discharged to the environment in wastewater. However, azo dyes can be degraded using various electron donors, and in this paper, Acid Orange 7 (AO7) degradation performance is investigated using methane (CH4) as the sole electron donor. Methane has multiple sources and is readily available and inexpensive. Experiments using 13C-labeled isotopes showed that AO7 degradation was coupled with anaerobic oxidation of methane (AOM) and, subsequently, affected by the initial concentrations of AO7. Higher concentrations of AO7 could inhibit the activity of microorganisms, which was confirmed by the long-term performance of AO7 degradation, with maximum removal rates of 8.94 mg/(L·d) in a batch reactor and 280 mg/(L·d) in a hollow fiber membrane bioreactor (HfMBR). High-throughput sequencing using 16S rRNA genes showed that Candidatus Methanoperedens, affiliated to ANME-2d, dominated the microbial community in the batch reactor and HfMBR. Additionally, the relative abundance of Proteobacteria bacteria (Phenylobacterium, Pseudomonas, and Geothermobacter) improved after AO7 degradation. This outcome suggested that ANME-2d alone, or acting synergistically with partner bacteria, played a key role in the process of AO7 degradation coupled with AOM.

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Keywords

Azo dyes / AO7 degradation / Anaerobic methane oxidation / Microbial community / ANME-2d

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Yanan Bai, Xiuning Wang, Fang Zhang, Raymond Jianxiong Zeng. Acid Orange 7 degradation using methane as the sole carbon source and electron donor. Front. Environ. Sci. Eng., 2022, 16(3): 34 DOI:10.1007/s11783-021-1468-5

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References

[1]

Bai Y N, Wang X N, Wu J, Lu Y Z, Fu L, Zhang F, Lau T C, Zeng R J (2019). Humic substances as electron acceptors for anaerobic oxidation of methane driven by ANME-2d. Water Research, 164: 114935

[2]

Bai Y N, Wang X N, Zhang F, Wu J, Zhang W, Lu Y Z, Fu L, Lau T C, Zeng R J (2020). High-rate anaerobic decolorization of methyl orange from synthetic azo dye wastewater in a methane-based hollow fiber membrane bioreactor. Journal of Hazardous Materials, 388: 121753

[3]

Brás R, Gomes A, Ferra M I, Pinheiro H M, Goncalves I C (2005). Monoazo and diazo dye decolourisation studies in a methanogenic UASB reactor. Journal of Biotechnology, 115(1): 57–66

[4]

Cai C, Shi Y, Guo J, Tyson G W, Hu S, Yuan Z (2019). Acetate production from anaerobic oxidation of methane via intracellular storage compounds. Environmental Science & Technology, 53(13): 7371–7379

[5]

Chen H, Zhao L, Hu S H, Yuan Z G, Guo J H (2018). High-Rate production of short-chain fatty acids from methane in a mixed-culture membrane biofilm reactor. Environmental Science & Technology Letters, 5(11): 662–667

[6]

Dafale N, Agrawal L, Kapley A, Meshram S, Purohit H, Wate S (2010). Selection of indicator bacteria based on screening of 16S rDNA metagenomic library from a two-stage anoxic-oxic bioreactor system degrading azo dyes. Bioresource Technology, 101(2): 476–484

[7]

Dai R, Chen X, Luo Y, Ma P, Ni S, Xiang X, Li G (2016). Inhibitory effect and mechanism of azo dyes on anaerobic methanogenic wastewater treatment: Can redox mediator remediate the inhibition? Water Research, 104: 408–417

[8]

Ding J, Lu Y Z, Fu L, Ding Z W, Mu Y, Cheng S H, Zeng R J (2017). Decoupling of DAMO archaea from DAMO bacteria in a methane-driven microbial fuel cell. Water Research, 110: 112–119

[9]

Ettwig K F, Zhu B, Speth D, Keltjens J T, Jetten M S M, Kartal B (2016). Archaea catalyze iron-dependent anaerobic oxidation of methane. Proceedings of the National Academy of Sciences of the United States of America, 113(45): 12792–12796

[10]

Fernando E, Keshavarz T, Kyazze G (2014). Complete degradation of the azo dye Acid Orange-7 and bioelectricity generation in an integrated microbial fuel cell, aerobic two-stage bioreactor system in continuous flow mode at ambient temperature. Bioresource Technology, 156: 155–162

[11]

Fu L, Bai Y N, Lu Y Z, Ding J, Zhou D, Zeng R J (2019). Degradation of organic pollutants by anaerobic methane-oxidizing microorganisms using methyl orange as example. Journal of Hazardous Materials, 364: 264–271

[12]

Fu L, Li S W, Ding Z W, Ding J, Lu Y Z, Zeng R J (2016). Iron reduction in the DAMO/Shewanella oneidensis MR-1 coculture system and the fate of Fe(II). Water Research, 88: 808–815

[13]

Georgiou D, Aivasidis A (2006). Decoloration of textile wastewater by means of a fluidized-bed loop reactor and immobilized anaerobic bacteria. Journal of Hazardous Materials, 135(1–3): 372–377

[14]

Gonçalves I C, Lopes L, Pinheiro H M, Ferra M I (2009). Behaviour of different anaerobic populations on the biodegradation of textile chemicals. Journal of Hazardous Materials, 172(2–3): 1236–1243

[15]

Haroon M F, Hu S, Shi Y, Imelfort M, Keller J, Hugenholtz P, Yuan Z, Tyson G W (2013). Anaerobic oxidation of methane coupled to nitrate reduction in a novel archaeal lineage. Nature, 500(7464): 567–570

[16]

Ilić Đurđić K, Ostafe R, Prodanović O, Đurđević Đelmaš A, Popović N, Fischer R, Schillberg S, Prodanović R (2021). Improved degradation of azo dyes by lignin peroxidase following mutagenesis at two sites near the catalytic pocket and the application of peroxidase-coated yeast cell walls. Frontiers of Environmental Science & Engineering, 15(2): 19

[17]

Işık M, Sponza D T (2004). Decolorization of azo dyes under batch anaerobic and sequential anaerobic/aerobic conditions. Journal of Environmental Science and Health. Part A, Toxic/Hazardous Substances & Environmental Engineering, 39(4): 1107–1127

[18]

Kalyani D C, Patil P S, Jadhav J P, Govindwar S P (2008). Biodegradation of reactive textile dye Red BLI by an isolated bacterium Pseudomonas sp. SUK1. Bioresource Technology, 99(11): 4635–4641

[19]

Kapdan I K, Tekol M, Sengul F (2003). Decolorization of simulated textile wastewater in an anaerobic–aerobic sequential treatment system. Process Biochemistry, 38(7): 1031–1037

[20]

Knittel K, Boetius A (2009). Anaerobic oxidation of methane: progress with an unknown process. Annual Review of Microbiology, 63(1): 311–334

[21]

Liu Y, Zhang Y, Quan X, Zhang J, Zhao H, Chen S (2011). Effects of an electric field and zero valent iron on anaerobic treatment of azo dye wastewater and microbial community structures. Bioresource Technology, 102(3): 2578–2584

[22]

Liu Y N, Zhang F, Li J, Li D B, Liu D F, Li W W, Yu H Q (2017). Exclusive extracellular bioreduction of methyl orange by azo reductase-free Geobacter sulfurreducens. Environmental Science & Technology, 51(15): 8616–8623

[23]

Lu Y Z, Ding Z W, Ding J, Fu L, Zeng R J (2015). Design and evaluation of universal 16S rRNA gene primers for high-throughput sequencing to simultaneously detect DAMO microbes and anammox bacteria. Water Research, 87: 385–394

[24]

Lu Y Z, Fu L, Ding J, Ding Z W, Li N, Zeng R J (2016). Cr(VI) reduction coupled with anaerobic oxidation of methane in a laboratory reactor. Water Research, 102: 445–452

[25]

Luo J H, Chen H, Hu S, Cai C, Yuan Z, Guo J (2018). Microbial selenate reduction driven by a denitrifying anaerobic methane oxidation biofilm. Environmental Science & Technology, 52(7): 4006–4012

[26]

Luo J H, Wu M, Liu J, Qian G, Yuan Z, Guo J (2019). Microbial chromate reduction coupled with anaerobic oxidation of methane in a membrane biofilm reactor. Environment International, 130: 104926

[27]

Luo Y H, Chen R, Wen L L, Meng F, Zhang Y, Lai C Y, Rittmann B E, Zhao H P, Zheng P (2015). Complete perchlorate reduction using methane as the sole electron donor and carbon source. Environmental Science & Technology, 49(4): 2341–2349

[28]

Mahmood S, Khalid A, Arshad M, Mahmood T, Crowley D E (2016). Detoxification of azo dyes by bacterial oxidoreductase enzymes. Critical Reviews in Biotechnology, 36(4): 639–651

[29]

Manu B, Chaudhari S (2002). Anaerobic decolorisation of simulated textile wastewater containing azo dyes. Bioresource Technology, 82(3): 225–231

[30]

Méndez-Paz D, Omil F, Lema J M (2005a). Anaerobic treatment of azo dye Acid Orange 7 under fed-batch and continuous conditions. Water Research, 39(5): 771–778

[31]

Méndez-Paz D, Omil F, Lema J M (2005b). Anaerobic treatment of azo dye Acid Orange 7 under batch conditions. Water Research, 36(2): 264–272

[32]

Nie W B, Ding J, Xie G J, Tan X, Lu Y, Peng L, Liu B F, Xing D F, Yuan Z, Ren N (2021). Simultaneous nitrate and sulfate dependent anaerobic oxidation of methane linking carbon, nitrogen and sulfur cycles. Water Research, 194: 116928

[33]

Oon Y S, Ong S A, Ho L N, Wong Y S, Oon Y L, Lehl H K, Thung W E, Nordin N (2018). Disclosing the synergistic mechanisms of azo dye degradation and bioelectricity generation in a microbial fuel cell. Chemical Engineering Journal, 344: 236–245

[34]

Raghoebarsing A A, Pol A, Van De Pas-Schoonen K T, Smolders A J, Ettwig K F, Rijpstra W I, Schouten S, Damste J S, Op Den Camp H J, Jetten M S, Strous M (2006). A microbial consortium couples anaerobic methane oxidation to denitrification. Nature, 440(7086): 918–921

[35]

Ren Z J (2017). Microbial fuel cells: Running on gas. Nature Energy, 2(6): 17093

[36]

Saratale R G, Saratale G D, Chang J S, Govindwar S P (2011). Bacterial decolorization and degradation of azo dyes: A review. Journal of the Taiwan Institute of Chemical Engineers, 42(1): 138–157

[37]

Timmers P H, Welte C U, Koehorst J J, Plugge C M, Jetten M S, Stams A J (2017). Reverse Methanogenesis and Respiration in Methanotrophic Archaea. Archaea (Vancouver, B.C.), 2017: 1654237

[38]

van Der Zee F P, Villaverde S (2005). Combined anaerobic-aerobic treatment of azo dyes: A short review of bioreactor studies. Water Research, 39(8): 1425–1440

[39]

Wallenius A J, Dalcin Martins P, Slomp C P, Jetten M S M (2021). Anthropogenic and environmental constraints on the microbial methane cycle in coastal sediments. Frontiers in Microbiology, 12: 631621

[40]

Wang Z, Yin Q, Gu M, He K, Wu G (2018). Enhanced azo dye Reactive Red 2 degradation in anaerobic reactors by dosing conductive material of ferroferric oxide. Journal of Hazardous Materials, 357: 226–234

[41]

Willetts J, Ashbolt N J (2000). Understanding anaerobic decolourisation of textile dye wastewater: Mechanism and kinetics. Water Science and Technology, 42(1–2): 409–415

[42]

Xu S, Wu X, Lu H (2021). Overlooked nitrogen-cycling microorganisms in biological wastewater treatment. Frontiers of Environmental Science & Engineering, 15(6): 133

[43]

Yu L, Zhang X Y, Wang S, Tang Q W, Xie T, Lei N Y, Chen Y L, Qiao W C, Li W W, Lam M H W (2015). Microbial community structure associated with treatment of azo dye in a start-up anaerobic sequenced batch reactor. Journal of the Taiwan Institute of Chemical Engineers, 54: 118–124

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