AZO DYE REDUCTION AND BIODEGRADABILITY MECHANISMS DURING AN ANAEROBIC PROCESS

Authors

  • Wimonmas Boonyungyuen School of Environmental Engineering, Institute of Engineering, Suranaree University of Technology, Nakhon Ratchasima, 30000, Thailand.
  • Boonchai Wichitsathian School of Environmental Engineering, Institute of Engineering, Suranaree University of Technology, Nakhon Ratchasima, 30000, Thailand.
  • Patcharin Racho School of Environmental Engineering, Institute of Engineering, Suranaree University of Technology, Nakhon Ratchasima, 30000, Thailand.

Keywords:

Azo dye reduction, biodegradability kinetics, COD fraction

Abstract

An anaerobic process for azo dye treatment had a high performance in organic removal with values reaching 85.51% and 90.29% for total chemical oxygen demand (TCOD) and soluble chemical oxygen demand, respectively. At the same time, the process was also capable of color removal. The absorption peak of anaerobic effluent appeared in wavelengths ranging between 195 nm to 246 nm which is identified as being in the aromatic amine regions. The Fourier transform infrared spectrum of anaerobic effluent represented the aromatic region. Therefore, azo dyes were degraded to aromatic compounds during the anaerobic process. The anaerobic influent contained a very high soluble inert chemical oxygen demand (SI) fraction with 60.68% of TCOD. However, the SI fraction was reduced by the anaerobic process at 93.46% removal. It is possible that the SI fraction was adsorbed on the microorganism surface and/or the dead cell composition. The maximum specific growth rate (μmax) and sludge yields were found in the anaerobic influent fed condition that had higher values than in the effluent fed condition. That caused a high organic concentration in the influent. However, the μmax of the heterotroph microorganism was still high at the anaerobic effluent fed condition. This enabled the aerobic treatment to be capable of aromatic amine removal at S0/X0 ratio 0.151-0.156.

References

APHA.(2005). Standard Methods for the Examination of Water and Wastewater. 21th ed. American Public Health Association, Washington, DC, USA, 1200p.

Ekama, G.A., Dold, P.L., and Marais, G.V.R. (1986). Procedures for determining influent COD fractions and the maximum specific growth rate of heterotrophs in activated sludge systems. Water Sci. Technol., 18:91-114.

Gottlieb, A., Shaw, C., Smith, A., Wheatley, A., and Forsythe, S. (2003). The toxicity of textile reactive azo dyes after hydrolysis and decolourisation. J. Biotechnol., 101:49-56.

Işik, M. and Sponza, D. (2004).Monitoring of toxicity and intermediates of C.I. Direct Black 38 azo dye through decolorization in an anaerobic/aerobic sequential reactor system. J. Hazard Mater., 114(1-3):29-39.

Laowansiri, S., Vinitnantharat, S., Chaiprasert, P., and Ha, S.R. (2008). Anaerobic degradation kinetics of reactive dye with different carbon sources. J. Environ. Biol., 29(3):309-314.

Liu, Y., Liu, Q.S., and Tay, J.H. (2005).Initial conditions-dependent growth kinetics in microbial batch culture. Process Biochem., 40:155-160.

Ng,W.J., Sim, T.S., Ong, S.L., Ng, K.Y., Ramasamy, M., and Tan, K.N. (1994). Sequencing batch reactor (SBR) removal of toxicity from combined sewage. Bioresource Technol., 47(2):107-112.

Orhon, D., Karahan, Ö., and Sözen, S. (1999). The effect of residual microbial products on the experimental assessment of the particulate inert COD in wastewaters. Water Res., 33(14):3191-3203.

Pinheiro, H.M., Touraud, E., and Thomas, O. (2004). Aromatic amines from azo dye reduction: Status review with emphasis on direct UV spectrophotometric detection in textile industry wastewaters. Dyes Pigments, 61:121-139.

Puvaneswari, N., Muthukrishnan, J., and Gunasekaran, P. (2006).Toxicity assessment and microbial degradation of azo dyes. Indian J. Exp. Biol., 44:618-626.

Robinson, T.G., McMullan, G., Marchant, R., and Nigam, P. (2001). Remediation of dyes in textile effluent:A critical review on current treatment technologies with a proposed alternative. Bioresource Technol., 77:247-255.

Sponza, D.T. and Işik, M. (2005). Reactor performances and fate of aromatic amines through decolorization of Direct Black 38 dye under anaerobic/aerobic sequentials. Process Biochem., 40:35-44.

Telke, A., Kalyani, D., Jadhav, J., and Govindwar, S. (2008). Kinetics and mechanism of Reactive Red 141 degradation by a bacterial isolate Rhizobium radiobacter MTCC 8161. ActaChim. Slov., 55:320-329.

Van der Zee, F.P. and Villaverde, S. (2005).Combined anaerobic-aerobic treatment of azo dyes - A short review of bioreactor studies. Water Res., 39:1425-1440.

Weisburger, J.H. (2002).Comments on the history and importance of aromatic and heterocyclic amines in publichealth. Mutat. Res. -Fund. Mol. M., 9(20):506-507.

Wentzel, M.C., Mbewe, A., Lakay, M.T., and Ekama, G.A. (1999). Batch test for characterization of the carbonaceous materials in municipal wastewaters. Water SA., 25(3):327-335.

Zille, A., Górnacka, B., Rehorek, A., and Cavaco-Paulo, A. (2005).Degradation of azo dyes by Trametesvillosa Laccase over long periods of oxidation conditions. Appl. Environ. Microb., 71(11):6711-6718.

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Published

2026-08-28

How to Cite

Boonyungyuen, W., Wichitsathian, B., & Racho, P. (2026). AZO DYE REDUCTION AND BIODEGRADABILITY MECHANISMS DURING AN ANAEROBIC PROCESS. Suranaree Journal of Science and Technology, 20(1), 1–9. retrieved from https://ph04.tci-thaijo.org/index.php/SUJST/article/view/13832

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Research Article