Polyethylene glycol improves phenol removal by immobilized turnip peroxidase

Share Embed


Descrição do Produto

Bioresource Technology 99 (2008) 8605–8611

Contents lists available at ScienceDirect

Bioresource Technology journal homepage: www.elsevier.com/locate/biortech

Polyethylene glycol improves phenol removal by immobilized turnip peroxidase F. Quintanilla-Guerrero a, M.A. Duarte-Vázquez b, B.E. García-Almendarez a, R. Tinoco c, R. Vazquez-Duhalt c, C. Regalado a,* a

Departamento de Investigación y Posgrado en Alimentos PROPAC, Universidad Autónoma de Querétaro, Facultad de Química, C.U. Cerro de las Campanas s/n, Querétaro, Qro 76010, Mexico b NUCITEC S.A. de C.V. Comerciantes 15-3, Peñuelas, Querétaro, Qro 76148, Mexico c Instituto de Biotecnología UNAM Av. Universidad 2001 Col. Chamilpa Cuernavaca Morelos 62215, Mexico

a r t i c l e

i n f o

Article history: Received 25 September 2007 Received in revised form 3 April 2008 Accepted 3 April 2008 Available online 23 May 2008 Keywords: Peroxidase Phenolic compounds Immobilization Polyethylene glycol

a b s t r a c t Purified peroxidase from turnip (Brassica napus L. var. esculenta D.C.) was immobilized by entrapment in spheres of calcium alginate and by covalent binding to Affi-Gel 10. Both immobilized Turnip peroxidase (TP) preparations were assayed for the detoxification of a synthetic phenolic solution and a real wastewater effluent from a local paints factory. The effectiveness of phenolic compounds (PC’s) removal by oxidative polymerization was evaluated using batch and recycling processes, and in the presence and in the absence of polyethylene glycol (PEG). The presence of PEG enhances the operative TP stability. In addition, reaction times were reduced from 3 h to 10 min, and more effective phenol removals were achieved when PEG was added. TP was able to perform 15 reaction cycles with a real industrial effluent showing PC’s removals >90% PC’s during the first 10 reaction cycles. High PC’s removal efficiencies (>95%) were obtained using both immobilized preparations at PC’s concentrations 50% removal, reported 10 phenol removal cycles, using the same reaction time. Thus, the protective effect of PEG during phenol removal by peroxidase activity is clearly demonstrated. 3.7. Thermal stability of free and immobilized TP The thermal stability of the free, covalent immobilized, and alginate-entrapped peroxidase was monitored after incubating at 50, 60 and 70 °C for various time intervals. Heat inactivation rate increased with the temperature and the length of heat exposure. Free enzyme retained 50% of the original activity within the first fivemin incubation at 70 °C, while the covalently and alginate-immobilized peroxidase exhibited close to 85% and 70%, respectively, of their original activity at the same conditions. Arrhenius plots were prepared and the activation energy for peroxidase destruction, DG and DH were calculated (Table 3). Free native turnip peroxidase showed lower values of the thermodynamic parameters evaluated (Ea, DG and DH), when compared to those obtained for both immobilized TP preparations. Results from Table 3 demonstrated that the covalently immobilized was signif-

120

Alginate entrapped

Residual activity (%) Phenol removal (%)

100 80 60 40 20

120

Covalently immobilized 100

Residual activity (%) Phenolremoval (%)

8610

80 60 40 20 0 0

1

2

3

4

5

6

7

8

9 10 11 12 13 14 15

Reaction cycle Fig. 7. Effect of reaction cycles number on the efficiency of phenolic compounds removal from a paints factory wastewater, and on residual enzyme activity, using covalently immobilized TP through column operation. Cycle contact time = 10 min, [PEG] = 100 mg l1. TP activity 1.2 U ml1, 1.09 mM total phenols concentration, 1.7 mM H2O2. Free TP removed 99 ± 1% phenols, and showed a residual activity of 60 ± 3%, in a single cycle process.

Table 3 Thermodynamic values of thermal inactivation of native and immobilized preparations of turnip peroxidase (± standard deviation) TP preparation Native Alginate-entrapped Covalently immobilized

Ea (kJ mol1) a

113.9 ± 6.2 159.5 ± 8.3b 170.4 ± 9.5b

DG (kJ mol1) a

103.2 ± 4.8 106.4 ± 5.3a 107.0 ± 5.1a

DH (kJ mol1) 111.0 ± 5.9a 156.6 ± 8.8b 167.5 ± 9.3b

Different letters within the same column are significantly different (p < 0.05).

icantly more thermally stable than the alginate-entrapped TP. This higher thermostability and catalytic efficiency of covalent immobilized peroxidase, make it a good alternative for many biotechnological processes in which a thermally stable enzyme is required. 4. Conclusion We can conclude so far that the presence of PEG in the reaction mixture protects TP from inactivation during phenol polymerization. This protection allows to extend the enzyme lifetime when it is immobilized, both covalently or entrapped, increasing the number of reaction cycles with high removal efficiency. Phenol removal from a real wastewater effluent was efficiently performed by immobilized TP in presence of PEG. The alginate-entrapped TP showed an unexpectedly higher efficiency in phenols removal than the covalently immobilized enzyme, despite peroxidase activity losses due to enzyme diffusion out of the matrix, which was attributed to the PEG-TP confinement within the alginate matrix. This intimate PEG-TP contact was not achieved by the recycle system used for phenols removal by covalently immobilized peroxidase. A large-scale enzymatic process for industrial effluent treatment is expected to be developed with immobilized TP that should be stable enough to make the process economically feasible. Acknowledgement

0 0

1

2

3

4

5

6

7

8

9 10 11 12 13 14 15

We are grateful to CONACYT for a Ph.D. scholarship to FQG.

Reaction cycle References Fig. 6. Effect of reaction cycles number on the efficiency of phenolic compounds removal from a paints factory wastewater, and on residual enzyme activity, using calcium alginate-entrapped TP. Cycle contact time = 10 min, [PEG] = 100 mg l1, TP activity (free and immobilized) 1.2 U ml1, 1.09 mM total phenols concentration, 1.7 mM H2O2. Free TP removed 99 ± 1% phenols, and showed a residual activity of 60 ± 3%, in a single cycle process.

Agostini, E., Medina, M.I., Milrad de Forchetti, S.R., Tigier, H., 1997. Properties of two anionic peroxidase isoenzymes from turnip (Brassica napus L.) roots. J. Agric. Food Chem. 45, 596–598. Aitken, M.D., 1993. Waste treatment applications of enzymes: opportunities and obstacles. Chem. Eng. J. 52, B49–B58.

F. Quintanilla-Guerrero et al. / Bioresource Technology 99 (2008) 8605–8611 Akhtar, S., Husain, Q., 2006. Potential applications of immobilized bitter gourd (Momordica charantia) peroxidase in the removal of phenols from polluted water. Chemosphere 65, 1228–1235. Aoyama, H., Hojo, H., Takahashi, K.L., Shimizu, N., Araki, M., Harigae, M., Tanaka, N., Shirasaka, N., Kuwahara, M., Nakashima, N., Yamamoto, E., Saka, M., Teramoto, S.J., 2005. A two-generation reproductive toxicity study of 2,4-dichlorophenol in rats. Toxicol. Sci. 30, 59–78. APHA (American Public Health Association), 1992. Standard Methods for the Examination of Water and Wastewater, 18th ed. APHA, Washington, DC. Ausubel, F., Brent, R., Kingston, R., Moore, D., Seidman, J.G., Smith, J.A., Struhl, K., 1995. Short Protocols in Molecular Biology, third ed. John Wiley and Sons, New York, NY, USA. pp. 10–38. Bodalo, A., Gomez, J.L., Gomez, E., Bastida, J., Maximo, M.F., 2006a. Comparison of commercial peroxidases for removing phenol from water solutions. Chemosphere 63, 626–632. Bodalo, A., Gomez, J.L., Gomez, E., Hidalgo, A.M., Murcia, M.D., Gomez, M., 2006b. Removal of phenolic compounds from wastewaters I. Chemical treatments. Ing. Quim. (Madrid) 38, 141–146. Bradford, M.M., 1976. A rapid sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 31, 125–128. Brattain, M.G., Marks, M.E., Pretlow, T.G., 1976. The purification of horseradish peroxidase by affinity chromatography on Sepharose-bound concanavalin. Anal. Biochem. 72, 346–352. Caza, N., Bewtra, J.K., Biswas, N., Taylor, K.E., 1999. Removal of phenolic compounds from synthetic wastewater using soybean peroxidase. Water Res. 33, 3012– 3018. Childs, R.E., Bardsley, W.G., 1975. The steady-state kinetics of peroxidase with 2,20 azino-bis-(3-ethyl-benzathiazoline-6-sulphonic acid) as chromogen. J. Biochem. 145, 93–103. Clementi, F., Palade, G.E., 1969. Intestinal Capillaries I. Permeability to peroxidase and ferritin. J. Cell Biol. 41, 33–58. Cooper, V.A., Nicell, J.A., 1996. Removal of phenols from a foundry wastewater using horseradish peroxidase. Water Res. 30, 954–964. Dalal, S., Gupta, M.N., 2007. Treatment of phenolic wastewater by horseradish peroxidase immobilized by bioaffinity layering. Chemosphere 67, 741–747. Deborde, M., Gunten, U.V., 2008. Reactions of chlorine with inorganic and organic compounds during water treatment-kinetics and mechanisms: A critical review. Water Res. 42, 13–51. Duarte-Vázquez, M.A., García-Almendarez, B., Regalado, C., Whitaker, J.R., 2000. Purification and partial characterization of three turnip (Brassica napus L. var. esculenta D.C.) peroxidases. J. Agric. Food Chem. 48, 1574–1579. Duarte-Vázquez, M.A., García-Almendarez, B., Regalado, C., Whitaker, J.R., 2001. Purification and properties of a neutral peroxidase from turnip (Brassica napus L. var. purple top white globe) roots. J. Agric. Food Chem. 49, 4450–4456. Duarte-Vázquez, M.A., García-Padilla, S., García-Almendárez, B.E., Whitaker, J.R., Regalado, C., 2007. Broccoli processing wastes as a source of peroxidase. J. Agric. Food Chem. 55, 10396–10404. Duarte-Vázquez, M.A., Ortega-Tovar, M., García-Almendárez, B., Regalado, C., Whitaker, J.R., 2003a. Removal of aqueous phenolic compounds from a model system by oxidative polymerization with turnip (Brassica napus L. var. purple top white globe) peroxidase. J. Chem. Technol. Biotechnol. 78, 42–47.

8611

Duarte-Vázquez, M.A., Whitaker, J.R., Rojo-Dominguez, A., García-Almendárez, B., Regalado, C., 2003b. Isolation and thermal characterization of an acidic isoperoxidase from turnip roots. J. Agric. Food Chem. 51, 5096–5102. EPA, 1980. Industrial wastewater. US Environmental Protection Agency. Report No. EPA-600/8-80-26. EPA, 1991. US Environmental Protection Agency. Superfund national priorities list for remediation. 40 CFR 423.A. Code of Federal Regulations. Fraser, J., Bickerstaff, G., 1997. Immobilization of enzymes and cells. In: Bickerstaff, G.F. (Ed.), Methods in Biotechnology, vol. 1. Humana Press, Totowa, NJ, USA, pp. 61–66. Ganjidoust, H., Tatsumi, K., Wada, S., Kawase, M., 1996. Role of peroxidase and chitosan in removing chlorophenols from aqueous solution. Water Sci. Tech. 34, 151–159. Gomez, J.L., Bodalo, A., Gomez, E., Bastida, J., Hidalgo, A.M., Gomez, M., 2006. Immobilization of peroxidases on glass beads: an improved alternative for phenol removal. Enzyme Microb. Technol. 39, 1016–1022. Hannoun, B., Stephanopoulos, G., 1986. Diffusion coefficients of glucose and ethanol in cell-free and cell-occupied calcium alginate membranes. Biotechnol. Bioeng. 28, 829–835. Husain, Q., Jan, U., 2000. Detoxification of phenols and aromatic amines from polluted wastewater by using phenol oxidases. J. Sci. Ind. Res. 59, 286–293. JMP, 1995. Statistical Software, version 3.0. SAS Institute, Cary, North Carolina, USA. Karam, J., Nicell, J.A., 1997. Potential applications of enzymes in waste treatment. J. Chem. Technol. Biotechnol. 69, 141–153. Karim, M.R., Hashinaga, F., 2002. Preparation and properties of immobilized pummelo limonoid glucosyltransferase. Process Biochem. 38, 809–814. Klibanov, A.M., Tu, T.M., Scott, K.P., 1983. Peroxidase catalyzed removal of phenols from coal conversion wastewater. Science 221, 259–261. Kobayashi, S., Fukuda, T., Kawaguchi, K., Chang, H., Toda, S., Kawamura, H., 1972. Chronic toxicity of 2,4-dichlorophenol in mice: a simple design for checking the toxicity of residual metabolites of pesticides. J. Med. Soc. 19, 356–362. Laemmli, U.K., 1970. Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature 227, 680–685. Nakamoto, S., Machida, N., 1992. Phenol removal from aqueous solutions by peroxidase-catalyzed reaction using additives. Water Res. 26, 49–54. Nicell, J.A., Al-Kassim, L., Bewtra, J.K., Taylor, K.E., 1993. Wastewater treatment by enzyme catalyzed polymerization and precipitation. Water Res. 27, 1629–1639. Sardar, M., Gupta, M.N., 2005. Immobilization of tomato pectinase on Con Aseralose 4B by bioaffinity layering. Enzyme Microb. Technol. 37, 355–359. Tatsumi, K., Wada, S., Ichikawa, H., 1996. Removal of chlorophenols from wastewater by immobilized horseradish peroxidase. Biotechnol. Bioeng. 51, 126–130. Valderrama, B., Ayala, M., Vázquez-Duhalt, R., 2002. Suicide inactivation of peroxidases and the challenge of engineering more robust enzymes. Chem. Biol. 9, 555–565. Ward, G., Hadar, Y., Bilkis, I., Konstantinovsky, L., Dosoretz, C.G., 2001. Initial steps of ferulic acid polymerization by lignin peroxidase. J. Biol. Chem. 276, 18734– 18741. Whitaker, J.R., 1994. Principles of Enzymology for the Food Sciences. second ed.. Marcel Dekker, NY, USA. pp. 565–577. Yu, J., Taylor, K., Zou, H., Biswas, N., Bewtra, J.K., 1994. Phenol conversion and dimeric intermediates in horseradish peroxidase-catalyzed phenol removal from water. Environ. Sci. Technol. 28, 2154–2160.

Lihat lebih banyak...

Comentários

Copyright © 2017 DADOSPDF Inc.