OPTIMIZATION OF TOTAL SOLUBLE PROTEIN PRODUCTION BY Trametes sp. isolate B7 AND ENZYMATIC DEGRADATION OF SYNTHETIC DYES
AUTHORSBenjamin Vandelun Ado, Abiodun Anthony Onilude, Tivkaa Joseph Amande
Filamentous fungi as a source of bioproteins for biotechnological applications are preferred over bacteria and yeasts due to their excellent yield and total volume of production. Fungal laccases are useful because of high redox potentials and low substrate specificity to xenobiotics. However, challenges for large-scale utilizations are low enzyme yield and high cost of production. Saw-dust of Terminalia superba abounds locally and was utilized as alternative substrate for production using various optimization processes. Trametes sp. isolate B7 was isolated and identified using molecular techniques. Optimum pH and temperature for total soluble protein (TSP) and laccase activity were pH 5.0 (3.6 mg/mL, 2356 U/mL) and 25oC (2.3 mg/mL, 2395 U/mL), respectively. Enhanced production of TSA occurred in Cu2+ (2.70 mg/L) and Ca2+ (2.50 mg/L) at 3 mM. Laccase activity was recorded at 1 - 2 mM Cu2+ (2379 U/mL) and 3 - 4 mM Ca2+ (2385 U/mL). Productions of TSP and laccase activity were higher using ammonium sulphate and ammonium chloride respectively. Glucose induced the best TSP and laccase activity of 3.6 mg/mL and 2395 U/mL respectively. TSP and laccase activity were best on day 14 (3.6 mg/mL) and day 18 (2395 U/mL) respectively. Percentage degradation of synthetic dyes using crude laccase 1000 U/mL (and 2000 U/mL) were: Remazol Brilliant Blue Royal 100% (77%), Phenol red 28% (36%), Congo red 75% (64%), and Malachite green 62% (28%) respectively. The ability of laccase to degrade Phenol red and other synthetic dyes without using enzyme mediators made it a valuable tool for biotechnological applications.
KEYWORDSTrametes sp., Total soluble protein, Laccase activity, Optimization, Synthetic dyes, Enzymatic degradation
Filamentous fungi are efficient sources for extracellular production of proteins both enzymic and non-enzymic, which are applied in a wide variety of processes in the fields of environment, industry and food biotechnology. Total soluble proteins as secondary metabolites are usually induced by stress factors including limited carbon and nitrogen levels among others in media formulations. They include ligninolytic enzymes like laccases, peroxidases and oxidases, hydrolytic enzymes such as pectinases, cellulases and hemicellulases and degradative enzymes such as proteases, amylases (Mtui, 2009). Laccases of fungal origin are more useful in industrial and biotechnological applications because of their catalytic properties, high redox potentials and low substrate specificity for synthetic dyes, phenols, polyphenols, aryl diamines, anilines, hydroxyindols, methoxy substituted phenols, benzenethiols, inorganic/ organic metal compounds and many other xenobiotics (Kunamneni et al., 2008).
Studies have shown that some Wood Rot Fungi (WRF) contain all three classes of ligninolytic enzymes, whereas others may contain only one or two of these enzymes (Poojary et al., 2012). Trametes versicolar, Pleurotus ostreatus, Pleurotus eryngii, Agaricus blazei, and Clitocybe maxima are suitable for large-scale production of laccases while Ganoderma lucidum is an efficient producer of laccases, Mn oxidizing peroxidases and lignin peroxidases (Aftab and Ahmad, 2015). Martins et al. (2011) also reported that fungi such as Phanerochaete chrysosporium and Trametes versicolor, Trametes hirsuta, Bjerkandera adusta, Irpex lacteus, Dichomitus squalens, Funalia trogii, Pycnoporus sanguineus, Phlebia radiata and Daedalea flavida are of biotechnological importance, because they carry out enzymatic degradation of a wide variety of recalcitrant compounds including synthetic dyes resulting in detoxification and mineralization.
Globally, more than 100,000 dyes are commercially available with an annual production of over 7×105 tonnes of the dyestuffs (Itodo et al., 2017). Extensive utilization of these occur in diverse industrial processes such as textile and leather dyeing, paper printing and coloured photography, cosmetics, food, pharmaceuticals as well as additives to petroleum products (Gonawala1 et al., 2014). As a result, approximately 10 – 15% of used dyes are released into the environment as wastewater which contaminates surface water, soils and underground water by infiltration (Hassaan and Nerm, 2017). Among the many classes of synthetic dyes used in the textile and dyeing industries, triphenylmethane group of dyes such as crystal violet and malachite green are the largest and most commonly used in almost every type of application. Most of the synthetic dyes are characterized by high stability in presence of light and high temperatures, and are fast to detergents and attacks of microorganisms. In addition, they exist in wide arrays of colours along with the ease and low cost of synthesis compared to natural dyes (Roushdy and Abdel-Shakour, 2011).
However, many synthetic dyes are toxic, carcinogenic or prepared from known carcinogens or other aromatic compounds that may cause harm to humans, animals or other forms of aquatic resources (Songserm et al., 2012). For instance, Malachite green which is employ in dyeing of jute, leather, silk, cotton, wool and ceramics is also a potent antiprotozoan and antifungal. Nevertheless, it is highly poisonous to cells of mammals and has been implicated in promoting the formation of hepatic tumors in rodents as well as reproductive abnormalities in rabbits and fish. When reduced to leucomalachite green, it may persist in tissues of edible fish for extended periods through bioaccumulation, and therefore it is of public health concern in terrestrial and aquatic habitats (Fallah and Barani, 2014). The structural similarity of malachite green to other carcinogenic triphenylmethane dyes also raises suspicion of carcinogenicity. Crystal violet on the other hand has been identified as a thyroid and liver carcinogen in rodents while pararosaniline is a bladder carcinogen in humans (Suwannawong et al., 2010).
Aromatic compounds and their derivatives are pollutants of high priority because they impact negatively on aquatic organisms even at low concentrations. Treatments of these pollutants can be achieved using conventional methods. However, these methods are expensive, time consuming and often lead to formation of toxic residues (Villegas et al., 2016). Several studies have reported the decolourization of synthetic dyes by fungal species using laccase as the main enzyme during the process (Songserm et al., 2012). The use of laccase an oxido-reductive enzyme in biological treatment effectively oxidises pollutants to less soluble compounds that are easily removed by sedimentation and filtration (Moturi and Singara-Charya, 2009). In addition, biological treatments are less expensive and environmentally-friendly.
However, challenges often encountered in large-scale utilization include the high cost of production, low yield and unstable enzymes. Thus, the solution lies in optimization of process parameters and utilization of suitable alternative substrates eg lignocellulose for cheap production of Total Soluble Protein (TSP) and enzymes in Solid State Fermentation Lignocellulose consist of lignin, cellulose and hemicelluloses and are the largest renewable source of carbohydrates that could undergo bioconversion to value-added products during fermentation. They are mostly ‘waste products’ of pre-harvest and post-harvest losses as a result of agricultural processing. They include saw-dust, grasses, waste paper, agricultural residues, food industry residues and municipal solid wastes. Apart from value-added products the process of bioconversion also removes wastes from the environment. It has been established that during fermentation nutrient utilization pathways of filamentous fungi influence metabolic diversity and allow fungi to utilize a variety of complex compounds as nutrients. For example, the growth of Aspergillus terreus, Trichoderma sp, Cyathus stercoreus, Lentinus squarrosulus, Lentinus edodes, Trametes pubescens, Pleurotus sp, Penicillium camemberti, Phanerochaete chrysosporium at 25 – 35°C for 3 – 22 days resulted in 45 – 75% and 65 – 80% holocellulose and lignin degradation, respectively using lignocellulosic substrate (Mtui, 2009).
Due to diverse applications of bioproteins such as laccases and the high cost of production coupled with low yields and stability it is important to identify new sources with high production. The use of cheap alternative substrates such as saw-dust would lower the cost and enhance large-scale production both for commercial purposes and applications in enzymatic degradation of synthetic dyes and other xenobiotics currently employed in different industries. The objective of our study was to meet the demand for low-cost bioprotein production by Trametes sp. isolate B7 through optimization of process parameters and utilization of same for enzymatic degradation of synthetic dyes.
MATERIALS AND METHODS
Substrate collection and processing
Wood samples of Terminalia superba were collected from Gboko plank market, Benue State, Nigeria. Samples were passed through an electric sliding-table saw machine to obtain wood blocks which were oven dried to constant weight at 80oC. The blocks were directly fed into a motorized rotary machine and crushed into saw-dust particles. The saw-dust was then passed through a 2 mm wire mesh of metallic sieve to obtain particles of even sizes and thereafter dispensed into plastic bags and sealed.
Isolation and Identification of fungus
The fungus was isolated from a decaying wood in Benue Polytechnic Campus, Ugbokolo, Benue State, Nigeria. Pieces of sample were aseptically transferred onto sterile Potato Dextrose Agar (PDA) plates and incubated at 27 ± 2oC for 7 days. Pure cultures were obtained by sub-culturing onto fresh sterile PDA plates and were thereafter placed on PDA slants for refrigeration at 4oC. Five-day old fungal cultures on PDA plates were observed for both cultural and morphological characteristics (Domsch et al., 2007). The fungal isolate was identified using molecular and phylogenetic characterization as described in Ado et al. (2018). The sequence was deposited in GenBank under the accession number MK024175.
Production of growth medium
The Lignin Modifying Medium (LMM) used to moisten the saw-dust sample had the following composition (gL-1) glucose 10 g, Ammonium tartrate 2 g, KH2PO4 1 g, MgSO4.7H2O 0.5 g, KCl 0.5 g, Yeast extract 1 g, Soy tone 5 g, CuSO4.5H2O (150 µm), EDTA 0.5 g, FeSO4 0.2 g, ZnSO4 0.0 1g, MnCl2.4H2O 0.00 3g, H3BO4 0.03 g, CoCl2.6H2O 0.02 g, CuCl2.2H2O 0.001 g, Na2MoO4.2H2O 0.003 g (Poojary et al., 2012).
Solid state fermentation of total soluble protein
Ten millilitres of the moistening medium was added to 100 g of the saw-dust with approximately 70% moisture content in 250 mL Erlenmeyer flask and sterilized by autoclaving at 121oC for 20 minutes. One percent (w/v) aqueous glucose solution was separately autoclaved at 110oC (10 psi) for 10 minutes and 2 mL aseptically added to the fermenting flask (Gomes et al., 2009). The flask was allowed to cool and inoculated with two 5 mm agar plugs of actively growing mycelia from 5-day old fungi cultures on PDA and incubated for 18 days. Each experiment was carried out in duplicate.
Optimization of total soluble protein and laccase activity
Extraction and determination of total soluble protein
Total soluble protein was extracted by addition of 100 mL 0.1M citrate-phosphate buffer (pH 5.0) into the fermenting flask. The mixture was stirred with a glass rod for 30 minutes and filtered with cheese-cloth to remove saw-dust and fungal mycelia. The crude filtrate was then filtered with 90 mm Whatman No. 1 Filter paper to obtain a clear filtrate which was refrigerated at 4oC. Protein concentration was quantified using the method of Lowry et al. (1951) and the standard curve obtained by plotting various concentrations of Egg albumin (BDH).
Effect of pH on total soluble protein and laccase activity
The pH of the moistening medium was adjusted to pH values ranging from 3.0 – 8.0 before sterilization and the general procedure carried out as earlier described in solid state fermentation of total soluble protein. After inoculation the flasks were incubated at 27 ± 2oC for 18 days (Urairuj et al., 2003; Sivakumar et al., 2010).
Effect of temperature on total soluble protein and laccase activity
The fermenting flasks were moistened with the medium (pH 5.0) before sterilization and the general procedure repeated as described in solid state fermentation of TSP. Incubation was carried out at 15oC, 25oC, 35oC, and 45oC for 18 days (Urairuj et al., 2003).
Effect of copper and calcium ions on total soluble protein and laccase activity
The effect of metal ions was determined by adding 10 mL of 1, 2, 3, 4 and 5 mM Ca2+ and Cu2+ solutions in their chloride forms; separately, 48 hours for stability before addition of the moistening medium (Wuyep et al., 2003). The general procedure was performed at pH 5.0 and incubation carried out at 27 ± 2oC for 18 days.
Effect of ammonium sulphate and ammonium chloride on total soluble protein and laccase activity
The effect of nitrogenous sources was determined by substituting 2 g/L ammonium tartrate with ammonium sulphate and ammonium chloride, separately in concentrations of 0.3, 1.0, 3.0 and 6.0 g/L and the medium adjusted to pH 5.0. The general procedure was performed and incubation carried out at 27 ± 2oC for 18 days (Urairuj et al., 2003; Sivakumar et al., 2010). The control was carried out using distilled water instead of (NH4)2SO4 or NH4Cl solution.
Effect of different carbon sources on production of total soluble protein and laccase activity
The effect of different sugars on total soluble protein production and laccase activity was carried out by replacing 10 g/L of glucose in the medium with equimolar concentration of the following sugars: lactose, sucrose, maltose and fructose (Singh and Abraham, 2013). The general procedure was performed at pH 5.0 and incubation carried out at 27 ± 2oC for 18 days.
Effect of incubation time on production of total soluble and laccase activity
The general procedure was performed at pH 5.0 and incubation carried out at 27 ± 2oC for 6 – 34 days.
Assay for laccase activity of total soluble protein
Laccase activity was determined at 420 nm using 2, 2’-azino-bis (3-ethylbenz-thiazoline-6-sulfonic acid) ABTS as described by Mtui and Masalu, (2008). One Unit of laccase activity was defined as activity of an enzyme that catalyzes the conversion of 1µmol of ABTS (ɛ=36,000 M-1 cm-1) per minute.
Application of crude laccase in enzymatic degradation of synthetic dyes
The decolourizing potential of crude laccase was tested using selected dyes at concentration of 0.01% (w/v) dissolved in sterile distilled water. The reaction mixture consisting of equal volume aqueous solution of dye and crude protein of 1000 U/mL and 2000 U/mL (1:1), separately, in citrate phosphate buffer (pH 5.0) was incubated at 27 ± 2o C in the dark for 1, 24, 48, 72 and 120 hours. Decolourization of dyes was determined by monitoring the decrease in absorbance at the wavelength of maximum absorption for each dye: Phenol Red (475 nm), Congo Red (497 nm), Crystal Violet (590 nm), Remazol Brilliant Blue Royal (RBBR) (587 nm) and Malachite Green (620 nm) (Moturi and Singara-Charya, 2009; Stoilova et al., 2010). Control tests were performed using a heat-denatured crude enzyme. The experiment was carried out in triplicates and activity of decolourization calculated thus:
(Aini – Afin)
D% = 100 x _____________
D = Decolourization.
Aini = Initial absorbance.
Afin = Final absorbance of dye after incubation time.
(Moturi and Singara-Charya, 2009).
Results obtained from this study were subjected to analysis of variance using one way ANOVA and differences between means were separated by Duncan Multiple Range Test (Duncan, 1955).
RESULTS AND DISCUSSION
In the study, the optimum pH for production of total soluble protein by Trametes sp. isolate B7 was pH 5.0 with 3.6 mg/mL followed by pH 3.0 and pH 7.0 each with 3.2 mg/mL, respectively. Equally, laccase activity followed the same pattern with the best production of 2356 U/mL at pH 5.0 followed by pH 3.0 and pH 7.0 as shown in Figure 1. This showed that the optimum pH for TSP production coincided with the highest laccase activity. This agreed with the study that microbial proteins are produced in higher yield at a pH near to the optimum for enzyme production (Chanakya et al., 2010). Sivakumar et al. (2010) also reported the critical effect of pH on culture medium as its affects growth and secretion of bioproteins but stated that the optimum varies according to microorganisms. Several works have shown that the production of enzyme by fungal strains is best at pH 4 – 6 while others placed the range at pH 3.5 – 7.0 (Sivakumar et al., 2010; Singh and Abraham, 2013). The optimum pH for production of bioproteins and enzyme activity as shown in the study was within the range reported by other researchers. It is important to note that the actual pH optimum for fungal growth and secretion of TSP is specie and strain-specific coupled with the nature of lignocellulosics used in addition to the concentration of hydrogen ions present in the medium (Elisashvili and Kachlishvili, 2009; Chanakya et al., 2010).
The effect of temperature on total soluble protein production and laccase activity is presented in Figure 2. Result indicates that both total soluble protein production and laccase activity were best at 25oC with 2.3 mg/mL and 2395 U/mL respectively. However, protein production and enzyme activity declined steadily with increase in temperature. It has been reported that Trichoderma koningii secreted maximum amount of soluble protein in SSF at 33oC while optimum production of soluble protein by Xylariaceae occurred at 30oC (Urairuj et al., 2003; Chanakya et al., 2010). The difference is probably due to differences in fungal species. Similarly, reports on the effect of temperature on laccase production showed the temperature range of 25 – 30oC as optimum for laccase production by Trametes sp., Pleurotus sp. and Dichomitus squalens (Iqbal et al., 2011) which goes in line with the study. In addition, the optimum temperature for fungal growth and production of enzymatic and non-enzymatic proteins lies close to the temperature in its natural habitat. At these temperatures fungi membranes are highly permeable while the synthetic machinery function at its peak; consequently, the rate of substrate conversion reaches its maximum (Bhattacharya et al., 2011). However, higher temperatures tend to denature metabolic activities such as fatty acid synthesis and membrane fluidity resulting to decrease in production (Schulte, 2015).
Figure 3 present the effects of Cu2+ ions on total soluble protein production and laccase activity. Results show that Cu2+ stimulated high laccase activity at 1 – 2 mM with 2379 U/mL followed by a sudden decline at 3 – 5 mM concentration while total soluble protein production was high at 3 mM with 2.70 mg/mL but declined at 4 – 5 mM. Stajia et al. (2007) and Kumar et al. (2011) reported the regulatory effects of copper on transcription of genes for laccase production in addition to the inhibition of extracellular proteases that degrade laccases resulting to increased turnover in soluble protein production as well as laccase activity and stability. Stajia et al. (2007) reported the stimulatory effect of 1 mM copper chloride on production of laccase by Trametes pubescens but placed the optimal concentration at 1.5 – 2.0 mM which coincided with our result. However, as concentration increased above the threshold Cu2+ ion became toxic resulting in decreased laccase activity and soluble protein production as shown in the study. The effect of Ca2+ on total soluble protein production and laccase activity is shown in Fig. 4. Results indicate high laccase activity of 2379 U/mL (1 mM), 2365 U/mL (2 mM) and 2385 U/mL at 3 – 4 mM. The fungus was able to secrete high amounts of laccase on both low and high concentrations of Ca2+ because it improved the extracellular structure of the fungal proteins by acting as stabilizers (Wuyep et al., 2003). However, production of total soluble protein was generally lower than Cu2+ ion but more stable because of the stabilizing effect of the metal ion on extracellular proteins.
Figure 1 Effect of pH on production of total soluble protein and laccase activity. Bar represent standard error of the mean.
Figure 2 Effect of temperature on production of total soluble protein and laccase activity. Bar represent standard error of the mean.
Figure 3 Effect of copper ions concentration on total soluble protein production and laccase activity. Bar represent standard error of the mean.
Figure 4 Effect of calcium ions concentration on total soluble protein production and laccase activity. Bar represent standard error of the mean.
The study investigated the effect of ammonium chloride and ammonium sulphate on total soluble production and laccase activity as presented in Figure 5. Production of total soluble protein was high in ammonium sulphate supplemented medium with 2.14 mg/mL as to 1.44 mg/L by ammonium chloride, while laccase activity was high using ammonium chloride supplemented medium with 2024 U/mL but drastically low in ammonium sulphate with 277 U/mL. Other authorities also reported maximum laccase activity with ammonium chloride using Coriolus versicolor and Pleurotus ostreatus instead of ammonium sulphate (Elsayet et al., 2012). On the contrary, another work showed maximum laccase production with ammonium sulphate using Trametes hirsuta MTCC 11397 (Dhakar and Pandey, 2013).
Figure 6 shows the effect of different carbon sources on total soluble protein production and laccase activity. Carbon sources appear to regulate the production of bioproteins in fungi but the source is specie specific. In this study, glucose was best for production of total soluble protein with 3.6 mg/mL followed by fructose, maltose and lactose while sucrose was the lowest with 1.5 mg/mL. Significant production of laccase by T. pubescens has been reported on glucose and cellobiose while Pleurotus sajoro-caju produced higher amounts of laccase on glucose and fructose than lactose (Elisashvili and Kachlishvilli, 2009). In the study, laccase activity was best on glucose and lactose with 2395 U/mL and 1838 U/mL but lowest on fructose with 809 U/mL. Revankar and Lele (2006) in his work also stated that production of laccase by Pleurotus ostreatus was highest on glucose and starch but lowest on fructose. Also, Ding et al. (2012) reported increased laccase production on glucose compared to maltose, sucrose, lactose and starch. It is evident that this variation in carbon sources was probably due to specie specificity and differences in substrate utilization.
Figure 7 presents result of the effect of incubation time on total soluble protein production and laccase activity. Production of total soluble protein increased from day 6 with 0.9 mg/mL to its peak on day 14 with 3.6 mg/mL. Thereafter, production declined progressively for the remaining days of incubation. Many authors have reported different incubation periods for optimum production of crude enzymes. Das et al. (2011) stated that P. ostreatus produce the highest quantity of crude laccase on the 25th day of incubation. On the contrary, Elisashvili et al. (2008) and Sivakumar et al. (2010) reported maximum laccase production on the 7th and 10th day of incubation using Lentinus edodes and Ganoderma sp, respectively; while Ding et al. (2012) reported maximum laccase production on the 11th day with rubber wood saw-dust. Another work maintained that depending on the fungal strain and culture medium the peaks of laccase production varies from 5 – 14 days of incubation (Elisashvili and Kachlishvilli, 2009). From this study the peak of total soluble protein was day 14 while the peak for laccase activity was day 18 with 2395 U/mL. Aftab and Ahmad (2015) reported maximum production of laccase by Ganoderma lucidum on day 16 which lies close to our study. The difference in peaks of laccase activity was probably based on differences in fungi species and the type of lignocellulosic substrate (Elsayet et al., 2012).
Figure 5 Effect of different concentrations of ammonium chloride and ammonium sulphate on total soluble protein production and laccase activity. Bar represent standard error of the mean.
Figure 6 Effect of different carbon sources on production of total soluble protein and laccase activity. Bar represent standard error of the mean.
Figure 7 Effect of incubation time on production of total soluble protein and laccase activity. Bar represent standard error of the mean.
The ability of fungi to decolourize dyes has been reported in a number of isolates including T. versicolor. In this study, crude protein from Trametes sp. isolate B7 enzymatically degraded synthetic dyes of diverse structures as shown in Fig. 8. Phenol red attained 28% and 36% degradation using 1000 U/mL and 2000 U/mL crude protein respectively after 48 hours of incubation. The ability of the crude protein to degrade Phenol red without the use of mediators is an important characteristic since Phenol red has a high oxidation potential. This suggests that the crude enzyme possessed the capacity to oxidize a wide range of substrates (Saparrat et al., 2002). Nevertheless, with prolonged incubation of 72 to 120 hours the extent of enzymatic degradation dropped. This is because enzymatic degradation of dyes is a multi-step process that involves a decrease in absorbance of the visible peak at the beginning. However, after 72 hours there is a general increase in absorbance due to polymerization of dye fragments resulting in darker solutions (Zille et al., 2005).
The extent of degradation of RBBR, Congo red and Malachite green were 100%, 75% and 62% using 1000 U/mL crude protein and 77.4% 64% and 28% using 2000 U/mL crude protein respectively. The degree of decolourization was not the same in all the dyes probably due to the enzyme concentrations, their substrate specificity as well as the complex structure of many of the synthetic dyes (Poojary et al., 2012). In a study, 100% of RBBR was decolourized in 6 hours and Congo red in 13 days using 2000 U/mL crude laccase of T. versicolor (Stoilova et al., 2010). Interestingly, crude protein containing laccase from Trametes sp. isolate B7 decolourized 100% of RBBR in 24 hours and 75% of Congo red within 72 hours of this study. These differences are attributed to the fact that the redox potential of enzymes varies with the source which could determine the need of mediators for decolourization of specific dyes (Stoilova et al., 2010). Reports indicate that crude laccase from L. polychrous decolourized Rhodamine B and Congo red using the mediator ABTS (Suwannawong et al., 2010). However, this study showed that crude laccase from Trametes sp. isolate B7 decolourized 75% Congo red without any enzyme mediators. More so, the crude laccase was able to decolourize Congo red unlike crude laccases from P. radiata strain BP-11-2, which failed to decolourize the dye (Suwannawong et al., 2010).
Figure 8 Percentage decolourization of synthetic dyes using 1000 U/mL and 2000 U/mL crude enzymes.
Bar represent standard error of the mean.
Optimization of cultural and nutritional factors for the production of TSP and increased laccase activity by Trametes sp. isolate B7 using saw-dust of Terminalia superba proved very useful in TSP production and enzymatic degradation of different synthetic dyes. Temperature had the most profound effect on laccase activity with optimum at 25oC (2395 U/mL) while pH 5.0 was optimum for TSP production (3.6 mg/mL). Ca2+ and Cu2+ showed considerable influence on laccase activity at 3 – 4 mM (2385 U/mL) and 1 – 2 mM (2379) respectively. Glucose was the preferred source of carbon both for TSP production and laccase activity. Ammonium chloride favoured high laccase activity and ammonium sulphate enhanced higher TSP production. Effect of incubation time showed optimum production of TSP on day 14 and laccase activity on day 18. In the study, the extent of enzymatic degradation of RBBR, Phenol red, Congo red and Malachite green by crude laccase 1000 U/mL were 100%, 28%, 75% and 62% respectively. Enzymatic degradation of RBBR, Phenol red, Congo red and Malachite green by crude laccase 2000 U/mL were 77%, 36%, 64% and 28% respectively. The ability of crude enzyme to degrade all the dyes including Phenol red without enzyme mediators is important. In addition the structural similarity of the dyes to many recalcitrant compounds and the extended substrate range makes the enzyme a suitable candidate for several industrial and biotechnological applications.
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