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Production of Pleurotus sajor-caju crude enzyme broth and its applicability for the removal of bisphenol A

Abstract

Bisphenol A is an endocrine interfering compound, produced and used on a large scale worldwide. Chemical and biologic methods can be used to remove it from the environment. Biological methods are considered less costly, safer and, according to green chemistry definitions, an environmentally correct method. Considering the use of a crude enzyme broth, without any downstream process, the costs could be mostly reduced. Thus, the removal of bisphenol A by Pleurotus sajor-caju crude enzyme broth was investigated. Initially, the agro-industrial wastes were characterized and, the composition of the culture medium and the bioreactor culture conditions were defined. The enzyme produced in the highest concentration was characterized and the crude broth used in the bisphenol A removal assays. The OXI45 culture medium presented the highest laccase activity (1,850.7 U L-1, 350 rpm). Greater laccase stability was observed at 20 - 40 oC and pHs 5 - 7. Vanillin and ferulic acid (considered mediator compounds) were identified in the crude broth, probably helping on the obtention of the high value of removal effectiveness (0.052 mg U-1 h-1). The results indicate the potential use of the Pleurotus sajor-caju crude enzyme broth to obtain an enzymatic formulation for application in the environmental area.

Key words
Banana wastes; Basidiomycetes; endocrine disruptor; enzymatic activity Submerged culture

INTRODUCTION

Fungi of the Pleurotus genus are considered to be good producers of enzymes such as cellulases, hemicellulases, laccases, manganese peroxidases and lignin peroxidases (Libardi-Junior et al. 2011LIBARDI-JUNIOR N, CORREA M, BONATTI-CHAVES M, GERN RMM, WISBECK E, SCHLOSSER D & FURLAN SA. 2011. Production and applications of Pleurotus laccase. In: Soccol CR, Pandey A, Soccol VT and Larroche C (Eds), Advances in bioprocess in food industry, New Delhi: Asiatech Pub., New Delhi, India, p. 36-61., 2012, Pandey et al. 2017PANDEY A, NEGI S & SOCCOL CR. 2017. Current Developments in Biotechnology and Bioengineering: Production, Isolation and Purification of Industrial Products, 1st ed., United States: Elsevier, 886 p.). They grow in a wide variety of agro-industrial wastes and are easily cultivated in both liquid and solid media (Bonatti et al. 2004BONATTI M, KARNOPP P, SOARES HM & FURLAN SA. 2004. Evaluation of Pleurotus ostreatus and Pleorotus sajor-caju nutricional charactistics when cultivated in different lignocellulosic wastes. Food Chem 88: 425-428., Elisashvili et al. 2008ELISASHVILI V, PENNINCKX M, KACHLISHVILI E, TSIKLAURI N, METREVELI E, KHARZIANI T & KVESITADZE G. 2008. Lentinus edodes and Pleurotus species lignocellulolytic enzymes activity in submerged and solid-state fermentation of lignocellulosic wastes of different composition. Bioresource Technol 99: 457-462., Quevedo-Hidalgo et al. 2015QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127.). The northeastern region of Santa Catarina, Brazil, is a large banana producer and, consequently, a large generator of agro-industrial wastes which can be used in biotechnological routes, such as fungal enzyme production, reducing production costs and heling in solving environmental problems arising from their accumulation in nature (Bonatti et al. 2004BONATTI M, KARNOPP P, SOARES HM & FURLAN SA. 2004. Evaluation of Pleurotus ostreatus and Pleorotus sajor-caju nutricional charactistics when cultivated in different lignocellulosic wastes. Food Chem 88: 425-428., Osma et al. 2011OSMA JF, TOCA-HERRERA JL & RODRÍGUEZ-COUTO S. 2011. Cost analysis in laccase production. J Environ Manage 92: 2907-2912., Pandey et al. 2017PANDEY A, NEGI S & SOCCOL CR. 2017. Current Developments in Biotechnology and Bioengineering: Production, Isolation and Purification of Industrial Products, 1st ed., United States: Elsevier, 886 p.). These wastes are defined as carbon sources in the composition of the culture medium, but, at the same time, also as inductors for the production of lignocellulolytic enzymes by fungi (Elisashvili et al. 2008ELISASHVILI V, PENNINCKX M, KACHLISHVILI E, TSIKLAURI N, METREVELI E, KHARZIANI T & KVESITADZE G. 2008. Lentinus edodes and Pleurotus species lignocellulolytic enzymes activity in submerged and solid-state fermentation of lignocellulosic wastes of different composition. Bioresource Technol 99: 457-462., Rashad et al. 2010RASHAD MM, ABDOU HM, SHOUSHA WGH, ALI MM & EL-SAYED NN. 2010. Purification and characterization of extracellular polygalacturonase from Pleurotus ostreatus using citrus limonium waste. J Appl Sci Res 6: 81-88., Libardi-Junior et al. 2012LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156., Tinoco-Valência et al. 2014TINOCO-VALÊNCIA R, GÓMEZ-CRUZ C, GALINDO E & SERRANO-CARREÓN L. Toward an understanding of the effects of agitation and aeration on growth and laccases production by Pleurotus ostreatus. J Biotechnol 177: 67-73., Quevedo-Hidalgo et al. 2015QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127.).

The cultivation in liquid medium has some advantages in relation to the cultivation in solid medium such as better process control, less cultivation time and greater enzymatic activity. In this type of cultivation, several factors deserve attention in order to maximize enzyme production, such as the composition of the culture medium, temperature, airflow, agitation rate and the carrying out of the production process (Hess et al. 2002HESS J, LEITNER C, GALHAUP C, KULBE KD, HINTERSTOISSER B, STEINWENDER M & HALTRICH D. 2002. Enhanced formation of extracelular laccase activitity by the white-rot fungus Trametes multicolor. In: Finkelstein M, Mcmillan JD and Davison BH (Eds), Biotechnology for Fuels and Chemicals. Appl Biochem Biotech, Totowa: Humana Press, NJ, USA, p. 229-241., Fenice et al. 2003FENICE M, SERMANNI GG, FEDERICI F & D’ANNIBALE A. 2003. Submerged and solid-state production of laccase and Mn-peroxidase by Panus tigrinus on olive mil wastewater-based media. J Biotechnol 100: 77-85., Bettin et al. 2011BETTIN F, ROSA LR, MONTANARI Q, CALLONI R, GAIO TA, MALVESSI E, SILVEIRAMM & DILLON AJP. 2011. Growth kinetics, production, and characterization of extracellular laccases from Pleurotus sajor-caju PS-2001. Process Biochem 46: 758-764., Tinoco-Valência et al. 2014). In spite of the substantial literature on the production of lignocellulolytic enzymes by fungi of the Pleurotus genus, few studies have been found regarding the influence of culture conditions, mainly in bioreactor, on the production of enzymes by the Pleurotus sajor-caju species. Furthermore, information such as optimum pH and temperature for enzyme activity as well as enzyme stability with pH and temperature, are often divergent, which is extremely important for the viability of production on a larger scale.

Oxidative enzymes, such as laccases, are widely used in an extensive variety of industrial segments, such as the chemical, textile, pulp and paper, food segments, etc. (Libardi-Junior et al. 2011LIBARDI-JUNIOR N, CORREA M, BONATTI-CHAVES M, GERN RMM, WISBECK E, SCHLOSSER D & FURLAN SA. 2011. Production and applications of Pleurotus laccase. In: Soccol CR, Pandey A, Soccol VT and Larroche C (Eds), Advances in bioprocess in food industry, New Delhi: Asiatech Pub., New Delhi, India, p. 36-61., Pandey et al. 2017PANDEY A, NEGI S & SOCCOL CR. 2017. Current Developments in Biotechnology and Bioengineering: Production, Isolation and Purification of Industrial Products, 1st ed., United States: Elsevier, 886 p.). More recently, their application has extended to the environmental area, as in the removal of endocrine-interfering compounds such as the bisphenol A (Chang & Chang 2016CHANG B & CHANG Y. 2016. Biodegradation of toxic chemicals by Pleurotus eryngii in submerged fermentation and solid-state fermentation. J Microbiol Immunol 49: 175-181., de Freitas et al. 2017DE FREITAS EN, BUBNA GA, BRUGNARI T, KATO CG & PERALTA RM. 2017. Removal of bisphenol A by laccases from Pleurotus ostreatus and Pleurotus pulmonarius and evaluation of ecotoxicity of degradation products. Chem Eng J 330: 1361-1369., Barrios-Estrada et al. 2018BARRIOS-ESTRADA C, ROSTRO-ANALANIS MJ, PARRA AL, BELLEVILLE M-P & PARRA-SALDÍVAR R. 2018. Potentialities of active membranes with immobilized laccase for Bisphenol A degradation. Int J Biol Macromol 108: 837-844.). It is considered to be one of the most widely used synthetic compounds on the planet (Jalal et al. 2018JALAL N, SURENDRANATH AR, PATHAK JL, YU S & CHUNG CY. 2018. Bisphenol A (BPA) the mighty and the mutagenic. Toxicology Res-Uk 5: 76-84.). These compounds have the ability to interfere in the endocrine system of organisms causing adverse implications for development and reproduction as well as neurological and immune system changes (Michalowicz 2014MICHALOWICZ J. 2014. Bisphenol A – Sources, toxicity and biotransformation. Environ Toxicol Phar 37: 738-758., Sifakis et al. 2017SIFAKIS S, ANDROUTSOPOULOS VP, TSATSAKIS AM & SPANDIDOS DA. 2017. Human exposure to endocrine disrupting chemicals: effects on the male and female reproductive systems. Environ Toxicol Phar 51: 56-70., Jalal et al. 2018JALAL N, SURENDRANATH AR, PATHAK JL, YU S & CHUNG CY. 2018. Bisphenol A (BPA) the mighty and the mutagenic. Toxicology Res-Uk 5: 76-84.).

Both chemical and biological methods are proposed in literature for the removal of bisphenol A from the environment. However, chemical methods present some disadvantages in relation to biological methods, such as high cost and the formation of toxic compounds. Thus, it is believed that biological degradation would be a less costly, safer method and, according to Green Chemistry definitions, environmentally correct (de Freitas et al. 2017DE FREITAS EN, BUBNA GA, BRUGNARI T, KATO CG & PERALTA RM. 2017. Removal of bisphenol A by laccases from Pleurotus ostreatus and Pleurotus pulmonarius and evaluation of ecotoxicity of degradation products. Chem Eng J 330: 1361-1369., Pandey et al. 2017PANDEY A, NEGI S & SOCCOL CR. 2017. Current Developments in Biotechnology and Bioengineering: Production, Isolation and Purification of Industrial Products, 1st ed., United States: Elsevier, 886 p.). Most studies reported in literature use oxidative enzymes, generally in their purified or enzyme extract form, free or immobilized, synthesized by different microorganisms for the removal bisphenol A. However, no study is reported using the Pleurotus genus crude enzyme broth, without any downstream processing.

Therefore, considering the biotechnological production of oxidative enzymes by fungi and the environmental aspects, the objectives of this work were to characterize the banana wastes (banana peel powder and immersion water of banana straw) used in the culture medium composition; to study the production of oxidative enzymes by Pleurotus sajor-caju in bioreactor and to validate the efficacy of the crude enzyme broth, without any downstream processing, in the degradation of the endocrine interfering bisphenol A.

MATERIALS AND METHODS

Microorganism and maintenance

Pleurotus sajor-caju CCB 019 was obtained from the Center for Basidiomycete Cultivation of the University of São Paulo. The strain was grown in WDA (Wheat Dextrose Agar) (Furlan et al. 1997FURLAN SA, VIRMOND LJ, MIERS D, BONATTI M, GERN RMM & JONAS R. 1997. Mushroom strains able to grow at high temperatures and low pH values. World J Microb Biot 13: 689-692.) medium and stored under refrigeration (4°C).

Chemical characterization of banana wastes

The immersion water of banana straw and the banana peel powder were analyzed in terms of organic matter, organic carbon, total carbohydrate, monosaccharide composition, crude fiber, hemicellulose, cellulose, lignin, total nitrogen, protein, C/N ratio, ash and pH (AOAC 1984AOAC - ASSOCIATION OF OFFICIAL ANALYTICAL CHEMISTS. 1984. Official methods of analysis, 14th ed., Washington, DC., Breene 1990BREENE WM. 1990. Nutritional and medicinal value of specialty mushrooms. J Food Protect 53: 883-894.). The analyses were carried out in triplicate.

Enzyme production

A. Influence of medium composition

Three culture media were evaluated: Manachini Solution (2 g L-1 KH2PO4; 1 g L-1 (NH4)2SO4; 0,1 g L-1 MgSO4; 0,9 g L-1 Na2HPO4.2H2O; 1 g L-1 yeast extract, dissolved in distilled water (Manachini et al. 1987MANACHINI PL, FORTINA MG & PARINI C. 1987. Purification and properties of an endopolygalacturonase produced by Rhizopus stolonifera. Biotechnol Lett 9(3): 219-224.)); Manachini Modified Solution (same mineral salts as Manachini Solution, in the same concentrations, but dissolved in immersion water of banana straw. The immersion water of banana straw was obtained by immersing 150 g of dry banana straw in 3 L of water, for approximately 12 hours) (Bonatti et al. 2004BONATTI M, KARNOPP P, SOARES HM & FURLAN SA. 2004. Evaluation of Pleurotus ostreatus and Pleorotus sajor-caju nutricional charactistics when cultivated in different lignocellulosic wastes. Food Chem 88: 425-428.) and OXI medium (immersion water of banana straw and 5.4 mM ammonium tartrate (Libardi-Junior et al. 2011LIBARDI-JUNIOR N, CORREA M, BONATTI-CHAVES M, GERN RMM, WISBECK E, SCHLOSSER D & FURLAN SA. 2011. Production and applications of Pleurotus laccase. In: Soccol CR, Pandey A, Soccol VT and Larroche C (Eds), Advances in bioprocess in food industry, New Delhi: Asiatech Pub., New Delhi, India, p. 36-61.)). In these experiments (shake flasks culture) the OXI medium was added of 60 g L-1 banana peel powder, named OXI60 culture medium. All culture media were supplemented with 10 g L-1 glucose. Depending on the enzyme to be produced, laccase (Lac), manganese peroxidase (MnP) or lignin peroxidase (LiP), the following were added to the culture medium: CuSO4 anhydride 150 μM, Mn2+ 0.05 mM or veratryl alcohol 4 mM, respectively. The initial pH of the culture media was adjusted to 6.0 using H3PO4 12 M and NaOH 6 M solutions when necessary (Libardi-Junior et al. 2011LIBARDI-JUNIOR N, CORREA M, BONATTI-CHAVES M, GERN RMM, WISBECK E, SCHLOSSER D & FURLAN SA. 2011. Production and applications of Pleurotus laccase. In: Soccol CR, Pandey A, Soccol VT and Larroche C (Eds), Advances in bioprocess in food industry, New Delhi: Asiatech Pub., New Delhi, India, p. 36-61., 2012).

The experiments were carried out in 500 mL Erlenmeyer flasks containing 100 mL of culture medium. The flasks were sterilized, inoculated with two 12 mm diameter agar discs containing mycelium and incubated at 30°C and 105 rpm (reciprocal agitation) for 12 days (Libardi-Junior et al. 2012LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156.). Samples were periodically collected, frozen and later analyzed for enzyme activities. All experiments were carried out in triplicate.

B. Influence of agitation rate

The agitation rates evaluated were 100, 350 and 500 rpm. The experiments were carried out in batch culture in a stirred tank reactor (B. Braun, Biostat® B model) of 4 L of working volume (0.4 L of inoculum and 3.6 L of culture medium) (Supplementary Material - Figure S5). The cultures were incubated at 100, 350 and 500 rpm, 30ºC, and 0.37 L min-1 air flow. The initial pH value was adjusted at 6,0 by the addition of NaOH 6N and H3PO4 12N (Bonatti-Chaves et al. 2014BONATTI-CHAVES M, LIBARDI-JUNIOR N, BORGES G, WISBECK E, GERN R, FURLAN SA & FURIGO JUNIOR A. 2014. Production of bioactive substances in fed-batch and semi-continuous culture by Pleurotus ostreatus. Chem Engineer Trans 38: 307-312.). In these experiments the OXI medium was added of 10 g L-1 glucose, 150 μM CuSO4 anhydride and 45 g L-1 instead of 60 g L-1 banana peel powder (as described in item A). Therefore, for the experiments in the bioreactor, the medium was named OXI45 culture medium. The concentration of banana peel powder had be altered due to insufficient homogenization promoted by the high concentration of banana peel powder (60 g L-1) into the bioreactor. The experiments were carried out until total glucose consumption and samples were periodically colleted, centrifuged (3000 rpm, 10 minutes) and the supernatant used for enzymatic determinations. All experiments were carried out in duplicate.

The inoculums were prepared in 2 L Duran flasks containing 0.4 L mL of OXI medium added of 10 g L-1 glucose and 150 μM CuSO4 anhydride. The Duran flasks were sterilized, inoculated with all the mycelium obtained from a Petri dish, after 7 days growth, and incubated at 30°C and 105 rpm (reciprocal agitation) for 6 days (Furlan et al. 2008FURLAN SA, GERN RMM, WISBECK E, BONATTI-CHAVES M, SILVEIRA MLL & SILVA HH. 2008. In: CURRENT TOPICS ON BIOPROCESSES IN FOOD INDUSTRY, vol I: Possibilities of Pleurotus applications in food, health and environmental technologies. Koutinas A, Pandey A and Larroche C (Eds), Asiatech, Nova Delhi, p. 495.).

Enzyme characterization

For determining optimum pH, the enzymatic reaction was conducted in McIlvain buffer with pH values ranging from 2.5 to 7.5. For determining optimum temperature, the enzymatic reaction was conducted with temperatures ranging from 20 to 50 °C. In both experiments, the other conditions foreseen in the enzymatic activity test were maintained (Libardi-Junior et al. 2012LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156.). The crude enzyme broth was incubated at different time intervals (2 to 72 hours), and pH values 3.0, 5.0 and 7.0 for determining pH stability, as well as temperatures varying between 20 and 50 °C for determining temperature stability (Libardi-Junior et al. 2012LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156.). For determining the Michaelis-Mentes constant (Km) and the maximum reaction rate (Vmáx), ABTS (2.2´-azino-bis-[3-ethyltiazoline-6-sulfonate]) was used and the assays carried out in optimum temperature and pH. The Origin 8.0 PRO® software was used to calculate Km and Vmáx, by linearization of Michaelis-Menten equation by the Lineweaver-Burk method (Libardi-Junior et al. 2012LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156.). All experiments were carried out in triplicate.

Bisphenol A degradation

Mixtures containing 1.5 mL of crude enzyme broth (200 U L−1 of laccase activity) and 0.5 mL of bisphenol A (500 mg L-1 - 95% purity, Sigma-Aldrich) were incubated at room temperature and samples were taken at 24, 48 and 72 hours. All experiments were carried out in triplicate.

Analyses

Glucose concentration was evaluated using the enzymatic method of glucose oxidase-peroxidase (Glicose-E, CELM, Brasil). The laccase, manganese peroxidase and lignin peroxidase activity were measured as described by Buswell et al. (1996)BUSWELL JA, CA Y & CHANG S. 1996. Effect of nutrient nitrogen and manganese on manganese peroxidase and laccase production by Lentinula (Lentinus) edodes. Fems Microbiol Lett 128: 81-87., Glenn & Gold (1985)GLENN JK & GOLD MH. 1985. Purification and characterization of an extracellular Mn(II)-dependent peroxidase from the lignin-degrading basidiomycete, Phanerochaete chrysosporium. Arch Biochem Biophys 242: 329-341. and Tien & Kirk (1984)TIEN M & KIRK TK. 1984. Lignin-degrading enzyme from Phanerochaete chrysosporium: purification, characterization, and catalytic properties of a unique H2O2-requiring oxygenase. P Natl Acad Sci 81: 2280-2284., respectively.

Bisphenol A concentration was evaluated as follows: prior to the extraction process, a drop of concentrated acetic acid was added to the samples, which were then shaken. The bisphenol A was then extracted using ethyl ether. The supernatant was analyzed for the bisphenol A concentration using Agilent 6890 gas chromatograph with FID detector. The HP-5 column (5% phenylmethylsiloxane), held at 290°C during injection and then programmed at 140°C min-1 to 310°C, for 10 minutes, was used for quantitative analysis. The bisphenol A was identified by its typical retention times. The concentrations were calculated based on calibration curve established with external standard of bisphenol A.

Gallic acid, ferulic acid and vanillin were identified in the P. sajor-caju crude enzyme broth as follows: 1 mL of the sample was diluted in equal volume of ethanol:ultrapure water (1:4) solution and filtered by a membrane filter (0.20 µm) directly in a vial for chromatography analyses. The standard solution was obtained dissolving the standard compounds in equal solution (ethanol:ultrapure water, 1:4). The analyze was performed using high performance liquid chromatography-tandem mass spectrometry (LC-MS/MS method). The spectrometer was operated on the positive ionization mode using multiple-reaction monitoring (MRM). The chromatographic separation was carried out on an Agilent Zorbax SB-C18 (RRHT) column (2.10 x 50 mm, 1.8 µm) maintained at 40oC. The mobile phase consisted of formic acid 0.1% (A), acetonitrile (B) and MeOH (D). The mobile phases A and D were maintained constant at 5%. The gradient started with mobile phase B rising from 5% to 65% in 5 minutes and reaching 80% in 12 minutes. The concentration was then kept in isocratic mode for 8 minutes. Subsequently, the concentration of mobile phase decreased to 5% in 1 minute, and then the column was equilibrated at this condition for 4 minutes. An injection volume of 2 µL was used.

Statistical analysis

All data were submitted to the Dixon Q test (Rorabacher 1991RORABACHER DB. 1991. Statistical treatment for rejection of deviant values: critical values of Dixon’s “Q” parameter and related subrange ratios at the 95% confidence level. Anal Chem 63: 139-146.). The results were expressed as means and submitted to analysis of variance using the Tukey Test, significance level 5% (Origin 8.0 PRO®).

RESULTS AND DISCUSSION

Chemical characterization

A very important factor for enzymatic production by lignocellulolitic fungi is the chemical nature of the compounds used in the culture medium composition (Elisashvili et al. 2008ELISASHVILI V, PENNINCKX M, KACHLISHVILI E, TSIKLAURI N, METREVELI E, KHARZIANI T & KVESITADZE G. 2008. Lentinus edodes and Pleurotus species lignocellulolytic enzymes activity in submerged and solid-state fermentation of lignocellulosic wastes of different composition. Bioresource Technol 99: 457-462., Tinoco-Valência et al. 2014, Carvalho et al. 2012CARVALHO CSM, AGUIAR LVB, SALES-CAMPOS C, MINHONI MTA & ANDRADE MCN. 2012. Applicability of the use of waste from different banana cultivars for the cultivation of the oyster mushroom. Braz J Microbiol 43(2): 819-826.). According to Table I, the immersion water of banana straw and the banana peel powder presented organic material and organic carbon contents equal to 70.4 and 39.1%, and 76.2 and 42.3%, respectively. The total carbohydrate content for the banana peel powder was 11%. The main carbohydrates in the immersion water were glucose (31.6%) and galactose (31.5%). The nitrogen and protein contents in immersion water and in banana peel powder were 2.8 and 12.4%, and 2.5 and 11.8%, respectively. According to Carvalho et al. (2012)CARVALHO CSM, AGUIAR LVB, SALES-CAMPOS C, MINHONI MTA & ANDRADE MCN. 2012. Applicability of the use of waste from different banana cultivars for the cultivation of the oyster mushroom. Braz J Microbiol 43(2): 819-826., the excess of mineral or organic N in the culture media, in addition to exercising a negative effect on mycelial growth, may inhibit synthesis of the enzymes that degrade the lignin. In this work, the C/N ratio was 13.8 and 16.9 for immersion water and banana peel powder, respectively.

Table I
Chemical composition of banana wastes (mean value ± standard error).

The crude fiber content found in the banana peel powder was 7%, and the hemicellulose, lignin and cellulose contents were 9.5, 7.2 and 6.6%, respectively (Table I). Crude fiber, lignin, hemicellulose and cellulose are defined as carbon sources as well as inductors for the production of lignocellulolitic enzymes by fungus (Elisashvili et al. 2008ELISASHVILI V, PENNINCKX M, KACHLISHVILI E, TSIKLAURI N, METREVELI E, KHARZIANI T & KVESITADZE G. 2008. Lentinus edodes and Pleurotus species lignocellulolytic enzymes activity in submerged and solid-state fermentation of lignocellulosic wastes of different composition. Bioresource Technol 99: 457-462., Libardi-Junior et al. 2012LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156., Quevedo-Hidalgo et al. 2015QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127.). The floriculture wastes were characterized by Quevedo-Hidalgo et al. (2015)QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127. for enzyme production by Pleurotus ostreatus in submerged culture. The wastes presented cellulose content varying from 38.4 to 49.6%, hemicellulose from 7.5 to 8.8%, lignin from 9.5 to 17.5% and N from1.94 to 2%. The substrate including chrysanthemum waste and the inducers (Cu+2 and Mn2+) increased 4.8 times the laccase production. According to the authors, the lignin content in this kind of waste exercises a positive influence on the production of laccase by Pleurotus ostreatus.

The addition of lignin in the culture medium by Tinoco-Valência et al. (2014) for enzyme production by Pleurotus ostreatus also exercised a strong positive influence on the laccase production. Moreover, when Cu+2 was added simultaneously to the lignin to the culture medium, the laccase activity increases more than when both are added separately, showing the synergistic effect between the inducers and on enzyme production.

The ash content in the immersion water and banana peel powder (Table I) were 28.6 and 12.8% respectively. Ash content provides an indication of sample richness in mineral elements (Quevedo-Hidalgo et al. 2015QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127.). Some metals are considered enzymatic inducers, such as Cu+2 and Mn+2. The pH values found in this study are close to neutrality (around 6.0). Studies showed a pH adjustment close to neutrality for the production of laccases by basidiomycete fungi (Bettin et al. 2011BETTIN F, ROSA LR, MONTANARI Q, CALLONI R, GAIO TA, MALVESSI E, SILVEIRAMM & DILLON AJP. 2011. Growth kinetics, production, and characterization of extracellular laccases from Pleurotus sajor-caju PS-2001. Process Biochem 46: 758-764., Pandey et al. 2017PANDEY A, NEGI S & SOCCOL CR. 2017. Current Developments in Biotechnology and Bioengineering: Production, Isolation and Purification of Industrial Products, 1st ed., United States: Elsevier, 886 p.).

Influence of medium composition – Assays in shake flasks

According to Figure 1, the highest laccase activity was observed when using the OXI60 culture medium, with the highest activity observed on the 12th day of cultivation (2,416.5 ± 35.5 U L-1). For the assays using Mananchini Solution and Manachini Modified Solution it was observed laccase activity equal to each other and significantly lower than those obtained using the OXI60 culture medium.

Figure 1
Laccase activity (Lac) mean values obtained in P. sajor-caju cultivation using OXI60, Manachini Solution and Manachini Modified Solution culture media.

According to Figure 2, the greatest manganese peroxidase activity was also observed when using the OXI60 culture medium, with highest activity observed on the 12th day of cultivation (7.62 ± 0.36 U L-1). The manganese peroxidase productivity (0.64 U L-1 day-1) was lower than that found in literature. However, the laccase productivity (201.4 U L-1 day-1) was higher than that found in literature, suggesting the OXI60 culture medium to be efficient on the laccase production.

Figure 2
Manganese peroxidase (MnP) mean values obtained in P. sajor-caju cultivation using OXI60, Manachini Solution and Manachini Modified Solution culture media.

Libardi-Junior et al. (2012)LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156. obtained laccase activity by Pleurotus ostreatus equal to 1,575 ± 93.02 U L-1 on the 9th day (productivity equal to 175 U L-1 day-1) using culture medium composed of water, 40 g L-1 banana peel powder and CuSO4 150 µM. Elisashvili et al. (2008)ELISASHVILI V, PENNINCKX M, KACHLISHVILI E, TSIKLAURI N, METREVELI E, KHARZIANI T & KVESITADZE G. 2008. Lentinus edodes and Pleurotus species lignocellulolytic enzymes activity in submerged and solid-state fermentation of lignocellulosic wastes of different composition. Bioresource Technol 99: 457-462., using mandarin, apple and banana peels in the culture medium composition, obtained manganese peroxidase activity of 58 U L-1 on the 8th day (productivity 7.25 U L-1 day-1). Quevedo-Hidalgo et al. (2015)QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127. evaluated the effect of floriculture wastes in enzyme synthesis by basidiomycetes obtaining as a result 429 and 32 U L-1, on the 7th and 10th days, for laccase (productivity 61.3 U L-1 day-1) and manganese peroxidase (productivity 3.2 U L-1 day-1), respectively.

The Pleurotus sajor-caju cultivation, regardless of the culture medium, showed no activity for the lignin peroxidase enzyme.

Influence of agitation rate – Assays in bioreactor

According to Figure 3, the highest laccase activity (1,850.7 ± 674.8 U L-1) was observed at the assay using agitation rate of 350 rpm, which is statistically different from the other assays (Tukey test p < 0.05) (Table II). The maximum laccase activities for cultivation at 100 and 500 rpm were 9.25 ± 2.18 and 207.2 ± 18.6 U L-1, respectively. The maximum laccase activities for cultivation at 100 and 500 rpm were 9.25 ± 2.18 and 207.2 ± 18.6 U L-1, respectively. By decreasing agitation rate it was hoped that the effect of shear stress on the mycelium would be reduced and, through this, maybe an increase in the laccase activity by Pleurotus sajor-caju would be observed. According to described by Fenice et al. (2003)FENICE M, SERMANNI GG, FEDERICI F & D’ANNIBALE A. 2003. Submerged and solid-state production of laccase and Mn-peroxidase by Panus tigrinus on olive mil wastewater-based media. J Biotechnol 100: 77-85. and Tinoco-Valência et al. (2014), higher agitation rates normally have a negative influence on the production of enzymes by fungus. However, Fernández-Alejandre et al. (2016)FERNÁNDEZ-ALEJANDRE KI, FLORES N, TINOCO-VALENCIA R, CARO C, FLORES C, GALINDO E & SERRANO-CARREÓN L. 2016. Diffusional and transcriptional mechanisms involved in laccases production by Pleurotus ostreatus CP50. J Biotechnol 223: 42-49. observed the opposite effect, that is, the increase in agitation rate encouraged the formation of smaller pellets and higher laccase activity values. The authors justify these results as being due to the non-existence of possible diffusion restriction in the pellets, and consequently, no type of nutritional restriction. In this study, when the agitation rate was increased to 500 rpm, the laccase activity was approximately 22 times greater than in the assay using 100 rpm.

Table II
Kinetic parameters of the assays using agitations rate 100, 350 and 500 rpm (mean value ± standard error).
Figure 3
Glucose concentration (∙∙∙, ▲ and Δ), laccase activity (–, ■ and □ ) and pH (∙- , ● and ○) in P. sajor-caju cultivation (a) 100 rpm; (b) 350 rpm; (c) 500 rpm.

The laccase productivity and the laccase conversion factor were also the highest in the assay using 350 rpm (Table II). The laccase productivity was equal to 18.21 U L-1 h-1 in the assay using 350 rpm, more specifically, this value is 130 and 9 times greater than in the assays using 100 and 500 rpm, respectively. The productivity value obtained in this study, was superior to productivity obtained by Tinoco-Valência et al. (2014) (14 U L-1 h-1) and Aggelis et al. (2003)AGGELIS G, ICONOMOU D, CHRISTOU M, BOKAS D, KOTZAILIAS S, CHRISTOU G, TSAGOU V & PAPANIKOLAOU S. 2003. Phenolic removal in a model olive oil mill wastewater using Pleurotus ostreatus in bioreactor cultures and biological evaluation of the process. Water Res 37: 3897-3904. (0.38 U L-1 h-1) using P. ostreatus species. Productivity values superior to those obtained in this work were also found (considering only assays in bioreactor), however none with the Pleurotus sajor-caju species. Hess et al. (2002)HESS J, LEITNER C, GALHAUP C, KULBE KD, HINTERSTOISSER B, STEINWENDER M & HALTRICH D. 2002. Enhanced formation of extracelular laccase activitity by the white-rot fungus Trametes multicolor. In: Finkelstein M, Mcmillan JD and Davison BH (Eds), Biotechnology for Fuels and Chemicals. Appl Biochem Biotech, Totowa: Humana Press, NJ, USA, p. 229-241. obtained laccase production by T. multicolor, in bioreactor assays, equal to 29 U L-1 h-1. Liu et al. (2016)LIU J, YU Z, LIAO X, LIU J, MAO F & HUANG Q. 2016. Scalable production, fast purification, and spray drying of native Pycnoporus laccase and circular dichroism characterization. J Clean Prod 127: 600-609. obtained laccase production by Pycnoporus sp. equal to 0.35 U mL-1 h-1 (350 U L-1 h-1).

Enzyme characterization

Effect of pH and temperature on laccases activity

It can be seen in Figure 4a that the optimum pH for the reaction was 3.0, being pH values above 5.0 not favorable to the reaction (around 50% loss of laccase activity). According to Figure 4b, is observed that laccase activity is stable for all temperatures evaluated.

Figure 4
Stability of the P. sajor-caju laccase at (a) different pH values and (b) different temperatures.

The optimum pH and temperature values observed in this study can be compared with optimum pH and temperature values found by various authors (Table III), using the same substrate (2,2’-azino-bis(3-ethylbenzothiazoline-6-sulphonic acid) - ABTS) for different Pleurotus laccase isoforms. Bettin et al. (2011)BETTIN F, ROSA LR, MONTANARI Q, CALLONI R, GAIO TA, MALVESSI E, SILVEIRAMM & DILLON AJP. 2011. Growth kinetics, production, and characterization of extracellular laccases from Pleurotus sajor-caju PS-2001. Process Biochem 46: 758-764. observed three optimum pH peaks (2.4, 3.2 and 4.4), the authors justified the three activity peaks as being due to the different laccase isoforms produced by fungus. In general, laccases are more stable at acidic pH, with the optimum pH for ABTS substrate oxidation being less than 4.0 (Baldrian 2006BALDRIAN P. 2006. Fungal laccases - occurrence and properties. Fems Microbiol Rev 30: 215-242.). According to Galhaup et al. (2002)GALHAUP C, GOLLER S, PETERBAUER CK & STRAUSS J. 2002. Characterization of the major laccase isoenzyme from Trametes pubescens and regulation of its syntesis by metal ions. Microbiology 148: 2159-2169., the decrease in the reaction rate with increasing pH is characteristic of reactions with non-phenolic substrates, such as ABTS, in which the oxidation of the substrate occurs in a single phase, resulting directly in the ABTS radical cation (Johannes & Majcherczyk 2000JOHANNES C & MAJCHERCZYK A. 2000. Laccase activity tests and lacase inhibitors. J Biotechnol 78: 193-199.).

Table III
Optimum pH and temperature values of the laccase isoforms originating from different Pleurotus species.

Stability with the pH and temperature

Greater laccase stability is observed in pH 5 and 7 (Figure 5a). At pH 7 the enzymatic activity remains stable throughout the incubation time and at pH 5 the activity decreases by only 23.7% in 72 hours. At pH 3.0, (optimum pH, as shown in Figure 4a) the enzyme loses 100% of its activity in 8 hours of incubation. Behavior similar was observed by Kumar et al. (2012)KUMAR VV, SATHYASELVABALA V, PREMKUMAR MP, VIDYADEVI T & SIVANESAN S. 2012. Biochemical characterization of three phase partitioned laccase and its application in decolorization and degradation of synthetic dyes. J Mol Catal B Enzym 74: 63- 72., the pH 4.0 was observed as the optimum pH and the pH 6.0 was the most favorable with activity around 97%, up to 50 hours of incubation. Libardi-Junior et al. (2012)LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156. found greater stability, for laccases from Pleurotus ostreatus, in pH 6.0, and pH 4.0 as the optimum pH. Extreme pH values negatively influenced enzyme stability, with the pH 3.0 and 8.0, in 4 hours of incubation, showing less than 5% activity.

Figure 5
Stability of the P. sajor-caju laccase during incubation in (a) pH 3.0, 5.0 and 7.0; and (b) 20, 30, 40 and 50oC.

According to Figure 5b, the laccase activity is stable for the range of temperatures 20 to 40 oC (around 100% activity). A loss of 40% activity is observed after 8 hours at 50 oC. Kumar et al. (2012)KUMAR VV, SATHYASELVABALA V, PREMKUMAR MP, VIDYADEVI T & SIVANESAN S. 2012. Biochemical characterization of three phase partitioned laccase and its application in decolorization and degradation of synthetic dyes. J Mol Catal B Enzym 74: 63- 72. observed the highest stability (100%) at 25 °C (18 h of incubation). At the temperature of 37 and 45 °C, the decay of 50% of the activity occurs in 14 and 8 hours, respectively. Higher temperatures, such as 50 and 60 °C, the decay of 100% of the activity occurs in 4 h and 2 hours, respectively. Zucca et al. (2011)ZUCCA P, RESCIGNO A, OLIANAS A, MACCIONI S, SOLLAI FA & SANJUST E. 2011. Induction, purification, and characterization of a laccase isozyme from Pleurotus sajor-caju and the potential in decolorization of textile dyes. J Mol Catal B-Enzym 68: 216-222. observed as the optimum reaction temperature, 30 oC (8 hours of incubation, 97% of its initial activity). At temperatures of 40 and 50 °C, after 8 hours, 60% of the initial activity remained present, while only 40% remained active at 60 °C. At 70 °C, after 1 hour, the enzyme was completely inactivated. Libardi-Junior et al. (2012)LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156. observed, for laccase from Pleurotus ostreatus, that at room temperature, in 72 hours, activity less than 20% and at 50 oC the enzyme had been almost completely deactivated. Bettin et al. (2011)BETTIN F, ROSA LR, MONTANARI Q, CALLONI R, GAIO TA, MALVESSI E, SILVEIRAMM & DILLON AJP. 2011. Growth kinetics, production, and characterization of extracellular laccases from Pleurotus sajor-caju PS-2001. Process Biochem 46: 758-764. observed, for Pleurotus sajor-caju laccase, greater stability at temperatures of 20 and 30°C. At 40°C a drop of 50% of activity was observed in 48 hours and, at 50 and 60°C the enzyme was inactivated in less than 5 hours.

Determination of Michaelis-Menten constant and maximum reaction rate

The laccase kinetic Km and Vmáx parameters for different Pleurotus species are presented in Table IV. It is possible to observe values of Km varying from 0.014 to 0.607 mM and Vmáx values varying from 0.0003 to 1.25 mM min-1. These variations can be explained by the differences in culture media compositions used by the different authors, thus different isoenzymes are produced by each species, as well as laccase activity inhibiting compounds. It also can be explained by the type of substrate used for the enzymatic quantification (ABTS, DPM, syringaldazine, guayacol, etc.). In this study, the Km and Vmáx values show the affinity of the enzyme for the substrate (ABTS), as well as high catalytic efficiency.

Table IV
Kinetic parameters for laccase enzymes from different Pleurotus species.

Bisphenol A degradation

A reduction of 40 and 100% in bisphenol A (500 mg L-1) concentration was observed after 24 and 48 hours, respectively, of incubation with Pleurotus sajor-caju crude enzyme broth (200 U L-1). The term effectiveness (defined as the amount of bisphenol A removed/(initial laccase activity x time to removal)) was used to discuss the results. Table V presents the values of effectiveness obtained in this study and those obtained by the other authors (0.000015 to 0.052 mg U-1 h-1).

Table V
Effectiveness values of different studies on BPA removal by Pleurotus laccases.

The highest value was obtained in this study (Table V). A possible suggestion for this result can be the presence of the natural small-molecular weight compounds in the Pleurotus sajor-caju crude enzyme broth that can act as redox mediators and improve the performance of laccases on the bisphenol A removal. In this study vanillin (3- methoxy-4-hydroxybenzaldehyde) and ferulic acid (3- (4-hydroxy-3-methoxyphenyl) prop-2E-enoic acid) were identified in the Pleurotus sajor-caju crude enzyme broth (Figures S1, S2, S3 and S4). According to Piscitelli et al. (2011)PISCITELLI A, GIARDINA P, LETTERA V, PEZZELLA C, SANNIA G & FARACO V. 2011. Industion and transcriptional regulation of laccases in fungi. Curr Genomics 12: 104-112., phenolic and aromatic compounds with a similar structure to that of lignin or lignin derivatives are usually added to the culture media in order to increase laccase production. Parenti et al. (2013)PARENTI A, MUGUERZA E, IROZ AR, OMARINI A, CONDE E, ALFARO M, CASTANERA R, SANTOYO F, RAMIREZ L & PISABARRO AG. 2013. Induction of laccase activity in the White rot fungus using water polluted with wheat straw extracts. Bioresource Technol 133: 142-149. also found vanillin and ferulic acid, as well as gallic acid (3, 4, 5-trihydroxybenzoic acid), in the immersion water of wheat straw used for the laccases production by Pleurotus ostreatus. The absence and/or low concentration of the mediators in the extracts obtained from submerged and solid-state culture of Pleurotus ostreatus, Pleurotus pulmonarius and Pleurotus eryngii, as well as in the purified enzyme, can justify the lower effectiveness obtained by some authors cited in Table V.

Erkurt (2015)ERKURT HA. 2015. Biodegradation and detoxification of BPA: involving laccase and a mediator. Clean – Soil Air Water 43(6): 932-939., in assays related to bisphenol A degradation by fungal laccases, observed greater removal percentage (100% in 90 minutes) as well as higher enzyme stability (60%) using Funalia trogii crude enzyme broth and using the inactivated crude broth added from the commercial enzyme purified from Trametes versicolor, than when using only the commercial purified enzyme in the assays. The author suggests that the enhanced laccase stability was probably due to an interaction between the polymer products present in the crude enzyme broth which gave protection to the laccase enzyme. De Freitas et al. (2017)DE FREITAS EN, BUBNA GA, BRUGNARI T, KATO CG & PERALTA RM. 2017. Removal of bisphenol A by laccases from Pleurotus ostreatus and Pleurotus pulmonarius and evaluation of ecotoxicity of degradation products. Chem Eng J 330: 1361-1369. observed higher bisphenol A removal using nondialysed Pleurotus ostreatus and Pleurotus pulmonarius crude laccase extracts than when using dialyzed extracts, showing the positive influence of the natural mediators present in the extracts on the enzyme reaction.

Another possible explanation for the high effectiveness obtained in this study can be due to the polarity of the culture medium (in this study OXI45 culture medium was used, described in item A). Solvents with high polarity tend to increase the solubility of the polar substrates in the culture medium, providing faster and more selective reactions (Baldrian 2006BALDRIAN P. 2006. Fungal laccases - occurrence and properties. Fems Microbiol Rev 30: 215-242.). Additionally, the water linked to the protein would increase the mobility and flexibility of the active sites of the enzyme and the polarization of the protein structure, enhancing the enzymatic activity (Asadgol et al. 2014ASADGOL Z, FOROOTANFAR H, REZAEI S, MAHVI AH & FARAMARZI MA. 2014. Removal of phenol and bisphenol-A catalyzed by laccase in aqueous solution. J Environ Health Sci Eng 12: 93. DOI: 10.1186/2052-336X-12-93. PMID: 25031840; PMCID: PMC4100752.). The results presented in this work suggest the potential use of Pleurotus sajor-caju crude enzyme broth, without necessity of downstream processing, for obtaining an enzymatic formulation for application in the environmental area in the future.

ACKNOWLEDGMENTS

This research was supported by the Fundação de Amparo à Pesquisa e Inovação do Estado de Santa Catarina (FAPESC) [grant number 15636/2012-1]; the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) [grant number 308581/2014-8]; and the FAP/UNIVILLE [grant number 8826].

REFERENCES

  • AGGELIS G, ICONOMOU D, CHRISTOU M, BOKAS D, KOTZAILIAS S, CHRISTOU G, TSAGOU V & PAPANIKOLAOU S. 2003. Phenolic removal in a model olive oil mill wastewater using Pleurotus ostreatus in bioreactor cultures and biological evaluation of the process. Water Res 37: 3897-3904.
  • AOAC - ASSOCIATION OF OFFICIAL ANALYTICAL CHEMISTS. 1984. Official methods of analysis, 14th ed., Washington, DC.
  • ASADGOL Z, FOROOTANFAR H, REZAEI S, MAHVI AH & FARAMARZI MA. 2014. Removal of phenol and bisphenol-A catalyzed by laccase in aqueous solution. J Environ Health Sci Eng 12: 93. DOI: 10.1186/2052-336X-12-93. PMID: 25031840; PMCID: PMC4100752.
  • BALDRIAN P. 2006. Fungal laccases - occurrence and properties. Fems Microbiol Rev 30: 215-242.
  • BARRIOS-ESTRADA C, ROSTRO-ANALANIS MJ, PARRA AL, BELLEVILLE M-P & PARRA-SALDÍVAR R. 2018. Potentialities of active membranes with immobilized laccase for Bisphenol A degradation. Int J Biol Macromol 108: 837-844.
  • BETTIN F, ROSA LR, MONTANARI Q, CALLONI R, GAIO TA, MALVESSI E, SILVEIRAMM & DILLON AJP. 2011. Growth kinetics, production, and characterization of extracellular laccases from Pleurotus sajor-caju PS-2001. Process Biochem 46: 758-764.
  • BONATTI M, KARNOPP P, SOARES HM & FURLAN SA. 2004. Evaluation of Pleurotus ostreatus and Pleorotus sajor-caju nutricional charactistics when cultivated in different lignocellulosic wastes. Food Chem 88: 425-428.
  • BONATTI-CHAVES M, LIBARDI-JUNIOR N, BORGES G, WISBECK E, GERN R, FURLAN SA & FURIGO JUNIOR A. 2014. Production of bioactive substances in fed-batch and semi-continuous culture by Pleurotus ostreatus. Chem Engineer Trans 38: 307-312.
  • BREENE WM. 1990. Nutritional and medicinal value of specialty mushrooms. J Food Protect 53: 883-894.
  • BUSWELL JA, CA Y & CHANG S. 1996. Effect of nutrient nitrogen and manganese on manganese peroxidase and laccase production by Lentinula (Lentinus) edodes. Fems Microbiol Lett 128: 81-87.
  • CARVALHO CSM, AGUIAR LVB, SALES-CAMPOS C, MINHONI MTA & ANDRADE MCN. 2012. Applicability of the use of waste from different banana cultivars for the cultivation of the oyster mushroom. Braz J Microbiol 43(2): 819-826.
  • CHANG B & CHANG Y. 2016. Biodegradation of toxic chemicals by Pleurotus eryngii in submerged fermentation and solid-state fermentation. J Microbiol Immunol 49: 175-181.
  • DE FREITAS EN, BUBNA GA, BRUGNARI T, KATO CG & PERALTA RM. 2017. Removal of bisphenol A by laccases from Pleurotus ostreatus and Pleurotus pulmonarius and evaluation of ecotoxicity of degradation products. Chem Eng J 330: 1361-1369.
  • ELISASHVILI V, PENNINCKX M, KACHLISHVILI E, TSIKLAURI N, METREVELI E, KHARZIANI T & KVESITADZE G. 2008. Lentinus edodes and Pleurotus species lignocellulolytic enzymes activity in submerged and solid-state fermentation of lignocellulosic wastes of different composition. Bioresource Technol 99: 457-462.
  • ERKURT HA. 2015. Biodegradation and detoxification of BPA: involving laccase and a mediator. Clean – Soil Air Water 43(6): 932-939.
  • FENICE M, SERMANNI GG, FEDERICI F & D’ANNIBALE A. 2003. Submerged and solid-state production of laccase and Mn-peroxidase by Panus tigrinus on olive mil wastewater-based media. J Biotechnol 100: 77-85.
  • FERNÁNDEZ-ALEJANDRE KI, FLORES N, TINOCO-VALENCIA R, CARO C, FLORES C, GALINDO E & SERRANO-CARREÓN L. 2016. Diffusional and transcriptional mechanisms involved in laccases production by Pleurotus ostreatus CP50. J Biotechnol 223: 42-49.
  • FURLAN SA, GERN RMM, WISBECK E, BONATTI-CHAVES M, SILVEIRA MLL & SILVA HH. 2008. In: CURRENT TOPICS ON BIOPROCESSES IN FOOD INDUSTRY, vol I: Possibilities of Pleurotus applications in food, health and environmental technologies. Koutinas A, Pandey A and Larroche C (Eds), Asiatech, Nova Delhi, p. 495.
  • FURLAN SA, VIRMOND LJ, MIERS D, BONATTI M, GERN RMM & JONAS R. 1997. Mushroom strains able to grow at high temperatures and low pH values. World J Microb Biot 13: 689-692.
  • GALHAUP C, GOLLER S, PETERBAUER CK & STRAUSS J. 2002. Characterization of the major laccase isoenzyme from Trametes pubescens and regulation of its syntesis by metal ions. Microbiology 148: 2159-2169.
  • GLENN JK & GOLD MH. 1985. Purification and characterization of an extracellular Mn(II)-dependent peroxidase from the lignin-degrading basidiomycete, Phanerochaete chrysosporium. Arch Biochem Biophys 242: 329-341.
  • HESS J, LEITNER C, GALHAUP C, KULBE KD, HINTERSTOISSER B, STEINWENDER M & HALTRICH D. 2002. Enhanced formation of extracelular laccase activitity by the white-rot fungus Trametes multicolor. In: Finkelstein M, Mcmillan JD and Davison BH (Eds), Biotechnology for Fuels and Chemicals. Appl Biochem Biotech, Totowa: Humana Press, NJ, USA, p. 229-241.
  • JALAL N, SURENDRANATH AR, PATHAK JL, YU S & CHUNG CY. 2018. Bisphenol A (BPA) the mighty and the mutagenic. Toxicology Res-Uk 5: 76-84.
  • JOHANNES C & MAJCHERCZYK A. 2000. Laccase activity tests and lacase inhibitors. J Biotechnol 78: 193-199.
  • KUMAR VV, SATHYASELVABALA V, PREMKUMAR MP, VIDYADEVI T & SIVANESAN S. 2012. Biochemical characterization of three phase partitioned laccase and its application in decolorization and degradation of synthetic dyes. J Mol Catal B Enzym 74: 63- 72.
  • LIBARDI-JUNIOR N, CORREA M, BONATTI-CHAVES M, GERN RMM, WISBECK E, SCHLOSSER D & FURLAN SA. 2011. Production and applications of Pleurotus laccase. In: Soccol CR, Pandey A, Soccol VT and Larroche C (Eds), Advances in bioprocess in food industry, New Delhi: Asiatech Pub., New Delhi, India, p. 36-61.
  • LIBARDI-JUNIOR N, GERN RMM, FURLAN SA & SCHLOSSER D. 2012. Laccase production by the aquatic ascomycete Phoma sp. UHH 5-1-03 and the white rot basidiomycete Pleurotus ostreatus DSM 1833 during submerged cultivation on banana peels and enzyme applicability for the removal of endocrine-disrupting chemicals. Appl Biochem Biotech 167: 1144-1156.
  • LIU J, YU Z, LIAO X, LIU J, MAO F & HUANG Q. 2016. Scalable production, fast purification, and spray drying of native Pycnoporus laccase and circular dichroism characterization. J Clean Prod 127: 600-609.
  • MACELLARO G, PEZZELLA C, CICATIELLO P, SANNIA G & PISCITELLI A. 2014. Fungal laccases degradation of endocrine disrupting compounds. BioMed Research International, Article ID 614038, 8 p. DOI: 10.1155/2014/614038.
  • MANACHINI PL, FORTINA MG & PARINI C. 1987. Purification and properties of an endopolygalacturonase produced by Rhizopus stolonifera. Biotechnol Lett 9(3): 219-224.
  • MICHALOWICZ J. 2014. Bisphenol A – Sources, toxicity and biotransformation. Environ Toxicol Phar 37: 738-758.
  • MORE SS, RENUKA PS, PRUTHVI K, SWETHA M, MALINI S & VEENA SM. 2011. Isolation, purification, and characterization of fungal laccase from Pleurotus sp. Enzyme Research, Article ID 248735, 7 p. DOI:10.4061/2011/248735.
  • OSMA JF, TOCA-HERRERA JL & RODRÍGUEZ-COUTO S. 2011. Cost analysis in laccase production. J Environ Manage 92: 2907-2912.
  • PAKHADNIA YG, MALINOUSKI NI & LAPLO AG. 2009. Purification and characteristics of an enzyme with both bilirubin oxidase and laccase activities from mycelium of the basidiomycete Pleurotus ostreatus. Biochemistry-US 74(9): 1027-1034.
  • PANDEY A, NEGI S & SOCCOL CR. 2017. Current Developments in Biotechnology and Bioengineering: Production, Isolation and Purification of Industrial Products, 1st ed., United States: Elsevier, 886 p.
  • PARENTI A, MUGUERZA E, IROZ AR, OMARINI A, CONDE E, ALFARO M, CASTANERA R, SANTOYO F, RAMIREZ L & PISABARRO AG. 2013. Induction of laccase activity in the White rot fungus using water polluted with wheat straw extracts. Bioresource Technol 133: 142-149.
  • PISCITELLI A, GIARDINA P, LETTERA V, PEZZELLA C, SANNIA G & FARACO V. 2011. Industion and transcriptional regulation of laccases in fungi. Curr Genomics 12: 104-112.
  • QUEVEDO-HIDALGO B, NARVÁEZ-RINCÓN PC, PEDROZA-RODRÍGUEZ AM & VELÁSQUEZ-LOZANO ME. 2015. Production of lignocellulolytic enzymes from floriculture residues using Pleurotus ostreatus. Univ Scient 20: 117-127.
  • RASHAD MM, ABDOU HM, SHOUSHA WGH, ALI MM & EL-SAYED NN. 2010. Purification and characterization of extracellular polygalacturonase from Pleurotus ostreatus using citrus limonium waste. J Appl Sci Res 6: 81-88.
  • RORABACHER DB. 1991. Statistical treatment for rejection of deviant values: critical values of Dixon’s “Q” parameter and related subrange ratios at the 95% confidence level. Anal Chem 63: 139-146.
  • SAHAY R, YADAV RSS & YADAV KDS. 2008. Purification and characterization of extracellular laccase secreted by Pleurotus sajor-caju MTCC 141. Chinese J Biotechnol 24(12): 2068-2073.
  • SIFAKIS S, ANDROUTSOPOULOS VP, TSATSAKIS AM & SPANDIDOS DA. 2017. Human exposure to endocrine disrupting chemicals: effects on the male and female reproductive systems. Environ Toxicol Phar 51: 56-70.
  • TIEN M & KIRK TK. 1984. Lignin-degrading enzyme from Phanerochaete chrysosporium: purification, characterization, and catalytic properties of a unique H2O2-requiring oxygenase. P Natl Acad Sci 81: 2280-2284.
  • TINOCO-VALÊNCIA R, GÓMEZ-CRUZ C, GALINDO E & SERRANO-CARREÓN L. Toward an understanding of the effects of agitation and aeration on growth and laccases production by Pleurotus ostreatus. J Biotechnol 177: 67-73.
  • ZUCCA P, RESCIGNO A, OLIANAS A, MACCIONI S, SOLLAI FA & SANJUST E. 2011. Induction, purification, and characterization of a laccase isozyme from Pleurotus sajor-caju and the potential in decolorization of textile dyes. J Mol Catal B-Enzym 68: 216-222.

Publication Dates

  • Publication in this collection
    26 Mar 2021
  • Date of issue
    2021

History

  • Received
    23 Sept 2019
  • Accepted
    12 Jan 2020
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