Heat-Resistant Properties of α-Chymotrypsin Adsorbed onto Biomass Charcoal Powder

Abstract

Biomass charcoal powder (BCP) was used as a carrier for immobilization of α-chymotrypsin through adsorption. BCP was derived from plant biomass wastes such as dumped bamboos by oxygen-free pyrolysis at low temperatures and grinding with a jet mill. The activity of adsorbed α-chymotrypsin was strongly dependent upon the kind of BCP. The thermal denaturation curve of adsorbed α-chymotrypsin was shifted to high temperature, compared to that of free one. When α-chymotrypsin adsorbed onto BCP of bamboos was incubated at 45°C, the half-life of adsorbed α-chymotrypsin was 2.6 times greater than that of free one. After incubation at 45°C, the remaining activity of adsorbed α-chymotrypsin markedly depended on the kind of BCP.

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Noritomi, H. , Kurihara, S. , Endo, N. and Kato, S. (2014) Heat-Resistant Properties of α-Chymotrypsin Adsorbed onto Biomass Charcoal Powder. Journal of Biomaterials and Nanobiotechnology, 5, 179-185. doi: 10.4236/jbnb.2014.53021.

1. Introduction

Adsorption of enzymes onto various water-insoluble carriers has attracted continuous attention in the fields of biotechnology, fine chemistry, pharmacy, and biosensor, since the immobilization of enzymes by adsorption has been considered as the simplest and most economical method [1] [2] . Furthermore, since the performances of adsorbed enzymes such as activity, specificity, and stability largely depend upon the physical and chemical surface properties of carriers, it is possible to derive the desired performances of enzymes by selecting a suitable carrier [3] .

On the other hand, technologies for producing useful products such as fuels and materials from biomass waste have been developed in order to establish recycling society. Plant biomass charcoal prepared from plant biomass wastes has been widely studied as renewable resources. Plant biomass charcoal has been applied to soil amendments, adsorbents, humidity control materials, materials for wastewater treatment, and catalysts [4] -[9] . However, plant biomass wastes have not sufficiently been recycled yet, compared to other wastes, although an enormous amount of plant biomass wastes has been discharged in the world. Moreover, the development in the high value-added function of plant biomass charcoal has been desired.

In order to assess the property of plant biomass charcoal as a biomaterial, we have so far investigated the interaction between a protein and plant biomass charcoal derived from dumped adzuki beans and so on, when hen egg white lysozyme (HEWL) was used as a model protein, and have found out that plant biomass charcoal effectively adsorbs HEWL, and HEWL adsorbed onto plant biomass charcoal exhibits the enhanced storage stability at low temperatures and the excellent thermal stability at high temperatures, compared to those of free HEWL [10] -[12] . In addition, we have reported that plant biomass charcoal can sufficiently adsorbs α-chymotrypsin [13] .

In the present work, in order to assess the generality on the stabilization effect of plant biomass charcoal on proteins, we employed bovine pancreas α-chymotrypsin as a model protein, since it is well investigated regarding its structure, functions, and properties [14] . The finely grinded biomass charcoal powder was derived from plant biomass wastes such as dumped bamboos by oxygen-free pyrolysis at low temperatures and grinding with a jet mill.

2. Materials and Methods

2.1. Materials

α-Chymotrypsin (EC 3.4.21.1 from bovine pancreas) (Type II, 52 units/mg solid) was purchased from Sigma-Aldrich Co. (St. Louis, USA). p-Nitrophenyl acetate was obtained from Wako Pure Chemical Industries, Ltd. (Osaka, Japan).

2.2. Preparation and SEM Image of Biomass Charcoal Powder

Under nitrogen atmosphere, dumped bamboos were dried at 180˚C for 2 hr, were pyrolyzed at 450˚C for 2 hr, were carbonized at 350˚C for 3 hr, and then were cooled at 100˚C for 1 hr by pyrolyzer (EE21 Pyrolyzer, EEN Co. Ltd., Japan), as shown in Figure 1. Biomass charcoal powder (BCP) was obtained by grinding the resultant biomass charcoal (BC) with jet mill (100AS, Fuji Sangyo Co. Ltd., Japan). BCP of waste adzuki beans or woods was prepared by the same method.

The SEM micrograph was obtained using a scanning electron microscope (JSM-7500FA, JEOL, Japan) operating at 15 kV. The sample for SEM was prepared on a carbon tape without vapor deposition.

2.3. Adsorption of α-Chymotrypsin onto BCP

As a typical procedure, 5 mL of 0.01 M phosphate buffer solution at pH 7 containing 300 μM α-chymotrypsin and 3 g/L BCP was placed in a 10-mL test tube with a screw cup, and was incubated at 25˚C and 120 rpm for 24 h. After adsorption, the mixture was filtrated with a membrane filter (pore size: 0.1 μm, Millipore Co. Ltd.) to col-

Figure 1. Scheme of preparation of biomass charcoal.

lect α-chymotrypsin adsorbed onto BCP. The amount of α-chymotrypsin adsorbed onto BCP was calculated by subtracting the amount of α-chymotrypsin included in the supernatant liquid after adsorption from the amount of α-chymotrypsin in the aqueous solution before adsorption. The amount of α-chymotrypsin was measured at 280 nm by UV/vis spectrophotometer (UV-1800, Shimadzu Co. Ltd.).

2.4. Measurement of Activity of Free and Adsorbed α-Chymotrypsin

α-Chymotrypsin activity was determined using p-nitrophenyl acetate as a substrate [15] . Four mL of 0.01 M phosphate buffer solution at pH 7.5 containing free or adsorbed α-chymotrypsin (29.5 μM) was added to 16 mL of 0.01 M phosphate buffer solution at pH 7.5 containing 750 μM p-nitrophenyl acetate, and the mixture was incubated at 25˚C and 120 rpm. The absorbance of the mixture was periodically measured at 400 nm by UV/vis spectrophotometer (UV-1800, Shimadzu Co. Ltd.).

2.5. Effect of Temperature on Stability of Free and Adsorbed α-Chymotrypsin

In order to assess the thermal stability of free and adsorbed α-chymotrypsin, the activity of free or adsorbed α-chymotrypsin was measured after free or adsorbed α-chymotrypsin was stored in 0.01 M phosphate buffer solution at pH 7.5 and 45˚C for 10 min, and then was cooled at 25˚C for 60 min. The residual activity was obtained by Equation (1).

(1)

3. Results and Discussion

3.1. Characterization of BCP

The present method for preparing BCP is an environmentally benign process, since plant biomass wastes are not burned in the process of pyrolysis at low temperatures. As seen in Figure 2, the morphology in BC of bamboos was kept, similar to that in native bamboos. Additionally, functional groups containing oxygen atoms are formed by thermal decomposition of cellulose and hemicelluloses at low temperatures, and are useful for the adsorption of proteins [16] .

Figure 3 shows the scanning electron micrograph of BCP of bamboos. As seen in the figure, any distinguishing roughness was not observed on the surface of BCP of bamboos. In our previous work [10] , the mean diameter of BCP of bamboos was 7 μm. Specific surface area of BCP of bamboos was 294 m2/g [13] . The pore

Figure 2. Photographs of BCP of bamboos: (a) raw bamboos; (b) biomass charcoal (BC) of bamboos after pyrolysis; (c) biomass charcoal powder (BCP) of bamboos obtained after grinding.

Figure 3. SEM image of BCP of bamboos.

diameter peak was less than 2.6 nm [13] . The ζ potential of BCP of bamboos was −53.5 mV at solution pH 7 [10] . Moreover, from the results of 13C-NMR and X-ray photoelectron spectroscopy (XPS), acidic functional groups such as phenols, carbonyl groups, and carboxyl groups were detected in BCP [10] .

3.2. Activity of α-Chymotrypsin Adsorbed onto Different Kinds of Biomass Charcoal Powder

The surface chemical and pore properties of BCP are strongly dependent upon a kind of plant biomass wastes [10] [13] . In order to assess the influence of the kind of BCP on the activity of α-chymotrypsin adsorbed onto BCP, the activities of α-chymotrypsin adsorbed onto BCP prepared from different kinds of plant biomass wastes were investigated. As seen in Figure 4, the activity of adsorbed α-chymotrypsin was smaller than that of free one. Moreover, the activity of adsorbed α-chymotrypsin markedly depended upon the kind of BCP, and the activity of α-chymotrypsin adsorbed onto BCP of bamboos was the highest value. The activity of α-chymotrypsin adsorbed onto BCP of bamboos was 1.48 μmol/min·g of enzyme, while that of free α-chymotrypsin was 8.67 μmol/min·g of enzyme. Therefore, the effectiveness factor, which was defined as the ratio of the activity of α-chymotrypsin adsorbed onto BCP to that of free one, exhibited 0.17. On the other hand, from the results of 13C-NMR and XPS, acidic functional groups such as phenols, carbonyl groups, and carboxyl groups are detected on the surface of BCP [10] . Moreover, since the amount of α-chymotrypsin adsorbed onto BCP is strongly influenced by the solution pH and the salt concentration, electrostatic interactions and hydrogen bonds via functional groups largely contribute to the adsorption of enzymes onto BCP [13] . Thus, it is suggested that the flexibility of enzymes might be limited by the adsorption. Additionally, it is possible that enzymes are partially denatured, and the active site of enzymes is shielded due to the undesired orientation of enzyme molecules through the adsorption.

3.3. Dependence of the Remaining Activity of α-Chymotrypsin Adsorbed onto Bamboo Charcoal on Incubation Temperature

Figure 5 shows the relationship between the incubation temperature and the remaining activity of free α-chymotrypsin (α-CT) or α-chymotrypsin adsorbed onto BCP of bamboos after the incubation time for 10 min. As seen in the figure, the dependence of the remaining activity on the temperature exhibited the sigmoid curve. The remaining activity of α-chymotrypsin adsorbed onto BCP of bamboos gradually dropped in the range from 35˚C to 55˚C, and still exhibited 12% at 55˚C, which was four times larger than that of free enzyme, although the remaining activity of free α-chymotrypsin dramatically decreased with an increase in temperature in the range from 35˚C to 55˚C. Additionally, the transition temperature of α-chymotrypsin adsorbed onto BCP of bamboos was around 46˚C, whereas that of free α-chymotrypsin was around 41˚C, similar to that measured by fluorescence analysis [17] . These results indicated that adsorbing α-chymotrypsin onto BCP of bamboos effectively enhanced the thermal stability of α-chymotrypsin. Specifically, the difference of the remaining activity between adsorbed enzyme and free enzyme was observed around 50˚C, where is the optimum temperature of α-chymotrypsin [14] . In addition to the maintenance of enzyme structures due to the adsorption of enzyme molecules, it

Figure 4. Activities of α-chymotrypsin adsorbed onto different BCP.

Figure 5. Thermal denaturation curves of free α-chymotrypsin and α-chymotrypsin adsorbed onto BCP of bamboos. The aqueous solution of free α-chymotrypsin or α-chymotrypsin adsorbed onto BCP of bamboos was incubated at requisite temperature for 10 min.

was suggested that the autolysis of enzymes was inhibited by adsorbing enzyme molecules onto BCP of bamboos, while free enzyme was gradually denatured in water by autolysis.

3.4. Time Dependent Inactivation of α-Chymotrypsin

In general, the activity of enzymes gradually decreases with an increase in incubation time. Figure 6 shows the time course of remaining activities of free α-chymotrypsin and α-chymotrypsin adsorbed onto BCP of bamboos at pH 7.5 and 45˚C. Free α-chymotrypsin solution was transparent during the incubation. On the other hand, any cohesion of adsorbed enzymes was not observed during the incubation. Thus, the intermolecular aggregation among unfolded proteins was not observed at the present enzyme concentration. The figure revealed that the adsorbed enzyme retained relatively high catalytic activity. In the figure, the relationship of the remaining activities of free and adsorbed enzymes with incubation time can be correlated by first-order kinetics. As shown in Table 1, the half-life of adsorbed enzymes was 2.6 times longer than that of free enzymes. Thus, the robust stability of enzymes was obtained by adsorbing enzyme molecules onto BCP.

3.5. Remaining Activity of α-Chymotrypsin Adsorbed onto Different Kinds of Biomass Charcoal Powder after Heat Treatment

In order to extend our study, the remaining activities of α-chymotrypsin adsorbed onto BCP prepared from different kinds of plant biomass wastes after the incubation at 45˚C for 10 min were investigated. The stability of α-chymotrypsin was sufficiently enhanced by adsorbing α-chymotrypsin onto BCP, as shown in Figure 7, compared to that of free α-chymotrypsin. The sequence of the remaining activity of BCP-adsorbed α-chymotrypsin went as follows: BCP of bamboos > BCP of woods > BCP of adzuki beans. On the other hand, the sequence of the remaining activity of BCP-adsorbed HEWL went as follows: BCP of adzuki beans > BCP of woods > BCP of bamboos in our previous work [12] . These results indicate that a suitable kind of BCP to one protein depends upon a kind of protein.

4. Conclusion

We have demonstrated that BCP is useful to protein carrier from the standpoint of the activity and stability of α- chymotrypsin. The kind of BCP affected the activity and stability of adsorbed α-chymotrypsin. Especially, α- chymotrypsin adsorbed onto BCP of bamboos exhibited sufficient activity and stability. On the other hand, HEWL adsorbed onto BCP of adzuki beans showed excellent storage and thermal stability [11] [12] . Therefore, a suitable kind of BCP to one protein is dependent upon a kind of protein. There are various kinds of plant bio-

Figure 6. Time course of remaining activities of free α-chymotrypsin and α-chymotrypsin adsorbed onto BCP of bamboos through the heat treatment at 45˚C.

Figure 7. Effect of kind of BCP on remaining activity of α-chymotrypsin adsorbed onto BCP after heat treatment at 45˚C for 10 min.

Table 1. Rate constants and half-lives of inactivation of α-chymotrypsin at 45˚C.

mass waste on earth. Accordingly, the enhancement in the performance of proteins shown by adsorbing proteins onto BCP would be encouraging for its choice in application such as a biomaterial.

Acknowledgements

This work was supported by a Grant-in-Aid for Scientific Research from Japan Society for the Promotion of Science (C) (No. 24561013).

NOTES

*Corresponding author.

Conflicts of Interest

The authors declare no conflicts of interest.

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