PMCCPMCCPMCC

Search tips
Search criteria 

Advanced

 
Logo of mycobiologyAboutInstructions to Authorse-SubmissionMycobiologyThis Article
 
Mycobiology. 2017 March; 45(1): 52–56.
Published online 2017 March 31. doi:  10.5941/MYCO.2017.45.1.52
PMCID: PMC5395502

Screening and Production of Manganese Peroxidase from Fusarium sp. on Residue Materials

Abstract

In this study, we report the manganese peroxidase production ability from a Fusarium sp. strain using an inexpensive medium of agriculture residues of either rice straw or wood chips as carbon source. The highest manganese peroxidase activity on rice straw medium and on wood chips was 1.76 U/mL by day 9 and 1.91 U/mL by day 12, respectively.

Keywords: Fusarium sp., Hard wood chips, Manganese peroxidase, Rice traw

Lignocellulose biomass is a complex biopolymer consisting of cellulose, hemicellulose, pectin, and lignin; the first three components account for 70% dry weight. Lignocellulose biomass has been proposed as a potential carbon source for the production of biofuels. However, this potential has been limited by the high cost of pretreament processing to convert lignocelluloses to fermentable sugar needs to be overcome [1]. Lignocellulose biomass pretreatment is a process in which lignin links are broken to produce cellulose and hemicellulose which can be further degraded by cellulases, hemicellulases, respectively. Pretreatment methods comprise physical pretreatment, chemical pretreatment, solvent fractionation, and biological decomposition. Compare to other methods, biological decomposition using organisms or enzymes is preferred due to the environmentally friendly nature, less energy consume and high efficiency [2,3].

Manganese peroxidases (MnPs) (EC 1.11.1.13) belong to a unique enzyme groups that hydrolyze lignin substrates in nature; other members are lignin peroxidases, laccases, and versatile peroxidases. MnPs are extracellular glycoproteins with an iron protoporphyrin IX (heme) prosthetic group. MnPs are assumed to be the first in the line of proteins expressed during fungal catabolism of lignin [4,5]. Due to its lignin hydrolysis ability, there has been developing interest in MnPs. Potential application of MnPs has been extended in biopulping [6], biobleaching [7], and bioremediation [8].

Naturally, MnPs are found mainly in white-rot fungi, such as Phanerochaete chrysosporium, Ganoderma sp., Pleurotus sp., Trametes sp., and Irpex lacteus [4,5]. More recently, the production of ligninolytic enzymes including MnP was demonstrated in Phyllosticta, Aspergillus, Fusarium, and Penicillium [9,10]. However, knowledge of MnP secreted by Fusarium is limited.

This study identified biological production of MnP from tropical forest wood decay materials. MnP production was also investigated an inexpensive medium containing rice straw or wood chips as the carbon source.

Wood decay fungal mycelia were collected from Thua Thien Hue province, Vietnam forest bulk during the rainy season November and December, and stored at −20[degree celsius]. One gram bulk material was dissolved in 50 mL of sterilized water. One hundred microliters of the supernatant was spread on peptone dextrose agar (PDA; 2% peptone, 20% potato, 1.5% agar) and incubated at 28[degree celsius] until colonies form. Fungal mycelia were transferred to a fresh PDA plate for storage and determination of MnP activity.

MnP producing strains were detected by inoculating fungal mycelia on basal salts medium containing 0.01% guaiacol as described previously [11]. After 24 days culture, the MnP producing strains were confirmed by a halo to colony ratio of oxidized guacicol around the fungal colonies.

To investigate MnP production, the selected fungal strain was cultured on the rice straw or wood chips medium. Rice straw was collected from a farm in Hue City, Vietnam, and blender to yield material ≤ 2 mm in size. Wood chips were collected from local wood furniture factory. The selected strain was cultured in 5 mL PD liquid medium (2% peptone, 20% potato) at 30[degree celsius] for 3 days with shaking at 180 rpm. One milliliter of the culture was transferred into 50 mL MnP production medium containing 5% (w/v) rice straw or wood chips, and 0.2 g/L KH2PO4, 0.05 g/L MgSO4·7H2O, 0.01 g/L CaCl2·2H2O, 0.08 g/L CuSO4·5H2O, 0.05 g/L Na2MoO4·2H2O, 0.033 g/L MnSO4·H2O, 0.043 g/L ZnSO4·7H2O, and 0.05 g/L FeSO4·7H2O. The culture was maintained at 30[degree celsius] for 24 days with shaking at 180 rpm. One milliliter of fluid was collected at intervals of 3-day and MnP activity was measured. All chemicals were of analytical quality.

MnP activity was measured as described previously with slight modification [12]. Briefly, 100 µL of culture medium was incubated with 900 µL of 50 mM sodium malonate buffer containing 1 mM MnSO4. The reaction was initiated by adding hydrogen peroxide to a final concentration of 0.1 mM followed by incubation at 35[degree celsius] for 30 min. The complex form of Mn3+-malonate was qualified at 270 nm (ε270 = 11.59/mM/cm). One unit enzyme was defined as amount of required enzyme to produce 1 µmol product per minute under the experimental conditions.

The effect of pH on crude MnP was investigated at different pH levels ranging from 3.0 to 8.0. One hundred milliliters crude MnP was incubated with 900 µL of 50mM sodium malonate buffer containing 1 mM MnSO4 at 35[degree celsius] for 1 hr. Enzyme activity was qualified as described above. The optimal temperature for crude MnP was determined by assaying for enzyme activity at optimum pH and temperature from 20[degree celsius] to 50[degree celsius] at intervals of 5[degree celsius]. Enzyme was incubated with buffer for 1 hr at the appropriate temperatures before determination.

The effect of metal ions on enzyme were analyzed by incubating the enzyme solution in buffer containing 5 mM Mn2+, Al3+, Cu2+, Co2+, Fe2+, Mg2+, Ca2+, or Zn2+ in 1 hr at the optimal pH and temperature. The residual enzyme activity was measured as described above.

Fungal mycelia were cultured on 5mL PD medium and maintained for 3 days as described above. Mycelia were harvested by centrifuging at 14,000 rpm and 4[degree celsius] for 5 min, and washed with autoclaved distilled water. The washed mycelia were resuspended in 500 µL cetyltrimethyl ammonium bromide (CTAB) buffer (100 mM Tris-HCl, pH 8; 1.4M NaCl; 20 mM ethylenediaminetetraacetic acid; 2% CTAB; 0.2% β-mercaptoethanol). Cell walls were broken by sonication at 60 Hz in 6-sec interval for 5 min using a VC-130 sonicator (Sonics, Newton, CT, USA) and incubated at 65[degree celsius] for 30 min. Supernatants were harvested by centrifugation 14,000 rpm and 4[degree celsius] for 10 min. Fungal genomic DNA was purified by adding 500 µL of a 25 : 24 : 1 volume mixture of phenol : chloroform : isopropanol and mixed well by vortexing. The supernatant following centrifugation at 14,000 rpm for 10 min at 4[degree celsius] was recovered and transferred to new 1.5 mL tube. Genomic DNA was precipitated with two volume of pure ethanol, follow by washing with 70% ethanol, and was dissolved in 50 µL distilled-water.

The basic morphology characterization of the isolation was observed using an Eclipse 55i microscope (Nikon, Tokyo, Japan), while molecular identification was performed by the internal transcribed spacer 1 and 4 (ITS 1-4) sequence [13]. Briefly, the ITS region was amplified by PCR using 40 ng genomic DNA, 10pmol of each primer (ITS1, 5′-TCCGTAGGTGAACCTGCGG-3′ and ITS4, 5′-TCCTCCGCTTATTGATATGC-3′) and 1× Master mix (Invitrogen, Carlsbad, CA, USA) in a 25 µL reaction volume and following standard protocol. PCR products were qualified by 1% agarose gel electrophoresis and visualized with 0.5% ethidium bromide. Finally, PCR products were purified and sequenced using ITS1 and ITS4 primers. The sequence was Blast-search against the NCBI nucleotide database and the fungal strain was defined.

To identify the MnP producing microorganisms, we first isolated fungi from wood decal material grown on PDA medium. Approximately after 3-day inoculation, the fungal mycelia were observed. Total of eleven fungal mycelia which showed different morphotypes such as color, diameter of mycelia, and microscopic observation of spore formation were isolated and purified by placing of each specimen to new PDA medium. The pure cultures were stored on PDA plates at 4[degree celsius] and sub-cultured on PDA plates at 28[degree celsius] for 7 days for further studies. To screening potential peroxidase production, the mycelia were transferred into a new Petri dish containing PDA supplemented with 0.01% guaiacol. The potential secretion of peroxidase into medium was indicated by a guaiacol oxidation zone (Fig. 1A). The isolation mycelia had a light white-yellow color with a white cap in central zones. The diameter of mycelia at the 3-day incubation was 6 cm (Fig. 1B).

Fig. 1
Growth and morphology of Fusarium sp. HUIB01. A, Growth of Fusarium sp. on peroxidase selected medium containing 0.1% guaciacol; B, Growth of Fusarium sp. on peptone dextrose agar medium; C, Morphology of Fusarium sp. The fungus was grown on peroxidase ...

MnP production from the selected fungal strain was examined by growth on medium containing rice straw or wood chips as the carbon source. On 3-day of incubation, MnP activity was 1.1 and 0.81 U/mL on the medium containing rice straw or wood chips, respectively. MnP activity was highest after 9 days culture on rice straw medium, reaching 1.76 U/mL, and after 12 days culture of wood chips medium, reaching 1.91 U/mL (Fig. 2A). Enzyme accumulation decreased to ≤ 50% of maximal activity after 18 days cultivation in both media.

Fig. 2
A, Manganese peroxidase (MnP) production from Fusarium sp. HUIB01 on rice straw (closed circle) and wood chips medium (closed diamond); B, Effect of pH on crude MnP activity; C, Effect of temperature on crude MnP activity; D, Effect of metal ion on crude ...

A study of Fusarium concolor ligninolytic enzyme reported that on wheat straw medium, the fungus was able to produce laccase, lignin peroxidase, and MnP under liquid fermentation; MnP activity was 0.9 U/g biomass as an intracellular protein [10]. A certain level of MnP was found on extracellular enzyme of Fusarium verticillioides [9] and Fusarium solani [14]. Similarly, we observed MnP in supernatant with a level of expression in accordance with F. verticillioides.

The effect of pH on MnP was studied (Fig. 2B). Similar to other MnPs, the MnP displayed high activity in an acidic medium with a pH around 4.0. The results also indicated MnP is very sensitive to pH. Enzyme activity decreased rapidly when pH was ≥ 5.0 and ≤ 3.0. The retained activity was ≤ 60% maximum activity, especially above pH 6. Phanerochaete chrysosporium is one of the most well studied fungus model for MnP production. The optimal pH of P. chrysosporium MnP is reported 2.5–4.0 [15,16]. However, MnP produced from Trametes has a higher pH optimal with a range of 4.0–5.5 [17].

MnP activity dramatically increased when the temperature was increased from 20[degree celsius] and reached its highest activity at 35[degree celsius]. Enzyme activity diminished with increasing temperature. The retained MnP activity was ≤ 30% when the reaction temperature was ≥ 50[degree celsius] (Fig. 2C). The optimal temperature of the presently studied is in accordance with MnP from P. chrysosporium [18] but differs from Trametes MnP, which displayed an optimal temperature of 70[degree celsius] [17].

We also examined the effect of various metal ions on MnP activity. Metal ions inhibited MnP activity (Fig. 2D) except for Mn2+. Mn2+ did not affect MnP activity from Trametes, but Zn2+, Na+, Mg2+, and Al3+ reduced enzyme activity, similar to the present observation. Trametes MnP was strongly against Ni2+, Li+, Ca2+, and K+ [17].

The morphology characterization revealed common shape of Fusarium species such as straight elongation of microconidia, barely notched of basal cells, papillate curved of apical cells [19,20]. We also performed molecular identification of the strain through the sequence of ITS1-4 region. We obtained a PCR product with size of 550 bp. The PCR product was then sequenced and the sequence was searched against the NCBI database using BLAST function. The strain was highly relevant to Fusarium species such as Fusarium sp. E8524h (HQ117863), F. solani C239 (KU377471), F. solani OUCMBI110106 (KP269017), and F. lateritium CBPPR0046 (KT211538) (Fig. 3). Hence, it was designated as Fusarium sp. HUIB01. The ITS sequence was also deposited on NCBI with accession number KX388183. In this study, we isolated a potential MnP producing fungal strain isolated from a forest area. The strain produced MnP under fermentation separately using rice straw and wood chips as the carbon source. Highest MnP activity on rice straw medium was 1.76 U/mL and 1.91 U/mL on wood chips medium. The crude enzyme had optimal pH and temperature of 4.0 and 35[degree celsius], respectively. Genetic comparison of the strain to others revealed it to be Fusarium sp. Our findings point the way to a strategy capable of achieving the enzymatic conversion of biomass residual to a valuable product.

Fig. 3
Phylogenetic relationship tree among Fusarium sp. HUIB01 and other Fusarium strains based on the internal transcribed spacer rDNA gene sequences. The Fusarium sp. HUIB01 was marked as asterisk. The tree was generated using MEGA 6.0 software.

ACKNOWLEDGEMENTS

This research was supported by Basic Science and Technology Program, Hue University (No. DHH2015-15-03) and the World Academy of Sciences (No. 15-097RG/BIO/AS-I-FR3240287089). In partly, this research was also supported by the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIP) (No. 2014R1A2A1A11051376). We thank the Institute of Biotechnology, Hue University for kindly providing the facilities for this research.

References

1. Kumar R, Singh S, Singh OV. Bioconversion of lignocellulosic biomass: biochemical and molecular perspectives. J Ind Microbiol Biotechnol. 2008;35:377–391. [PubMed]
2. Zhao XQ, Zi LH, Bai FW, Lin HL, Hao XM, Yue GJ, Ho NW. Bioethanol from lignocellulosic biomass. Adv Biochem Eng Biotechnol. 2012;128:25–51. [PubMed]
3. Chundawat SP, Beckham GT, Himmel ME, Dale BE. Deconstruction of lignocellulosic biomass to fuels and chemicals. Annu Rev Chem Biomol Eng. 2011;2:121–145. [PubMed]
4. Manavalan T, Manavalan A, Heese K. Characterization of lignocellulolytic enzymes from white-rot fungi. Curr Microbiol. 2015;70:485–498. [PubMed]
5. Janusz G, Kucharzyk KH, Pawlik A, Staszczak M, Paszczynski AJ. Fungal laccase, manganese peroxidase and lignin peroxidase: gene expression and regulation. Enzyme Microb Technol. 2013;52:1–12. [PubMed]
6. Liew CY, Husaini A, Hussain H, Muid S, Liew KC, Roslan HA. Lignin biodegradation and ligninolytic enzyme studies during biopulping of Acacia mangium wood chips by tropical white rot fungi. World J Microbiol Biotechnol. 2011;27:1457–1468. [PubMed]
7. Moreira MT, Feijoo G, Palma C, Lema JM. Continuous production of manganese peroxidase by Phanerochaete chrysosporium immobilized on polyurethane foam in a pulsed packed-bed bioreactor. Biotechnol Bioeng. 1997;56:130–137. [PubMed]
8. Qin X, Zhang J, Zhang X, Yang Y. Induction, purification and characterization of a novel manganese peroxidase from Irpex lacteus CD2 and its application in the decolorization of different types of dye. PLoS One. 2014;9:e113282. [PMC free article] [PubMed]
9. Pant D, Adholeya A. Enhanced production of ligninolytic enzymes and decolorization of molasses distillery wastewater by fungi under solid state fermentation. Biodegradation. 2007;18:647–659. [PubMed]
10. Li L, Li XZ, Tang WZ, Zhao J, Qu YB. Screening of a fungus capable of powerful and selective delignification on wheat straw. Lett Appl Microbiol. 2008;47:415–420. [PubMed]
11. Xu C, Singh D, Dorgan KM, Zhang X, Chen S. Screening of ligninolytic fungi for biological pretreatment of lignocellulosic biomass. Can J Microbiol. 2015;61:745–752. [PubMed]
12. Wariishi H, Valli K, Gold MH. Manganese(II) oxidation by manganese peroxidase from the basidiomycete Phanerochaete chrysosporium: kinetic mechanism and role of chelators. J Biol Chem. 1992;267:23688–23695. [PubMed]
13. Manter DK, Vivanco JM. Use of the ITS primers, ITS1F and ITS4, to characterize fungal abundance and diversity in mixed-template samples by qPCR and length heterogeneity analysis. J Microbiol Methods. 2007;71:7–14. [PubMed]
14. Saparrat MC, Martínez MJ, Tournier HA, Cabello MN, Arambarri AM. Production of ligninolytic enzymes by Fusarium solani strains isolated from different substrata. World J Microbiol Biotechnol. 2000;16:799–803.
15. Mester T, Tien M. Engineering of a manganese-binding site in lignin peroxidase isozyme H8 from Phanerochaete chrysosporium. Biochem Biophys Res Commun. 2001;284:723–728. [PubMed]
16. Gu L, Lajoie C, Kelly C. Expression of a Phanerochaete chrysosporium manganese peroxidase gene in the yeast Pichia pastoris. Biotechnol Prog. 2003;19:1403–1409. [PubMed]
17. Zhang H, Zhang S, He F, Qin X, Zhang X, Yang Y. Characterization of a manganese peroxidase from white-rot fungus Trametes sp.48424 with strong ability of degrading different types of dyes and polycyclic aromatic hydrocarbons. J Hazard Mater. 2016;320:265–277. [PubMed]
18. Saravanakumar T, Palvannan T, Kim DH, Park SM. Manganese peroxidase H4 isozyme mediated degradation and detoxification of triarylmethane dye malachite green: optimization of decolorization by response surface methodology. Appl Biochem Biotechnol. 2013;171:1178–1193. [PubMed]
19. Chehri K, Ghasempour HR, Karimi N. Molecular phylogenetic and pathogenetic characterization of Fusarium solani species complex (FSSC), the cause of dry rot on potato in Iran. Microb Pathog. 2014;67–68:14–19. [PubMed]
20. Leslie JF, Summerell BA. The Fusarium laboratory manual. Oxford: Blackwell Publishing; 2006.

Articles from Mycobiology are provided here courtesy of Korean Society of Mycology