Next Article in Journal
Combined Transcriptome and Metabolome Profiling Provide Insights into Cold Responses in Rapeseed (Brassica napus L.) Genotypes with Contrasting Cold-Stress Sensitivity
Previous Article in Journal
A Comprehensive Analysis of the DUF4228 Gene Family in Gossypium Reveals the Role of GhDUF4228-67 in Salt Tolerance
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Functional Characterization of Laccase Isozyme (PoLcc1) from the Edible Mushroom Pleurotus ostreatus Involved in Lignin Degradation in Cotton Straw

1
State Key Laboratory of Horticultural Crop Germplasm Resources Creation and Utilization of Ministry of Agriculture and Rural Affairs, Institute of Horticulture Research, Anhui Academy of Agricultural Sciences, Hefei 230031, China
2
College of Life Science, Anhui Agricultural University, Hefei 230036, China
3
Provincial Resource Database of Wood Rot Edible Mushrooms in Anhui Province, Hefei 230031, China
*
Author to whom correspondence should be addressed.
These authors contributed equally to this work.
Int. J. Mol. Sci. 2022, 23(21), 13545; https://doi.org/10.3390/ijms232113545
Submission received: 9 October 2022 / Revised: 1 November 2022 / Accepted: 3 November 2022 / Published: 4 November 2022
(This article belongs to the Section Molecular Microbiology)

Abstract

:
Fungal laccases play important roles in the degradation of lignocellulose. In this study, the laccase producing cotton straw medium for Pleurotus ostreatus was optimized by single-factor and orthogonal experiments, and to investigate the role of Lacc1 gene, one of the laccase-encoding genes, in the degradation of cotton straw lignin, an overexpression strain of Lacc1 gene was constructed, which was analyzed for the characteristics of lignin degradation. The results demonstrated that the culture conditions with the highest lignin degradation efficiency of the P. ostreatus were the cotton straw particle size of 0.75 mm, a solid–liquid ratio of 1:3 and containing 0.25 g/L of Tween in the medium, as well as an incubation temperature of 26 °C. Two overexpression strains (OE L1-1 and OE L1-4) of Lacc1 gene were obtained, and the gene expression increased 12.08- and 33.04-fold, respectively. The results of 1H-NMR and FTIR analyses of significant changes in lignin structure revealed that Lacc1 gene accelerated the degradation of lignin G-units and involved in the cleavage of β-O-4 linkages and the demethylation of lignin units. These findings will help to improve the efficiency of biodelignification and expand our understanding of its mechanism.

1. Introduction

Laccase is a multi-copper oxidase that catalyzes the oxidation of various phenolic and non-phenolic substrates associated with the lignin structure, while reducing oxygen to water [1,2,3]. Due to the wide range of natural substrates, laccase is used in several fields of industrial and biotechnological applications, such as improvement of fiber properties, degradation of antibiotics and other pharmaceutical products, fuels, detoxification of environmental pollutants, stabilization of lignin by providing chemical precursors, and pulp bleaching paper industry [4,5,6,7,8]. Most of the known laccase enzymes originated from fungi, especially white rot fungi that can perform lignin degradation [9,10,11].
Fungal laccase is encoded by a multigene family and there are multiple isozymes that are mainly involved in physiological processes such as lignin degradation, fruiting body formation, pigment formation in asexual development and pathogenesis [12,13,14,15,16]. Jiao et al. [17] analyzed the expression patterns of 12 laccase encoding genes distributed in the genome of P. ostreatus PC15 strain and hypothesized that PoLac2 might be closely related to lignin degradation by P. ostreatus. While PoLac3 and PoLac5 may be related to the formation of fruiting primordium and fruiting body, respectively, PoLac12 may be related to the development of P. ostreatus fruiting body, and overexpression of PoLac2 gene was found to enhance the laccase activity and lignin degradation of P. ostreatus. Lu et al. [18] performed qRT-PCR on 11 Laccase genes of Volvariella volvacea, and hypothesized that Vvlcc3 was involved in stipe elongation by combining with heterologous expression in Pichia pastoris. Analysis of the transcriptome of different developmental stages and different tissues of Flammulina velutipes revealed that the expression of lac4 gene was higher than other laccase genes at all developmental stages, suggesting it is involved in the biotransformation of lignin [19]. Successful overexpression of the Pblac1 gene in white-rot fungus Polyporus brumalis revealed that the transformed strain exhibited higher lignin degradation activity and effective decolorization of RBBR dye compared to the wild type [20]. Homologous overexpression of the Gtlcc3 gene in brown-rot fungus Gloeophyllum trabeum resulted in transformed strains with significantly higher lignin degradation and ethanol production than the wild type [21]. At present, the functional roles of laccase genes are mostly at the speculative stage, and the specific functional roles of each isoenzyme are not clearly defined, and there are fewer studies related to functional verification and molecular mechanisms.
Crop straw is mainly composed of cellulose, hemicellulose and lignin, in which cellulose molecules are embedded in a barrier formed by covalent bonding of lignin and hemicellulose, making it difficult for enzymes to contact with cellulose molecules, reducing the utilization and nutritional value of straw, which is the main obstacle to the effective conversion of lignocellulosic [22,23]. Cotton as one of the important economic crops in China, its harvest will also produce a large number of byproducts-cotton straw [24,25]. With the development of science and technology, urbanization and the improvement of living standards, the application of cotton straw as a living fuel decreases, and is burned in the fields by cotton farmers, both wasting resources and polluting the environment. On the contrary, the application of cotton straw as a base material has been further strengthened. However, cotton straw is similar to branch of tree, and compared with corn, rice and wheat straws, they have higher lignin content, which greatly limits the degradation by microorganisms [26].
In a previous study, it was found that Pleurotus ostreatus Suping 1 could be produced on cotton straw substrates [17], but the optimal production conditions and lignin degradation mechanism of cotton straw were not clear. Therefore, in this study, the optimal conditions for lignin degradation by P. ostreatus Suping 1 on cotton straw substrate were firstly screened by medium optimization experiments. Then, the Lacc1 gene of P. ostreatus Suping 1 was obtained by homologous cloning, and the molecular mechanism of Lacc1 in lignin degradation of cotton straw was analyzed by overexpression technique. The results of this study provide new insights into the mechanism of lignin degradation by white-rot fungi and provide useful guidance for the promotion and application of the laccase in P. ostreatus.

2. Results

2.1. Optimized Culture Factors for Laccase Production in P. ostreatus Suping 1

The degradation rate of cotton straw lignin by P. ostreatus Suping 1 differed significantly (p > 0.05) among the four treatments with straw particle size of 5 mm, 0.75 mm, 0.425 mm and 0.25 mm. The highest degradation rate of cotton straw lignin was found at the straw particle size of 0.75 mm (Figure 1a). However, there was no significant difference (p > 0.05) in the effect of the ability of P. ostreatus Suping 1 to degrade cotton straw lignin in the four treatments of the solid–liquid ratio of 1:2, 1:3, 1:4 and 1:5 (Figure 1b). Among the three temperature experimental groups at 20 °C, 25 °C, and 27 °C, the degradation rate of cotton straw in the 25 °C experimental group differed significantly from that in the 20 °C experimental group (p < 0.05) and not significantly different from that in the 27 °C experimental group (p > 0.05), and the degradation rate of cotton straw at 27 °C was slightly higher than that at 25 °C, indicating that the ability of P. ostreatus Suping 1 to degrade lignin increased with the increase in temperature in a certain temperature range (Figure 1c). The treatment groups with the addition of surfactant Tween 80 concentration of 0.1 g/L, 0.2 g/L, 0.3 g/L, 0.4 g/L and 0.5 g/L showed significant differences in the degradation rate of cotton straw, except for Tween 80 at concentrations of 0.4 g/L and 0.5 g/L (p > 0.05), and P. ostreatus Suping 1 degraded cotton straw lignin the most at the Tween 80 content of 0.2 g/L (Figure 1d).
Based on the results of the Single-factor optimization experiments, nine different formulations were prepared, and the experimental runs were carried out based on the experimental matrix, and the observed responses are shown in Table 1. The laccase activity of P. ostreatus Suping 1 was significantly different under different combinations of factors. No. 5, which was under the multifactorial conditions of straw particle size of 0.75 mm, solid–liquid ratio of 1:3, incubation temperature at 26 °C and Tween content of 0.25 g/L, had the highest laccase activity of 125.65 ± 8.36 U/mL, which was significantly stronger than other culture conditions. This indicates that the laccase production ability of P. ostreatus Suping 1 is stronger under No. 5 culture condition. Among the four factors to be investigated, in descending order of importance, the effect on the laccase activity of P. ostreatus Suping 1 was B > A > C > D, which means that the most influential factor was the solid–liquid ratio, followed by the straw particle size, again by the incubation temperature, and the least influential was the Tween 80 content (Table 2).

2.2. Cloning and Analysis of the Laccase-Encoding Gene (Lacc1) in P. ostreatus Suping 1

In the genome of P. ostreatus Suping 1, the full-length cDNA sequences of Lacc1 gene were 1599 bp. By comparison, the CDS sequence of the Lacc1 gene in strain P. ostreatus Suping 1 differed from that in strain P. ostreatus PC15 by nine nucleotides (Figure 2a). DNA sequence analysis showed that 20 exons were interrupted by 19 introns in Lacc1 of P. ostreatus Suping 1 (Figure 2b) and have three Cu-oxidase domains (Figure 2c). The mRNA expression level of Lacc1 gene in mycelial period (10 d, 20 d and 30 d), fruiting primordium, juvenile mushroom and maturation mushroom of P. ostreatus Suping 1 was detected by qRT-PCR, and the results showed that the expression of Lacc1 gene increased and then decreased in these culture stages of P. ostreatus Suping 1, and the highest expression was in mycelial period (30 d), followed by fruiting primordium (Figure 2d). This indicates that it may perform physiological functions more in the mycelium and fruiting primordium stage.

2.3. Overexpression of Lacc1 Gene

To investigate the lignin degradation function of the Lacc1 gene, the CDS sequence of the Lacc1 gene from P. ostreatus Suping 1 was cloned into pCAMBIA1304 and transformed into P. ostreatus Suping 1 using the ATMT method, driven by the Pogpd promoter. Subsequently, four transformants were randomly selected to verify whether the reporter gene β-glucosidase (gus) was inserted into the genome of P. ostreatus Suping 1. The results showed that these mutants showed the presence of the amplification product of gus. In addition, GUS histochemical assays showed that after 10 h of staining, the immature substrates of the mutants turned blue in the buffer of GUS staining, whereas the wild type did not, indicating that GUS was expressed in the mutants. The results indicated that the exogenous Lacc1 gene had been successfully integrated into the genome of the P. ostreatus Suping 1 (Figure 3a). After cultivating in the cotton straw medium for 30 days, the expression of Lacc1 gene in each transformant was detected, in which the expression of Lacc1 gene in OE L1-1 and OE L1-4 was 12.08 and 33.04 times higher than that in the wild-type strain, respectively (Figure 3b).

2.4. Characterization of the Function of Lacc1 Gene in Lignin Degradation of Cotton Straw

To clarify the function of the Lacc1 gene in lignin degradation of cotton straw, wild-type and overexpressed P. ostreatus Suping 1 were cultured in cotton straw medium and their laccase activity was measured at days 5, 10, 15, 20, 25 and 30, as well as their ability to degrade cotton straw lignin (30th day). The overexpressed transformants OE L1-1 and OE L1-4 secreted higher extracellular laccase activity than the wild type, except on the 15th day when the extracellular laccase activity was lower than that of the wild type, especially on the 5th day of incubation which was significantly higher than that of the wild type, with an approximately 1-fold increase in laccase activity (Figure 4a). The lignin degradation rate of the wild-type strain was 48.56 ± 0.23% for cotton straw. The lignin degradation rates of overexpressed transformants were 51.89 ± 0.94% (OE L1-1) and 51.10 ± 0.31% (OE L1-4), respectively (Figure 4b). The lignin degradation rates of the overexpressed transformants were increased by 6.86% (OE L1-1) and 5.23% (OE L1-4), respectively, compared to the wild type. Thus, it was direct evidence that Lacc1 gene was involved in the biodegradation of cotton straw lignin.

2.5. FTIR Analysis of the Degradation Products from Lignin

To explore the molecular mechanism of Laac1 gene involved in lignin degradation. Lignin was extracted from cotton straw medium inoculated with OE L1-4 and WT for 30 days, and the structural changes in lignin degradation were determined using infrared spectroscopy to resolve the characteristics of absorption peaks and corresponding functional groups in each infrared spectrogram (Figure 5a, b). The intensity of the absorption peak of each functional group is the intensity ratio to that of the absorption peak at 1508 cm−1. The absorption peak at 2924 cm−1 was mainly C-H stretching in methyl and methylene groups, where the relative absorption intensity of lignin in the culture medium of OE L1-4 was 0.75, and the relative absorption intensity of lignin in the culture medium of wild-type strain was 0.95. The reduced intensity of lignin in the culture medium of OE L1-4 indicates that the Lacc1 gene may promote the demethylation/demethoxylation reaction of the methyl/methoxy on the benzene ring of the lignin monomer. The absorption peak at 1635 cm−1 corresponds to the C=O stretching in conjugated aryl ketene of carbonyl groups, and the relative absorption intensity at 1635 cm−1 of lignin from culture medium of wild-type strain was higher than that of culture medium inoculated with OE L1-4, indicating that overexpression of the Lacc1 gene reduced the carbonyl conjugated aromatic ketone C=O-related reaction of lignin (e.g., production of phenolic hydroxyl groups, etc.). The absorption peaks at 1595 cm−1 and 1506 cm−1 corresponded to the Aromatic skeletal vibrations plus C=O stretching and Aromatic skeletal vibrations, respectively, and the cultures inoculated with wild-type and OE L1-4 strains had comparable relative intensities at both absorption peaks, indicating that the Lacc1 gene was not affecting the opening and degradation of the benzene rings in lignin (Table 3).

2.6. 1H-NMR Analysis of the Degradation Products from Lignin

NMR hydrogen spectroscopy has also been applied to determine structural changes in lignin degradation (Figure 5c, d and Table 4). Based on the 1H-NMR spectrogram for the acetylated lignin, the lignin range was distinguished, and linin was integrated to calculate the proton ratio between functional groups and bond-type structures [28]. The percentage of Aromatic protons in guaiacyl units of acetylated lignin in cotton straw medium cultured with OE L1-4 was decreased to 0.64 (CDCl3 was 1) compared to wild type (0.68). This indicates that the Lacc1 gene accelerates the degradation of G-unit lignin. However, the percentage of Aromatic protons in syringyl units of acetylated lignin in cotton straw medium cultured with OE L1-4 was increased to 0.45 (CDCl3 was 1) compared to wild type (0.35). It is hypothesized that the Lacc1 gene affects the degradation of S-unit lignin. The percentage of acetylated lignin Hα of β-O-4 and β-1 structures and Hγ and Hβ of β-O-4 structures in cotton straw medium inoculated with OE L1-4 after 30 days of incubation was higher than that of the wild type, whereas the percentage of Hα of β-β structures was lower than that of the wild type, indicating that Lacc1 gene is involved in the breaking of chemotactic bonds in β-β structures. Compared with the wild type, the cotton straw medium inoculated with OE L1-4 showed a significant increase in the proportion of H of aromatic acetates for acetylated lignin, whereas its proportion of H of aliphatic acetates showed a significant decrease. This indicates that the Lacc1 gene is involved in the production of phenolic hydroxyl substances and the reduction in alcoholic hydroxyl substances in lignin degradation.

3. Discussion

Studies have shown that the substrates cellulose: lignin ratios were found to be positively correlated to mycelial growth rates and to mushroom yield of P. ostreatus [30,31], and cotton straw is a substrate with high lignin content. In reports on cotton straw culture of edible mushrooms, it was found that higher yields could be obtained by applying to cotton straw culture of edible mushrooms relative to other crop substrates [32,33,34,35], in which lignin degrading enzymes played a crucial role [36,37,38]. In this study, we first screened the optimum culture conditions for laccase enzyme activity of P. ostreatus Suping 1. The final culture conditions for the highest lignin degradation efficiency of the P. ostreatus Suping 1 were determined by single-factor and orthogonal experiments: the size of cotton straw particle size in the medium was 0.75 mm, the medium had a solid–liquid ratio of 1:3, and contained 0.25 g/L of Tween, as well as the incubation temperature was 26 °C.
Two overexpression strains (OE L1-1 and OE L1-4) of Lacc1 gene were obtained by Agrobacterium tumefaciens-mediated method, and the gene expression increased 12.08 and 33.04-fold at day 30, respectively, and the enzyme activity of OE L1-4 strain increased 71.05% at day 30 compared to WT strain, whereas the enzyme activity of OE L1-1 strain was not significantly different from WT strain, showing the difference between gene expression level and gene product yields, probably due to the time required for gene translation into protein [39,40]. The lignin degradation rate of the medium was increased by 6.86% and 5.23% for OE L1-1 and OE L1-4 strains, respectively, and there was inequivalence between the lignin degradation ability and the increase in the fold to gene expression, probably due to the different mRNA translation efficiency of the two overexpression strains [41,42].
The lignin in cotton straw were characterized by wet chemistry (carbohydrate analysis) and spectroscopy methods (FT-IR, 13C and 1H-13C HSQC NMR spectroscopy) as well as gel permeation chromatography (GPC), which showed that the lignin in cotton straw belonged to typical G-S lignin, mainly composed of G-type units (59%) and distinct S-type units (40%), and the inter-unit linkages were mainly composed of β-O-4’ (75.6%) and β-β’ (12.2%) [43]. To investigate the details of lignin biodegradation, Dong et al. used FTIR with CP/MAS13C -NMR to study the characteristics and process of sugarcane bagasse degradation by three lignin degrading fungi, Phanerochaete chrysosporium PC2, Lentinula edode LE16 and P. ostreatus PO45, and found that all three strains preferentially degraded the S-unit of sugarcane bagasse lignin [44]. In contrast, Zhang et al. used FTIR and 2D HSQC NMR to determine the lignin composition of degraded sacrau poplar and found that the G-unit lignin was more susceptible to degradation by Trametes pubescens C7571 and T. versicolor C6915 than the S-unit lignin, and found that the cleavage of β-O-4 linkages and the degradation of β-5 and β-β linkages clearly occurred [27]. It is observed that the preferential degradation of S- or G-units in lignin, as well as the cleavage of linkages of different bond types, is related to the strain class. In this study, the G/S of acetylated lignin in cotton straw after 30 days of incubation with the wild-type strain was 1.94, and the G/S of acetylated lignin in cotton straw with OE L1-4 was 1.42. Compared with the wild-type control, the G/S of acetylated lignin in the overexpressed strain was reduced, indicating that the Lacc1 gene accelerates the degradation of lignin G-units. In addition, the G/S ratio of acetylated lignin in cotton straw medium inoculated with OE L1-4 strain was 1.42, which was lower than that of acetylated lignin in cotton straw medium inoculated with wild-type strain (1.94), but still higher than that of original acetylated lignin (1.20). It indicates that the Lacc1 gene only slowed down the degradation of S-unit and accelerated the degradation of G-unit, but the degradation of S-unit was still faster than that of G-unit, that is, overexpression of Lacc1 gene did not change the preferential degradation of S-unit in cotton straw lignin by P. ostreatus. Meanwhile, the Lacc1 gene was found to be involved in the cleavage of β-O-4-type linkages.
From the ratio of H proton of aromatic acetates content to H proton of aliphatic acetates content, the ratio of phenolic to alcoholic hydroxyl groups in lignin can be obtained [29]. The ratio of phenolic to alcoholic hydroxyl groups in the acetylated lignin of cotton straw after 30 days of incubation with wild-type strains was 0.23, and the ratio of phenolic to alcoholic hydroxyl groups in the acetylated lignin of cotton straw of OE L1-4 increased to 0.36. It was demonstrated that the degradation of lignin by the Lacc1 gene was mainly reflected in the demethylation of lignin units and thus promoting the depolymerization of the units, which is consistent with the inference that the degradation of lignin by Lacc1 may be mainly reflected in the demethylation of lignin units rather than the oxidative breaking of the chemical bonds between the lignin benzene ring structures [45].

4. Materials and Methods

4.1. Strains

The Pleurotus ostreatus Suping 1 strain was provided by Vegetable Research Institute, Jiangsu Academy of Agricultural Sciences and preserved in the Institute of Horticulture, Anhui Academy of Agricultural Sciences. The Escherichia coli DH5α and Agrobacterium tumefaciens EHA105 strain were preserved in the laboratory. The pCAMBIA1304-Pogpd-PoLac1 plasmids were constructed with the pCAMBIA1304 plasmids also kept in the same laboratory.

4.2. Single-Factor Optimization of Lignin Degradation in Cotton Straw by Pleurotus ostreatus

Straw particle size. Five grams of cotton straw with particle sizes of 5 mm, 0.75 mm, 0.425 mm and 0.25 mm were weighed into culture flasks, 22 mL of nutrient solution was added and autoclaved at 121 °C for 30 min. The nutrient solution was prepared by ammonium tartrate (22.0 g/L), macronutrients (20 g/L KH2PO4, 13.8 g/L MgSO4·7H2O, 1.0 g/L CaCl2, 0.6 g/L NaCl), trace elements (0.35 g/L MnSO4·H2O, 60 g/L FeSO4·7H2O, 110 mg/L CoCl2·6H2O, 60 mg/L ZnSO4·7H2O, 95 mg/L CuSO4·5H2O, 6 mg/L AlK(SO4)2·12H2O, 6 mg/L H3BO3, 6 mg/L Na2MoO4·2H2O), VB1 (100 mg/L) and water in the ratio of 1:15:15:3:16. Three P. ostreatus Suping 1 pieces of about 1 cm in diameter from PDA medium (boiled juice of 200 g/L potato, 20.0 g/L glucose, and 15.0 g/L agar added to solid medium) were inoculated into each culture flask and incubated at 25 °C for 20 days in the dark to determine the remaining medium lignin content.
Solid–liquid ratio. Five grams of cotton straw with particle sizes of 0.425 mm were weighed into culture flasks and 10 mL, 15 mL, 20 mL and 25 mL of nutrient solution were added to each treatment to make the solid–liquid ratio (w/v) 1:2, 1:3, 1:4 and 1:5, respectively, and autoclaved at 121 °C for 30 min. Different treatments were inoculated with P. ostreatus Suping 1 and the remaining medium lignin content was measured after 20 days of dark incubation at 25 °C.
Temperature. Five grams of cotton straw with a particle size of 0.425 mm were weighed into the culture flask, 22 mL of nutrient solution was added, sterilized and inoculated with P. ostreatus Suping 1. Then, the remaining lignin content of the medium was measured after 20 days of incubation under dark conditions at 20 °C, 25 °C and 27 °C, respectively.
Tween. Five grams of cotton straw with a particle size of 0.425 mm were weighed into the culture flask and 22 mL of nutrient solution containing different concentrations of Tween 80 was added, with final concentrations of Tween 80 are 0.1 g/L, 0.2 g/L, 0.3 g/L, 0.4 g/L and 0.5 g/L, respectively, and inoculated with P. ostreatus Suping 1 after sterilization. Then, after 20 days of culture at 25 °C in the dark, the remaining lignin content in the medium was measured.

4.3. Orthogonal Array Optimization of Lignin Degradation in Cotton Straw by P. ostreatus

The orthogonal experiment was performed with four factors of straw particle size (A), solid–liquid ratio (B), incubation temperature (C) and Tween content (D), and three levels of each factor were selected, as in Table 5, using orthogonal test L9 (34) with nine treatments, each treatment was inoculated with five bottles and replicated three times. After 20 days of incubation, five bottles of medium were mixed and tested for lignin content, and the lignin degradation rate of P. ostreatus Suping 1 was statistically calculated, and the effect of each treatment factor on the lignin degradation rate of P. ostreatus Suping 1 was analyzed by ANOVA and Duncan’s multiple comparisons using SPSS version 17.0 statistical analysis software.

4.4. Determination of Lignin Content

After culture of P. ostreatus Suping 1 strains, the solid residue substrates were dried in an oven at 60 °C to a constant weight. 100 mL of acid washing buffer (4 mol/L HCl) was used to digest 1 g of the dried substrate residue for 60 min. The samples were then washed with acetone and petroleum ether using a cold leaching device. Subsequently, the sample was washed with 12 mol/L sulfuric acid solution for 3 h. Then, the sample was washed to neutral and dried in a vacuum oven at 130 °C to a constant weight. The dried samples were ashed in a muffle furnace at 550 °C for 2 h. After cooling, the samples were weighed and the lignin content in the substrate residue was calculated [46].
Lignin   content   % = Weight   of   residue   after   drying   at   130   ° C g Weight   of   residue   after   ashing   at   550   ° C   g 1   g

4.5. Optimization of Laccase Production by Orthogonal Array Method

Orthogonal array design was adopted for four culture conditions using Minitab 16 software to evaluate the factors influencing the yield of laccase. Each independent variable was tested at three levels such as high, middle, and low level. The symbol code and actual level of the variables and the experimental design are shown in Table 2. Four factors such as straw particle size, solid–liquid ratio, temperature, and Tween contents were studied in 9 experiments to calculate the standard error. The triplicate verification test was performed to check the optimum condition and the average value was taken as the response.

4.6. Laccase Activity Assay

The samples were removed every 5 days and 15 mL of purified water was added in batches and extracted overnight at 4 °C. Thereafter, shaking extraction was performed at 200 r/min for 1 h, followed by freezing centrifugation at 12,000 r/min for 10 min. Finally, the supernatant was obtained as the crude enzyme solution. The laccase activity was calculated by examining the oxidation of 2,2-azobis-(3-ethylbenzothiazoline-6-sulfonic acid) (ABTS) at 420 nm. One unit of activity was defined as the amount of enzyme converting 1 μmol of substrate per minute [47].

4.7. Cloning and Expression Pattern Analysis of Lacc1 in P. ostreatus Suping 1

The genomic DNA and RNA of P. ostreatus Suping 1 were extracted using the EasyPure®Plant Genomic DNA Kit (Trans, Beijing) and RNAprep Pure Plant Kit (Tiangen, China), respectively. Subsequently, the CDS sequence of LACC1 (KDQ27217.1) from strain P. ostreatus PC15 (GCA_000697685.1) submitted to NCBI was used to design primers (Lac1-F and Lac1-R, Table 6) to amplify the Lacc1 gene sequence of P. ostreatus Suping 1 using the DNA and cDNA of P. ostreatus Suping 1 as templates, respectively. The amplified PCR products were purified, ligated to the pMD18-T vector (Takara, Dalian) and sequenced. The CDS sequence of Lacc1 gene of P. ostreatus Suping 1 was used to design qRT-PCR primers (Lac1-qF and Lac1-qR) to detect the expression pattern of Lacc1 gene in different growth stages of P. ostreatus Suping 1. RNA reverse transcription was performed using TransScript® One-Step RT-PCR SuperMix (Trans, China) and qRT-PCR was performed using the Bio-rad Cfx96 Touch™ Deep Well Real-Time PCR detection system. The PCR volume was 20 μL, and cyph (transcript ID: 1058252) was set as the reference gene [48]. Three parallel replicates were set for each sample. Finally, relative gene expression was calculated by the 2−ΔΔCt method. The reactions were contained in the following: 10 μL of TransStart Tip Green qRT-PCR SuperMix (2×) (Trans, China), 2 μL of template cDNA, 0.8 μL of forward and reverse primers and ddH2O to 20 μL. The PCR amplification conditions were performed as follows: 98 °C for 2 min, followed by 40 cycles of 98 °C for 10 s, 60 °C for 10 s and 68 °C for 30 s.

4.8. Agrobacterium Tumefaciens-Mediated Transformation of P. ostreatus

The glyceraldehyde-3-phosphate dehydrogenase (gpd) promoter was cloned from P. ostreatus [49]. Then, it was inserted into the expression plasmids pCAMBIA1304 to replace its CAMV35S promoter by using the restriction sites of Hind III and Nco I. Subsequently, Lacc1 were cloned from P. ostreatus Suping 1 using specific primers (Lac1-eukF and Lac1-eukR, Table 5), respectively. The PCR products were digested with Bgl II and Spe I (Takara), then inserted into the pCAMBIA1304-Pogpd vector. Final vector plasmids were designated as pCAMBIA1304-Pogpd-PoLac1.
The A. tumefaciens strains EHA105, harboring pCAMBIA1304-Pogpd-PoLac1, were cultivated at 28 °C in LB medium (containing antibiotics kanamycin and rifampicin) to an OD600 of 0.6–0.8. Bacterial cells were then collected, centrifugated, and suspended in an induction medium (IM, boiled juice of 200 g L−1 potato, 20.0 g L−1 glucose, and including 200 μmol/L acetosyringone) to an OD600 of 0.5–0.6, pH 5.5, and the virulence of A. tumefaciens was induced by shaking at 150 rpm for 6 h at 28 °C.
The mycelia masses (0.9 × 0.9 cm) of P. ostreatus were grown on PDA for 7 days was immersed in pre-inducing bacterial culture for 30 min and then placed on solid induction medium for 4 days. Subsequently, the co-cultured mycelia were transferred to PDA with 100 μg/mL hygromycin and 300 μg/mL cefotaxime. The stability of the transformation was confirmed by subculturing colonies onto selective medium three times, then cultured on PDA for three generates to rejuvenate mycelia [50].

4.9. PCR Analysis and Visual Detection of β-Glucuronidase (GUS)

The genomic DNA of the putative transformants was extracted using the EasyPure®Plant Genomic DNA Kit (Trans, China). To confirm that the gene had been integrated into the genome, primers GUS-F and GUS-R (Table 1) for the GUS gene were used to verify whether the T-DNA was inserted by PCR (conditions: 94 °C for 3 min, followed by 35 cycles of amplification, 94 °C for 30 s, 59 °C for 30 s, 72 °C for 100 s, and ending after 10 min at 72 °C). To verify the expression of the introduced GUS reporter gene, the presumptive transformants were detected with the GUS Histochemical Assay Kit (MKbio, Shanghai).

4.10. Fourier Transform Infrared Spectroscopy (FTIR) Analysis

After cultivating for 30 days with the wild type and transformants, cotton stalks were removed and dried at 40 °C. According to the previous methods [51], milled wood lignin was extracted and purified. FTIR analysis was performed to determine the functional groups converted during the degradation of lignin by Lacc1-encoded laccase. Local microscopic FTIR with a KBr wafer was used, for which the milled wood lignin samples are homogeneous and representative. The micro-FTIR spectra of local areas of the wafer specimen were measured using a NICOLET iN10 MX spectrometer (Thermos Nicolet Corporation, Madison, WI, USA); connected to a Nicolet NicPlan IR microscope and an MCT detector. The spectral range was taken from 4000 to 650 cm−1 at a resolution of 4 cm−1.

4.11. 1H-NMR

Lignin was extracted from the uncultured substrates and the substrates that were cultured with P. ostreatus after 30 days. A total of 20 mg of milled wood lignin samples was weighed and dissolved in 2 mL of pyridine: acetic anhydride (1:1) mixture. Nitrogen was charged into the reaction bulb, which was placed in the dark at room temperature for 72 h. After the reaction was completed, the reactant was dripped into diethyl ether until precipitate was formed, after which the solution was centrifuged to separate the precipitate. The precipitate was then washed with diethyl ether six to eight times to remove the pyridine odor from the precipitate. Finally, the completely acetylated lignin was obtained. The acetyl-treated lignin samples were dissolved in 0.5 mL of DMSO, with tetramethylsilane as the internal standard. Finally, the 1H-NMR assay was conducted with a Bruker-400 superconducting NMR spectrometer (Bruker, Fällanden, Switzerland) at a frequency of 400 MHz [44].

Author Contributions

Conceptualized the idea for the study and performed most of experimental operations, G.L.; performed some of experimental operations and data analysis and led the writing of the manuscript, Y.W.; critically reviewed the data analysis, and contributed substantially to the writing, G.L. and H.Z.; made key suggestions for improving the paper, P.Z., G.Z. and C.L. All authors have participated in the preparation of this study. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by the Key Research and Development Projects of Anhui Province (201904F06020025) and the Doctoral Matching Funds Project for Agricultural Research (340000211264005000407).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

  1. Madhavi, V.; Lele, S.S. Laccase: Properties and applications. Bioresources 2009, 4, 1694–1717. [Google Scholar]
  2. Mayolo-Deloisa, K.; Gonzalez-Gonzalez, M.; Rito-Palomares, M. Laccases in food industry: Bioprocessing, potential industrial and biotechnological applications. Front. Bioeng. Biotechnol. 2020, 8, 222. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Brugnari, T.; Braga, D.M.; dos Santos, C.S.A.; Torres, B.H.C.; Modkovski, T.A.; Haminiuk, C.W.I.; Maciel, G.M. Laccases as green and versatile biocatalysts: From lab to enzyme market-an overview. Bioresour. Bioprocess. 2021, 8, 131. [Google Scholar] [CrossRef]
  4. Arregui, L.; Ayala, M.; Gomez-Gil, X.; Gutierrez-Soto, G.; Eduardo Hernandez-Luna, C.; Herrera de los Santos, M.; Levin, L.; Rojo-Dominguez, A.; Romero-Martinez, D.; Saparrat, M.C.N.; et al. Laccases: Structure, function, and potential application in water bioremediation. Microb. Cell Fact. 2019, 18, 1–33. [Google Scholar] [CrossRef] [Green Version]
  5. Pandiyan, K.; Singh, A.; Singh, S.; Saxena, A.K.; Nain, L. Technological interventions for utilization of crop residues and weedy biomass for second generation bio-ethanol production. Renew. Energ. 2019, 132, 723–741. [Google Scholar] [CrossRef]
  6. Mayr, S.A.; Subagia, R.; Weiss, R.; Schwaiger, N.; Weber, H.K.; Leitner, J.; Ribitsch, D.; Nyanhongo, G.S.; Guebitz, G.M. Oxidation of various kraft lignins with a bacterial laccase enzyme. Int. J. Mol. Sci. 2021, 22, 13161. [Google Scholar] [CrossRef]
  7. Yang, L.-H.; Qiao, B.; Xu, Q.-M.; Liu, S.; Yuan, Y.; Cheng, J.-S. Biodegradation of sulfonamide antibiotics through the heterologous expression of laccases from bacteria and investigation of their potential degradation pathways. J. Hazard. Mater. 2021, 416, 125815. [Google Scholar] [CrossRef]
  8. Zheng, X.-T.; Dong, Y.-Q.; Liu, X.-D.; Xu, Y.-L.; Jian, R.-K. Fully bio-based flame-retardant cotton fabrics via layer-by-layer self assembly of laccase and phytic acid. J. Clean. Prod. 2022, 350, 131525. [Google Scholar] [CrossRef]
  9. Gutierrez, A.; del Rio, J.C.; Martinez, A.T. Microbial and enzymatic control of pitch in the pulp and paper industry. Appl. Microbiol. Biotechnol. 2009, 82, 1005–1018. [Google Scholar] [CrossRef] [Green Version]
  10. Moreno, A.D.; Ibarra, D.; Alvira, P.; Tomas-Pejo, E.; Ballesteros, M. A review of biological delignification and detoxification methods for lignocellulosic bioethanol production. Crit. Rev. Biotechnol. 2015, 35, 342–354. [Google Scholar] [CrossRef]
  11. Suryadi, H.; Judono, J.J.; Putri, M.R.; Eclessia, A.D.; Ulhaq, J.M.; Agustina, D.N.; Sumiati, T. Biodelignification of lignocellulose using ligninolytic enzymes from white-rot fungi. Heliyon 2022, 8, e08865. [Google Scholar] [CrossRef] [PubMed]
  12. Wesenberg, D.; Kyriakides, I.; Agathos, S.N. White-rot fungi and their enzymes for the treatment of industrial dye effluents. Biotechnol. Adv. 2003, 22, 161–187. [Google Scholar] [CrossRef] [PubMed]
  13. Zhao, J.; Kwan, H.S. Characterization, molecular cloning, and differential expression analysis of laccase genes from the edible mushroom Lentinula edodes. Appl. Environ. Microbiol. 1999, 65, 4908–4913. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  14. Liu, X.; Zain ul Arifeen, M.; Xue, Y.; Liu, C. Genome-wide characterization of laccase gene family in Schizophyllum commune 20R-7-F01, isolated from deep sediment 2 km below the seafloor. Front. Microbiol. 2022, 13, 923451. [Google Scholar] [CrossRef]
  15. Liu, N.; Cao, Z.; Cao, K.; Ma, S.; Gong, X.; Jia, H.; Dai, D.; Dong, J. Identification of laccase-like multicopper oxidases from the pathogenic fungus Setosphaeria turcica and their expression pattern during growth and infection. Eur. J. Plant Pathol. 2019, 153, 1149–1163. [Google Scholar] [CrossRef]
  16. Sun, S.J.; Liu, J.Z.; Hu, K.H.; Zhu, H.X. The level of secreted laccase activity in the edible fungi and their growing cycles are closely related. Curr. Microbiol. 2011, 62, 871–875. [Google Scholar] [CrossRef]
  17. Jiao, X.; Li, G.; Wang, Y.; Nie, F.; Cheng, X.; Abdullah, M.; Lin, Y.; Cai, Y. Systematic analysis of the Pleurotus ostreatus laccase gene (PoLac) family and functional characterization of PoLac2 involved in the degradation of cotton-straw lignin. Molecules 2018, 23, 880. [Google Scholar] [CrossRef] [Green Version]
  18. Lu, Y.; Wu, G.; Lian, L.; Guo, L.; Wang, W.; Yang, Z.; Miao, J.; Chen, B.; Xie, B. Cloning and expression analysis of Vvlcc3, a novel and functional laccase gene possibly involved in stipe elongation. Int. J. Mol. Sci. 2015, 16, 28498–28509. [Google Scholar] [CrossRef] [Green Version]
  19. Wang, W.; Liu, F.; Jiang, Y.; Wu, G.; Guo, L.; Chen, R.; Chen, B.; Lu, Y.; Dai, Y.; Xie, B. The multigene family of fungal laccases and their expression in the white rot basidiomycete Flammulina velutipes. Gene 2015, 563, 142–149. [Google Scholar] [CrossRef]
  20. Ryu, S.-H.; Cho, M.-K.; Kim, M.; Jung, S.-M.; Seo, J.-H. Enhanced lignin biodegradation by a laccase-overexpressed white-rot fungus Polyporus brumalis in the pretreatment of wood chips. Appl. Biochem. Biotechnol. 2013, 171, 1525–1534. [Google Scholar] [CrossRef]
  21. Arimoto, M.; Yamagishi, K.; Wang, J.; Tanaka, K.; Miyoshi, T.; Kamei, I.; Kondo, R.; Mori, T.; Kawagishi, H.; Hirai, H. Molecular breeding of lignin-degrading brown-rot fungus Gloeophyllum trabeum by homologous expression of laccase gene. AMB Express 2015, 5, 81. [Google Scholar] [CrossRef] [PubMed]
  22. Brown, M.E.; Chang, M.C.Y. Exploring bacterial lignin degradation. Curr. Opin. Chem. Biol. 2014, 19, 1–7. [Google Scholar] [CrossRef] [PubMed]
  23. Makela, M.R.; Marinovic, M.; Nousiainen, P.; Liwanag, A.J.M.; Benoit, I.; Sipila, J.; Hatakka, A.; de Vries, R.P.; Hilden, K.S. Aromatic metabolism of filamentous fungi in relation to the presence of aromatic compounds in plant biomass. Adv. Appl. Microbiol. 2015, 91, 63–137. [Google Scholar] [PubMed]
  24. Li, Y.; Zhang, Q. Effects of naturally and microbially decomposed cotton stalks on cotton seedling growth. Arch. Agron. Soil Sci. 2016, 62, 1264–1270. [Google Scholar] [CrossRef]
  25. Wang, Q.; Tuohedi, N. Polyurethane foams and bio-polyols from liquefied cotton stalk agricultural waste. Sustainability 2020, 12, 4214. [Google Scholar] [CrossRef]
  26. Salame, T.M.; Knop, D.; Levinson, D.; Mabjeesh, S.J.; Yarden, O.; Hadar, Y. Inactivation of a Pleurotus ostreatus versatile peroxidase-encoding gene (mnp2) results in reduced lignin degradation. Environ. Microbiol. 2014, 16, 265–277. [Google Scholar] [CrossRef]
  27. Lu, W.; Yan, W.C.; Chen, J.C.; Feng, H.; Gao, P.J. Function of the iron-binding chelator produced by Coriolus versicolor in lignin biodegradation. Sci. China Ser. C Life Sci. 2008, 51, 214–221. [Google Scholar]
  28. Philippoussis, A.; Zervakis, G.; Diamantopoulou, P. Bioconversion of agricultural lignocellulosic wastes through the cultivation of the edible mushrooms Agrocybe aegerita, Volvariella volvacea and Pleurotus spp. World J. Microbiol. Biotechnol. 2001, 17, 191–200. [Google Scholar] [CrossRef]
  29. Koutrotsios, G.; Mountzouris, K.C.; Chatzipavlidis, I.; Zervakis, G.I. Bioconversion of lignocellulosic residues by Agrocybe cylindracea and Pleurotus ostreatus mushroom fungi—Assessment of their effect on the final product and spent substrate properties. Food Chem 2014, 161, 127–135. [Google Scholar] [CrossRef]
  30. Khan, S.M.; Nawaz, A.; Ali, M.A.; Ahmad, T.; Khan, N.A.; Atiq Ur, R. Response of oyster mushroom on different agricultural wastes of southern punjab. Pak. J. Agric. Sci. 2012, 49, 127–130. [Google Scholar]
  31. Wang, J.T.; Wang, Q.; Han, J.R. Yield, polysaccharides content and antioxidant properties of the mushroom Agaricus subrufescens produced on different substrates based on selected agricultural wastes. Sci. Hortic. 2013, 157, 84–89. [Google Scholar] [CrossRef]
  32. Sardar, H.; Ali, M.A.; Anjum, M.A.; Nawaz, F.; Hussain, S.; Naz, S.; Karimi, S.M. Agro-industrial residues influence mineral elements accumulation and nutritional composition of king oyster mushroom (Pleurotus eryngii). Sci. Hortic. 2017, 225, 327–334. [Google Scholar]
  33. Song, T.; Shen, Y.; Jin, Q.; Feng, W.; Fan, L.; Cao, G.; Cai, W. Bacterial community diversity, lignocellulose components, and histological changes in composting using agricultural straws for Agaricus bisporus production. PeerJ 2021, 9, e10452. [Google Scholar] [CrossRef]
  34. Nakamura, Y.; Sungusia, M.G.; Sawada, T.; Kuwahara, M. Lignin-degrading enzyme production by Bjerkandera adusta immobilized on polyurethane foam. J. Biosci. Bioeng. 1999, 88, 41–47. [Google Scholar] [CrossRef]
  35. Rao, R.G.; Ravichandran, A.; Kandalam, G.; Kumar, S.A.; Swaraj, S.; Sridhar, M. Screening of wild basidiomycetes and evaluation of the biodegradation potential of dyes and lignin by manganese peroxidases. Bioresources 2019, 14, 6558–6576. [Google Scholar]
  36. Shabaev, A.V.; Moiseenko, K.V.; Glazunova, O.A.; Savinova, O.S.; Fedorova, T.V. Comparative analysis of Peniophora lycii and Trametes hirsuta exoproteomes demonstrates "shades of gray" in the concept of white-rotting fungi. Int. J. Mol. Sci. 2022, 23, 10322. [Google Scholar] [CrossRef] [PubMed]
  37. He, M.; He, Y.; Luo, Q.; Wang, M. From DNA to protein: No living cells required. Process Biochem. 2011, 46, 615–620. [Google Scholar] [CrossRef]
  38. Corradi, E.; Baudet, M.-L. In the right place at the right time: miRNAs as key regulators in developing axons. Int. J. Mol. Sci. 2020, 21, 8726. [Google Scholar] [CrossRef]
  39. Roy, B.; Jacobson, A. The intimate relationships of mRNA decay and translation. Trends Genet. 2013, 29, 691–699. [Google Scholar]
  40. Hanson, G.; Coller, J. Codon optimality, bias and usage in translation and mRNA decay. Nat. Rev. Mol. Cell Biol. 2018, 19, 20–30. [Google Scholar] [CrossRef]
  41. Kang, S.; Xiao, L.; Meng, L.; Zhang, X.; Sun, R. Isolation and structural characterization of lignin from cotton stalk treated in an ammonia hydrothermal system. Int. J. Mol. Sci. 2012, 13, 15209–15226. [Google Scholar] [CrossRef]
  42. Dong, X.Q.; Yang, J.S.; Zhu, N.; Wang, E.T.; Yuan, H.L. Sugarcane bagasse degradation and characterization of three white-rot fungi. Bioresour. Technol. 2013, 131, 443–451. [Google Scholar] [CrossRef] [PubMed]
  43. Zhang, L.; You, T.; Zhou, T.; Zhang, L.; Xu, F. Determining lignin degradation in white-rot fungi-treated sacrau poplar: Lignin structural changes and degradation compound analysis. Bioresources 2016, 11, 3972–3986. [Google Scholar] [CrossRef] [Green Version]
  44. Yan, B.; Stark, R.E. Biosynthesis, molecular structure, and domain architecture of potato suberin: A (13)C NMR study using isotopically labeled precursors. J. Agric. Food Chem. 2000, 48, 3298–3304. [Google Scholar] [CrossRef] [PubMed]
  45. Xue, D.; Na, R.; Guo, J.F.; Liu, T. Study on the construction of recombined plasmid pMG36e-lacc1 and the electroporation of Lactobacillus buchneri. Bio-Med. Mate.r Eng. 2014, 24, 3855–3861. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  46. Van Soest, P.J.; Robertson, J.B.; Lewis, B.A. Methods for dietary fiber, neutral detergent fiber, and nonstarch polysaccharides in relation to animal nutrition. Bio-Med. Mater. Eng. 1991, 74, 3583–3597. [Google Scholar] [CrossRef]
  47. Ya, Y.; Sakamoto, T.; Honda, Y.; Kagotani, Y.; Izumitsu, K.; Suzuki, K.; Irie, T. The white-rot fungus Pleurotus ostreatus transformant overproduced intracellular cAMP and laccase. Biosci. Biotechnol. Biochem. 2013, 77, 2309–2311. [Google Scholar] [CrossRef] [Green Version]
  48. Castanera, R.; Perez, G.; Omarini, A.; Alfaro, M.; Pisabarro, A.G.; Faraco, V.; Amore, A.; Ramirez, L. Transcriptional and enzymatic profiling of Pleurotus ostreatus laccase genes in submerged and solid-state fermentation cultures. Appl. Environ. Microbiol. 2012, 78, 4037–4045. [Google Scholar] [CrossRef] [Green Version]
  49. Yin, C.; Zheng, L.; Zhu, J.; Chen, L.; Ma, A. Characterization of the highly active fragment of glyceraldehyde-3-phosphate dehydrogenase gene promoter for recombinant protein expression in Pleurotus ostreatus. FEMS Microbiol. Lett. 2015, 362, fnv010. [Google Scholar] [CrossRef] [Green Version]
  50. Ding, Y.; Liang, S.; Lei, J.; Chen, L.; Kothe, E.; Ma, A. Agrobacterium tumefaciens mediated fused egfp-hph gene expression under the control of gpd promoter in Pleurotus ostreatus. Microbiol. Res. 2011, 166, 314–322. [Google Scholar] [CrossRef]
  51. Yan, C.; Yin, M.; Zhang, N.; Jin, Q.; Fang, Z.; Lin, Y.; Cai, Y. Stone cell distribution and lignin structure in various pear varieties. Sci. Hortic. 2014, 174, 142–150. [Google Scholar] [CrossRef]
Figure 1. Single-factor test for screening the optimal conditions for lignin degradation in cotton straw by P. ostreatus Suping 1 with different (a) straw particle size, (b) solid–liquid ratio, (c) temperature and (d) concentration of Tween 80. a,b,c,d indicate significant differences among treatments (p ≤ 0.05).
Figure 1. Single-factor test for screening the optimal conditions for lignin degradation in cotton straw by P. ostreatus Suping 1 with different (a) straw particle size, (b) solid–liquid ratio, (c) temperature and (d) concentration of Tween 80. a,b,c,d indicate significant differences among treatments (p ≤ 0.05).
Ijms 23 13545 g001
Figure 2. The characterization and expression pattern in P. ostreatus Suping 1 of laccase-encoding gene (Lacc1). (a) CDS sequence alignment of Lacc1 between P. ostreatus PC15 and P. ostreatus Suping 1; (b) gene structure of Lacc1 in P. ostreatus Suping 1; (c) the Pfam domain matches and features of Lacc1 in P. ostreatus Suping 1; (d) the expression pattern of Lacc1 gene in different growth stages of P. ostreatus Suping 1. Different letters above the chart columns indicate significant differences among treatments (p ≤ 0.05).
Figure 2. The characterization and expression pattern in P. ostreatus Suping 1 of laccase-encoding gene (Lacc1). (a) CDS sequence alignment of Lacc1 between P. ostreatus PC15 and P. ostreatus Suping 1; (b) gene structure of Lacc1 in P. ostreatus Suping 1; (c) the Pfam domain matches and features of Lacc1 in P. ostreatus Suping 1; (d) the expression pattern of Lacc1 gene in different growth stages of P. ostreatus Suping 1. Different letters above the chart columns indicate significant differences among treatments (p ≤ 0.05).
Ijms 23 13545 g002aIjms 23 13545 g002b
Figure 3. Overexpression of Lacc1 gene in P. ostreatus Suping 1. (a) GUS analysis of Lacc1 gene overexpression transformants; (b) gene-relative transcript abundance of wild type (WT) and transformants (OE L1-n) after cultivating in the cotton straw medium for 30 days. Different letters above the chart columns indicate significant differences among treatments (p ≤ 0.05).
Figure 3. Overexpression of Lacc1 gene in P. ostreatus Suping 1. (a) GUS analysis of Lacc1 gene overexpression transformants; (b) gene-relative transcript abundance of wild type (WT) and transformants (OE L1-n) after cultivating in the cotton straw medium for 30 days. Different letters above the chart columns indicate significant differences among treatments (p ≤ 0.05).
Ijms 23 13545 g003
Figure 4. Laccase activity and lignin degradation rates of overexpressed transformants. (a) Evolution of the laccase activity of wild-type (WT) and Lacc1 gene overexpressed transformants (OE L1-1 and OE L1-4) of P. ostreatus Suping 1 in cotton straw medium; (b) lignin degradation rates of wild type and transformants after cultivating in the cotton straw medium for 30 days. Different letters above the chart columns indicate significant differences among treatments (p ≤ 0.05).
Figure 4. Laccase activity and lignin degradation rates of overexpressed transformants. (a) Evolution of the laccase activity of wild-type (WT) and Lacc1 gene overexpressed transformants (OE L1-1 and OE L1-4) of P. ostreatus Suping 1 in cotton straw medium; (b) lignin degradation rates of wild type and transformants after cultivating in the cotton straw medium for 30 days. Different letters above the chart columns indicate significant differences among treatments (p ≤ 0.05).
Ijms 23 13545 g004
Figure 5. Infrared spectroscopy and 1H NMR analysis of lignin degradation products from cotton straw medium inoculated with wild-type (WT) and Lacc1 gene overexpressed transformants (OE L1-4) of P. ostreatus Suping 1 for 30 days. (a) Infrared spectroscopy analysis of cotton straw medium –inoculated with wild-type strain; (b) Infrared spectroscopy analysis of cotton straw medium inoculated with OE L1-4 strain; (c) 1H NMR analysis of cotton straw medium inoculated with wild-type strain; (d) 1H NMR analysis of cotton straw medium inoculated with OE L1-4 strain.
Figure 5. Infrared spectroscopy and 1H NMR analysis of lignin degradation products from cotton straw medium inoculated with wild-type (WT) and Lacc1 gene overexpressed transformants (OE L1-4) of P. ostreatus Suping 1 for 30 days. (a) Infrared spectroscopy analysis of cotton straw medium –inoculated with wild-type strain; (b) Infrared spectroscopy analysis of cotton straw medium inoculated with OE L1-4 strain; (c) 1H NMR analysis of cotton straw medium inoculated with wild-type strain; (d) 1H NMR analysis of cotton straw medium inoculated with OE L1-4 strain.
Ijms 23 13545 g005
Table 1. Experimental matrix and response values from randomized runs in orthogonal array.
Table 1. Experimental matrix and response values from randomized runs in orthogonal array.
RunCode Variable LevelReal Variable LevelLaccase Activity (U/mL) *
ABCDStraw Particle Size (mm)Solid–Liquid Ratio (w/v)Temperature (°C)Tween (g/L)
1332311:4270.2597.8 ± 2.2 c
221220.751:2270.212.3 ± 0.9 e
313120.51:4260.250 ± 0 cd
4311111:2260.1531.6 ± 2.2 e
522130.751:3260.25125.6 ± 8.4 a
6323211:3280.280.4 ± 1.5 cd
711330.51:2280.2511.1 ± 1.9 e
812210.51:3270.1557.9 ± 1.1 d
923310.751:4280.15115.3 ± 1.0 b
* Different letters in the table indicate significant differences among treatments (p ≤ 0.05).
Table 2. Analysis of different factors and levels on the degradation of cotton straw lignin by P. ostreatus.
Table 2. Analysis of different factors and levels on the degradation of cotton straw lignin by P. ostreatus.
FactorsLevelRSignificance
K1K2K3
A: Straw particle size (mm)5.57 ± 0.189.43 ± 0.787.34 ± 0.173.86 ± 0.912
B: Solid–liquid ratio (w/v)2.86 ± 0.139.84 ± 0.989.64 ± 0.097.23 ± 0.871
C: Temperature (°C)8.83 ± 0.976.10 ± 0.127.42 ± 0.12.74 ± 1.23
D: Tween (g/L)7.37 ± 0.16.18 ± 0.298.82 ± 0.992.64 ± 1.264
Table 3. Infrared spectrum analysis of cotton straw lignin after degradation.
Table 3. Infrared spectrum analysis of cotton straw lignin after degradation.
Infrared Spectrum Analysis [27]Relative Intensities of Absorption Peaks Ai/A1508
Peak/cm−1Functional group stretchingWTOE L1-4
3435O-H stretching in hydroxyl groups1.661.55
2924C-H stretching in methyl and methyene groups0.950.76
1720C=O stretching in unconjugated ketone0.970.97
1635C=O stretching in conjugated aryl ketene of carbonyl groups1.141.12
1595Aromatic skeletal vibrations plus C=O stretching1.101.11
1506Aromatic skeletal vibrations0.990.99
1460C-H deformation in methyl1.021.02
1419aromatic skeletal combined with C-H in plane stretching1.021.00
1330Condensation of guaiacyl unit and syringyl unit, syringyl unit and CH2 bending stretching0.960.94
1267G ring plus C=O stretching1.101.15
1218Aromatic C-O stretching (S units)1.051.09
1128Aromatic C-H in plane deformations1.141.18
1033Aromatic C-H in-plane deformation plus C-O deform. In primary alcohols plus C=O stretching1.030.99
Table 4. 1H-NMR analysis of acetylated lignin from cotton straw medium after degradation.
Table 4. 1H-NMR analysis of acetylated lignin from cotton straw medium after degradation.
Chemicalshift Region (δ)Type of Protons [29]Percentage of Protons (%)
WTOE L1-4
7.1–6.8Aromatic protons in guaiacyl units0.680.64
6.8–6.3Aromatic protons in syringyl units0.350.45
6.2–5.8Hα of β-O-4 and β-1 structures0.260.31
5.2–4.9Hydrocarbon protons0.080.17
4.9–4.4Hγ and Hβ of β-O-4 structures0.811.11
4.4–4.1Hα of β-β structures0.800.71
4.1–2.8H of methoxyl groups4.834.92
2.7–2.2H of aromatic acetates1.121.52
2.2–1.7H of aliphatic acetates4.824.16
1.7–1.5Hydrocarbon protons0.550.37
Table 5. Factors and levels of orthogonal test.
Table 5. Factors and levels of orthogonal test.
LevelStraw Particle Size (mm)Solid–Liquid Ratio (w/v)Temperature (°C)Tween Content (g/L)
10.501:2260.15
20.751:3270.20
31.001:4280.25
Table 6. Primer sequence used in this study.
Table 6. Primer sequence used in this study.
Primer NamePrimer Sequence (5′-3′)
Lac1-FATGCGCACATTCTCCCGCTTTCTC
Lac1-RCTAGGTTGGGAGCAAACCGCCTTTTTCC
Lac1-qFCGGTACATCTTAGCACCCAATG
Lac1-qRGGACAGGGCTCGCTGGTT
cyph-FGACATTGCTATCGACTCCCAG
cyph-RGAAATTCCTTGCAGTCTTGGG
Pogpd-4FCGGAATTCTCTGGAATCGTTATCTCGGT
Pogpd-1RCGGGATCCCGTGGACAGGCTTTTGGGAATA
Lac1-eukFGAAGATCTGATGCGCACATTCTCCCGCTTTCTC
Lac1-eukRGGACTAGTGGTTGGGAGCAAACCGCCTTTTTC
GUS-FGTCCTGTAGAAACCCCAACCCGTGA
GUS-RTTTGCCTCCCTGCTGCGGTTTTTCA
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Li, G.; Wang, Y.; Zhu, P.; Zhao, G.; Liu, C.; Zhao, H. Functional Characterization of Laccase Isozyme (PoLcc1) from the Edible Mushroom Pleurotus ostreatus Involved in Lignin Degradation in Cotton Straw. Int. J. Mol. Sci. 2022, 23, 13545. https://doi.org/10.3390/ijms232113545

AMA Style

Li G, Wang Y, Zhu P, Zhao G, Liu C, Zhao H. Functional Characterization of Laccase Isozyme (PoLcc1) from the Edible Mushroom Pleurotus ostreatus Involved in Lignin Degradation in Cotton Straw. International Journal of Molecular Sciences. 2022; 23(21):13545. https://doi.org/10.3390/ijms232113545

Chicago/Turabian Style

Li, Guoqing, Yahui Wang, Peilei Zhu, Guiyun Zhao, Caiyu Liu, and Hongyuan Zhao. 2022. "Functional Characterization of Laccase Isozyme (PoLcc1) from the Edible Mushroom Pleurotus ostreatus Involved in Lignin Degradation in Cotton Straw" International Journal of Molecular Sciences 23, no. 21: 13545. https://doi.org/10.3390/ijms232113545

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop