Biodegradation of Remazol Brilliant Blue R using isolated bacterial culture (<i>Staphylococcus</i>sp. K2204)

Velayutham, Karthikeyan; Kumar, Madhava Anil; Pushparaj, Mohanapriya; Thanarasu, Amudha; Devaraj, Thiruselvi; Periyasamy, Karthik; Sivanesan, S.

doi:10.1080/09593330.2017.1369579

Cited by 45 publications

(25 citation statements)

References 51 publications

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“…During the process of dyeing wastewater treatment, the growth, reproduction rate, and biodegradation activities of microorganisms, and also the solubility of pollutants are affected by temperature (Pearce et al, 2003). In general, the optimum temperature range for bacterial decolorization of dyes is in a narrow range and is consistent with bacterial growth: temperature ranges between 25 and 37 °C (Cui DZ et al, 2016;Velayutham et al, 2018). The decolorization rate of Reactive Blue 4 by Staphylococcus hominis subsp.…”

Section: Effect Of Temperature On Bacterial Anthraquinone Dye Degradamentioning

confidence: 97%

Bacterial degradation of anthraquinone dyes

Wang

et al. 2019

J. Zhejiang Univ. Sci. B

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Anthraquinone dyes, which contain anthraquinone chromophore groups, are the second largest class of dyes after azo dyes and are used extensively in textile industries. The majority of these dyes are resistant to degradation because of their complex and stable structures; consequently, a large number of anthraquinone dyes find their way into the environment causing serious pollution. At present, the microbiological approach to treating printing and dyeing wastewater is considered to be an economical and feasible method, and reports regarding the bacterial degradation of anthraquinone dyes are increasing. This paper reviews the classification and structures of anthraquinone dyes, summarizes the types of degradative bacteria, and explores the possible mechanisms and influencing factors of bacterial anthraquinone dye degradation. Present research progress and existing problems are further discussed. Finally, future research directions and key points are presented.

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Section: Effect Of Temperature On Bacterial Anthraquinone Dye Degradamentioning

confidence: 97%

Bacterial degradation of anthraquinone dyes

Wang

et al. 2019

J. Zhejiang Univ. Sci. B

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“…Corroborate the previous study degradation of AR88 into aliphatic and tertiary amines by appearance of the peak at 1643 -1 -1 cm for C=C stretch and peak at 1345 cm for S=O stretch which indicated the presence of aromatic compounds . 1284 cm and 1212 cm after treatment showed deformation of aromatic compound benzoquinoline, alkane (Velayutham et al, 2018) present in dye effluent. The results of spectra were identified according to Roeges and Baas,(1994) who offered a guide to the characteristics of the frequencies band in wave number to identify the functional groups according to the inter and intramolecular interactions created due to vibrational frequencies for the effluent.…”

Section: Preparation Of Bacterial Inoculum Using Extracted Glucosementioning

confidence: 96%

Utilizing Borassus flabellifer sprout peel sugars by Pseudomonas fluorescence for degradation of textile effluent

Sathya¹,

Franklin²,

Balaji³

et al. 2019

JEB

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The present investigation deals with the extraction of sugars from tuber peels of Borassus flabellifer and their subsequent utilization for the growth of a bacterial isolate. The study also aims to degrade the textile effluent using B. flabellifer sprout peel sugar supplemented bacterial isolate. The isolate was screened from a textile effluent and was identified as Pseudomonas fluorescence. The sugar peels were pretreated by dilute acid hydrolysis and extracted sugars were used as supplement for the growth of Pseudomonas fluorescence. The textile effluent was treated with the bacterial isolate for degradation. The decolorization and degradation was monitored using UV-Visible spectrophotometry, Fourier Transform Infrared (FT-IR) Spectroscopy and Gas Chromatography With Mass Spectrometry (GC-MS). B. flabellifer sprout peel sugar was supplemented as a macronutrient to support the growth of Pseudomonas fluorescence for the degradation of textile effluent. Higher decolorization efficiency (95%) within 7 days under aerobic condition at pH-7.0 and temperature 35˚C was achieved. The present study showed that the growth of Pseudomonas fluorescence was possible in tuber peel extracted sugars which was used as a carbon source. The bacteria grown in tuber peel extracted sugars was able to decolorize and degrade the textile effluent.

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“…These data corroborate previous studies, for various dyes, conducted with this type of seed. According to Karthikeyan et al (2017), the germination index and growth of Vigna radiata seeds, treated with the products of the biodegradation of the Remazol Brilliant Blue R dye by Staphylococcus sp. K2204, were higher when compared to the seeds exposed to the Remazol Brilliant Blue R (100 mg L −1 ).…”

Section: Phytotoxicitymentioning

confidence: 99%

Microbial fuel cell-induced production of fungal laccase to degrade the anthraquinone dye Remazol Brilliant Blue R

et al. 2019

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The anthraquinone dye Remazol Brilliant Blue R is largely used in the textile industry. However, its removal from wastewaters is costly and complex. Many methods have been tested to solve this ecological problem, but there is still a need for efficient methods. We propose here an alternative use of a two-chambered microbial fuel cell (MFC), fuelled with domestic wastewater in the anodic chamber, to degrade a simulated textile dye effluent made of Remazol Brilliant Blue R inoculated with an immobilised fungal strain, Pleurotus ostreatus URM 4809, as a laccase producer, in the cathodic chamber. The MFC showed continuous synthesis of laccase in the cathodic chamber, which, in turn, promoted the rapid decolourisation, of more than 86% of the textile dye effluent. The yield was further increased by the addition of glycerol. Electrochemical monitoring also indicated an increase in power density and current density. After 20 days of MFC operation, 62.1% of organic matter was removed in the anodic compartment, thus leaving the effluent with a much lower toxicity.

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Biodegradation of Remazol Brilliant Blue R using isolated bacterial culture (Staphylococcussp. K2204)

Cited by 45 publications

References 51 publications

Bacterial degradation of anthraquinone dyes

Bacterial degradation of anthraquinone dyes

Utilizing Borassus flabellifer sprout peel sugars by Pseudomonas fluorescence for degradation of textile effluent

Microbial fuel cell-induced production of fungal laccase to degrade the anthraquinone dye Remazol Brilliant Blue R

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