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Decolourization of malachite green dye by endolichenic fungi from the lichen Usnea sp.: A novel study on their dye removal potential
⁎Corresponding author. adeline.ting@monash.edu (Adeline Su Yien Ting) adelsuyien@yahoo.com (Adeline Su Yien Ting)
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Received: ,
Accepted: ,
This article was originally published by Elsevier and was migrated to Scientific Scholar after the change of Publisher.
Peer review under responsibility of King Saud University.
Abstract
Abstract
Objective
This novel study explored the potential of two endolichenic fungi, Pseudopestalotiopsis theae (PT, accession number MG881833) and Astrocystis bambusae (AB, accession number MH370741) in decolorizing Malachite Green (MG).
Methods
Their efficacy in dye decolorization was compared to non-endolichenic fungus Trichoderma asperellum (TA, accession number KP792512). Decolorization test was performed using MG (100 ppm) for 14 days (absorbance at 617 nm) to determine decolorization efficiency (DE, %). The pellet was collected for FTIR analysis (4000 to 700 cm−1, 50-scan speed) while the supernatant was analysed with UV-spectral analysis (300–800 nm) to detect for biodegradation.
Results
P. theae demonstrated the highest decolorization efficiency (DE%) at 89.22%, followed by T. asperellum (76.19%) and A. bambusae (67.69%). Common functional groups (i.e., —OH, —COOH, —NH, —CH, C⚌O, ⚌C—H) were detected in all isolates and their roles in biosorption were evident by the shifts in peaks and peak intensity. Biodegradation of MG was concluded based on UV-spectra peaks at 617 nm, which were significantly reduced (or absent).
Conclusion
This study is the first to reveal that endolichenic fungi P. theae and A. bambusae are capable of decolorizing the toxic dye malachite green.
Keywords
Decolorization
Endolichenic fungi
FTIR
Malachite green
- AB
-
Astrocystis bambusae
- ANOVA
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One-way Analysis of Variance
- DE
-
decolorization efficiency
- ELF
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Endolichenic fungi
- FTIR
-
Fourier transformed infra-red
- MG
-
malachite green
- PDA
-
potato dextrose agar
- PDB
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potato dextrose broth
- PT
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Pseudopestalotiopsis theae
- SPSS
-
Statistical Package for the Social Science
- TA
-
Trichoderma asperellum
- UV–vis
-
ultraviolet visible
Abbreviations
1 Introduction
Endolichenic fungi (ELF) are found in lichens and are ubiquitous in the environment. They have been recovered from lichen species across a vast geographical region; from the Arctic and Antarctic regions to the tropics (Arnold et al., 2009; Kannangara et al., 2009; U’ren et al., 2010; Suryanarayanan et al., 2017). Existing reports suggested ELF predominantly comprise of species of Ascomycota (Pezizomycotina) (U’ren et al., 2010; Kellogg and Raja, 2017), Basidiomycota and Zygomycota (Tripathi and Joshi, 2015). Examples of common ELF include Aspergillus versicolor (Li et al., 2015), Penicillium sp. and Chrysosporium sp. (Kannangara et al., 2009).
The ELF are similar to the endophytic fungi based on species identified, transmission mode, phylogenetic relationship and evolutionary history (Arnold et al., 2009; Hawas et al., 2012; Waqas et al., 2014). The two ELF in this study, Pseudopestalotiopsis theae (PT) and Astrocystis bambusae (AB), are known endophytes (Peláez et al., 2008; Maharachchikumbura et al., 2014; Dai et al., 2017) but their nature as ELF is novel. In addition, ELF has not been explored for bioremediation, although they are valued for their metabolites (e.g. xanthones, alkaloids, quinones, anthraquinones, pyrones, furanones, steroids and benzopyranoids) (Wang et al., 2012; Dou et al., 2014; Zheng et al., 2014; Santiago and Ting, 2019).
This study therefore, aims to establish the potential of ELF in removing toxic dyes, particularly triphenylmethane (TPM) dyes. TPM dyes are cationic, N-methylated diaminotriphenylmethane dyes, used extensively for various industries (printing, textile, food, paper), and include the malachite green dye (MG) (Chen et al. 2019). MG is toxic and carcinogenic and although biological removal of MG has been attempted using non-endolichenic fungi (Chen and Ting, 2015a; 2015b), exploration using ELF remains novel. The potential use of ELF for bioremediation is associated with their lichen hosts. Kulkarni et al. (2014) used the lichen Permelia perlata to decolorize (80.4% decolorization efficiency, DE) Solvent Red 24. In another study, the lichen Dermatocarpon vellereceum decolorized Navy Blue HE22 (87.4% DE) (Kulkarni et al., 2018). Dye degradation by these lichens was attributed to the enzymes laccase, manganese peroxidase and lignin peroxidase. However, as lichens are extremely slow-growing, ELF are sought as alternatives to decolorize dyes, especially with reports that ELF are capable of secreting similar enzymes as their lichen hosts (Kannangara et al., 2009; Beckett et al., 2013).
This study embarks on discovering the dye degradation potential of two ELF species (Pseudopestalotiopsis theae and Astrocystis bambusae), and their potential for removal of MG dye. ELF are explored as their lichen host have shown good potential for dye remediation. Furthermore, ELF are similar to endophytes, and may have similar dye degrading potential as endophytes. Therefore, in this study, the efficacy of the ELF is compared against a non-endolichenic fungus, Trichoderma asperellum, which is an endophyte. This will be one of the first attempts in realizing the dye degradation activities of ELF.
2 Materials and methods
2.1 Culture establishment and generation of fungal biomass
The ELF Pseudopestalotiopsis theae (PT, accession number MG881833) and Astrocystis bambusae (AB, accession number MH370741) were obtained as pure stock cultures. These isolates were isolated from the lichen Usnea pectinata (Sagada Mountain Province, Philippines) and U. bismolliuscula (Bukit Larut, Perak, Malaysia), respectively. The non-endolichenic fungus Trichoderma asperellum (TA, accession number KP792512) was also obtained as stock culture, previously been isolated from Phragmites sp., a phytoremediator plant (Sim et al., 2016). The isolates were cultured on potato dextrose agar (PDA, Friendemann Schmidt) and incubated at room temperature (RT, 25 ± 2 °C). To generate biomass, ten mycelial plugs (5 mm diameter) of each isolate were inoculated into 250 mL potato dextrose broth (PDB, Friendemann Schmidt) and incubated (100 rpm, RT) (Innova 44 stackable incubator shaker, New Brunswick Scientific) for 5 days or until sufficient biomass is attained (Chew and Ting, 2016). The mycelium was then harvested via filtration through sterile cheesecloth, rinsed with sufficient amount of distilled water, and weighed to 0.5 g fresh weight (Macharchand and Ting, 2017). The fresh biomass was used for subsequent experiments.
2.2 Dye decolorization activities
Malachite Green (MG) (CAS-No.2437–29-8, Friendemann Schmidt) dye was added into 25 mL autoclaved MilliQ water (18.2 MΩ, Sartorius, Malaysia) to produce the dye solution (100 ppm concentration). The fresh fungal biomass (0.5 g) (from section 2.1) was then inoculated into the dye solution and incubated for 14 days (25 ± 2 °C, 120 rpm). Non-inoculated (untreated) MG solution was assigned as negative control and incubated similarly. For every 24 h-interval (until day 14), 2 mL of dye solution was pipetted and centrifuged (10,000 rpm, 10 min), and the absorbance of the supernatant read at 617 nm (Tecan Spark M10 plate reader). The pellet was collected for FTIR analysis. The procedure was repeated for all isolates and the decolorization efficiency (DE, %) (Equation 1) was determined as follows: where Ai represented initial absorbance and Ao for observed absorbance upon treatment with the isolates (Macharchand and Ting, 2017).
2.3 Ultraviolet–visible (UV–vis) spectral analysis for detection of biodegradation potential
Fresh fungal biomass (0.5 g) was introduced into 25 mL of MG solution, and incubated for 14 days (100 rpm, RT). Non-treated dye solution was assigned as negative control and incubated similarly. Two mL of aliquot was withdrawn every 24-h interval for the next 14 days. The suspension was centrifuged (10,000 rpm, 10 min) and the absorbance of the supernatant was measured (300 to 800 nm) with a UV–vis spectrophotometer (UviLine 9400, Secomam). The UV–vis spectra peaks (day 1–14) for treated and non-treated (control) MG solutions were then plotted and compared (Macharchand and Ting, 2017).
2.4 FTIR-analysis of fungal biomass in Malachite Green solution
The biomass of AB, PT and TA were collected at day 1 and 8 from treated solutions (Section 2.2). The pellet obtained was oven-dried (50 °C) overnight, and ground into powder form using pestle and mortar. Single-reflection attenuated total reflection spectra (within 4000–400 cm−1) was obtained using the FTIR spectrometer conducted under ambient temperature. Data were collected within the mid-infrared region from 4000 to 700 cm−1 (50-scan speed) to exclude interference (Chew and Ting, 2016).
2.5 Statistical analysis
Each experiment was conducted in triplicates, and the data analysed with One-way Analysis of Variance (ANOVA) using Statistical Package for the Social Science (SPSS) version 22.0 (IBM). Means were compared using Tukey’s Test (Honestly Significant Difference, HSD(0.05)).
3 Results
3.1 Decolorization of Malachite Green dye
All three isolates decolorized MG, resulting in hues of bluish green. The isolate P. theae (PT) was most effective with significantly highest DE (71.42%), compared to T. asperellum (TA) (64.16% DE) and A. bambusae (AB) (55.39% DE) (Fig. 1). A difference of 7.26% in DE was observed for PT and TA. Decolorization of MG by PT was also more effective compared to AB, resulting in a difference of 16.03% in DE.Decolourisation efficiency (DE%) of T. asperellum (TA), P. theae (PT) and A. bambusae (AB) on Malachite Green (MG) (100 mg L-1). Mean comparisons with the same letter and font type are not significantly different according to Tukey’s Test (HSD0.05). Error bars indicate standard deviation of means.
The dye decolorization rate was, however, more rapidly observed when TA was used for dye treatment. The DE was increasing significantly for the first 4 days, with maximum DE attained by day 4 (66.77%). On the contrary, dye decolorization by both ELF (PT, AB) were less rapid than TA. Decolorization activities peaked at day 5 for both isolates (79.27% and 55.14%, for PT and AB, respectively) (Fig. 2). By day 14, PT demonstrated the highest DE with 89.22% DE, compared to TA (76.19% DE) and AB (67.69% DE) (Fig. 2).Decolourisation efficiency (DE%) of T. asperellum (TA), P. theae (PT) and A. bambusae (AB) on Malachite Green (MG) (100 mg L-1). Mean comparisons with the same letter and font type are not significantly different according to Tukey’s Test (HSD0.05). Comparisons are made across time (days) within the same isolate. Error bars indicate standard deviation of means.
3.2 UV–vis spectra
By day 1, the spectra peak for MG (at 617 nm) treated with TA (absorbance = 2.008) had the lowest absorbance compared to AB (absorbance = 2.099) and PT (absorbance = 2.381). Spectrum for negative control (untreated MG) remained the highest (absorbance = 2.568) (Fig. 3). By day 14, the untreated MG solution retained the absorbance peak at 617 nm (absorbance = 2.499), but treatment with PT (absorbance = 0.271), TA (absorbance = 0.581) and AB (absorbance = 0.753) showed diminished peaks (Fig. 3). The UV–vis spectra suggested possible degradation of MG as the dye chromophore was no longer detected. PT was concluded to have the most potential for biodegradation of MG dye (Fig. 3).UV–vis spectra of Malachite Green (MG) (100 mg L-1) at (A) day 1 and (B) day 14 after treatment with T. asperellum (TA), P. theae (PT) and A. bambusae (AB). Spectra for control (non-inoculated/untreated) MG solution is included.
3.3 FTIR spectra
The FTIR spectra for TA, PT and AB revealed the presence of additional functional groups (1000–2000 cm−1) detected post-treatment in MG (Figs. 4–6). The major functional groups detected were hydroxyl (—OH), carboxyl (—COOH), amine (—NH) and alkane (—CH). Other functional groups observed include the stretching of C⚌O in esters (peaks at 1745.26 cm−1) and ⚌C—H bending in aromatic rings (peaks at 815.49 cm−1) (Supplementary File-Table S1-S6). The FTIR spectra also revealed that AB in natural form (pre-treatment with MG), have lesser functional groups (∼4 major groups) (Fig. 4) compared to TA (∼6 major groups) (Fig. 5) and PT (∼6 major groups) (Fig. 6). The number of major functional groups for AB remained the lowest of the three isolates, even post-treatment, with only ∼ 5 major groups detected compared to ∼ 8 major groups for both TA and PT (Figs. 4–6).FTIR spectra analysis of A. bambusae (AB) (A) at day 1 and (B) day 14 after inoculation for the treatment of Malachite Green (MG) solutions. For each of the peaks, the following primary functional groups are detected; (a) hydroxyl, (b) amine and (c) alkanes.
FTIR spectra analysis of T. asperellum (TA) (A) at day 1 and (B) day 14 after inoculation for the treatment of Malachite Green (MG solutions). For each of the peaks, the following primary functional groups are detected; (a) hydroxyl, (b) amine, (c) alkanes and (d) other groups.
FTIR spectra analysis of P. theae (PT) (A) at day 1 and (B) day 14 after inoculation for the treatment of Malachite Green (MG solutions). For each of the peaks, the following primary functional groups are detected; (a) hydroxyl, (b) amine, (c) alkanes and (d) other groups.
For AB, the bands representing the stretching of C⚌O in esters and ⚌C—H bending in aromatic rings were absent (Fig. 4). Binding of MG to AB is ascribed to —OH and —NH (shifts from 3280.31 cm−1 to 3281.49 cm−1), asymmetric CH2— and CH3— stretching vibrations (shifts from 2924.28 cm−1 to 2923.06 cm−1) and CH3 deformations (shifts from 1373.16 cm−1 to 1362.90 cm−1) (Fig. 4). Bands at 1633.82 cm−1 (C⚌N and C⚌O stretching within the aromatic ring) shifted to 1634.77 cm−1. A new peak observed at 1518.79 cm−1 (C—H bending in aromatic ring), suggested the possible binding of the MG dye to AB (Fig. 4).
The FTIR spectra for both PT and TA were similar. For PT, binding of MG was detected by shifts in peaks from 3278.01 cm−1 to 3275.21 cm−1 (hydroxyl (—OH) and amine (—NH)), from 2922.95 cm−1 to 2923.28 cm−1, 2853.24 cm−1 to 2858.02 cm−1 (symmetric and asymmetric CH2— and CH3— stretching vibration), from 1374.26 cm−1 to 1372.96 cm−1 (CH3 deformations) and emergence of peaks at 1518.20 cm−1 (C—H bending in aromatic ring) and 813.66 cm−1 (⚌C—H bending in aromatic ring) (Fig. 6). For TA, exposure to MG resulted in shifts for the hydroxyl (—OH) and amine (—NH) groups (from 3269.18 cm−1 to 3272.13 cm−1) and for symmetric and asymmetric CH2— and CH3— stretching vibrations and CH3 deformations from 2923.23 cm−1, 2853.54 cm−1 and 1375.91 cm−1 to 2923.02 cm−1, 2854.01 cm−1 and 1374.49 cm−1, respectively (Fig. 5). New peaks were detected at 814.81 cm−1 (C—H bending in aromatic ring) after 14 days of treatment in MG.
To summarize, the FTIR spectra revealed that PT and AB shared similar major functional groups as the non-endolichenic TA. The number of functional groups may have a predisposition on the dye decolourization activities, as AB, which has the lowest number of functional groups, demonstrated lower dye decolourization efficiency and vice versa. Another critical observation is that new peaks were detected in all isolates post-treatment of MG, i.e. ⚌C—H bending in aromatic ring (814.81 cm−1 or 813.66 cm−1) for TA and PT, and C⚌C stretching vibration in the benzene ring (1518.20 cm−1 or 1518.19 cm−1) for PT and AB. Isolate PT, with the highest decolourization activities, was discovered to have both these new peaks.
4 Discussion
This study has discovered that ELF have the potential to decolorize MG dye. P. theae (PT) is phylogenetically related to Pestalotiopsis, which has been reported to decolourize raw textile effluents of reactive dyes (∼79.30 ± 1.70 % DE) (Verma et al. 2010). Interestingly, decolorization of MG by A. bambusae (AB) is reported for the first time. Although these ELF were isolated from pristine environments, they showed potential for dye removal, supporting their similarity to their lichen hosts and endophytes in removing dyes.
The dye decolorization efficiencies are presumably associated to the type and number of functional groups present. With lower number and types of functional groups found, poorer decolorization activities were observed. Hydroxyl (—OH), amine (—NH), alkane groups of symmetric and asymmetric CH2— and CH3— stretching vibration, CH3 deformations, C⚌N, C⚌O groups and C⚌C ring in lignin, or C⚌O in esters; are all responsible to bind cationic dyes (i.e. MG) via biosorption. Binding with dye molecules changes/shifts peaks of hydrogen bonds of functional groups (Zhang et al., 2011; Al Prol et al., 2017), while emergence of new peaks may arise from organic acids produced by fungi (Oberle-Kilic et al., 2013). The UV–vis spectra resonated with the FTIR results, suggesting ELF decolorized MG effectively. On the contrary, isolate A. bambusae (AB) which has lesser functional groups compared to T. asperellum (TA) and P. theae (PT) (absence of C⚌N and C⚌O stretching of carboxyl groups and C⚌C ring in lignin), demonstrated inferior decolorization activities.
From these observations, ELF is concluded to decolorize MG via biosorption and biodegradation as their main mechanisms. Biosorption occurs immediately as dye molecules bind to the functional groups present on the surface of fungal mycelium, reflected by the rapid decolorization rate, which plateaus once the binding sites are saturated and equilibrium is achieved (Khalaf, 2008; Rybczyńska-Tkaczyk and Korniłłowicz-Kowalska, 2016; Macharchand and Ting, 2017). Biodegradation involves enzymatic breakdown of the dyes evident by diminishing spectra peaks (Kaushik and Malik, 2009). Although enzymatic analyses were not performed, the differences in spectra peaks from the UV–vis analysis concurs that biodegradation through enzymatic processes likely occurred (Chen and Ting, 2015a, 2015b; Macharchand and Ting, 2017). Furthermore, Pestalotiopsis and Trichoderma have been profiled to produce enzymes related to biodegradation such as laccase, lignin-peroxidase or NADH-DCIP reductase (Verma et al., 2010; Shedbalkar and Jadhav, 2011; Macharchand and Ting, 2017). This study can benefit from further optimization studies to determine the optimum operational parameters for successful decolorization of MG. The toxicity of treated MG and the by-products produced can also be further examined. Although these are not investigated at this stage, previous studies using fungi have shown that optimum parameters are isolate dependent and treated dyes are often less toxic than original dye solutions observed from phytotoxicity tests (Chen and Ting, 2015a, 2015b; Chen et al., 2019).
5 Conclusion
This study revealed the dye decolorization potential of ELF (P. theae and A. bambusae). P. theae has better decolorization efficiency compared to the non-endolichenic T. asperellum, while A. bambusae was the least effective. The decolorization activities were attributed to both biosorption and biodegradation activities. Findings here highlighted the significant attributes of ELF, and their potential in decolorizing dyes. Further exploration into new bioremediative potential of ELF can be conducted in future.
Acknowledgements
The authors extend their gratitude to Monash University Malaysia for the facilities to conduct the study.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
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Appendix A
Supplementary data
Supplementary data to this article can be found online at https://doi.org/10.1016/j.jksus.2021.101579.
Appendix A
Supplementary data
The following are the Supplementary data to this article: