Potential of Typha angustifolia for phytoremediation of heavy metals from aqueous solution of phenol and melanoidin

Typha angustifolia was evaluated for various heavy metals (Cu, Pb, Ni, Fe, Mn, and Zn) bioremediation potential from aqueous solution containing variable concentrations of phenol (100–800 mg l^?1) and melanoidin (2500–8500 Co–Pt) at 20, 40, and 60 days. The concentration of phenol (200–400 mg l^?1) along with melanoidin 2500 Co–Pt showed optimum for phytoremediation of tested heavy metals, while, higher concentrations of melanoidin (5600–8500 Co–Pt) showed toxic effect on T. angustifolia along with phenol. Phenol and melanoidin showed adverse effect on T. angustifolia of up to 20 days incubation, but this leads to induction of peroxidase and ascorbic acid activity to cope with adverse conditions. Subsequently, as pollutants were decreased along with plant growth, peroxidase and ascorbic acid also declined. However, with reduction of peroxidase, catalase level was increased. The Cu, Zn, and Ni were accumulated at maximum in all tested conditions. The TEM observations of T. angustifolia showed clotted deposition of metals and shrinkage of cell in root, breakdown of spongy and palisade parenchyma of leaves at higher concentration of phenol (100 mg l^?1) and melanoidin (5500 Co–Pt). Thus, this study concluded that T. angustifolia could be a potential phytoremediator for heavy metals from metal, melanoidin, and phenol containing industrial wastewater at optimized condition.     

Sequential degradation of <Emphasis Type="Italic">p</Emphasis>-cresol by photochemical and biological methods

Sequential photo-and biodegradation of p-cresol was studied using a mercury lamp, as well as KrCl and XeCl excilamps. Preirradiation of p-cresol at a concentration of 10^?4 M did not affect the rate of its subsequent biodegradation. An increase in the concentration of p-cresol to 10^?3 M and in the duration preliminary UV irradiation inhibited subsequent biodegradation. Biodegradation of p-cresol was accompanied by the formation of a product with a fluorescence maximum at 365 nm (λ_ex = 280 nm), and photodegradation yielded a compound fluorescing at 400 nm (λ_ex = 330 nm). Sequential UV and biodegradation led to the appearance of bands in the fluorescence spectra that were ascribed to p-cresol and its photolysis products. It was shown that sequential use of biological and photochemical degradation results in degradation of not only the initial toxicant but also the metabolites formed during its biodegradation.     

Demonstration of Laccase in the White Rot Basidiomycete Phanerochaete chrysosporium BKM-F1767

It has been widely reported that the white rot basidiomycete Phanerochaete chrysosporium, unlike most other white rot fungi, does not produce laccase, an enzyme implicated in lignin biodegradation. Our results showed that P. chrysosporium BKM-F1767 produces extracellular laccase in a defined culture medium containing cellulose (10 g/liter) and either 2.4 or 24 mM ammonium tartrate. Laccase activity was demonstrated in the concentrated extracellular culture fluids of this organism as determined by a laccase plate assay as well as a spectrophotometric assay with ABTS [2,2(prm1)-azinobis(3-ethylbenzathiazoline-6-sulfonic acid)] as the substrate. Laccase activity was observed even after addition of excess catalase to the extracellular culture fluid to destroy the endogenously produced hydrogen peroxide, indicating that the observed activity is not due to a peroxidase. Sodium dodecyl sulfate-polyacrylamide gel electrophoresis followed by activity staining with ABTS revealed the presence of a laccase band with an estimated M(infr) of 46,500.     

Effect of Concentration of Organic Chemicals on Their Biodegradation by Natural Microbial Communities

The effect of concentration on the biodegradation of synthetic organic chemicals by natural microbial communities was investigated by adding individual ¹⁴C-labeled organic compounds to stream water at various initial concentrations and measuring the formation of ¹⁴CO₂. The rate of degradation of p-chlorobenzoate and chloroacetate at initial concentrations of 47 pg/ml to 47 μg/ml fell markedly with lower initial concentrations, although half or more of the compound was converted to CO₂ in 8 days or less. On the other hand, little mineralization of 2,4-dichlorophenoxyacetate and 1-naphthyl-N-methylcarbamate, or the naphthol formed from the latter, occurred when these compounds were present at initial concentrations of 2 to 3 ng/ml or less, although 60% or more of the chemical initially present at higher concentrations was converted to CO₂ in 6 days. It is concluded that laboratory tests of biodegradation involving chemical concentrations greater than those in nature may not correctly assess the rate of biodegradation in natural ecosystems and that low substrate concentration may be important in limiting biodegradation in natural waters.     

Degradation of Carbazole by Microbial Cells Immobilized in Magnetic Gellan Gum Gel Beads

Polycyclic aromatic heterocycles, such as carbazole, are environmental contaminants suspected of posing human health risks. In this study, we investigated the degradation of carbazole by immobilized Sphingomonas sp. strain XLDN2-5 cells. Four kinds of polymers were evaluated as immobilization supports for Sphingomonas sp. strain XLDN2-5. After comparison with agar, alginate, and κ-carrageenan, gellan gum was selected as the optimal immobilization support. Furthermore, Fe₃O₄ nanoparticles were prepared by a coprecipitation method, and the average particle size was about 20 nm with 49.65-electromagnetic-unit (emu) g⁻¹ saturation magnetization. When the mixture of gellan gel and the Fe₃O₄ nanoparticles served as an immobilization support, the magnetically immobilized cells were prepared by an ionotropic method. The biodegradation experiments were carried out by employing free cells, nonmagnetically immobilized cells, and magnetically immobilized cells in aqueous phase. The results showed that the magnetically immobilized cells presented higher carbazole biodegradation activity than nonmagnetically immobilized cells and free cells. The highest biodegradation activity was obtained when the concentration of Fe₃O₄ nanoparticles was 9 mg ml⁻¹ and the saturation magnetization of magnetically immobilized cells was 11.08 emu g⁻¹. Additionally, the recycling experiments demonstrated that the degradation activity of magnetically immobilized cells increased gradually during the eight recycles. These results support developing efficient biocatalysts using magnetically immobilized cells and provide a promising technique for improving biocatalysts used in the biodegradation of not only carbazole, but also other hazardous organic compounds.     

Relationship between the Molecular Weight and the Color Intensity of Color Components of Melanoidin from the Glycine-Xylose System

The molecular weights of color components (designated as P1, P2, P3, P4, P5, P6, P7 and P8 in order of elution from a DEAE-cellulose column) isolated by the conversion of color components of melanoidin produced from the glycine-xylose system in an oxidative browning were studied in relation to the color intensity. The molecular weights of P5, P6, P7 and P8 estimated by gel filtration on Sephadex G–50, G–75 and G–150 using dextran as a standard were approximately 2,140, 3,550, 5,600 and 14,200, respectively. The molecular weights of P1, P2, P3 and P4 could not be estimated by the gel filtration method because of their low values.

On the other hand, a linear relationship between Kd, the distribution coefficient in dextran gel, and E₄₅₀ (E) of the color components was observed. Thus, there is considered to be a linear relationship between log E and log molecular weight (M). The correlation coefficient between log E and log M was calculated to be from 0.96 to 0.98 in the visible wavelength region. Therefore, the equation, E=k × M^α was adopted. The value, E=2.15 × M^0.29 was obtained from melanoidin prepared from the glycine-xylose system. The molecular weights of P1, P2, P3 and P4 were calculated from the equation to be 290, 360, 700 and 1,200, respectively. The equation, E=k × M^α, was demonstrated to be reasonably applicable to the melanoidin from Glu-, Lys-, Gly₂-, Gly-Leu-, and Gly₃-xylose systems. It is concluded that the polymerization of the structural unit in melanoidin occurs in an oxidative browning and that their color tone is darkened and the color in melanoidin is increased by polymerization according to the equation, E=k × M^α.     

Purification and Some Properties of Melanoidin Decolorizing Enzymes,P-III and P-IV,from Mycelia of Coriolus versicolor Ps4a

Melanoidin decolorizing enzymes (MDE) were extracted from mycelia of Coriolus versicolor Ps4a and purified by DEAE-Sephadex, DEAE-Sephacel and Sephadex G-200 column chromatographies. MDE of this strain consisted of a main fraction, P-fraction, and a minor fraction, E-fraction, and the P-fraction was composed of at least five enzymes. P-III and P-IV in the P-fraction were picked as typical enzymes of this strain, and their enzymatic properties were investigated. P-III had a molecular weight of 48,400 ~ 50,000, an optimum pH of 5.5 and an optimum temperature of 30~35°C. P-III required glucose and 02 for the appearance of the activity, and was inhibited by p-CMB, N-BSI, Ag⁺ and o-phenanthroline.

On the other hand, P-IV had a molecular weight of 43,800 ~ 45,000, an optimum pH of 4.0~4.5 and an optimum temperature of 30~35°C. P-IV could decolorize melanoidin in the absence of glucose and O₂, and was inhibited weakly by Ag⁺, p-CMB and N-BSI. P-IV is the enzyme that attacks the melanoidin directly in comparison with P-III which attacks melanoidin indirectly as in the sub-reaction of sugar oxidase.

Incidentally, a multiplicative effect between P-III and P-IV for decolorization was observed.     

Kinetics of phenol degradation using Pseudomonas putida MTCC 1194

Pseudomonas putida (MTCC 1194) has been used to degrade phenol in water in the concentration range 100–1000?ppm. The inhibition effects of phenol as substrate have become predominant above the concentration of 500?ppm (5.31?mmoles/dm³). The optimum temperature and initial pH required for maximum phenol biodegradation were 30?°C and 7.00 respectively. From the degradation data the activation energy (E _a ) was found to be equal to 13.8?kcal/g mole substrate reacted. The most suitable inoculum age and volume for highest phenol degradation were 12?hrs and 7% v/v respectively. Surfactants had negligible effect on phenol biodegradation process for this microorganism. Monod model has been used to interpret the free cell data on phenol biodegradation. The kinetic parameters have been estimated upto initial concentration of 5.31?mmoles/dm³. μ _max and K _S gradually increased with higher concentration of phenol. However, beyond the phenol concentration of 5.31?mmoles/dm³, the inhibition became prominant. The μ _max has been to be a strong function of initial phenol concentration. The simulated and the experimental phenol degradation profiles have good correspondence with each other.     

Kinetics and pathway of biodegradation of dibutyl phthalate by Pleurotus ostreatus

Dibutyl phthalate (DBP) is a plasticizer, whose presence in the environment as a pollutant has attained a great deal of attention due to its reported association with endocrine system disturbances on animals. Growth parameters, glucose uptake, percentage of removal efficiency (%E) of DBP, biodegradation constant of DBP (k) and half-life of DBP biodegradation (t_1/2) were evaluated for Pleurotus ostreatus grown on media containing glucose and different concentrations of DBP (0, 500 and 1000 mg l^?1). P. ostreatus degraded 99.6 % and 94 % of 500 and 1000 mg of DBP l^?1 after 312 h and 504 h, respectively. The k was 0.0155 h^?1 and 0.0043 h^?1 for 500 and 1000 mg of DBP l^?1, respectively. t_1/2 was 44.7 h and 161 h for 500 and 1000 mg of DBP l^?1, respectively. Intermediate compounds of biodegraded DBP were identified by GC-MS and a DBP biodegradation pathway was proposed using quantum chemical calculation. DBP might be metabolized to benzene and acetyl acetate, the first would be oxidated to muconic acid and the latter would enter into the Krebs cycle. P. ostreatus has the ability to degrade DBP and utilizes it as source of carbon and energy.     

Biodegradation of 4-bromophenol by Arthrobacter chlorophenolicus A6 in batch shake flasks and in a continuously operated packed bed reactor

The present study investigated growth and biodegradation of 4-bromophenol (4-BP) by Arthrobacter chlorophenolicus A6 in batch shake flasks as well as in a continuously operated packed bed reactor (PBR). Batch growth kinetics of A. chlorophenolicus A6 in presence of 4-BP followed substrate inhibition kinetics with the estimated biokinetic parameters value of μ _max = 0.246 h^?1, K _i = 111 mg L^?1, K _s  = 30.77 mg L^?1 and K = 100 mg L^?1. In addition, variations in the observed and theoretical biomass yield coefficient and maintenance energy of the culture were investigated at different initial 4-BP concentration. Results indicates that the toxicity tolerance and the biomass yield of A. chlorophenolicus A6 towards 4-BP was found to be poor as the organism utilized the substrate mainly for its metabolic maintenance energy. Further, 4-BP biodegradation performance by the microorganism was evaluated in a continuously operated PBR by varying the influent concentration and hydraulic retention time in the ranges 400–1,200 mg L^?1 and 24–7.5 h, respectively. Complete removal of 4-BP was achieved in the PBR up to a loading rate of 2,276 mg L^?1 day^?1.     

Screening of Microorganisms to Decolorize a Model Melanoidin and the Chemical Properties of a Microbially Treated Melanoidin

A microbe of Streptomyces werraensis TT 14, which was newly isolated from soil, decolorized the model melanoidin prepared from glucose and glycine, the decolorization rate being 64% in the optimal medium of pH 5.5 (2.0% starch, 1.0% yeast, 0.3% NaCl, and 0.3% CaC0₃) and 45% in a synthetic medium. There was virtually no difference in the UV-VIS absorption spectra of the microbially treated melanoidin and the control. The peaks of the gel permeation chromatogram for the treated melanoidin and for the control showed the same retention times, but lower molecular weight compounds increased in the decolorized melanoidin. The Cu(II)-chelating activity of the decolorized melanoidin was reduced to about half that of the control. The melanoidin component of pI 2.5 was increased and that of pI 3.5 was reduced by the microbial treatment.     

Simultaneous biodegradation ofp-cresol and phenol by the basidiomycetePhanerochaete chrysosporium

Summary The fungusPhanerochaete chrysoporium BKM-F-1767 was able to degrade high concentrations ofp-cresol (up to 150 mg L^–1) provided that glucose was added as a carbon and energy source and conditions favourable to ligninolytic enzyme activities were used, i.e. a nitrogen-limited medium. The fungus also simultaneously degradedp-cresol (50 mg L^–1) and phenol (50 mg L^–1) in a mixture at similar rates. Kinetics ofp-cresol biodegradation were almost identical whether the compound was tested individually or in a mixture with phenol.     

Resistance of alkylphenol ethoxylate containing six ethoxylene units to biodegradation under the conditions of OECD (Organization for Economic Co-operation and Development) screening test

Biodegradation of a commercially available mixture of octylphenol ethoxylates (Triton X-100) under the condition of OECD 301E screening test was studied by using electrospray ionisation mass spectrometry. It was found that ethoxylate containing six ethoxylene units (OPEO₆) is more resistant to the biodegradation process than other ethoxylates (e.g. than OPEO₅ and OPEO₇). After 40 days of biodegradation process the signal of OPEO₆ was clearly seen, but signals of OPEO₅ and OPEO₇ were not detected. After 40 days, all OPEO_n with n > 4 were converted into carboxylated derivatives. Carboxylated derivatives were observed in negative ion mode as OPEO_n-CH₂COO^? ions. Biodegradation of OPEO₅-CH₂COOH (carboxylated derivative correspondent of OPEO₆) occurred slower than biodegradation of the others, as resulted from obtained ESI mass spectra.     

Isolation of Trilobatin,a Sweet Dihydrochalcone-Glucoside from Leaves of Vitis piasezkii Maxim. and V. saccharifera Makino

The effect of melanoidin, prepared with a D-glucose and glycine system, on cholesterol metabolism in rats was examined. Male rats of the Wistar strain weighing ca. 140 g were fed a high-cholesterol diet supplemented with nondialyzable melanoidin for three weeks. The dietary melanoidin suppressed elevation of the cholesterol level in both plasma and liver, while the cholesterol levels in feces and the contents of the caecum decreased unexpectedly. Neutral steroids other than cholesterol also decreased. However, chromatograhy of fecal steroids indicated that melanoidin markedly affected the intestinal metabolism of neutral steroids, including cholesterol. On the other hand, the fecal recovery of radioactivity from orally ingested 26 [27]-¹⁴C cholesterol was promoted by the added melanoidin, although the radioactive species were not identified. This suggested that the cholesterol level decreased due to the interference of melanoidin in the intestinal absorption of cholesterol.     

UV photolysis for accelerated quinoline biodegradation and mineralization

Sequentially and intimately coupled photolysis with biodegradation were evaluated for their ability to accelerate quinoline-removal and quinoline-mineralization kinetics. UV photolysis sequentially coupled to biodegradation significantly improved biomass-growth kinetics, which could be represented well by the Aiba self-inhibition model: UV photolysis increased the maximum specific growth rate (μ _max) by 15 %, and the inhibition constant (K _SI) doubled. An internal loop photo-biodegradation reactor (ILPBR) was used to realize intimately coupled photolysis with biodegradation. The ILPBR was operated with batch experiments following three protocols: photolysis alone (P), biodegradation alone (B), and intimately coupled photolysis and biodegradation (P&B). For P&B, the maximum quinoline removal rate (r _max) increased by 9 %, K _SI increased by 17 %, and the half-maximum-rate concentration (K _S) decreased by 55 %, compared to B; the composite result was a doubling of the quinoline-biodegradation rate for most of the concentration range tested. The degree of mineralization was increased by both forms of photolysis coupled to biodegradation, and the impact was greater for intimate coupling (18 % increase) than sequential coupling (5 %). The benefits of UV photolysis were greater with intimate coupling than with sequential coupling due to parallel transformation by biodegradation and photolysis.     

Management of soybean oil refinery wastes through recycling them for producing biosurfactant using Pseudomonas aeruginosa MR01

Biosurfactant production through a fermentation process involving the biodegradation of soybean oil refining wastes was studied. Pseudomonas aeruginosa MR01 was able to produce extracellular biosurfactant when it was cultured in three soybean oil refinement wastes; acid oil, deodorizer distillate and soapstock, at different carbon to nitrogen ratios. Subsequent fermentation kinetics in the three types of waste culture were also investigated and compared with kinetic behavior in soybean oil medium. Biodegradation of wastes, biosurfactant production, biomass growth, nitrate consumption and the number of colony forming units were detected in four proposed media, at specified time intervals. Unexpectedly, wastes could stimulate the biodegradation activity of MR01 bacterial cells and thus biosurfactant synthesis beyond that of the refined soybean oil. This is evident from higher yields of biodegradation and production, as revealed in the waste cultures (Y_{deg|(Soybean oil)} = 53.9 % < Y_deg|(wastes) and Y_P/S|(wastes) > Y_{P/S|(Soybean oil)} = 0.31 g g^?1, respectively). Although production yields were approximately the same in the three waste cultures (Y_P/S|(wastes) ? 0.5 g g^?1), microbial activity resulted in higher yields of biodegradation (96.5 ± 1.13 %), maximum specific growth rate (μ _max  = 0.26 ± 0.02 h^?1), and biosurfactant purity (89.6 %) with a productivity of 14.55 ± 1.10 g l^?1, during the bioconversion of soapstock into biosurfactant. Consequently, applying soybean oil soapstock as a substrate for the production of biosurfactant with commercial value has the potential to provide a combination of economical production with environmental protection through the biosynthesis of an environmentally friendly (green) compound and reduction of waste load entering the environment. Moreover, this work inferred spectrophotometry as an easy method to detect rhamnolipids in the biosurfactant products.     

A Red,Fluorescent Protein from Silkworm

Nondiffusable melanoidin obtained from a glycine-xylose system was heated in aqueous media, and the resulting chemical changes, as affected by the presence of oxygen, pH value, temperature and the addition of transitional metals, were investigated.

Melanoidin, when heated at 90°C in an aqueous solution, caused remarkable discolorization accompanied by the development of fluorescence, oxygen consumption and a noticeable variation of reductone content. Heated melanoidin became polydispersive in molecular weight on gel filtration chromatograms. There appeared reductones, ninhydrin-positive substances, fluorescent substances, aromatic amines, aliphatic carbonyls, and aliphatic primary amines and/or methylene groups in diffusâtes of melanoidin heated in various media.

An increase in pH value favored oxidative discolorization, while an increase in the concentration of transitional metals except Mn²⁺ restrained the discolorization. In the absence of oxygen, heated melanoidin brought about a slight strengthening of color and the accumulation of reductones ca. fifteen times more than the initial level, while in the presence of oxygen the increase of reductone content at the early period was followed by a rapid decrease.

According to the results obtained, the ambivalent reactivity of melanoidin, i.e. polymerization (colorization) and depolymerization (discolorization), was discussed in relation to influencing factors. A mechanism for the production of reductones in heated melanoidin was also proposed.     

Sulfate reduction and trichloroethylene biodegradation by a marine microbial community from hydrothermal vents sediments

Sulfate reduction (SR) and trichloroethylene (TCE) biodegradation at two different temperatures (37 and 70 °C) were investigated in enrichment cultures prepared with two different samples of sediments collected from hydrothermal vents. The unadapted sediments were incubated with sulfate (4 g L⁻¹) as the electron acceptor before TCE addition to enrich them in biomass and to establish a constant sulfate reduction (SR, 87% sulfate conversion and specific H₂S concentration of 90.81 ± 8.19 mg H₂S g VSS⁻¹), afterwards TCE was added at an initial concentration of 300 ??mol L⁻¹. The best results for TCE biodegradation were obtained at 37 °C. At this temperature, SR was up to 92%, whereas TCE biodegradation reached 75% and ethane was detected as the main degradation product. Under thermophilic conditions (70 °C) TCE biodegradation reached up to approximately 60% and the SR was 30% in 30 days of incubation with the chlorinated solvent. Along with these results, the 16S rDNA analysis from samples at 37 °C showed the presence of bacteria belonging to the genera: Clostridium, Bacillus and Desulfuromonas. The overall results on TCE degradation and SR suggest that cometabolic TCE degradation is carried out by sulfate or sulfur reducers and fermentative bacteria at mesophilic conditions.     

Effect of Emulsan on Biodegradation of Crude Oil by Pure and Mixed Bacterial Cultures

Crude oil was treated with purified emulsan, the heteropolysaccharide bioemulsifier produced by Acinetobacter calcoaceticus RAG-1. A mixed bacterial population as well as nine different pure cultures isolated from various sources was tested for biodegradation of emulsan-treated and untreated crude oil. Biodegradation was measured both quantitatively and qualitatively. Recovery of ¹⁴CO₂ from mineralized ¹⁴C-labeled substrates yielded quantitative data on degradation of specific compounds, and capillary gas chromatography of residual unlabeled oil yielded qualitative data on a broad spectrum of crude oil components. Biodegradation of linear alkanes and other saturated hydrocarbons, both by pure cultures and by the mixed population, was reduced some 50 to 90% after emulsan pretreatment. In addition, degradation of aromatic compounds by the mixed population was reduced some 90% in emulsan-treated oil. In sharp contrast, aromatic biodegradation by pure cultures was either unaffected or slightly stimulated by emulsification of the oil.     

The effects of carbon sources and micronutrients in fermented whey on the biodegradation of n-hexadecane in diesel fuel contaminated soil

Fermented whey has previously been shown to stimulate biodegradation of n-hexadecane in diesel contaminated soils. The proposed explanation for the stimulatory effect is that fermented whey provides easily accessible carbon and micronutrients, which give rise to an increased degrading biomass.The objective of this work has been to investigate the role of the different carbon sources and vitamins in fermented whey on the microbial degradation of n-hexadecane in soil.The effects of lactose, lactate, vitamins and free amino acids were tested in combinations according to a full factorial design experiment, at concentrations corresponding to those present in fermented whey. The target substance was ¹⁴C-labeled n-hexadecane in nutrient amended soil microcosms contaminated with 5000 mg diesel fuel kg⁻¹ dw. Biodegradation was monitored by determination of evolved ¹⁴CO₂.Significant effects on the biodegradation of n-hexadecane were observed for lactate and amino acids additions in a sandy soil. Lactate showed both an inhibitory effect in the early phase of the experiment and a stimulatory effect in the later phase. The effect of amino acids was slightly stimulatory, mainly evident as a shortening of the lag time.The degree of n-hexadecane degradation at the end of the experiment was correlated with the total concentration of organic compounds added to the soil.Scientific relevanceThere are a handful papers describing the potential of using organic amendments (often industrial by-products) with a content of both easily accessible carbon and micronutrients, to enhance the bioremediation of polluted soils. Enhanced biodegradation is often reported and the proposed explanations are that the combination of easily accessible carbon and micronutrients increases the degrading biomass.In this paper, we examine the effect of fermented whey on the degradation of n-hexadecane and correlate the observed effects on the biodegradation with the main components lactate, amino acids, lactose and B-vitamins. This has to our knowledge never been done before.