Continuous treatment of coloured industry wastewater using immobilized Phanerochaete chrysosporium in a rotating biological contactor reactor

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Abstract

Coloured industry wastewaters often contain dyes and other toxic ingredients, and, therefore, pose serious threat to the receiving environment. Among the available methods the eco-friendly biological method has gained maximum attention due to its many advantages over the traditional methods. In the present study, continuous biological treatment of coloured wastewater from a textile dyeing industry was investigated using the white rot fungus Phanerochaete chrysosporium in a rotating biological contactor (RBC) reactor. The raw wastewater was diluted with an equal volume of either distilled water or media containing glucose at varying concentrations to study its effect on the decolourization process. Results revealed that the wastewater could be decolourized to an extent of more than 64% when diluted with media containing glucose; and, a maximum decolourization efficiency of 83% was obtained with 10 g/l glucose concentration. COD removal efficiencies were also found to be consistent with the decolourization efficiencies of the wastewaters. Further, the results were correlated with the enzyme activities of manganese peroxidase (MnP) and lignin peroxidase (LiP) by the fungus, which were found to play some significant role in decolourization of the wastewater. Results of replacing the costly carbon source glucose in the decolourization media with the more cheap molasses, however, revealed very high COD removal efficiency, but low decolourization efficiency of the industry wastewater.

Highlights

► Textile wastewater decolourization was achieved using a RBC reactor system. ► Nutrient supplementation is necessary for efficient wastewater decolourization. ► Lignolytic enzymes produced by Phanerochaete chrysosporium play important role in the process. ► Sugarcane molasses can be an alternative to costly glucose for wastewater treatment.

Introduction

Wastewater originating from textile industries is a complex mixture of potentially polluting substances which imposes serious threat to the receiving environment. Normally, 1–15% of dyes used in the process remains and is often found in the effluent wastewater stream (Barka et al., 2009). Generally, colours are noticeable at a dye concentration of 1 mg/l and an average concentration of 300 mg/l has been reported in effluents from textile manufacturing processes (O’Neill et al., 1999). The absorption of light due to such coloured wastewater from industries creates problems to photosynthetic aquatic plants and algae. Compared to wastewaters from other industries, effluent from textile and dye manufacturing industries is most difficult to treat mainly due to the presence of synthetic dyes of complex aromatic chemical structure that render these compounds highly stable and hence recalcitrant to degradation (Kaushik and Malik, 2009). Wastewater decolourization can be, however, achieved by chemical and physical methods including adsorption, coagulation-flocculation, oxidation and electrochemical methods (Lin and Peng, 1996). On the contrary, these existing techniques suffer from one or more drawbacks, such as high cost, formation of hazardous by-products, intensive energy requirement etc. (Saratale et al., 2009). Further, while decolourization under anaerobic conditions can lead to toxic degradation products (Brown and DeVito, 1993), exposure to oxygen may cause reverse colourization of the degradation products (Knapp and Newby, 1995). On the other hand, microbial decolourization process offers to overcome all these drawbacks by reducing the complex colour components in the wastewater into simple compounds like carbon dioxide, ammonia and water in a cleaner and safer way than the conventional methods (Paszczynski et al., 1992).

Among the various microorganisms, the white rot fungus Phanerochaete chrysosporium secretes non-specific, extracellular ligninolytic enzymes and can degrade a wide variety of recalcitrant compounds like xenobiotics, dyestuffs, etc. Due to the extracellular enzyme system, substrate diffusion limitation is not observed which is generally encountered in bacteria. Another advantage of using P. chrysosporium is that they do not require preconditioning with the pollutant as enzyme production and secretion depends on nutrient limitation, which can be carbon or nitrogen, rather than the pollutant itself. In fact, the fungus has been extensively tested in decolourization studies due to its ability to degrade, partially or completely, a broad range of dyes such as heterocyclic, azo, anthraquinone, and vat (Rodriguez et al., 2000; Mielgo et al., 2003). Further, the extracellular enzyme system enables the white rot fungus to tolerate even high concentrations of such pollutants (Kapdan et al., 2000a, b).

Compared with other reactors, the rotating biological contactor (RBC) reactor is proving effective in treating complex wastewaters (Alemzadeh et al., 2002; Kapdan and Kargi, 2002; Axelsson et al., 2006), mainly because it offers high interfacial area generated in the rotating disc to establish good contact between the microbial species and pollutants in the system. Although a few studies have been performed on decolourization of wastewater using the immobilized fungus in laboratory-scale RBC reactors, all these studies are restricted only to synthetic wastewater prepared in the laboratory and/or under batch operated conditions. In addition, coloured wastewater from industries contains complex mixture of dyes and other ingredients, and, hence, there is a need to evaluate potential of the bioreactor system in decolourizing such real wastewaters. The present study was, therefore, aimed to decolourize wastewater from a textile dye industry using immobilized P. chrysosporium in a continuously operated RBC reactor.

Section snippets

Chemicals and reagents

Veratryl alcohol (3,4-dimethoxybenzyl alcohol, 96% pure) and Nitrilo tri acetic acid tri sodium salt used in the study were purchased from Sigma Chemicals (St. Louis, MO, USA). All other chemicals and reagents used were purchased from Merck India Ltd. Cheaply available sugarcane molasses was purchased from local market in Guwahati, India, and its composition is given in Table 1.

Microorganism and culture conditions

P. chrysosporium MTCC 787 used in the study was obtained from Institute of Microbial Technology, Chandigarh, India.

Decolourization and COD removal of the wastewater by dilution with distilled water

Preliminary experiments to treat the pH adjusted raw wastewater without any dilution failed probably because of its high COD content along with high concentrations of a mixture of dyes, which are known to exert some toxic effect on the fungus. Hence, initial decolourization experiments were carried by diluting the pH adjusted wastewater with distilled water. Results revealed that the decolourization efficiency was 64% at the end of 2 d, which however declined further to 53% at the end of this

Discussion

The scan results of the treated wastewaters revealed that the immobilized fungus could effectively decolourize the wastewater when it was supplemented with media containing glucose. In absence of any external carbon source or media containing nutrients, the fungus could decolourize the wastewater only to an extent of 53%. The observation that an external carbon source is required for the fungus to decolourize the wastewater is consistent with those of Swamy and Ramsay (1999), Radha et al. (2005)

Conclusion

The present study demonstrated that coloured industrial effluents can be effectively treated by immobilized P. chrysosporium in a continuously operated RBC reactor following its dilution with media containing nutrients and sugar, preferably glucose. Decolourization as high as 80% was achieved using an optimum concentration of 5 g/l glucose in the media. COD removal efficiencies in the various stages of operation in the reactor were also found to match well with the decolourization of the

Acknowledgements

The authors acknowledge with thanks the Council for Scientific and Industrial Research (CSIR), India, for funding this research work (scheme no. 38(1171)/07/EMR-II).

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    However, textile industry wastewater treatment with white-rot fungi has some limitations such as requirement of low pH values, long growth phase, long hydraulic retention time for full decolorization, and big reactor size (Singh and Arora, 2011; Nilsson et al., 2006; Blánquez et al., 2008; Łebkowska and Załęska-Radziwiłł, 2014). To overcome these limitations for biodegradation of textile industry wastewater treatment, immobilization of fungus has been used recently because of reusability, easy application, reducing costs (Guimarães et al., 2005; Pakshirajan and Kheria, 2012; Pakshirajan and Singh, 2010; Hameed and Ismail, 2018). Furthermore, using immobilization technique in a continuous mode bioreactor could be better strategy for textile industry wastewater treatment because it allows the long term utilization of microbial systems, high degradation rate, more resistant to environmental changes such as pH and temperature (Kurade et al., 2019).

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