In this work, recombinant Pichia pastoris GS115-lccA was cultured and expressed with the highest laccase activity of 2357 U/L with ABTS (2, 2′-nazinobis-(3-ethylbenzthiazoline-6-sulphonate)) as reacting substrate. To achieve the higher laccase activity, multiple key factos were screened (using a Plackett-Burman design of experiments methodology) related to the fermentation conditions for producing GS115-lccA. Subsequently, a Box-Behnken response surface methodology was employed for further optimization. The optimum fermentation conditions of the fermentation were obtained as follows: 0.603% methanol added into the culture every 24 h, medium optimal initial pH 7.1, and liquid medium volume of 20.4% provided the highest enzyme activity of 5235 U/L. The decolorization experiments of dyes (Reactive Blue KN-R and Acid Red 35) were carried with the laccase cultured by recombinant P. pastoris GS115-lccA. This purified enzyme showed excellent decolorization capacity. After 24 h, the decolorization of Reactive Blue KN-R with 100 mg/L at 50 °C, pH 4.5 using 20 mM acetate buffer with 2 U/mL purified enzyme was 91.33%, and for Acid Red 35, the decolorization was 78.96%. All results suggested that this laccase may be suitable for the wastewater treatment of similar azo and anthraquinone dyes from the deinking and dyeing industries.
Optimization of Fermentation Conditions for Laccase Production by Recombinant Pichia pastoris GS115-lccA Using Response Surface Methodology and Its Application to Dye Decolorization
Qi Li,a,b Jingcong Xie,a,b Linguo Zhao,a,b,* Qiuxia Xue,a and Jiangjun Pei a,b
In this work, recombinant Pichia pastoris GS115-lccA was cultured and expressed with the highest laccase activity of 2357 U/L with ABTS (2, 2′-nazinobis-(3-ethylbenzthiazoline-6-sulphonate)) as reacting substrate. To achieve the higher laccase activity, multiple key factors were screened (using a Plackett-Burman design of experiments methodology) related to the fermentation conditions for producing GS115-lccA. Subsequently, a Box-Behnken response surface methodology was employed for further optimization. The optimum fermentation conditions of the fermentation were obtained as follows: 0.603% methanol added into the culture every 24 h, medium optimal initial pH 7.1, and liquid medium volume of 20.4% provided the highest enzyme activity of 5235 U/L. The decolorization experiments of dyes (Reactive Blue KN-R and Acid Red 35) were carried with the laccase cultured by recombinant P. pastoris GS115-lccA. This purified enzyme showed excellent decolorization capacity. After 24 h, the decolorization of Reactive Blue KN-R with 100 mg/L at 50 °C, pH 4.5 using 20 mM acetate buffer with 2 U/mL purified enzyme was 91.33%, and for Acid Red 35, the decolorization was 78.96%. All results suggested that this laccase may be suitable for the wastewater treatment of similar azo and anthraquinone dyes from the deinking and dyeing industries.
Keywords: Laccase; Response surface methodology; Dye decolorization; Reactive Blue KN-R; Acid Red 35
Contact information: a: College of Chemical Engineering, Nanjing Forestry University, Nanjing 210037, China; b: Jiangsu Key Lab of Biomass-based Green Fuels and Chemicals, Jiangsu, 210037, China;
* Corresponding author: firstname.lastname@example.org
Laccases, which belong to the group of enzymes called the multi-copper oxidases, can catalyze the four-electron reduction of O2 to H2O with the concomitant oxidation of phenolic compounds (Solomon et al. 1996; Cusano et al. 2009). During the past decades, vast amount of laccases have been isolated and characterized from various sources such as fungal species, certain types of bacteria, and even some insects (Heinzkill et al. 1998; Diamantidis et al. 2000; Dittmer and Kanost 2010). Laccases derived from fungi are found to be efficient for degrading toxic compounds and for decoloring synthetic dyes, as well as for other biotechnological applications. Among these fungal species, Trametes versicolor has received considerable attention for its bioremediation potential (Madzak et al. 2006). The successful applications of laccase require large amounts production at low cost and short time. However, the production of laccase from original strains obtained by the optimization of culture medium and cultivation conditions does not meet modern-day demands of industry. One of the possible solutions is to produce the recombinant protein in a heterologous host. Consequently, various studies have been carried out to investigate the characteristics and cultivation conditions of the recombinant laccase production from Trametes versicolor from the yeast Pichia pastoris system for the expression of heterologous proteins, which are seen as the most cost-effective and green strategy of laccase production (He et al. 2011). For any heterologous protein, expression conditions need to be optimized in order to achieve high levels of protein production.
The biological process optimization, which aims to improve the activity of final product, is an indispensable phase of work for the biotechnological industry. Optimiza-tion techniques for these biological processes include two major categories, i.e. non-statistical optimization techniques (Sigal and Whyne 2010) and statistical optimization techniques (Box and Wilson 1951; Tanyildizi et al. 2005; Jo et al. 2008). In recent years, the statistical methods have become a powerful and effective approach for screening key factors rapidly from a multivariable system to optimize fermentation conditions. Several common optimization techniques were compared with each other, and the response surface method was introduced and applied (Box and Wilson 1951; Vasconcelos et al. 2000; Muralidhar et al. 2001; Liu et al. 2003). Optimization of media components for the production of laccase by response surface methodology has been reported in the case of different fungal strains (Trupkin et al. 2003; Nyanhongo et al. 2002). Therefore, in this present study, fermentation conditions for the recombinant yeast GS115-lccA were optimized by applying different statistical experimental designs and data analysis methods. Fermentation conditions were considered as independent variables, and laccase enzyme activity was the primary response value, to achieve the highest activity and provide the effective enzyme for the industrial application.
It is known that azo, anthraquinone, and indigo dyes are the major chromophores found in commercial dyes (Thurston 1994; Abadulla et al. 2000). Over 10,000 different dyes are in common use with an annual production of over 0.7 million tons of dyestuff being manufactured and 10 to 20% of dyes lost in the industrial effluents. Reactive dyes, including Reactive Blue KN-R and Reactive Red 7, form covalent bonds with cellulose during a typical dyeing process; such dyes are commonly used in cotton dyeing industries. It is evident that textile dyes in discharge effluents can have negative impacts on the entire ecosystem. Decolorization of these dyes by physical and chemical methods (coagulation-flocculation, adsorption, oxidation, ion-exchange, or electron chemistry) is prohibitively expensive, time-consuming, mostly inefficient and even unsafe (Sheng and Chi 1996; Mechichi et al. 2006). By contrast, as the highly free-radical-mediated and non-specific processes, the biodecolorization processes used the extracellular oxidative enzyme laccase which come from the Trametes versicolor are environmental-friendly and cost-competitive. Remazol Brilliant Blue R, as a starting material in the production of polymeric dyes, was studied on decolorization using purified laccase (Schliephake and Lonergan 1996). The dye was added on day three of the fermentation, and more than 48 h were required to get about 75% decolorization in the fungal culture. Previous researchers have reported that the laccase derived from P. ostreatus could decolorize 70% of malachite green for 24 h of incubation (Yan et al. 2009). Bromophenol blue could be decolorized by the laccase from Trametes sp.420. But the decolorization efficiency was relatively low. The redox mediator, such as ABTS, could increase the decolorization efficiency to 45% (Tong et al. 2007). Thus, laccase as a kind of valuable enzyme has potential to degrade a wider range of compounds.
The aim of this present investigation was to study the optimal fermentation conditions for laccase production in a shake flask using the response surface method and to purify the enzyme by ultrafiltration and ammonium sulfate precipitation. This research will lay the foundation for further applications of Trametes versicolor for the biodegra-dation of industrial dyes.
MATERIALS and METHODS
Fungus Strains and Growth Media
The recombinant strain Pichia pastoris GS115-lccA was preserved by Microbial Technology Research Laboratory, Nanjing Forestry University (NJFU).
YPD (yeast extract-peptone-dextrose) agar plates (+Zeocin): yeast extract 10 g/L, peptone 20 g/L, dextrose 20 g/L, and agar 20 g/L adding Zeocin (100 mg/L).
BMGY medium (buffered glycerol-complex medium) was prepared according to the manual of the EasySelect Pichia Expression Kit (Invitrogen, USA): 1% yeast extract, 2% peptone, 100 mM potassium phosphate, pH 6.0, 1.34 % YNB, 4×10-5% biotin, and 2% glycerol.
Expression of the Recombinant Laccase
The recombinant strain P. pastoris GS115 was incubated in 30 mL of BMGY medium for 24 h at 28 oC with constant shaking at 180 rpm. When OD600 reached values between 3.0 and 8.0, the cultures were harvested, resuspended in 30 mL of BMGY containing 0.3 mM Cu2+ with the initial pH 6.0, and incubated in the same conditions until an OD600 of 1.0 was reached. 100% methanol was added daily (final concentration 0.5% (v/v)) to maintain induction. The samples were centrifuged at 8,000 × g for 5 min. The supernatant was stored at 4 oC until used to determine enzyme activity.
Assay of Laccase Activity and Protein
The laccase activity assay system contains 1 mL of 1 mM ABTS (420 = 36,000 M-1cm-1) and 1980 μL 50 mM sodium citrate buffer (pH 4.5). The change in the absorbance at 420 nm of the mixture (at 50 °C) for 5 min was recorded every minute using a spectrophotometer. One enzyme activity unit (1 U) is defined as the amount of enzyme that oxidizes 1 μmol of substrate per minute (Childs and Bardsley 1975).
Protein concentrations were determined using the Bradford method with bovine serum albumin as a standard (Bradford 1976).
Plackett-Burman Design of Experiments (Plackett and Burman 1946)
The Plackett-Burman design of experiments, an efficient technique for medium-component optimization (Li et al. 2008), was used to select the key factors that signif-icantly influenced the laccase activity. Laccase activity was the measured response variable; nine independent variables were examined to determine the key fermentation components significantly affecting the activity of laccase. Based on the Plackett-Burman design, each factor was performed at two levels: -1 for the low level and +1 for high level. Table 1 lists the levels of the independent variables and Table 2 illustrates the combinations used for each run in the statistical design of experiment.
In the present study, nine assigned variables were screened in 12 experimental runs in addition with three runs at their center points. Laccase production was carried out in triplicate, and the factors significant at 95% level (P<0.05) were considered to have significant effect on laccase activity, and thus, used for the further optimization by response surface methodology. The analysis of variance for the data and the model coefficients were computed with the software Design-Expert® 7.1.6 (Stat-Ease, Inc., Minneapolis, MN, USA).
Table 1. Levels of the Variables in Plackett-Burman Design
Table 2. Plackett-Burman Design for the Laccase Production
Box-Behnken Response Surface Methodology (Box and Behnken 1960)
A response surface methodology was used to optimize the three key factors for enhanced laccase production based on Box-Behnken design. For statistical calculations, the relation between the coded values and real values are described as follows. The levels of the independent variables for each experimental run are shown in Table 3. In this paper, a three-factor and three-level second-order regression was performed; the Box-Behnken statistical design used 17 trial runs and the value of the dependent response variable was the average of three measurements. The polynomial coefficients were calculated and analyzed using the software Design-Expert® 7.1.6. Statistical analysis of the model was performed to evaluate the analysis of variance (ANOVA).
Purification of Recombinant Laccase
The supernatant (200 mL) was harvested from a culture of the recombinant P. pastoris GS115-lccA (16 days old). The supernatant was obtained from the cultured sample by centrifugation at a speed 6,000 g for 10 min; afterwards, the centrifuged sample was purified by the ultrafiltration using a CXA-50 50000 ultrafiltration membrane (Shanghai Yadong Nuclear Grade Resins Limited Company, China). The resulting filtrate was precipitated by adding (NH4)2SO4 to the final mass concentration of 80%. The protein was dissolved in 20 mM sodium citrate buffer (pH 4.5) and dialyzed 12 h against the same buffer.
Table 3. Box-Behnken Design with Three Independent Variables
Decolorization of Dye by Recombinant Laccases
The purified laccase which was produced by recombinant GS115-lccA was used to decolorize two dyes: Reactive Blue KN-R and Acid Red 35 (Zhejiang Runtu Chemical Group Limited Company, China). The structures are shown in Fig. 1. The involvement of Trametes versicolor laccases in dye decolorization was investigated with the purified enzymes. Decolorization was determined by measuring the decrease of the dye’s absorbance as its maximum visible wavelength and results are expressed in terms of a percentage. Laccase-catalyzed decolorization of synthetic dyes was carried out in 10 mL samples containing buffer (20 mM), a certain amount of purified enzyme and 100 mg/L dyes (Reactive Blue KN-R or Acid Red 35) were added.And the reaction system was reacted statically under the corresponding temperature for more than 24 h. During incubation, the time of decolorization was detected every 6 h by measuring the absorbance. Control samples without the enzyme were processed in parallel with the test samples. Then the decolorization of the two dyes was performed triple as described above.
In order to select the suitable decolorization conditions, the effects of main factors were investigated. The main factors and the variation ranges were as follows: buffers (citric acid-sodium citrate buffer, succinic acid – NaOH buffer, acetic acid-sodium acetate buffer, tartaric acid-sodium tartrate buffer), initial pH values (3.0 to 6.0), temperatures (30 to 70 oC), and enzyme dosage (1 to 5 U/L).
The absorption wavelengths of the two dyes were 610 nm for Reactive Blue KN-R and 505 nm for Acid Red 35. The decolorization efficiency of each dye was shown as dye decolorization (%), as given by Eq. 1,
The decolorization of dyes was calculated by means of the equation:
Decolorization (%) = [(Ci–Ct)/Ci] ×100 (1)
where Ci is the initial concentration of the dye, and Ct is the dye concentration at time t (Lorenzo et al. 2006).
Fig. 1. The structures of the two dyes: (a) Reactive Blue KN-R (b) Acid Red 35
The concentration of the dye was calculated according to the value of absorbance. Figure 2 indicated the linear relationship between concentration of the dye and the value of absorbance.
Fig. 2. The standard curve of the two dyes: (a) Reactive Blue KN-R (b) Acid Red 35
RESULTS and DISCUSSION
Evaluation of Important Parameters Affecting Laccase Activity
Although extensive studies (Bourbonnais et al. 1995; Hess et al. 2002) have been conducted with laccases from Trametes versicolor for potential industrial applications, Pichia pastorisGS115 is still the main host and preference for laccase production. The yield of the heterologous enzymes produced by the new laccase gene lccA of Pichia pastoris GS115 was lower than expected; the cultural conditions may have played an important role in the production yields of laccase. To improve the expression system, multiple cultural condition factors (rotate speed, methanol concentration, biotin concentration, initial OD600 (microbial concentration), Cu2+ concentration, Tween-80 concentration, liquid medium volume, initial pH and peptone concentration) were screened using a Plackett-Burman design of experiments. The identified key factors from these experiments were then optimized using a Box-Behnken response surface methodology.
The predicted regression equation from the Plackett-Burman design of experi-ments was as follows:
R1 = 2880.83+72.50X1-1055.83X2+150.83X3+235.83X4-25.83X5+ 152.50X7-850.83X8+747.50X9+204.17X11 (2)
where R1 is the predicted laccase enzyme activity (U/L) and X1–X11 are the coded independent variables as shown in Table 1.
Table 4. Evaluation of Significance of Various Factors
As can be seen in Table 4, the main effect of each variable upon laccase activity was estimated as the difference between both averages of measurement made at the high level (+1) and the low level (-1) of that factor. The activity of the laccase was strongly affected by the three key factors, which were methanol concentration, initial pH, and liquid medium volume; the other six factors had a negligible effect on laccase production. The coefficient of determination (R2) of the model was calculated to be 0.999, which indicated that 99.9% of the variability in the response could be explained by the model. The variables with confidence levels greater than 95% (P<0.05) were considered as significantly influencing laccase activity and were selected for the further optimization studies.
Optimization of Fermentation Conditions using Response Surface Methodology
Response surface methodology has been successfully applied in many recent biotechnological studies, such as improving the activity of laccases (Niladevi et al. 2009). In this paper, the optimal level of three key factors (methanol concentration, initial pH, and liquid medium volume) and their interactions on the laccase activity were further explored by the Box-Behnken design of experiments; the other six factors (rotation speed, biotin concentration, initial OD600, Cu2+ concentration, Tween-80 concentration, and peptone concentration) were held constant at their zero value (Table 1). By analyzing the experimental data, the following second-order polynomial equation was established to explain the laccase activity:
R1=2978.80-42.62X1+66.00X2+221.38X3-300.50X1X2-135.75X1X3 -119.50X2X3-409.78X12-717.03X22-413.27X32 (3)
where R1 is the predicted laccase enzyme activity (U/L), and X1, X2, and X3 are the coded values of methanol concentration, liquid medium volume, and initial pH, respectively.
Table 5. ANOVA for Response Surface Quadratic Model for Laccase Enzyme Activity
The analysis of the variance (ANOVA) was conducted to test the significance of the fit of the second-order polynomial equation to the experimental data as shown in the Table 5. The model’s F-value of 4.21 indicated the model is significant, and the p-value for “lack of fit” was 0.13, which indicated that the “lack of fit” was not significant at the 95% level of significance. The p-values were used as a tool to check significance of each independent variable (Montgomery 1996). The smaller the p-value becomes, the higher is the significance of the corresponding variable. The p-values in this study were less than 0.1000, which indicated the model’s terms were significant. In this experiment, the quadratic terms X12, X22, and X32were significant in the model. The p-values that were greater than 0.1000 indicated model terms that are not significant. Here, the R2 value was 0.998, which could explain 99.8% of the variability of the response. The results also indicated that the model could accurately predict the highest activity of laccase based on the condition values used during fermentation.
From Equation 3, the optimal coded values of X1, X2, and X3 were estimated to be 0.015, 0.004, and 0.1, respectively. The uncoded values were: methanol concentration 0.603%, liquid medium volume 20.4%, and initial pH 7.1. The model predicted that the maximum laccase activity to be 5360 U/L. To confirm these results, a validation experiment was performed under these optimized conditions in triplicate. The observed experimental values of laccase activity were 4916, 5458, and 5332 U/L with the average of 5235 U/L. The excellent correlation between predicted and measured values verifies the model’s predictability of production process.
Three-dimensional response surface plot described by the regression model (Eq. 3) can be used to further explain the results of the statistical analysis. The response surface plots shown in Fig. 3 indicated that there is a maximum value for the laccase enzyme activity, which depended on the levels of the factors in the medium. In Fig. 3a the initial pH was invariable, whereas the methanol concentration and liquid medium volume were changed as shown in Table 3. Similarly, as shown in Fig. 3b and 3c, the constant value was liquid medium volume and methanol concentration, respectively. Consequently, Fig. 3 showed the maximum laccase enzyme activity as 5360 U/L with the three key factors under the optimal conditions and other variables at their zero levels.
Fig. 3. Response surface plot for the laccase enzyme activity in terms of the effects: (a) X1 (Methanol concentration) and X2 (Liquid medium volume), (b) X1 (Methanol concentration) and X3 (Initial pH), and (c) X2 (Liquid medium volume) and X3 (Initial pH)
Purification and Characterization of Recombinant Laccase
The supernatant from fermentation was harvested from a culture of recombinant P. pastoris GS115-lccA (16 days old) by centrifugation; the resulting supernatant was purified by ultrafiltration and ammonium sulfate precipitation. The purification steps and relevant details, such as laccase activity, specific activity, and fold purification, are shown in Table 6. The results showed a 2.7-fold purification, which corresponded to a final enzyme yield of 31.8%.
The homogeneity of the purified laccases was checked on SDS-PAGE (Fig. 4). The enzyme showed a single band of approximately 58 kDa. So the production cost, the main bottleneck for application of laccase, will be reduced dramatically because of the simple purification steps.
Table 6. Purification of Recombinant P. pastoris GS115-lccA
Fig. 4. SDS-PAGE of the recombinant laccase GS115-LccA: Lane1: purified laccase by adding (NH4)2SO4 to the final mass concentration of 80% for only 12 h; Lane M: Molecular weight markers (10-170 kDa); Line 2: purified laccase by the ultrafiltration using a CXA-50 50000 ultrafiltration membrane; Line 3: Crude laccase
Decolorization of Dyes by Recombinant GS115-lccA
Laccase is known to have an ability to decolorize dyes of various classes (Knapp and Newby 1999). Different laccase isozymes from various sources are known to be diverse with respect to their efficiency to decolorize certain dyestuffs. For the practical application, the use of purified laccase is more economical and cost-effective. In this paper, the capability of the purified recombinant laccases, LccA, from the recombinant P. pastoris was assessed by using two dyes (Reactive Blue KN-R and Acid Red 35). To improve the decolorization of the Acid Red 35 and the Reactive Blue KN-R, conditions of the reaction were optimized by the single factor experiments.
Effect of Different Buffers on Decolorization
The effect of different pH buffer media (Citric acid-sodium citrate buffer, Succinic acid-NaOH buffer, acetic acid-sodium acetate buffer, tartaric acid-sodium tartrate buffer) on decolorization of dyes (100 mg/L) was studied. As shown in Fig. 5a, after 12 h, it was observed that different buffer media could influence the decolorization of dyes, which is useful to accelerate the decolorization of dyes. Among these buffers, the succinic acid-NaOH buffer was the best for Reactive Blue KN-R, and the citric acid-sodium citrate buffer was the best for the Acid Red 35. In the following experiment, the succinic acid-NaOH buffer and citric acid-sodium citrate buffer were chosen in decolorizing the two dyes respectively.
Effect of pH on Decolorization
Different pH values of 3.0, 4.0, 4.5, 5.0, and 6.0 where obtained by adjusting succinic acid-NaOH buffer solution and tartaric acid-sodium tartrate buffer for Reactive Blue KN-R and Acid Red 35, respectively. As shown in Fig. 5b, increasing the pH caused the decolorization of Reactive Blue KN-R to decrease. Meanwhile, the decolor-ization at the pH value of 3.0 and 4.0 were both good. The pH stability property of purified recombinant laccase is favorable for the potential applications of the enzyme. Consequently, additional experiments (pH stability of this recombinant enzyme) indica-ted that a pH value of 4.0 was the best for the decolorization of Reactive Blue KN-R. However, the decolorization of Acid Red 35 increased as the pH increased to 4.5; pH values greater than 4.5 resulted in lower decolorization of Acid Red 35. Therefore, the pH value of 4.5 was determined to be the best for the decolorization of Acid Red 35 by the laccase. Consequently, the pH values for the following experiments of decolorizing Reactive Blue KN-R and Acid Red 35 were 4.0 and 4.5, respectively.
Effect of Temperature on Decolorization
In previous studies, the optimal temperature of the recombinant laccase was 50 oC. Meanwhile, thermostability assays indicated that its residual activity was more that 50% after being incubated at 60 oC for 1 h. In practical applications, the high thermostability of the enzyme is desired because the longer active life means less consumption of the enzyme. The laccase was stable after incubation at 30, 40, and 50 oC for 2 h but residual activity dropped fast at 70 oC. Temperature stability properties of purified recombinant laccase were found to be favorable for the potential applications of the enzyme. The decolorization of the two dyes (Reactive Blue KN-R and Reactive Blue KN-R) were conducted at different temperatures (30, 40, 50, 60, and 70 °C), after 12 h, as shown in Fig. 5c. The optimum temperatures for decolorizing the Reactive Blue KN-R and the Acid Red 35 were 50 °C.
Increasing the temperature above 50 °C caused the decolorization of the two dyes to decrease, which was consistent with the temperature stability of laccase.
Effect of Enzyme Dosage on Decolorization
The higher the laccase activity, the shorter is the reaction time required for dye decolorization. According to the above conditions, the decolorization of the two dyes (100 mg/L) was accomplished with different enzyme dosages (1, 2, 3, 4, and 5 U/mL), as shown in Fig. 5d. As the enzyme dosage increased, the decolorization rate increased and the curve tended to level out after 24 h. The enzyme dosage in decolorizing Reactive Blue KN-R (anthraquinonic dye) and Acid Red 35 (azo dye) were 2 U/mL and 4 U/mL, respectively; in addition, GS115-lccA was better at decolorizing Reactive Blue KN-R than the Acid Red 35. The good decolorization rates further enabled laccase to decolorize the real textile industry wastewater containing synthetic dyes of different chemical structures such as anthraquinone, azo, etc.
In summary, the final maximum decolorization efficiency for 24 h of incubation was determined to be 91.33% for Reactive Blue KN-R and 78.96% for Acid Red 35, under their respective optimum conditions with 2 U/mL and 4 U/mL of enzyme dosage, respectively (Fig. 6). The different chemical structures of dyes might explain these differences in the decolorization efficiencies (Moldes et al. 2003). The described results demonstrated that the capability of decolorizing different dyes was positively related to the laccase activity. The ability of decolorizing these two dyes was dependent on laccase.
Fig. 5. Effect of conditions of the decolorization of the two dyes (the time of decolorization was 24 h): (a) Buffer of the decolorization reaction (1, Blank control 2, Citric acid-sodium citrate buffer 3, Succinic acid – NaOH buffer 4, acetic acid-sodium acetate buffer 5, tartaric acid-sodium tartrate buffer) (b) pH of the decolorization reaction (c) Temperature of the decolorization reaction, and (d) Laccase enzyme activity of the decolorization reaction
The superior points for the recombinant strain P. pastoris GS115-lccA derived from Trametes versicolor in comparison with some other laccases reported previously are summarized below: firstly, the capability of recombinant GS115-lccA for decolorizing Reactive Blue KN-R and Acid Red 35 was relatively good; Secondly, a high decolorization efficiency could be obtained by the recombinant laccase from Trametes versicolor without adding any mediator. That is, a redox mediator was not required for efficient decolorization of dyes by the recombinant laccase. This is more economical and cost-effective for its practical application. Thus, lccA derived from Trametes versicolor exhibits great potential and promising application for decolorizing and detoxifying industrial dyes in waste effluents. This work further provided strong evidence for the efficient function of laccase for decolorizing industrial dyes. Therefore, a further study will focus on assessing the phytotoxicity of the dyes before and after decolorization.
Fig. 6. Effect of time on the decolorization rate of the two dyes by recombinant GS115-lccA
- The recombinant strain Pichia pastoris GS115-lccA could be used to produce heterologous laccase with high enzymatic activity by optimizing the fermentation conditions. The optimum fermentation conditions were: methanol additive amount 0.601%, medium initial pH 7.1, and liquid medium volume 20.4%. The highest enzyme activity of 5235 U/L was achieved, which was 2.2 times the original laccase activity (2357 U/L).
- This enzyme showed excellent decolorization capacity for different dyes. The optima for the decolorizing systems for each dye were as follows: decolorization of Reactive Blue KN-R was achieved by reacting with 2 U/mL enzyme dosage at 50 °C using succinic acid-NaOH buffer (pH 4.0) for 24 h, and the decolorization efficiency for Reactive Blue KN-R of incubation was 91.33%; and the decolorization of Acid Red 35 was achieved with 4 U/mL enzyme dosage at 50 °C using tartaric acid-sodium tartrate buffer (pH 4.5) for 24 h, and the decolorization efficiency for Acid Red 35 was 78.96%, which was still relatively lower compared to Reactive Blue KN-R.
- In summary, our work indicated that this laccase may be used in decolorizing and decontaminating wastewater treatment of similar dyes such as azo, anthraquinones, etc. This work also suggested that laccase has great potential application for color removal of industrial wastewater and for reducing the impact of industrial wastewater on the environment.
This work was supported by the International Advanced Forestry Science and Technology Project Imported by State Forestry Administration (Grant No. 2011-4-15, 2010-4-19), and the project was funded by the Priority Academic Program Development of Jiangsu Higher Education Institutions. Ordinary university graduate student research innovation projects of Jiangsu province (Grant No. CXLX12_0529 and No. CXZZ12_0537) also funded the project.
Abadulla, E., Tzanov, T., Costa, S., Robra, K. H., Cavaco-Paulo, A., and Gubitz, G. M. (2000). “Decolorization and detoxification of textile dyes with a laccase from Trametes hirsuta,” Appl. Environ. Microbiol. 66(8), 3357-3362.
Bradford, M. M. (1976). “A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding,” Anal. Biochem. 72, 248.
Bourbonnais, R., Paice, M.G., Reid, I.D., Lanthier, P., and Yaguchi, M. (1995). “Lignin oxidation by laccase isozymes from Trametes versicolor and role of the mediator 2, 2’-azinobis (3-ethylbenzthiazoline-6-sulfonate) in kraft lignin depolymerisation,” Appl. Environ. Microbiol. 61(5), 1876-1880.
Box, G. E. P., and Behnken, E.W. (1960). “Some new three level designs for the study of quantitative variables,” Technometrics 2(4), 455-475.
Box, G. E. P. and Wilson, K. B. (1951). “On the experimental attainment of optimum conditions,” J. R. Stat. Soc. Ser. B Stat. Methodol. 13(1), 1-45.
Childs, R. E. and Bardsley, W. G. (1975). “The steady-state kinetics of peroxidase with 2, 2′-azino-di-(3-ethyl-benzthiazoline-6-sulphonic acid) as chromogen,” Biochem. J. 145(1), 93-103.
Cusano, A. M., Mekmouche, Y., Meglecz, E., and Tron, T. (2009). “Plasticity of laccase generated by homeologous recombination in yeast,” FEBS J. 276(19), 5471-5480.
Diamantidis, G., Effosse, A., Potier, P., and Bally, R. (2000). “Purification and characterization of the first bacterial laccase in the rhizospheric bacterium Azospirillum lipoferum,” Soil Biol. Biochem. 32(7), 919-927.
Dittmer, N. T., and Kanost, M. R. (2010). “Insect multicopper oxidases: diversity, properties and physiological roles,” Insect Biochem. Mol. Biol. 40(3), 179-188.
He, L. Y., Wang, G. B., Cao, F. L., and Zhao, L. G. (2011). “Cloning of laccase gene from Coriolus versicolor and optimization of culture conditions for Lcc1 expression in Pichia pastoris,” Adv. Mat. Res. 236-238(2011), 1039-1044.
Heinzkill, M., Bech, L., Halkier, T., Schneider, P., and Anke, T. (1998). “Characterization of laccases and peroxidases from wood rotting fungi (Family Coprinaceae),” Appl. Environ. Microbiol. 64(5), 1601-1606.
Hess, J., Leitner, C., Galhaup, C., Kulbe, K.D., Hinterstoisser, B., Steinwender, M., and Haltrich, D. (2002). “Enhanced formation of extracellular laccase activity by the white-rot fungus Trametes multicolor,” Appl. Biochem. Biotechnol. 98-100, 229-241.
Jo, J. H., Lee, D. S., Park, D., Choe, W. S., and Park, J. M. (2008). “Optimization of key process variables for enhanced hydrogen production by Enterobacter aerogenes using statistical methods,” Bioresour. Technol. 99(6), 2061-2066.
Knapp, J. S., and Newby, P.S. (1999). “The decolorization of a chemical industry effluent by white rot fungi,” Water Res. 33(2), 575-577.
Liu, J. Z., Weng, L. P., and Zhang, Q.L. (2003). “Optimization of glucose oxidase production by Aspergillus niger in a benchtop bioreactor using response surface methodology,” World J. Microbiol. Biotechnol. 19(3), 317-323.
Li, Y. Q., Jiang, H. X., Xu, Y. Q., and Zhang, X. H. (2008). “Optimization of nutrient components for enhanced phenazine-1-carboxylic acid production by gacA-inactivated Pseudomonas sp. M18G using response surface method,” Appl. Microbiol. Biotechnol. 77(6), 1207-1217.
Lorenzo, M., Moldes, D., and Sanroman, M. A. (2006). “Effect of heavy metals on the production of several laccase isoenzymes by Trametes versicolor and on their ability to decolourise dyes,” Chemosphere. 63(6), 912-917.
Madzak, C., Mimmi, M. C., Caminade, E., Brault, A., Baumberger, S., Briozzo, P., Mougin, C., and Jolivalt, C. (2006). “Shifting the optimal pH of activity for a laccase from the fungus Trametes versicolor by structure-based mutagenesis,” Protein Eng. Des. Sel. 19(2), 77-84.
Mechichi, T., Mhiri, N., and Sayad, S. (2006). “Remazol Brilliant Blue R decolorization by the laccase from Trametes trogii,” Chemosphere. 64(6), 998-1005.
Moldes, D., Gallego, P. P., Rodriguez, Couto, S., and Sanroman, A. (2003). “Grape seeds: The best lignocellulosic waste to produce laccase by solid state cultures of Trametes hirsuta,” Biotechnol. Lett. 25(6), 491-495.
Montgomery, D. C. (1996). “Design and analysis of experiments,” ISBN 0471157465, U.S.A.
Muralidhar, R. V., Chirumamila, R. R., and Marchant, R. (2001). A response surface approach for the comparison of lipase production by Candida cylindracea using two different carbon sources,” Biochem. Eng. J. 9(1), 17-23.
Nyanhongo, G. S., Gomes, J., Gübitz, G., Zvauya, R., Read, J. S., and Steiner, W. (2002). “Production of laccase by a newly isolated strain of Trametes modesta,” Bioresour. Technol.84(3), 259-63.
Niladevi, K. N., Sukumaran, R. K., Jacob, N., Anisha, G. S., and Prema, P. (2009). “Optimization of laccase production from a novel strain-Streptomyces psammoticus using response surface methodology,” Microbiol. Res. 164(1), 105-113.
Plackett, R. L., and Burman, J.P. (1946). “The design of optimum multifactorial experiments,” Biometrika. 33(4), 305-325.
Schliephake, K., and Lonergan, G. T. (1996). “Laccase variation during dye decolourisation in a 200 L packed-bed bioreactor,” Biotechnol. Lett. 18(8), 881-886.
Sheng, H. L., and Chi, P. F. (1996). “Continuous treatment of textile wastewater by combined coagulation, electrochemical oxidation and activated sludge,” Water Res. 30(3), 587-592.
Sigal, I. A., and Whyne, C.M. (2010). “Mesh morphing and response surface analysis: Quantifying sensitivity of vertebral mechanical behavior,” Ann. Biomed. Eng. 38(1), 41-56.
Solomon, E. I., Sundaram, U. M., and Machonkin, T. E. (1996). “Multicopper oxidases and oxygenases,” Chem. Rev. 96(6), 2563-2606.
Tanyildizi, M. S., Ozer, D., and Elibol, M. (2005). “Optimization of amylase production by Bacillus sp. using response surface methodology,” Process Biochem. 40(7) 2291-2296.
Thurston, C. F. (1994). “The structure and function of fungal laccases,” Microbiology. 140(1), 19-26.
Trupkin, S., Levin, L., Forchiassin, F., and Viale, A. (2003). “Optimization of a culture medium for ligninolytic enzyme production and synthetic dye decolourization using response surface methodology,” J. Ind. Microbiol. Biotechnol. 30(12), 682-690.
Tong, P. G., Hong, Y. Z., Xiao, Y. Z., Zhang, M., Tu, X. M., and Cui, T. G. (2007). “High production of laccase by a new basidiomycete Trametes sp.,” Biotechnol. Lett. 29(2), 295-301.
Vasconcelos, A. F. D., Barbosa, A. M., and Dekker, R. F. H. (2000). “Optimization of laccase production by Botryosphaeria sp. in the presence of veratryl alcohol by the response-surface method,” Proc. Biochem. 35(10), 1131-1138.
Yan, K. L., Wang, H. X., Zhang, X. Y., and Yu, H. B. (2009). “Bioprocess of triphenylmethane dyes decolorization by Pleurotus ostreatus BP under solid-state cultivation,” J. Microbiol. Biotechnol. 19(11), 1421-1430.
Article submitted: March 19, 2013; Peer review completed: May 27, 2013; Revised version received: May 30, 3013; Accepted: May 31, 2013; Published: June 13, 2013.