Abstract
A combination of extracellular enzymes secreted by Irpex lacteus KB-1.1 and Lentinus tigrinus LP-7 showed promising results in the reduction of kappa number of Acacia oxygen-delignified kraft pulp (A-OKP) in previous studies. However, the observed Kappa number reduction was low, and the bleaching process required further optimization. In the current study, the A-OKP was treated with a combination of extracellular enzymes of I. lacteus and L. tigrinus, with a subsequent alkaline peroxide extraction, which significantly improved the Kappa number reduction. The maximum achieved Kappa number reduction was 26%. The effects of static incubation and sterilization of the extracellular enzymes on biobleaching process were evaluated. Compared with a static biobleaching, biobleaching with shaking shortened the required incubation time required from 3 to 1 d. The utility of extracellular enzymes was tested with and without sterilization; no significant differences in Kappa number reduction, brightness, and physical properties of the pulp were observed. The physical properties of all pulp samples were improved following the enzymatic treatment. Furthermore, a low-cost medium containing wood powder supplemented with rice bran and palm sugar (WRBP) was used for the production of enzymes for biobleaching of A-OKP.
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A Pronounced Improvement of the Kappa Number Reduction and Pulp Properties Associated with the Use of Extracellular Enzymes Secreted by Selected Fungal Strains
Sitompul Afrida,a,b Toshihiro Watanabe,a and Yutaka Tamai c,*
A combination of extracellular enzymes secreted by Irpex lacteus KB-1.1 and Lentinus tigrinus LP-7 showed promising results in the reduction of kappa number of Acacia oxygen-delignified kraft pulp (A-OKP) in previous studies. However, the observed Kappa number reduction was low, and the bleaching process required further optimization. In the current study, the A-OKP was treated with a combination of extracellular enzymes of I. lacteus and L. tigrinus, with a subsequent alkaline peroxide extraction, which significantly improved the Kappa number reduction. The maximum achieved Kappa number reduction was 26%. The effects of static incubation and sterilization of the extracellular enzymes on biobleaching process were evaluated. Compared with a static biobleaching, biobleaching with shaking shortened the required incubation time required from 3 to 1 d. The utility of extracellular enzymes was tested with and without sterilization; no significant differences in Kappa number reduction, brightness, and physical properties of the pulp were observed. The physical properties of all pulp samples were improved following the enzymatic treatment. Furthermore, a low-cost medium containing wood powder supplemented with rice bran and palm sugar (WRBP) was used for the production of enzymes for biobleaching of A-OKP.
Keywords: Acacia kraft pulp; Biobleaching; Kappa number; Peroxide extraction
Contact information: a: Department of Bioscience and Chemistry, Hokkaido University, N9W9, Kita-ku, Sapporo 060-8589 Japan; b: STT Migas Balikpapan, Jl Soekarno Hatta Kilometer 8, Balikpapan 76125, East Kalimantan, Indonesia; c: Department of Forest Science, Hokkaido University, N9W9, Kita-ku, Sapporo 060-8589 Japan; *Corresponding author: ytamai@for.agr.hokudai.ac.jp
INTRODUCTION
The use of conventional chlorine-based chemicals in bleaching sequences at kraft mills is currently being reduced because of environmental concerns. As a new environmentally benign bleaching method, the use of enzymes has made an impact on the industrial bleaching of kraft pulp (Farrell et al. 1996). Most research to reduce the amount of chlorine in the pulp and paper industry has recently focused on hemicellulase, e.g., xylanase (Sharma and Kumar 2013); however, oxidative enzymes from white-rot fungi have been successfully applied in biobleaching on a laboratory scale (Moreira et al. 2003; Ibarra et al. 2006). The potential of incorporating oxidative enzymes for the development of chlorine-free pulp bleaching processes has been intensively studied (Paice et al. 1995). The oxidative enzymes secreted by white-rot fungi include manganese-dependent peroxidase (MnP) (Glenn and Gold 1985), lignin peroxidase (LiP) (Tien and Kirk 1984), manganese-independent peroxidase (MIP) (de Jong et al. 1992), and laccase (Lac) (Youn et al. 1995). Studies with different white-rot fungi revealed that MnP is more commonly correlated with delignification during biobleaching than LiP or Lac (Orth et al. 1993); the characteristics and role of MnP in biobleaching process have been extensively studied (Wariishi et al. 1991; Palma et al. 2000; Tello et al. 2000).
Despite extensive investigations of oxidative enzymes from white-rot fungi for biobleaching, it has yet to be industrialized. The major challenges in using of oxidative enzymes for pulp bleaching are cost and environmental health. For example, Lac is the most studied for biobleaching, requiring molecular oxygen and mediators such as 2,2′-azino-bis(3-ethylbenzthiazoline-6-sulfonic acid) (ABTS) or 1-hydroxybenzotriazole (HBT) (Call and Mücke 1997; Eugenio et al. 2010); however, utilization of ABTS or HBT as mediator, in industrial processes is hindered by their high cost and toxicity (Eugenio et al. 2010). In addition, using purified MnP in the mill is costly because this enzyme requires organic acid to stabilize Mn3+ and hydrogen peroxide for electron acceptor (Moreira et al. 2001).
The idea of this study is to find a system in biobleaching in which the enzymes are able to act like they do in their natural situation. Bajpai et al. (2006) have reported that the delignification and brightening observed with the fungus are not only due to MnP, LiP, or Lac alone, but also to the presence of some enzymes and cofactors in the system. This is because a single enzyme is not able to mimic the complete biological system. In addition, degradation of wood components in nature is a complex process involving the synergistic action of a large number of extracellular enzymes, together with low molecular-weight cofactors (Leonowicz et al. 1999; Aro et al. 2005). All these enzymes cooperate to degrade wood component in nature. This synergistic action of the enzymes could be imitated in biobleaching.
Recently, we reported that extracellular enzymes secreted by Irpex lacteus KB-1.1 and Lentinus tigrinus LP-7 have shown promising results in biobleaching of Acacia oxygen-delignified kraft pulp (A-OKP) using low-cost media of agricultural and waste forestry (Afrida et al. 2014). During biobleaching with the culture media, there was no addition of mediators or other factors. These results clearly show that the I. lacteus and L. tigrinus secreted some compounds into culture media that might stabilize the extracellular enzymes during biobleaching. However, some stages of the biobleaching process should be further improved to optimize Kappa number reduction, brightness, and physical properties of the pulp after enzymatic treatment.
The objective of the present study was to examine the biobleaching process by combining a treatment with extracellular enzymes produced by I. lacteus KB-1.1 and L. tigrinus LP-7 and a subsequent alkaline peroxide extraction. The biobleaching activities of these fungi greatly exceeded those of the highly lignin-degradative fungi Phanerochaete chrysosporium and Trametes versicolor (Afrida et al. 2009). The fungi were grown in a low-cost medium containing agricultural and forestry waste of wood rice bran palm sugar for the biobleaching of A-OKP.
EXPERIMENTAL
Materials
Fungal cultures
Irpex lacteus KB-1.1 and Lentinus tigrinus LP-7 were maintained on agar slants at 30 °C. The agar medium was prepared using 0.2% Acacia mangium wood powder, 0.01% guaiacol, and 1.6% potato dextrose agar (PDA) (Nishida et al. 1988). The pre-inocula were obtained by incubating the fungi on PDA at 30 °C for 7 d.
Culture media and enzyme production
The time-course determinations of lignolytic enzyme production were carried out in shallow static liquid cultures (10 mL media in 100 mL Erlenmeyer flasks) at 30 °C containing A. mangium wood powder (40- to 60-mesh) and rice bran (3:2) in a 1% aqueous solution of palm sugar (WRBP). The flasks were inoculated with single plugs (6 mm in diameter) from 1-week-old PDA cultures and incubated without shaking at 30 °C. Every 3 d (for 21 d), the cultures were filtered and centrifuged at 10,000 rpm (r = 55 mm), at 4 °C for 10 min, and the supernatants were used to assay enzyme activity. The experiment was carried out in triplicate.
Methods
Enzyme activity assays
Enzyme activities were determined using a UV-1600 Shimadzu spectrophotometer (Kyoto, Japan) at 40 °C. The method of Hirai et al. (1994) was slightly modified to determine lignolytic activity. MnP, MIP, and Lac activities were determined by monitoring the oxidation of 2,6-dimethoxyphenol at A470. The reaction mixtures for MnP activity contained 1 mM 2,6-dimethoxyphenol, 0.2 mM H2O2, and 1 mM MnSO4 in 50 mM malonate buffer (pH 4.5). The reaction mixtures for MIP activity were the same as for MnP, except that 1 mM EDTA was used instead of 1 mM MnSO4. The reaction mixtures for Lac activity contained 1 mM 2,6-dimethoxyphenol in 50 mM malonate buffer (pH 4.5). LiP activity was determined by monitoring the oxidation of veratryl alcohol at A310; reaction mixtures contained 1.7 mM veratryl alcohol and 0.2 mM H2O2 in 20 mM succinate buffer (pH 3.0).
Cellulase activity determination
The cellulase activity content of the pooled extracellular enzyme fractions of I. lacteus KB-1.1 and L. tigrinus LP-7, which was used for biobleaching treatment, was examined. The cellulase activity was determined by endo-β-1,4-glucanase activity by measuring the amount of reducing sugars released from low-viscosity carboxymethylcellulose (2% w/v) in 50 mM sodium citrate buffer (pH 4.8) at 40 °C for 30 min (Ghose 1987). A glucose standard curve was used to calculate the cellulase activity. The release of reducing sugars was measured using the dinitrosalicylic acid method (Miller 1959).
Pulp treatment
The industrial A-OKP was characterized by the International Standard Organization (ISO) brightness of 47.6% and Kappa number of 9. To determine the effect of consistency on biobleaching process of A-OKP, extracellular enzymes from I. lacteus KB-1.1 and L. tigrinus LP-7 cultures grown in WRBP medium were combined. The cultures were carried out in 100 mL Erlenmeyer flasks, with A-OKP that had been washed with distilled water until the filtrate was colorless. Different volumes of extracellular enzymes from WRBP cultures with maximum MnP activity were added to the A-OKP samples (equivalent to 1 g oven-dried weight), as follows: 10 mL (10% pulp consistency), 20 mL (5%), 34 mL (3%), and 50 mL (2%). The flasks were incubated statically at 40 °C for 3 d. The enzyme-free controls were performed in parallel and processed in the same manner as the enzyme-treated pulp. After treatment, the pulp samples were filtered and washed with distilled water, with a subsequent alkaline peroxide extraction. This experiment was carried out in triplicate and in parallel.
The effect of static incubation on the rate of the biobleaching process was determined as follows. The washed A-OKP was sterilized (121 °C, 20 min) in 200 mL Erlenmeyer flasks. A-OKP samples (equivalent to 6 g oven-dried weight) were treated with 120 mL of combined extracellular enzymes of I. lacteus KB-1.1 and L. tigrinus LP-7 (from WRBP cultures with a maximum MnP activity) and statically incubated at 40 °C for 3 d. In the controls, the extracellular enzymes were replaced with distilled water. After treatment, the pulp samples were filtered and washed with distilled water, with subsequent alkaline peroxide extraction. Two replicate enzymatic and control treatments were performed.
The effect of sterilizing the extracellular enzymes on the time-efficiency of the biobleaching process was assessed as follows. The extracellular enzymes were collected from I. lacteusKB-1.1 and L. tigrinus LP-7 cultures. For the “sterile” biobleaching condition, extracellular enzymes were prepared by filtration through a sterile Millipore filter (0.22 µm). For the “non-sterile” condition, the extracellular enzymes were used without filtration. The combined extracellular enzymes solutions (120 mL) were added to the A-OKP samples (equivalent to 6 g oven-dried weight) that had been sterilized beforehand by autoclaving (121 °C, 20 min). The flasks were incubated horizontally, with shaking (150 rpm) at 40 °C for 24 h. After the treatment, the pulp samples were filtered and washed with distilled water, with a subsequent alkaline peroxide extraction; their physical properties were then analyzed. Two replicate enzymatic and control treatments were performed.
Alkaline peroxide extraction
A modified alkaline peroxide extraction method of Wong et al. (1999) was used. The chelation step was carried out in double plastic bags with 3% pulp consistency and 1% Na-EDTA at 50 °C for 1 h. After the pulp was washed with distilled water, the extraction was carried out with 10% pulp consistency, 0.5% MgSO4, 2% Na2SiO3, 2% NaOH, and 2% peroxide at 80 °C for 2 h. After treatment, the pulp was filtered and washed with hot distilled water (60 to 70 °C).
Analytical techniques
All measurements were made according to the guidelines of Technical Association of the Pulp and Paper Industry (TAPPI), except for viscosity measurements, which were performed according to the Japan Wood Research Society (JWRS 2000). Pulp brightness was determined by using a colorimeter (Suga Test Instruments Co., Ltd, Tokyo, Japan). In this method, the brightness of white, near-white, and natural-colored pulp and paper is determined based on the directional reflectance factor at 457 nm (TAPPI T 452 om-92 1996). The Kappa number was determined using a micro-Kappa number measurement method (Berzins 1966). This micro-Kappa number can be used for the determination of the degree of pulp delignification and is equal to the volume (in mL) of 0.1 N potassium permanganate solutions that is consumed by 1 g of a moisture-free pulp under the appropriate conditions (TAPPI T 236 cm-85 1996). Laboratory handsheets were prepared (grammage of 60 g/m2) for the determination of the physical properties of the pulp (TAPPI TAPPI T 205 sp-95 1996), namely thickness (TAPPI T 411 om-89 1996), burst index (TAPPI T 403 om-91 1996), tensile index (TAPPI T 494 om-88 1996), and tear index (TAPPI T 414 om-88 1996).
RESULTS AND DISCUSSION
Extracellular Lignolytic Enzyme Activities
The time-course of lignolytic enzyme production by I. lacteus and L. tigrinus in shallow static culture in the economical WRBP medium was analyzed. Figure 1 shows the lignolytic activities of both strains grown in the WRBP medium.
Fig. 1. Time-courses of lignolytic enzyme production I. lacteus KB-1.1 (a) and L. tigrinus LP-7 (b). Filled diamond, MnP; filled square, MIP; filled triangle, Lac
Both strains produced MnP, MIP, and Lac; the MnP activity was the highest among these lignolytic enzymes. The lignolytic enzyme activities were higher in L. tigrinus cultures than in I. lacteus cultures; the only exception was the peak MnP activity in I. lacteus culture, which was 2-fold higher than that in the L. tigrinus culture. A maximum production of MnP was observed on days 6 and 12 for I. lacteus and L. tigrinus, respectively. These results indicated that neither I. lacteus nor L. tigrinus excreted LiP into the medium. The maximum enzyme activities obtained were as follows: MnP, 74 ± 7.5 µmol·L‑1·min-1; MIP 41 ± 4.0 µmol·L-1·min-1; and Lac, 18 ± 4.7 µmol·L-1·min-1.
In the current study, the use of WRBP medium leads to higher lignolytic activities in I. lacteus and L. tigrinus cultures, ca. 1 to 5 fold, than when WRBG medium is used (Afrida et al. 2014). Both strains produced MnP, MIP, and Lac, but not LiP. Previous studies show that I. lacteus produces LiP in shallow stationary culture under nitrogen-rich conditions (Novotný et al. 2004) and in a non-immersed liquid culture under nitrogen limitation (Rothschild et al. 2002). Thus, the type of substrate in the culture medium appears to determine the type and amount of extracellular enzymes produced by I. lacteus. There are no published reports on the ability of L. tigrinus to secrete LiP into the culture medium.
The growth of fungi was accompanied by the acidification of WRBP culture, with the pH approaching 5 after 21 days (Fig. 2). The rapid acidification of WRBP culture during the growth of I. lacteus and L. tigrinus was similar to that seen in the WRBG culture, with the pH reaching a value close to 5 at 21 d (Afrida et al. 2014).
Fig. 2. Change in culture pH of I. lacteus KB-1.1 (filled diamond) and L. tigrinus LP-7 (filled square) culture during lignolytic enzyme production
Pulp Treatment
Pooling of the extracellular enzymes of I. lacteus and L. tigrinus results in a greater Kappa number reduction (7.4%) than when single extracellular enzyme fractions are used (I. lacteus, 4.4% and L. tigrinus, 6.7%) (Afrida et al. 2014). Similarly, Kumar and Kumar (2004) observed that a combination of several bacteria for biobleaching is more effective than the use of a single bacterium. Moreover, a combination of fungal species has been used for the bioremediation of pulp and paper mill effluent (Malaviya and Rathore 2007). The pooling of several bacteria or fungi, or extracellular enzymes, gives better results than the use of a single bacterium of fungus, or any single extracellular enzyme. Considering of these results, in the present work a combination of the extracellular enzymes of I. lacteus and L. tigrinus was employed with the maximum MnP for the biobleaching. MnP is a key enzyme in the fungal biobleaching of kraft pulp (Bajpai et al. 2006). Moreira et al. (2001) reported that the maximum brightness obtained and a decrease in Kappa number of eucalyptus oxygen-delignified kraft pulp (ODKP) associated mostly to the production of MnP. For this reason, we used the MnP maximum for collecting the extracellular enzymes for biobleaching of A-OKP.
The feasibility of using fractions of I. lacteus and L. tigrinus WRBP cultures with the maximum MnP activity for the biobleaching of A-OKP was next examined. The effect of pulp consistency on the ability of the extracellular enzymes from WRBP culture to A-OKP was investigated using pulp preparations of four different consistencies (2%, 3%, 5%, and 10%) and was further examined with peroxide extraction to Kappa number reduction (Fig. 3).
Fig. 3. The effect of pulp consistency on kappa number reduction of A-OKP samples upon treatment with the combined extracellular enzymes from I. lacteus KB-1.1 and L. tigrinus LP-7 WRBP medium cultures
The results indicated the importance of the pulp-to-extracellular ratio. When the consistency was 2%, 3%, and 5%, the Kappa number reduction was remarkably decreased (19.8%, 14.8%, and 19.8%, respectively). The effects of these three pulp consistencies on the Kappa number reduction were not significantly different, as assessed by one-way ANOVA (P > 0.05). However, when the consistency was further increased from 5% to 10%, the Kappa number reduction was smaller, by about 6.2% (P < 0.05). Considering these results, 5% consistency was used in subsequent experiment. Geng et al. (2004) found that during softwood kraft pulp bleaching with a Lac/N-(-4-cyanophenyl)acetohydroxamic acid system, 5% pulp consistency resulted in a greater in Kappa number reduction than 10% pulp consistency. The optimal pulp consistency for decreasing the Kappa number in the current study was in the range of 2 to 5%, which coincides with the pulp consistency employed in other experiments (Wong et al. 1999; Ibarra et al. 2006; Fillat et al. 2010). Presumably, low pulp consistency facilitates the mixing and dissolution of enzymes into the pulp. Moreover, low consistency can facilitate the diffusion of lignolytic enzymes into pulp fibers.
Next, the effect of the incubation mode (static or shaking) on the biobleaching process was determined. There was a change of the pulp color during A-OKP biobleaching with extracellular enzymes (decolorization). The incubation was discontinued when the pulp changed from dark brown to light brown. For biobleaching with static incubation, pulp decolorization was observed on day 3. In contrast, during biobleaching with shaking, pulp decolorization occurred on day 1; further, the color of the pulp returned to dark brown. Biobleaching with shaking reduced the incubation time from 3 to 1 d. The Kappa number reduction was also increased by the shaking incubation, by about 2 to 3-fold, compared with the static incubation (Table 1). Interestingly, the use of sterile or non-sterile enzyme preparations, with shaking, was not noticeably different on the kappa number reduction. Moreover, none of the tested conditions (the static or shaking incubation and the sterile or non-sterile enzyme preparation) greatly differed in the viscosity or physical properties of the A-OKP (Tables 2 through 4), with the exception of slight increase in brightness (1.5-fold increase) when a sterile enzyme preparation was used (Table 1). Compared with the control samples, the physical properties of all pulp samples were improved by the enzymatic treatment and were further improved after an alkaline peroxide extraction.
Using the combined extracellular enzymes for A-OKP biobleaching and shaking resulted in a greater in Kappa number reduction, and a slightly increased brightness, than biobleaching with a static incubation. The A-OKP decolorization was more rapid during shaking (1 d) than during a static incubation (3 d). It is not entirely clear how the shaking affects the biobleaching efficacy. This effect may be due to the ease of diffusion and penetration of the enzymes into the pulp, and increased oxygen transfer in the culture medium. Swamy and Ramsay (1999) reported that shaking shortened the incubation time during decolorization of a textile dye, amaranth, from 20 d to 1 d. It is important to monitor the pulp color change during biobleaching because the pulp can turn back to dark brown, leading to an increase in Kappa number and decrease in brightness (data not shown). The decolorization of pulp fibers is further supported by the observation in the differential interference microscopy (Fig. 4). Compared to untreated pulp, pulp after enzymatic treatment showed lighter in fibers color.
In the current study, a biobleaching process was developed to improve the Kappa number reduction in A-OKP, by incorporating an alkaline peroxide extraction step after the enzymatic treatment. The maximum extent of Kappa number reduction obtained with a combination of the extracellular enzymes of I. lacteus and L. tigrinus, and a subsequent alkaline peroxide extraction was approximately 26%. The results of this study confirm that the Kappa number reduction is increased when A-OKP is treated with enzymes, followed by a subsequent alkaline peroxide extraction, over what was observed when A-OKP was treated with enzymes and washed with distilled water (Afrida et al. 2014). It is likely that the alkaline peroxide extraction activates the removal of residual lignin from A-OKP. An enzymatic treatment with subsequent alkaline peroxide extraction or peroxide extraction is an effective method for greatly improving the Kappa number reduction (Ehara et al. 1997; Chakar and Ragauskas 1999) and pulp properties (Babot et al. 2011).
The cellulase activity of the pooled extracellular enzyme fractions of I. lacteus and L. tigrinus was 99 ± 1.8 µmol·L-1·min-1. The high cellulase activity in the combined extracellular I. lacteus and L. tigrinus enzyme preparation adversely affected the enzyme-treated pulp, as demonstrated by the fact that pulp viscosity and physical properties were not significantly reduced after the enzymatic treatment.
Viscosity is an indirect indication of the cellulose quality (Moreira et al. 2003). Some reduction of pulp viscosity is associated with the most oxidative pulp delignification and bleaching treatment. A pronounced reduction in pulp viscosity negatively affects the pulp quality; however, the decrease of pulp viscosity during treatment with extracellular enzymes I. lacteusand L. tigrinus were moderate (33 to 119 mLg-1). Similar results were reported by Ibarra et al. (2006), who treated the pulp with a Lac mediator, with a 100 mLg‑1 loss of viscosity.
Table 1. Brightness, Viscosity, and Kappa Number of the Pulp after an Enzymatic Treatment and a Subsequent Peroxide Extraction
Table 2. Physical Properties of the Pulp after an Enzymatic Treatment with Shaking under Non-Sterile Conditions and a Subsequent Peroxide Extraction
Table 3. Physical Properties of the Pulp after an Enzymatic Treatment with Shaking under Sterile Conditions and a Subsequent Peroxide Extraction
Table 4. Physical Properties of the Pulp after an Enzymatic Treatment with Static Incubation under Non-Sterile Conditions and a Subsequent Peroxide Extraction
Fig. 4. Decolorization of A-OKP pulp fibers was observed by using differential interference microscopy. Untreated pulp (a) and treated pulp with extracellular enzymes (b). Black arrow indicates the fiber of the pulp.
The utilization of agricultural wastes for lignolytic enzyme production has attracted increasing attention (Elisashvili et al. 2006). Lignolytic enzymes have various potential applications in the chemical, fuel, food, pulp and paper, textile, and animal feed industries. Low-cost production is imperative for the employment of lignolytic enzymes on an industrial scale (Cabaleiro et al. 2002). One solution is to use agricultural and forestry waste for extracellular lignolytic enzyme production, for example, during submerged solid-state fermentation (Rivela et al. 2000; Elisashvili et al. 2006). However, the nutrition plays an important role in extracellular enzyme production, as the type and composition of the lignocellulosic substrate determine the type and amount of enzyme produced (Mikiashvili et al. 2004; Moldes et al. 2004).
A previous study (Afrida et al. 2014) demonstrated that wood rice bran glucose (WRBG) medium has the potential to be used as a culture medium for the production of stable extracellular enzymes without increasing the kappa number. We suggest that this stability is due to the secretion of different natural co-factors such as organic acids in culture medium. Organic acids (malonate and oxalate) produced by I. lacteus and L. tigrinus in WRBG culture medium are higher than in wood rice bran (WRB) and wood rice bran malonate (WRBM). According to Wariishi et al. (1992), organic acid plays an important role in MnP reactions because they dissociate of Mn3+ bound from the enzyme complex and stabilize Mn3+ in aqueous solutions. In the same study, they find that from several chelator agents tested, malonate show the most effective chelator for MnP activity. A study of biobleaching with semipurified MnP has shown that Mn3+-malonate complexes are responsible to the brightening and delignification of kraft pulp (Kondo et al. 1994). Thus, the high concentrations of malonate and oxalate secreted by I. lacteus and L. tigrinus in WRBG culture may correlate with activities and stabilities of delignifying extracellular enzymes.
However, the use of WRBG medium should be re-evaluated on account of the increasing cost of glucose. One possible substitute of glucose, palm sugar, which may be easily obtained from traditional markets in Indonesia, can be considered as carbon source for microbial extracellular lignolytic production. The calculated cost of 1 L of WRBG substrate is US $0.21; the calculated cost of 1 L of WRBP substrate is US $0.03. The potential application of WRBP as a culture medium for the large-scale production of extracellular lignolytic enzymes might therefore offer a remarkable economical advantage.
The present study demonstrated the potential of employing extracellular enzymes produced by I. lacteus KB-1.1 and L. tigrinus LP-7 in the biobleaching of A-OKP.
CONCLUSIONS
- This study demonstrated the potential of employing extracellular enzymes produced by I. lacteus KB-1.1 and L. tigrinus LP-7 in the biobleaching of A-OKP. The use of extracellular enzymes, with a subsequent alkaline peroxide extraction, resulted in a further improvement kappa number reduction, compared with a previous study (Afrida et al.2014).
- The performance of biobleaching with extracellular enzymes is improved with shaking and the latter reduces the incubation time by 48 h.
- The use of sterile vs. non-sterile enzyme preparations did not noticeably affect the kappa number reduction, viscosity, and pulp properties of A-OKP.
- The low cost of the WRBP medium may offer an economic advantage for large-scale enzyme production.
ACKNOWLEDGEMENTS
This work was partially supported by JSPS KAKENHI Grant Number 26252022.
REFERENCES CITED
Afrida, S., Tamai, Y., Watanabe, T., and Mitsuru, O. (2009). “Screening of white rot fungi for biobleaching of Acacia oxygen-delignified kraft pulp,” World Journal of Microbiology and Biotechnology 25(4), 639-647. DOI: 10.1007/s11274-008-9932-y
Afrida, S., Tamai, Y., Watanabe, T., and Mitsuru, O. (2014). “Biobleaching of Acacia kraft pulp with extracellular enzymes secreted by Irpex lacteus KB-1.1 and Lentinus tigrinus LP-7 using low-cost media,” World Journal of Microbiology and Biotechnology 30(8), 2263-2271. DOI: 10.1007/s11274-014-1647-7
Aro, N., Pakula, T., and Penttilä, M. (2005). “Transcriptional regulation of plant cell wall degradation by filamentous fungi,” FEMS Microbiology Reviews 29(4), 719-739. DOI: 10.1016/j.femsre.2004.11.006
Babot, E. D., Rico, A., Rencoret, J., Kalum, L., Lund, H., Romero, J., del Río, J. C., Martínez, A. T., and Gutiérrez, A. (2011). “Towards industrially-feasible delignification and pitch removal by treating paper pulp with Myceliophthora thermophila laccase and a phenolic mediator,” Bioresource Technology 102(12), 6717-6722. DOI: 10.1016/j.biortech.2011.03.100
Bajpai, P., Anand, A., and Bajpai, P. K. (2006). “Bleaching with lignin-oxidizing enzymes,” Biotechnology Annual Review 12, 349-378. DOI: 10.1016/S1387-2656(06)12010-4
Berzins, V. (1966). “Micro kappa number,” Pulp and Paper Magazine of Canada 67, 206-208. ISSN: 0033-4103
Cabaleiro, D. R., Rodrı́guez-Couto, S., Sanromán, A., and Longo, M. A. (2002). “Comparison between the protease production ability of ligninolytic fungi cultivated in solid state media,” Process Biochemistry 37(9), 1017-1023. DOI: 10.1016/S0032-9592(01)00307-7
Call, H. P., and Mücke, I. (1997). “History, overview and applications of mediated lignolytic systems, especially laccase-mediator-systems (Lignozym®-process),” Journal of Biotechnology 53(2-3), 163-202. DOI: 10.1016/S0168-1656(97)01683-0
Chakar, F. S., and Ragauskas, A. J. (1999). “The effects of oxidative alkaline extraction stages after laccaseHBT and laccaseNHAA treatments-An NMR study of residual lignins,” Journal of Wood Chemistry and Technology 20(2), 169-184. DOI: 10.1080/02773810009349631
de Jong, E., Field, J. A., and de Bont, J. A. M. (1992). “Evidence for a new extracellular peroxidase. Manganese inhibited peroxidase from the white-rot fungus Bjerkandera sp. BOS 55,” FEBS Letters 299(1), 107-110. DOI: 10.1016/0014-5793(92)80111-S
Ehara, K., Tsutsumi, Y., and Nishida, T. (1997). “Biobleaching of softwood and hardwood kraft pulp with manganese peroxidase,” Mokuzai Gakkaishi 43(10), 861-868. ISSN: 0021-4795
Elisashvili, V., Penninckx, M., Kashlishvili, E., Asatiani, M., and Kvesitadze, G. (2006). “Use of Pleurotus dryinus for lignocellulolytic enzymes production in submerged fermentation of mandarin peels and tree leaves,” Enzyme and Microbial Technology 38(7), 998-1004. DOI: 10.1016/j.enzmictec.2005.08.033
Eugenio, M. E., Santos, S. M., Carbajo, J. M., Martín, J. A., Martín-Sampedro, R., González, A. E., and Villar, J. C. (2010). “Kraft pulp biobleaching using an extracellular enzymatic fluid produced by Pycnoporus sanguineus,” Bioresource Technology 101(6), 1866-1870. DOI: 10.1016/j.biortech.2009.09.084
Farrell, R. L., Viikari, L., and Senior, D. J. (1996). “Enzyme treatments of pulp,” in: Pulp Bleaching-Principles and Practice, C. W. Dence and D. W. Reeve (eds.), TAPPI Press, Atlanta, GA, USA, pp. 363-378.
Fillat, A., Colom, J. F., and Vidal, T. (2010). “A new approach to the biobleaching of flax pulp with laccase using natural mediators,” Bioresource Technology 101(11), 4104-4110. DOI: 10.1016/j.biortech.2010.01.057
Geng, X., Li, K., and Xu, F. (2004). “Investigation of hydroxamic acids as laccase-mediators for pulp bleaching,” Applied Microbiology and Biotechnology 64(4), 493-496. DOI: 10.1007/s00253-003-1475-4
Ghose, T. K. (1987). “Measurement of cellulase activities,” Pure and Applied Chemistry 59(2), 257-268. DOI: 10.1351/pac198759020257
Glenn, J. K., and Gold, M. H. (1985). “Purification and properties of an extracellular Mn(II)-dependent peroxidase from the lignin-degrading basidiomycete, Phanerochaete chrysosporium,” Archives of Biochemistry and Biophysics 242(2), 329-341. ISSN: 0003-9861
Hirai, H., Kondo, R., and Sakai, K. (1994). “Screening of lignin-degrading fungi and ligninolytic enzyme activities during biological bleaching of kraft pulp,” Mokuzai Gakkaishi 40(9), 980-986. ISSN: 0021-4795
Ibarra, D., Camarero, S., Ramero, J., Martínez, M. J., and Martínez, A. T. (2006). “Integrating laccase-mediator treatment into an industrial-type sequence for totally chlorine-free bleaching of eucalypt kraft pulp,” Journal of Chemical Technology and Biotechnology 81(7), 1159-1165. DOI: 10.1002/jctb.1485
Japan Wood Research Society (JWRS) (2000). Monkushitsukagaku Jikken Manual, Buneido, Tokyo.
Kumar, R., and Kumar, A. (2004). “Process for bio-bleaching of kraft pulp using bacterial consortia,” U. S. Patent No. 7736879 B2.
Leonowicz, A., Matuszewska, A., Luterek, J., Ziegenhagen, D., Wojtaś-Wasilewska, M., Cho, N-S., Hofrichter, M., and Rogalski, J. (1999). “Review: Biodegradation of lignin by white rot fungi,” Fungal Genetik and Biology 27(2-3), 175-185. DOI: 10.1006/fgbi.1999.1150
Malaviya, P., and Rathore, V. S. (2007). “Bioremediation of pulp and paper mill effluent by a novel fungal consortium isolated from polluted soil,” Bioresource Technology 98(18), 3647-3651. DOI: 10.1016/j.biortech.2006.11.021
Mikiashvili, N., Wasser, S. P., Nevo, E., Chichua, E., and Elisahvili, V. (2004). “Lignocellulolytic enzyme activities of medicinally important basidiomycetes from different ecological niches,” International Journal of Medicinal Mushrooms 6(1), 63-71. DOI: 10.1615/IntJMedMushr.v6.i1.70
Miller, G. L. (1959). “Use of dinitrosalicylic acid reagent for determination of reducing sugar,” Analytical Chemistry 31(3), 426-428. DOI: 10.1021/ac60147a030
Moldes, D., Lorenzo, M., and Sanromán, M. A. (2004). “Different proportion of laccase isoenzymes produced by submerged cultures of Trametes versicolor grown on lignocellulosic waste,” Biotechnology Letters 26(4), 327-330. DOI: 10.1023/B:BILE.0000015452.40213.bf
Moreira, M. T., Sierra-Alvarez, R., Lema, J. M., Feijo, G., and Field, J. A. (2001). “Oxidation of lignin in eucalyptus kraft pulp by manganese peroxidase from Bjerkandera sp. strain BOS55,” Bioresources Technology 78(1), 71-79. DOI: 10.1016/S0960-8524(00)00161-9
Moreira, M. T., Feijoo, G., Canaval, J., and Lema, J. M. (2003). “Semipilot-scale bleaching of Kraft pulp with manganese peroxide,” Wood Science and Technology 37(2), 117-123. DOI: 10.1007/s00226-003-0175-7
Nishida, T., Kashino, Y., Mimura, A., and Takahara, Y. (1988). “Lignin biodegradation by white rot fungi I. Screening of lignin-degrading fungi,” Mokuzai Gakkaishi 34(6), 530-536. ISSN: 0021-4795
Novotný, Č., Svobodová, K., Kashinath, A., and Erbanová, P. (2004). “Biodegradation of synthetic dyes by Irpex lacteus under various growth conditions,” International Biodeterioration & Biodegradation 54(2-3), 215-223. DOI: 10.1016/j.ibiod.2004.06.003
Orth, A. B., Royse, D. J., and Tien, M. (1993). “Ubiquity of lignin-degrading peroxidase among various wood-degrading fungi,” Applied and Environmental Microbiology 59(12), 4017-4023. ISSN: 0099-2240
Paice, M. G., Bourbonnais, R., Reid, I. D., Archibald, F. S., and Jurasek, L. (1995). “Oxidative bleaching enzymes: A review,” Journal Pulp and Paper Science 21(8), J280-J284. ISSN: 0826-6220
Palma, C., Martínez, A. T., Lema, J. M., and Martínez, M. J. (2000). “Different fungal manganese-oxidizing peroxidise: A comparison between Bjerkandera sp. and Phanerochaete chrysosporium,” Journal of Biotechnology 77(2-3), 235-245. DOI: 10.1016/S0168-1656(99)00218-7
Rivela, I., Rodríguez, C., and Sanromán, A. (2000). “Extracellular lignolytic enzyme production by Phanerochaete chrysosporium in a new solid-state bioreactor,” Biotechnology Letters22(18), 1443-1447. DOI: 10.1023/A:1005607000999
Rothschild, N., Novotný, Č., Šašek, V., and Dosoretz, C. G. (2002). “Ligninolytic enzymes of the fungus Irpex lacteus (Polyporus tulipiferae): Isolation and characterization of lignin peroxidase,” Enzyme and Microbial Technology 31(5), 627-633. DOI: 10.1016/S0141-0229(02)00171-0
Sharma, M., and Kumar, A. (2013). “Xylanases: An overview,” British Biotechnology Journal 3 (1), 1-28. DOI: 10.9734/BBJ/2013/1784
Swamy, J., and Ramsay, J. A. (1999). “The evaluation of white rot fungi in the decoloration of textile dyes,” Enzyme and Microbial Technology 24(3-4), 130-137. DOI: 10.1016/S0141-0229(98)00105-7
TAPPI T205 sp-95 (1996), “Forming handsheets for physical tests of pulp,” TAPPI Press, Atlanta, GA, USA.
TAPPI T236 cm-85 (1996). “Kappa number of pulp,” TAPPI Press, Atlanta, GA, USA.
TAPPI T403 om-91 (1996), “Bursting strength of paper,” TAPPI Press, Atlanta, GA, USA.
TAPPI T411 om-89 (1996), “Thickness (caliper) of paper, paperboard, and combined board,” TAPPI Press, Atlanta, GA, USA.
TAPPI T414 om-88 (1996), “Internal tearing resistance of paper (Elmendorf-type method),” TAPPI Press, Atlanta, GA, USA.
TAPPI T452 om-92 (1996). “Brightness of pulp, paper, and paperboard (directional reflectance at 457 nm),” TAPPI Press, Atlanta, GA, USA.
TAPPI T494 om-88 (1996), “Tensile breaking properties of paper and paperboard (using constant rate of elongation apparatus,” TAPPI Press, Atlanta, GA, USA.
Tello, M., Corsini, G., Larrondo, L. F., Salas, L., Salas, L., and Vicuña, R. (2000). “Characterization of three new manganese peroxidise genes from the ligninolytic basidiomycete Ceriporiopsis subvermispora,” Biochimica et Biophysica Acta (BBA) – Gene Structure and Expression 1490(1-2), 137-144. DOI: 10.1016/S0167-4781(99)00227-4
Tien, M., and Kirk, T. K. (1984). “Lignin-degrading enzyme from Phanerochaete chrysosporium: purification, characterization and catalytic properties of a unique H2O2-requiring oxygenase,” Proceedings of the National Academy of Sciences of the United States of America 81(8), 2280-2284. ISSN: 1091-6490
Wariishi, H., Valli, K., and Gold, M. H. (1991). “In vitro depolymerization of lignin by manganese peroxidise of Phanerochaete chrysosporium,” Biochemical and Biophysical Research Communications 176(1), 269-273. DOI: 10.1016/0006-291X(91)90919-X
Wariishi, H., Valli, K., and Gold, M. H. (1992). “Manganese(II) oxidation by manganese peroxidase from the Basidiomycete Phanerochaete chrysosporium,” The Journal of Biological Chemistry 267(25), 23688-23695
Wong, K. K. Y., Anderson, K. B., and Kibblewhite, R. P. (1999). “Effects of the laccase-mediator system on the handsheet properties of two high kappa kraft pulps,” Enzyme and Microbial Technology 25(1-2), 125-131. DOI: 10.1016/S0141-0229(99)00022-8
Youn, H.-D., Hah, Y. C., and Kang, S.-O. (1995). “Role of laccase in lignin degradation by white-rot fungi,” FEMS Microbiology Letters 132(3), 183-188. DOI: 10.1111/j.1574-6968.1995.tb07831.x
Article submitted: June 3, 2017; Peer review completed: July 24, 2017; Revised version received and accepted: September 11, 2017; Published: September 21, 2017.
DOI: 10.15376/biores.12.4.8272-8285