In this study, we used traditional methods to isolate and screen for fungal laccases that have potential for use in the textile industry (dye decolorization) and a molecular marker to identify studied samples. Fifteen strains of basidiomycetes were isolated and screened for laccase activities on phenol, guaiacol and RBBR. Five strains showed positive laccase activities on all three substrates.
Trang 1This paper is available online at http://stdb.hnue.edu.vn
ISOLATION, SELECTION AND IDENTIFICATION OF LACCASE-PRODUCING
FUNGAL STRAINS AND ITS DYE DECOLORIZATION ABILITY
Duong Minh Lam and Truong Thi Chien
Faculty of Biology, Hanoi National University of Education
Abstract. Fungal studies have thus far received little attention from scientists in
Vietnam, especially regarding fungal diversity and their application in industrial
processes In this study, we used traditional methods to isolate and screen for fungal
laccases that have potential for use in the textile industry (dye decolorization) and
a molecular marker to identify studied samples Fifteen strains of basidiomycetes
were isolated and screened for laccase activities on phenol, guaiacol and RBBR
Five strains showed positive laccase activities on all three substrates The strain
CPB30 presented the largest halo zone diameter and was also fastest to decolorize
RBBR in a culture broth (within 64 hours of incubation) Using complete ITS
sequence analysis, the CPB30 strain was identified as being Trametes maxima
(T maxima CPB30) This strain expresses high laccase activity (614 -796 U/mL)
which warrants further applied research
Keywords: Laccase, Trametes maxima, RBBR, decolorization, Cuc Phuong.
1 Introduction
Water pollution is a serious problem in many countries and this is especially true
in developing countries where uncontrolled industrial processes are taking place A type
of pollutant that is currently being released into the environment is the dyes used in the fabric industry Laccases (benzenediol: oxygen oxidoreductases; EC 1.10.3.2) have been efficiently used to decolor and detoxify dyes due to the oxidizing capacity of laccases on
a wide variety of organic and inorganic compounds, including diphenols, polyphenols, substituted phenols, diamines and aromatic amines, with a concomitant reduction of
molecular oxygen to water [12] Laccases have been found in bacteria (Azospirillum lipoferum, Bacillus subtilis, Streptomyces lavendulae, S cyaneus) [2, 4, 7, 9] and plants, but it is predominantly found in fungi [1] Most of the laccases studied are of fungal
origin, especially from white-rot fungi, such as Phlebia radiata, Pleurotus ostreatus and
Received September 17, 2013 Accepted December 2, 2013.
Contact Duong Minh Lam, e-mail address: duong.minhlam@gmail.com
Trang 2Trametes versicolor Recently, laccases have been used in conjunction with other enzymes (cellulases, xylanases) in industrial applications such as pulp delignification, textile dye bleaching, biopolymer modification and bioremediation [3]
Screening for novel laccases with various characteristics that can be used in different industrial applications is important Different studies have been done on substrates, such as phenolic compounds (tannic, gallic, guaiacol and syringaldazine) and the polymeric dyes remazol brilliant blue R (RBBR) and Poly R-478, in order to discover microorganisms that produce laccases [10] These substrates are color indicators as they change color when oxidized by laccase which is produced by microorganisms and makes halozone around positive colonies However, it is not possible to precisely estimate the extent of laccase activity so normally only a general idea of laccase presence and activity can be given
Vietnam is a hot spot for biodiversity in the world, with 12,000 higher plant species It is estimated that 72,000 fungal species [5] are found in Vietnam and among them perhaps 15,000 - 20,000 are of the Basidiomycota phylum This is a huge source
of new and interesting compounds that are waiting to be discovered This study aims
to 1) isolate fungi from basidiomycetous samples collected in Cuc Phuong National Park, Vietnam, 2) screen for laccase-producing fungi using different color indicators, 3) estimate decolorization of the laccase of selected strain and 4) identify species level using ITS rDNA sequence analysis
2.1 Materials and methods
* Materials of the study:
15 fungal samples were collected in Cuc Phuong National Park in June 2011 Chemicals: guaiacol, remazol brilliant blue R (RBBR), 2,2’-azino-bis(3-ethylbenzothiazoline-6-sulfonic acid) (ABTS), diammonium salt, phenol, D-glucose All chemicals were supplied by Sigma and at a high purity level Media: PDA (Potato Dextrose Agar); Czapeck_Dox (30 g/L saccharose; 0.5 g/L MgSO4; 3.5 g/L NaNO3; 1.5 g/L K2HPO4; 0.5 g/L KCl; 0.01 g/L FeSO4; pH 5 - 5.5)
* Methods of the study:
- Isolation: Fresh fungal fruiting bodies collected from sites were taken to the
laboratory in 12 hours where dust and litter was removed from them Surface sterilization was done using 96% ethanol for 2 minutes The fruiting bodies were cut and torn into
2 halves using a sterile razor blade Internal tissues were removed and placed on a PDA medium
- Screening for laccase: Fungal cultures were grown on a PDA medium containing
phenol, guaiacol and RBBR as substrate for laccases The presence of laccases is shown
as a halo around the fungal colony Phenol and guaiacol were oxidized and become brown while RBBR changed from blue to light brown in the presence of laccases
Trang 3- Laccase activity assay: The fungal culture was inoculated in 100 ml of liquid
PDA medium in a flask and incubated at 30◦C for 90 hours, shaken at 160 rpm Then, the culture broth was centrifuged at 6000 rpm for 5 mins The culture supernatant was used as
a crude enzyme for laccase activity estimation Laccase activity was estimated based on the oxidization of ABTS (2,2’-azino-bis 3-ethylbenzothiazoline-6-sulfonic acid), which absorbs light best at 420 nm The enzymatic reaction includes 800 µL of 0.5 M acetate buffer, pH 5.0; 100 µL of 5 mM ABTS; and 100 µL of crude enzyme The reaction mixture was incubated for 10 minutes at 40◦C The reaction was stopped by adding 100
µL of TCA 50% (v/v) In the control test, TCA was added before adding the crude enzyme All other factors between the control and experimental tests were consistent and identical The differences in absorbance at OD420nm value between the control and experimental samples were used to calculate activity using the following formula [13]:
U/mL = [NA × (106/e420 × d) × V/v × F]/t where NA: increasing absorbance at 420nm; 106/e420 × d: conversion toµmol converted substrate/mL using the molar extinction coefficient (ǫABTS, 420 = 3600 M−1.mm−1); d: length of the light path in mm (10 mm); V: total volume (1000µL); v: volume of sample (100µL); V/v: dilution in assay (10); F: dilution factor of stock; t: reaction time (10 mins)
- Identification of the isolated strain: DNA extraction was carried out using a CTAB lysis buffer and phenol chloroform as outlined by Jeewon
et al [6] The complete ITS (including 5.8S) regions were amplified using primer pair ITS4 (5’- TCCTCCGCTTATTGATATGC-3’) and ITS5 (5’-GGAAGTAAAAGTCGTAACAA-GG-3’) The amplification conditions were performed in a 50µL reaction volume as follows: 5 µ of 10X PCR buffer, 0.2 mM each dNTP, 0.3 M of each primer; 1.5 mM MgCl2, 1 unit of Taq Polymerase and 10 ng DNA PCR parameters were as follows: Initial denaturation 94 ◦C for 3 min, 30 cycles of 94
◦C for 1 min, 52 ◦C for 50 s, 72◦C for 1 min, the final extension at 72 ◦C for 10 min
A characterization of the PCR products was done using agarose gel electrophoresis on a 1% agarose gel containing ethidium bromide as the staining agent DNA sequencing was performed by the Bioneer Company in Korea using both primers A BioEdit program was used to generate the consensus sequence of the sample studied Sequences used in the analysis were chosen from NCBI using a nucleotide Blast tool A neighbor-joining method was selected for sequence analysis and phylogenetic tree generation
2.2 Results and discussions
2.2.1 Fungal isolation and laccase screening
The collected basidiomycetous samples were isolated on PDA medium, obtaining
15 pure cultures All 15 strains were screened for laccase on three different substrates (phenol, guaiacol and RBBR) in Petri dishes Halozone appearing around a colony indicated the presence of laccase The results can be seen in Table 1
Trang 4Table 1 Laccase activity of 15 strains
Strains Phenol Guaiacol RBBR Strains Phenol Guaiacol RBBR
-(+): positive; (-): negative
Five strains (CPB12, CPB17, CPB21, CPB28 and CPB30) showed a high level of laccase activity on all three substrates The typical colors of the oxidized substrates were brown for phenol and guaiacol, and hyaline to pale brown for RBBR (Figure 1A, B) The CPB30 strain was selected for further study due to its large halozone diameter on all three substrates
Figure 1 Laccase activity of the five strains on different substrates: A - Guaiacol, B - RBBR
2.2.2 RBBR decolorization
Besides the tests on solid media, the five strains were also screened for decolorization in a culture broth into which was added RBBR 0.01% (w/v) Incubation was done at 30◦C, shaking at 160 rpm for 96 hours The CPB30 strain was the fastest to decolorize RBBR, after 60 hours of incubation, and the slowest was the CP21 strain, after
84 hours However, the strains showed different colors of oxidized RBBR (Figure 2) The CPB30 strain was the most effective in decolorizing RBBR and was the strain that showed the most promise for application in industrial treatment
Trang 5Figure 2 RBBR decolorization of some selected strains
2.2.3 Laccase activity of the CPB30 strain
Laccases from the CPB30 strain were quantitatively estimated using the described method considering incubation time in order to get a proper taking-sample time for other experiments (data not shown) The results are presented in Figure 3
Figure 3 Laccase activity of the CPB30 strain along with incubation time
The best time to collect the culture broth for laccase estimation was 84 - 90 hours, and the highest enzyme activity was 614.8 U/mL and 796.8 U/mL, corresponding to the broth without RBBR and with RBBR added The results show that RBBR played the role
of substrate and it was also the enzyme producing inducer
Laccases from fungi, especially from white rot fungi, have widely been studied However, few have been reported as having laccase activity that is as high as that of the CPB30 strain [8, 11] The results suggest that this CPB30 strain could potentially be used to produce laccases for many different purposes, particularly decolorization at an industrial scale
2.2.4 Molecular identification of the CPB30 strain
The complete coding sequence of ITS1-5.8S-ITS2 of rRNA includes 568 nucleotides, with single stranded molecular weight of 172087.00 Daltons, G+C content = 48.24% and A+T content = 51.76% The full sequence is shown below:
Trang 6The sequence was used to search for similar or close related sequences in the GenBank using the nBlast tool of the NCBI website The results show that the CPB30
is most closely related to Trametes maxima FPRI376 (JN164918) and T maxima 9
(JN164933) with a 99% similarity in sequence
Sequence analysis was done using available sequences of different Trametes
species The neighbor-joining method was run in ClustalX8.3 with 10000 replications and a tree was generated (Figure 4) This analysis confirms that the CPB30 strain was
derived from Trametes maxima and is therefore named T maxima CPB30.
Figure 4 The relationship of the CPB30 strain with other Trametes species based on the complete ITS sequence analysis using the neighbor-joining method
From the 15 isolated basidiomycetous cultures, 5 strains showed laccase activity
on all three substrates The five strains differed in time and capacity to decolorize RBBR
Trang 7added to culture broth Of the 5 strains, CPB30 was the strongest as it decolored RBBR within 64 hours of incubation while other strains took much longer (up to 84 hours) Molecular identification was applied to CPB30 and it was shown that this strain was
derived from Trametes maxima.
Acknowledgement The work was supported by the National Foundation for Science and
Technology (NAFOSTED) of Vietnam under grant number 106.07-2011.57
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