Decolourization and Detoxification of Methyl Red by Aerobic Bacteria from A Wastewater Treatment Plant

Bacterial cultures from a wastewater treatment plant degraded a toxic azo dye (methyl red) by decolourization. Complete decolourization using a mixed-culture was achieved at pH 6, 30 °C within 6 h at 5 mg/l methyl red concentration, and 16 h at 20—30 mg/l. Four bacterial species were isolated that were capable of growth on methyl red as the sole carbon source, and two were identified, namely Vibrio logei and Pseudomonas nitroreducens. The Vibrio species showed the highest methyl red degradation activity at the optimum conditions of pH 6--7, and 30—35 °C. Analysis by NMR showed that previously reported degradation products 2-aminobenzoic acid and N,N-dimethyl-1,4-phenylenediamine were not observed. The decolourized dye was not toxic to a monkey kidney cell line (COS-7) at a concentration of 250 μM. This revised version was published online in July 2006 with corrections to the Cover Date.     

Degradation of a tannery and textile dye,Navitan Fast Blue S5R by Pseudomonas aeruginosa

The degradation of Navitan Fast Blue S5R, a very important commercial diazo dye in the tannery and textile industries was investigated. Pseudomonas aeruginosa decolourized this dye at concentrations upto 1200 mg l^–1 and the organism was also able to decolourize various other tannery dyes at different levels. The organism required ammonium salts and glucose to co-metabolize the dye. Organic nitrogen sources did not support appreciable decolourization whereas, combined with inorganic nitrogen (NH₄NO₃) there was an increased effect on both growth and decolourization. Decolourization of this dye started when the organism reached late exponential growth phase and after 24 h of incubation nearly 90% of 100 mg l^–1 of the dye was decolourized. An oxygen insensitive azoreductase was involved in the decolourization mechanism. HPLC analysis confirmed the formation of metanilic acid from the dye, which on further incubation was completely metabolized under shaken culture condition.     

Optimisation for enhanced decolourization and degradation of Reactive Red BS C.I. 111 by Pseudomonas aeruginosa NGKCTS

Soil samples collected from dye contaminated sites of Vatva, Gujarat, India were studied for the screening and isolation of organisms capable of decolourizing textile dyes. The most efficient isolate, which showed decolourization zone of 48 mm on 300 ppm Reactive Red BS (C.I.111) containing plate, was identified as Pseudomonas aeruginosa. Reactive Red BS (C.I.111) was used as a model dye for the study. The isolated culture exhibited 91% decolourization of 300 ppm dye within 5.5 h over a wide pH range from 5.0 to 10.5 and temperature ranging from 30 to 40°C. The culture was able to decolourize more than 91% of Reactive Red BS under static conditions in presence of either glucose, peptone or yeast extract. Addition of 300 ppm of Reactive Red BS, in each step, in ongoing dye decolourization flask, gave more than 90% decolourization within 2 h corresponding to 136 mg l⁻¹ h⁻¹ dye removal rate. The isolate had the ability to decolourize six different reactive dyes tested as well as the actual dye manufacturing industry’s effluent. The degradation of the dye was confirmed by HPTLC.     

Effective bioremoval of reactive dye and heavy metals by Aspergillus versicolor

In this study, bioaccumulation of heavy metal and dye by Aspergillus versicolor was investigated. Optimum pH values of the maximum heavy metal bioaccumulation was found as 6 for 50 mg/L Cr(VI), Ni(II) and 5 for Cu(II) ions with the 99.89%, 30.05% and 29.06% removal yield, respectively. The bioremoval of the dye up to 800 mg/L at pH 5 and 6 was investigated and 27.15% and 28.95% removal rates were measured respectively. The presence of Cr(VI) with dye, decreased the uptake yield for both pollutants. In the medium with Cu(II) and dye, dye removal was not affected by Cu(II), but Cu(II) removal rate increased from 29.06% to 37.91% by the existence of the dye. When Ni(II) and dye were combined, neither pollutant affected the other’s removal yield. These results indicate that the isolated A. versicolor strain deserves attention as a promising bioaccumulator of heavy metal ions and reactive dyes in wastewater effluents.     

Decolourization of Amaranth dye by bacterial biofilm in batch and continuous packed bed bioreactor

The aim of this study was to exploit the bacterial biofilms to remove dyes from industrial effluents. Biofilms of strains AK1, AK2, VKY1 and a consortium on sheep bone chips were examined in batch, repeated batch and continuous packed bed bioreactor. Biofilms are more efficient for decolourization of Amaranth dye at three different dye concentrations (200, 400, and 600 mg l⁻¹). 100% decolourization of Amaranth dye was observed even at higher concentrations (400 and 600 mg l⁻¹) by all the tested biofilms in 24 h than that of corresponding free cells. The biofilms were superior over those of free cells and could be reused for more than 18 repeated cycles. In a packed bed bioreactor, biofilms could be operated with much higher dilution rates and at lower hydraulic retention time. Further, the decolourization of dye was confirmed by UV–visible spectrophotometer, TLC and HPLC analysis of Amaranth dye degradation products from packed bed bioreactor effluent.     

Copper catechol-driven Fenton reactions and their potential role in wood degradation

Metals can potentially play a role in the non-enzymatic processes involved in wood biodegradation. Dihydroxybenzenes reduce Cu(II)–Cu(I), which then react with H₂O₂ driving a Fenton reaction. In this work the degradation of veratryl alcohol (VA), the simplest non-phenolic lignin model compound, via a cuprous Fenton reaction mediated by 1,2-dihydroxybenzene (catechol, CAT) was studied. A factorial experimental design was performed to assess the impact of several experimental variables including, pH, and CAT, CuCl₂ and H₂O₂ concentrations on VA degradation. Optimized conditions were determined using a response surface modeling methodology (RSM). The greatest amount of VA degradation occurred at a CAT:CuCl₂:H₂O₂ ratio of 0.287:0.313:4.062, a pH of 3.6. A time-course measurement for VA degradation was performed under these experimental conditions and after an 8 h reaction period, 31% of the VA was degraded. Under the same experimental conditions, VA degradation by an iron CAT-driven Fenton reaction was more effective than the copper CAT-driven Fenton reaction. In a similar experiment, carboxymethyl cellulose (CMC) depolymerization was also determined. Only the iron CAT-driven Fenton reaction was found to depolymerize CMC. We suggest that the greater redox potential of the Fe(III)CAT complex compared to the Cu(II)CAT complex would dictate that under most environmental conditions, degradation of VA would occur by the iron complex only. This research has important implications for the mechanisms of brown rot fungal degradation in wood because it eliminates a pathway that had previously been proposed as a mechanism explaining free radical generation in the oxidative depolymerization of cellulose in the cell wall.     

Adsorption of Cu(II) on Oxidized Multi-Walled Carbon Nanotubes in the Presence of Hydroxylated and Carboxylated Fullerenes

The adsorption of Cu(II) on oxidized multi-walled carbon nanotubes (oMWCNTs) as a function of contact time, pH, ionic strength, temperature, and hydroxylated fullerene (C₆₀(OH)_n) and carboxylated fullerene (C₆₀(C(COOH)₂)_n) were studied under ambient conditions using batch techniques. The results showed that the adsorption of Cu(II) had rapidly reached equilibrium and the kinetic process was well described by a pseudo-second-order rate model. Cu(II) adsorption on oMWCNTs was dependent on pH but independent of ionic strength. Compared with the Freundlich model, the Langmuir model was more suitable for analyzing the adsorption isotherms. The thermodynamic parameters calculated from temperature-dependent adsorption isotherms suggested that Cu(II) adsorption on oMWCNTs was spontaneous and endothermic. The effect of C₆₀(OH)_n on Cu(II) adsorption of oMWCNTs was not significant at low C₆₀(OH)_n concentration, whereas a negative effect was observed at higher concentration. The adsorption of Cu(II) on oMWCNTs was enhanced with increasing pH values at pH < 5, but decreased at pH ≥ 5. The presence of C₆₀(C(COOH)₂)_n inhibited the adsorption of Cu(II) onto oMWCNTs at pH 4–6. The double sorption site model was applied to simulate the adsorption isotherms of Cu(II) in the presence of C₆₀(OH)_n and fitted the experimental data well.     

Production and characterization of laccase from Cyathus bulleri and its use in decolourization of recalcitrant textile dyes

Many fungi (particularly the white rot) are well suited for treatment of a broad range of textile dye effluents due to the versatility of the lignin-degrading enzymes produced by them. We have investigated decolourization of a number of recalcitrant reactive azo and acid dyes using the culture filtrate and purified laccase from the fungus Cyathus bulleri. For this, the enzyme was purified from the culture filtrate to a high specific activity of 4,022 IU mg⁻¹ protein, produced under optimized carbon, nitrogen and C/N ratio with induction by 2,6-dimethylaniline. The protein was characterized as a monomer of 58±5.0 kDa with carbohydrate content of 16% and was found to contain all three Cu(II) centres. The three internal peptide sequences showed sequence identity (80–92%) with laccases of a number of white rot fungi. Substrate specificity indicated highest catalytic efficiency (k _cat/K _M) on guaiacol followed by 2,2′-azino-bis(3-ethylthiazoline-6-sulfonic acid) (ABTS). Decolourization of a number of reactive azo and acid dyes was seen with the culture filtrate of the fungus containing predominantly laccase. In spite of no observable effect of purified laccase on other dyes, the ability to decolourize these was achieved in the presence of the redox mediator ABTS, with 50% decolourization in 0.5–5.4 days.     

In vivo decolourization of the polymeric dye poly R‐478 by corncob cultures of Phanerochaete chrysosporium

In this paper, the in vivo decolourization of the polymeric dye Poly R‐478 by semi‐solid‐state cultures of Phanerochaete chrysosporium BKM‐F‐1767 (ATCC 24725) was investigated, employing corncob as a support. In order to stimulate the ligninolytic system of the fungus, the cultures were supplemented with veratryl alcohol (2 mM) or manganese (IV) oxide (1 g/l). Maximum manganese‐dependent peroxidase (MnP) and lignin peroxidase (LiP) activities of around 2,000 U/l and 400 U/l were attained by the former, whereas the activities reached by the latter were of about 1,500 U/l and 200 U/l, respectively. Furthermore, laccase activity (around 150 U/l) was only detected in manganese (IV) oxide supplemented cultures. The polymeric dye Poly R‐478 (0.02 w/v) was added to three‐day‐old cultures. A percentage of biological decolourization of about 85% was achieved using cultures supplemented with veratryl alcohol, whereas MnO₂ cultures showed a rather lower percentage of around 58% after nine days of dye incubation. Moreover, a correlation between MnP activity and Poly R‐478 decolourization could be observed, indicating that this enzyme is mainly responsible for dye degradation. In the present work, the in vivo decolourizing capability of the ligninolytic complex secreted by P. chrysosporium was investigated under the above‐mentioned cultivation conditions, employing a model compound, such as the polymeric dye Poly R‐478.     

Potentiometric and spectroscopic studies on the solution molecular structures of copper(II)-[S]-2-[N-(2′-hydroxybenzyl)aminomethyl]pyrrolidine complexes, potential non-steroidal anti-inflammatory agents (NSAIDs)

The purpose of this study was to investigate the complexes formed by copper(II) with potential non-steroidal anti-inflammatory agents (NSAIDs) under physiological conditions. A former study suggested that 2-benzylaminomethylpyrrolidine ligands could be good candidates as potential OIL (OH-inactivating ligand) when complexed to copper(II). In order to assess the chemical behavior as OIL, [S]-2-[N-(2′-hydroxybenzyl)aminomethyl]pyrrolidine (OHbamp) was synthesized and bound to copper(II). Physico-chemical properties were determined at 37 °C in 0.15 M NaCl using glass electrode potentiometry, UV-Vis and circular dichroism spectroscopies, before and after copper(II) complexation. [Cu(OHbamp)(H₂O)₃]⁺ was the main complex found at both physiological and inflammatory pH values, showing appreciable stability at pathological pH compared to copper(II) complexes of histidine, the predominant low-molar-mass ligand of copper(II) in blood plasma. However, neutral species such as [Cu(OHbamp)₂(H₂O)₂] and [Cu(OHbamp)(OH)(H₂O)₃] are predominant only above pH 8, preventing a significant amount of drug from diffusing through membranes at inflammatory pH. In conclusion, copper(II)-OHbamp system does not meet all the requirements to be an OIL. Nevertheless, these results allow us to better identify the chemical features needed for a good OIL candidate.     

Circular dichroic studies on Cu(II) interactions with a protamine,scylliorhinine Z3

The interaction of Cu(II) with the protamine scylliorhinine Z₃ was studied by means of CD measurements. At a 1:1 molar ratio, three complexes are formed. (1) In the pH range 5–6.5, the results suggest the formation of a five-membered chelate ring through the coordination of two nitrogen atoms, the N-terminal and the contiguous peptide nitrogen. (2) At pH ≥ 6.4, there is involvement of the lateral NH₂ group of Arg; at pH 6.5–8, the formation of a 3N cupric complex is strongly suggested. (3) At pH ≥ 8, results indicate the formation of a 4N complex as a major species in Cu(II)-Z₃ solution. The transformation from a 2N to a 3N complex, and from a 3N to a 4N complex was followed with the help of the σ(αNH₂) → Cu(II) charge-transfer dichroic band transitions. At Cu(II):Z₃ molar ratios ≥ 2 and at pH > 8, a new dichroic band appears, indicating the involvement of the tyrosine residue side chain in metal-ion complexation.     

Biodegradation of C.I. Reactive Red 195 by <Emphasis Type="Italic">Enterococcus faecalis</Emphasis> strain YZ66

Synthetic dyes are extensively used in textile dyeing, paper, printing, colour photography, pharmaceutics, cosmetics and other industries. Among these, azodyes represents the largest and most versatile class of synthetic dyes. As high as 50% of the dyes are released into the environment during manufacture and usage. Traditional methods of treatment are found to be expensive and have operational problems. Biological decolourization has been investigated as a method to transform, degrade or mineralize azo dyes. In the present studies bacteria from soil from dye waste area, dye waste, sewage and dung were subjected to acclimatization with C.I. Reactive Red 195 an azo dye, in the basal nutrient media. The most promising bacterial isolate was used for further dye degradation studies. The 16s rRNA gene sequencing and biochemical characteristics revealed the isolated organism as Enterococcus faecalis strain YZ66. The strain showed 99.5% decolourization of the selected dye (Reactive Red 195–50 mg/l) within one and half hour in static anoxic condition. The optimum pH and temperature for the decolourization was 5.0 and 40°C respectively. The biodegradation was monitored by UV–Vis, FTIR, TLC and HPLC. The final products were characterized by Gas chromatography and Mass Spectrophotometry. Toxicity study demonstrated no toxicity of the biodegradation product. The results suggest that the isolated organism E. faecalis strain YZ 66 can be used as a useful tool to treat waste water containing reactive dyes.     

Evaluation and elimination of inhibitory effects of salts and heavy metal ions on biodegradation of Congo red by Pseudomonas sp. mutant

In this study, it was attempted to evaluate the influences and also recommended some elimination methods for inhibitory effects offered by salts and heavy metal ions. Congo red dye solution treated with mutant Pseudomonas sp. was taken as a model system for study. The salts used in this study are NaCl, CaCl₂ and MgSO₄·7H₂O. Though the growth was inhibited at concentrations above 4 g/l, toleration was achieved by acclimatization process. In case of heavy metal ions, Cr (VI) showed low inhibition up to 500 mg/l of concentration, compared to Zn (II) and Cu (II). It was due to the presence of chromium reductase enzyme which was confirmed by SDS-PAGE. Zn (II) and Cu (II) ion inhibitions were eliminated by chelation with EDTA. The critical ion concentrations obtained as per Han-Levenspiel model for Cr (VI), Zn (II) and Cu (II) were 0.8958, 0.3028 and 0.204 g/l respectively.     

Decolourization of textile dye Reactive Violet 5 by a newly isolated bacterial consortium RVM 11.1

Summary Soil samples collected from contaminated sites of Vatva, Gujarat, India were studied for screening and isolation of organisms capable of decolourizing textile dyes. A bacterial consortium RVM 11.1 was selected on the basis of rapid dye decolourization. Reactive Violet 5 (RV 5) was used as model dye. The consortium exhibited 94% decolourization ability within 37 h under a wide pH range from 6.5 to 8.5 and temperature ranging from 25 to 40 °C. The bacterial consortium was able to grow and decolourize RV5 under static conditions in the presence of glucose and yeast extract and also showed an ability to decolourize in the presence of starch in place of glucose. Maximum decolourization efficiency was observed at 200 ppm (mg/l) concentration of RV 5. Bacterial consortium RVM11.1 had the ability to decolourize 10 different dyes tested. The transformation and degradation products after decolourization were examined by HPTLC.     

Malachite green decolourization and detoxification by the laccase from a newly isolated strain of Trametes sp.

The decolourization and detoxification of the triarylmethane dye Malachite green (MG) by laccase from Trametes sp. were investigated. The laccase decolorized efficiently the dye down to 97% of 50 mg L^?1 initial concentration of MG when only 0.1 U mL^?1 of laccase was used in the reaction mixture. The effects of different physicochemical parameters were tested and optimal decolourization rates occurred at pH 6 and at temperatures between 50 and 60 °C. Decolourization of MG occurred in the presence of metal ions which could be found in textile industry effluent. 1-hydroxybenzotriazole (HBT) affected positively the decolourization of MG. The presence of some phenolic compounds namely ferulic, coumaric, gallic, and tannic acids was found to be inhibiting for the decolourization at a concentration of 10 mM.The effect of laccase inhibitors in the decolourization of MG was tested with l-cysteine, and ethylene diamine tetra-acetic acid (EDTA) at concentrations of 0.1, 1 and 10 mM. It was demonstrated that l-cysteine and EDTA inhibited the decolourization starting from 1 mM concentration. However, for NaCl a concentration of 100 mM was needed for the inhibition of laccase. The decolourization of MG resulted in the removal of its toxicity against Phanerochaete chrysosporium.The stability of the laccase toward temperature and HBT free radicals was also assessed during MG decolourization. It was shown that laccase was stable at 50 °C but in the presence of the laccase mediator HBT, the stability of the enzyme was severely affected resulting in a loss of 50% of the activity after 3 h incubation.     

Enhanced decolourization of Direct Red-80 dye by the white rot fungus <Emphasis Type="Italic">Phanerochaete chrysosporium</Emphasis> employing sequential design of experiments

Decolourization of Direct Red 80 (DR-80) by the white rot fungus Phanerochaete chrysosporium MTCC 787 was investigated employing sequential design of experiments. Media components for growing the white rot fungus were first screened using Plackett-Burman design and then optimized using response surface methodology (RSM), which resulted in enhancement in the efficiency of dye removal by the fungus. For determining the effect of media constituents on the dye removal, both percent dye decolourization and specific dye removal due to maximum enzyme activity were chosen as the responses from the experiments, and the media constituents glucose, veratryl alcohol, KH₂PO₄, CaCl₂ and MgSO₄ were screened to be the most effective with P values less than 0.05. Central composite design (CCD) followed by RSM in the optimization study revealed the following optimum combinations of the screened media constituents: glucose, 11.9 g l⁻¹; veratryl alcohol, 12.03 mM; KH₂PO₄, 23.08 g l⁻¹; CaCl₂, 2.4 g l⁻¹; MgSO₄, 10.47 g l⁻¹. At the optimum settings of the media constituents, complete dye decolourization (100% removal efficiency) and a maximum specific dye removal due to lignin peroxidase enzyme of 0.24 mg U⁻¹ by the white rot fungus were observed.     

Synthesis,structure and a fourier transform infrared study of Pt(II), Cu(II), and Mg(II) Complexes with xanthosine-5′-monophosphate

The reaction of xanthosine-5′'-monophosphate disodium salt (5′-XMPNa₂) with Pt(II), Cu(II) and Mg(II) ions produced compounds of the type cis- and trans-Pt(NH₃)₂(XMPNa₂)_nCl₂·xH₂O, where n = 1 or 2; Pt(XMPNa₂)_nCl₂·xH₂O, where n = 1-4, x = 1,4 & 6; Cu(XMP)·6H₂O and Mg(XMP)·xH₂O, where x = 9 or 4. In the complexes synthesized here at neutral pH values, the nucleotide binds through the N_7-atom of the purine ring system, whereas for Cu(II) and Mg(II) compounds obtained at pH = 4 a direct metal-phosphate interaction as well as N_τ bonding is proposed.     

Hydrothermal syntheses and characterizations of 0D to 3D polyoxotungstates linked by copper ions

A new family of hybrid organic-inorganic materials built from polyoxotungstates and Cu(II) ions as linkers has been synthesized by hydrothermal reactions from a mixture of sodium tungstate, copper chloride and ethylenediamine. The initial pH and the presence or absence of heteroelement (P, Si) control the nature of the polyoxotungstate clusters and their connectivity via the copper ions, and hence the dimensionality of the framework. In the absence of heteroelement, three compounds have been isolated: at low pH (5) the molecular compound [Cu(en)₂(H₂O)]₂[{Cu(en)₂}H₂W₁₂O₄₀] · 10H₂O (1) is formed, at neutral pH the 3D material [{Cu(en)₂}₃{Cu(en)}₂H₂W₁₂O₄₂] · 27H₂O (2) and at high pH (11) the 2D compound [Cu(en)₂(H₂O)₂][Cu(en)₂][{Cu(en)₂}₃H₂W₁₂O₄₂] · 15H₂O (3). In the whole range of pH (5-11.5) a single phase has been obtained with silicium as heteroelement, namely the 2D material [Cu(en)₂(H₂O)][{Cu(en)₂}₂SiW₁₁CuO₃₉] · 7H₂O (4) with chains of Keggin polyoxotungstates linked by {Cu(en)₂}²⁺ groups. Finally, a phosphotungstate with a chain-like structure has been characterized, [{Cu(en)₂}₃PW₁₁CuClO₃₉] · 6H₂O (5), at low pH (5) which differs from the phase obtained at higher pH.     

Study of copper(II) and nickel(II) ternary complexes involving tertiary amines and phenyl or hydroxylphenyl substituted amino acids

Formation constants of ternary complexes MAL, where M = Cu(II) or Ni(II). A = 2.2′bipyridyl. 1, 10-phenanthroline, and L = 3.4-dihydroxyphenylalanine (dopa), tyrosine, or phenylalanine have been determined by using the computer program SCOGS. It is observed that dopa coordinates with Cu(II)-A and Ni(II)-A through the aminocarboxylate and only over the pH range 3–8, though the ligand coordinates with free Cu(II) ion from the amino carboxylate end in the lower pH range (pH 2–4) and from the catechol end at the higher pH range (pH > 5). The visible spectrum of Cu-A-dopa is similar to that of Cu-A-phenylalanine or Cu-A-tyrosine over the entire pH range, confirming amino carboxylate coordination. Δ log K (K_MAL - log_KML) is found to be positive in all the six Cu(II) complexes. whereas it is negative in Ni(II) complexes. Release in the ternary complexes of the repulsion between the Cu(II) dπ electron and electrons delocalized over the phenyl ring has been proposed as a probable reason for the positive Δ log K.     

Binding of copper(II) to thyrotropin-releasing hormone (TRH) and its analogs

Spectroscopy (UV-Vis, ¹H NMR, ESR) and electrochemistry revealed details of the structure of the Cu(II)-TRH (pyroglutamyl-histidyl-prolyl amide) complex. The ¹H NMR spectrum of TRH has been assigned. NMR spectra of TRH in the presence of Cu(II) showed that Cu(II) initially binds TRH through the imidazole. TRH analogs, pGlu-His-Pro-OH, pGlu-(1-Me)His-Pro-amide, pGlu-His-(3,4-dehydro)Pro-amide, pGlu-His-OH, pGlu-Glu-Pro-amide, and pGlu-Phe-Pro-amide provided comparison data. The stoichiometry of the major Cu(II)-TRH complex at pH 7.45 and greater is 1:1. The conditional formation constant (in pH 9.84 borate with 12.0 mM tartrate) for the formation of the complex is above 10⁵ M⁻¹. The coordination starts from the 1-N of the histidyl imidazole, and then proceeds along the backbone involving the deprotonated pGlu-His amide and the lactam nitrogen of the pGlu residue. The fourth equatorial donor is an oxygen donor from water. Hydroxide begins to replace the water before the pH reaches 11. Minority species with stoichiometry of Cu-(TRH)_x (x = 2-4) probably exist at pH lower than 8.0. In non-buffered aqueous solutions, TRH acts as a monodentate ligand and forms a Cu(II)-(TRH)₄ complex through imidazole nitrogens. All the His-containing analogs behave like TRH in terms of the above properties.