Decolorization of the textile dyes Reactive Red 2 and Reactive Blue 4 using Bjerkandera sp. Strain BOL 13 in a continuous rotating biological contactor reactor

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Abstract

The decolorization of two different textile dyes, Reactive Red 2 and Reactive Blue 4, was studied in batch as well as continuous experiments using Bjerkandera sp. Strain BOL 13. The batch experiments were performed to study the decolorization of the dyes separately as well as in a mixture. The results from the experiments showed that the fungus decolorized both dyes. The absorbance was measured at 538 and 595 nm, the peak absorbance wavelengths of the red and blue dyes respectively. The absorbance decreased with 99% at both 538 and 595 nm in the experiments in which the dyes were studied separately at a concentration of 100 mg/l. The corresponding figure for the experiment in which the dyes were studied in a mixture was 98%. A continuous rotating biological contactor was then used to study the decolorization of mixtures of the two dyes at three different concentrations, e.g. 50, 100 and 200 mg/l of each of the dyestuff. The decrease in absorbance at 538 nm was 96% at the two lower dye concentrations while it was 81% at the highest concentration. The corresponding figures at 595 nm were 94 and 80%. The hydraulic retention time was 3 days. Scanning of the absorbance between 200 and 800 nm showed that three peaks disappeared in the UV range during treatment (246, 283 and 323.5 nm) and that a new plateau was formed around 270 nm.

Introduction

Wastewater from textile industries is a problem in large parts of the world. The degradation products of textile dyes are often carcinogenic. Furthermore, the absorption of light due to textile dyes creates problems to photosynthetic aquatic plants and algae [1], [2].

Reactive dyes are highly water-soluble polyaromatic molecules. The three most common groups are azo, anthraquinone and phthalocyanine dyes. They react with nucleophilic groups on the fabric forming covalent bonds, which gives a good fixation. Despite this, 10–50% of the dye will end up in the effluent because the dye molecule might react with hydroxyl ions in the solution, giving rise to even more water-soluble hydrolysed molecules [3]. Furthermore, the dye preparations are not homogenous. A range of different by-products, some of which are colored, will contribute to the pollution. Reactive dyes have been shown to pass ordinary aerobic sewage treatment unaffected [3], [4]. Some dyes are decolorized under anaerobic conditions however the effluent might be toxic [5], [6]. Furthermore, colorization was found to take place if the effluent is left untreated for a long period of time, in a study performed by Knapp and Newby [7]. Similar results were obtained during the present study when a continuous reactor with anaerobic microorganisms was used for the degradation of Reactive Blue 4 (unpublished data).

White rot fungi have also been used for the degradation of different dyes [8], [9], [10], [11], [12], [13], [14]. An advantage with these organisms is that they produce and excrete ligninolytic enzymes that are non-specific with regard to aromatic structure. This means that they are capable of degrading mixtures of aromatic compounds [12]. Most studies concerning degradation of dyes have however been preformed with one dye at a time. The most commonly used strains in regard to degradation of textile dyes are Phanerochaete chrysosporium and Coriolus versicolor [10], [12].

The aim of the study was to examine the metabolic potential of Bjerkandera sp. Strain BOL 13 regarding decolorization of a mixture of two representative dyes from two of the most commonly used groups of reactive dyes, Fig. 1, in a continuous reactor. A system with immobilised mycelia was used since results from an earlier study indicates that enzyme secretion is better in this kind of systems than in systems built on suspended cultures [15]. C. versicolor has furthermore been shown to efficiently decolorize Everzol Turquoise Blue G, a phthalocyanine dye, when a rotating biological contactor was used in batch mode [12].

Section snippets

Chemicals

The dyes were purchased from Sigma–Aldrich (Miluwaukee, USA) while yeast extract was bought from Difco (Detroit, USA). The rest of the chemicals were obtained from Merck (Darmstadt, Germany). The dyes, Reactive Red 2 and Reactive Blue 4 (C.I. 61205), were of a quality used for dyeing textiles while the rest of the chemicals were of pro analysis quality.

Storage of Bjerkandera sp. Strain BOL 13

A pure culture of Bjerkandera sp. Strain BOL 13 (GenBank accession number AY633927) was obtained from the fungal collection of the Universidad

Evaluation of metabolic potential of Bjerkandera sp. Strain BOL 13

The fungus was shown to be able to decolorize the dyes, both separately and in mixture. The diameters of the decolorized area of the plates are given in Table 1, Table 2 as a function of time. The fungus produced a large amount of biomass on the plates containing malt extract.

Batch experiments

The fungus was shown to be able to decolorize both Reactive Red 2 and Reactive Blue 4 in the liquid medium. The results of the absorbance measurements from the batch experiments are given in Fig. 3, Fig. 4, Fig. 5.

The

Discussion

The results show that Bjerkandera sp. Strain BOL 13 is efficient regarding decolorization of the dyes both separately and in mixture. This is of importance since real textile wastewater often contains mixtures of different kinds of dyes. The process worked well even after some biomass had been removed in order to decrease the risk for diffusion problems. The difference in dependence of glucose concentration at the dyestuff concentrations 100 and 200 mg/l might however depend on an incipient

Acknowledgments

SIDA/SAREC is gratefully acknowledged for its financial support. Frans-Peder Nilson is gratefully acknowledged for valuable discussions concerning analyses.

References (19)

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