Abstract:Reactive dyes are pernicious pollutants in textile effluent, which are to be treated passably before discharging into the environment. In the present study, a potential dye degrading bacterial strain Pseudomonas guariconensis was isolated from paddy rhizosphere and was characterized by 16S rRNA gene sequencing. The biodegradation ability of the strain was evaluated by time‐based study with immobilized bacterial cells in calcium alginate biocarrier matrix and also with free cells. The results indicated that the… Show more
“…Even though the observed decolourisation was lower than with the addition of extra carbon sources, the consortium can completely mineralise the dye. Bacillus lentus B1377 [38] was able to achieve complete mineralisation of RR120 when supplemented with NB, on other hand, Pseudomonas gualiconensis [39] was reported to produced toxic metabolite in similar condition. Most of RR120 decolouriser needs glucose/yeast extract more than 3 g/L to achieve significant decolourisation [16,26,30,39,40].…”
Section: Discussionmentioning
confidence: 97%
“…Bacillus lentus B1377 [38] was able to achieve complete mineralisation of RR120 when supplemented with NB, on other hand, Pseudomonas gualiconensis [39] was reported to produced toxic metabolite in similar condition. Most of RR120 decolouriser needs glucose/yeast extract more than 3 g/L to achieve significant decolourisation [16,26,30,39,40]. Consortium JR3 was able to do so with the least amount of co-substrate.…”
The application of microorganisms in azo dye remediation has gained significant attention, leading to various published studies reporting different methods for obtaining the best dye decolouriser. This paper investigates and compares the role of methods and media used in obtaining a bacterial consortium capable of decolourising azo dye as the sole carbon source, which is extremely rare to find. It was demonstrated that a prolonged acclimation under low substrate availability successfully isolated a novel consortium capable of utilising Reactive Red 120 dye as a sole carbon source in aerobic conditions. This consortium, known as JR3, consists of Pseudomonas aeruginosa strain MM01, Enterobacter sp. strain MM05 and Serratia marcescens strain MM06. Decolourised metabolites of consortium JR3 showed an improvement in mung bean’s seed germination and shoot and root length. One-factor-at-time optimisation characterisation showed maximal of 82.9% decolourisation at 0.7 g/L ammonium sulphate, pH 8, 35 °C, and RR120 concentrations of 200 ppm. Decolourisation modelling utilising response surface methodology (RSM) successfully improved decolourisation even more. RSM resulted in maximal decolourisation of 92.79% using 0.645 g/L ammonium sulphate, pH 8.29, 34.5 °C and 200 ppm RR120.
“…Even though the observed decolourisation was lower than with the addition of extra carbon sources, the consortium can completely mineralise the dye. Bacillus lentus B1377 [38] was able to achieve complete mineralisation of RR120 when supplemented with NB, on other hand, Pseudomonas gualiconensis [39] was reported to produced toxic metabolite in similar condition. Most of RR120 decolouriser needs glucose/yeast extract more than 3 g/L to achieve significant decolourisation [16,26,30,39,40].…”
Section: Discussionmentioning
confidence: 97%
“…Bacillus lentus B1377 [38] was able to achieve complete mineralisation of RR120 when supplemented with NB, on other hand, Pseudomonas gualiconensis [39] was reported to produced toxic metabolite in similar condition. Most of RR120 decolouriser needs glucose/yeast extract more than 3 g/L to achieve significant decolourisation [16,26,30,39,40]. Consortium JR3 was able to do so with the least amount of co-substrate.…”
The application of microorganisms in azo dye remediation has gained significant attention, leading to various published studies reporting different methods for obtaining the best dye decolouriser. This paper investigates and compares the role of methods and media used in obtaining a bacterial consortium capable of decolourising azo dye as the sole carbon source, which is extremely rare to find. It was demonstrated that a prolonged acclimation under low substrate availability successfully isolated a novel consortium capable of utilising Reactive Red 120 dye as a sole carbon source in aerobic conditions. This consortium, known as JR3, consists of Pseudomonas aeruginosa strain MM01, Enterobacter sp. strain MM05 and Serratia marcescens strain MM06. Decolourised metabolites of consortium JR3 showed an improvement in mung bean’s seed germination and shoot and root length. One-factor-at-time optimisation characterisation showed maximal of 82.9% decolourisation at 0.7 g/L ammonium sulphate, pH 8, 35 °C, and RR120 concentrations of 200 ppm. Decolourisation modelling utilising response surface methodology (RSM) successfully improved decolourisation even more. RSM resulted in maximal decolourisation of 92.79% using 0.645 g/L ammonium sulphate, pH 8.29, 34.5 °C and 200 ppm RR120.
“…Bacterial treatment Isolation of new strains or consortia from activated sludge, oxidation ditch, palm oil mill effluent or desert soil, alkali-, haloand thermophilic strains implementation, consortium with algae, bacteria immobilization, co-substrate addition, proposal of mechanisms, pathways genome and transcriptome analysis [109][110][111][112][113][114][115][116][117][118][119] Fungal treatment Implementation of microbial consortium (e.g., yeast consortium with ability of lignin valorization dye treatment and biodiesel production), fungi immobilization, isolation of new strains from plant roots or effluent site [120][121][122][123][124][125][126][127][128][129][130] Enzyme treatment Optimization of enzyme production, enzyme immobilization, metabolites and toxicity assessment [131][132][133][134][135][136] Algal treatment…”
In the last 3 years alone, over 10,000 publications have appeared on the topic of dye removal, including over 300 reviews. Thus, the topic is very relevant, although there are few articles on the practical applications on an industrial scale of the results obtained in research laboratories. Therefore, in this review, we focus on advanced oxidation methods integrated with biological methods, widely recognized as highly efficient treatments for recalcitrant wastewater, that have the best chance of industrial application. It is extremely important to know all the phenomena and mechanisms that occur during the process of removing dyestuffs and the products of their degradation from wastewater to prevent their penetration into drinking water sources. Therefore, particular attention is paid to understanding the mechanisms of both chemical and biological degradation of dyes, and the kinetics of these processes, which are important from a design point of view, as well as the performance and implementation of these operations on a larger scale.
“…The diverse sort of dyes and chemicals used in textile manufacturing makes textile effluents very complex in terms of chemical compositions. According to previous records, in addition to dyes and its auxiliaries over 8000 chemicals are added such as several acids, salts, surfactants, metals, oxidizing and reducing agents (Reddy and Osborne 2020). These recalcitrants in untreated effluents are both harmful to marine and terrestrial organisms and have prolonged effects on health (Hamidi et al, 2014).…”
Globally, textile industries are one of the major sectors releasing dye pollutants. This is the first report on the positive correlation between toxicity and COD of textile effluent along with the proposed pathway for enzymatic degradation of acid orange 10 using Geotrichum candidum within a very short stretch of time (18h). Removal efficiency of this mycoremedial approach after 18 h in terms of color, dye concentration as well as reduction of chemical oxygen demand (COD) and biological oxygen demand (BOD) in the treated effluent reached to 89%, 87%, 98.5% and 96.3% respectively. FT-IR analysis of the treated effluent confirmed biodegradation. The LC-MS analysis showed the degradation of acid orange 10, which was confirmed by the formation of two biodegradation products, 7-oxo-8-iminonapthalene-1,3-disulfonate and nitrosobenzene, which subsequently undergoes stepwise hydrogenation and dehydration to form aniline via phenyl hydroxyl amine as intermediate. The X-ray diffraction (XRD) studies showed that heavy metals content in the treated effluent has reduced along with decrease in % crystallinity, indicating biodegradation. The connection between toxicity and COD was also inveterated using Pearson’s correlation coefficient. Further the toxicological studies indicated the toxicity of raw textile effluent and relatively lower toxic nature of metabolites generated after biodegradation by G. candidum.
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