- Original article
- Open Access
Improvement of efficiency of brown coal biosolubilization by novel recombinant Fusarium oxysporum laccase
AMB Express volume 8, Article number: 133 (2018)
Clean coal technologies (e.g. coal biosolubilization) are of essential value, especially in Europe, where coal is the national wealth and other energy sources like crude oil are not available. Fusarium oxysporum LOCK 1134, the strain isolated from brown coal, efficiently biosolubilizes lignite. The obtained liquefied products contain 50% less sulfur and over 99% less mercury than the crude coal. Moreover, the liquefied coal can be modified further by laccase. In this study F. oxysporum laccase was expressed in Pichia pastoris for the first time and was assessed as an additional agent for coal degradation. The novel laccase contributes to humic and fulvic acids release from liquefied coal due to introduction of oxygen into coal structure. The effect is increased when a natural redox mediator, sinapic acid, is present in the reaction mixture—up to 30% and 80% respectively. Humic acids obtained by biological process are environmentally friendly fertilizers that may have stimulating effects on crop growth.
Brown coal is an important energy source in Europe. However, it is discouraged to be traditionally burnt due to its low calorific value and harmful substances that are created upon combustion, such as nitrogen and sulfur oxides. Liquefaction of coal offers converting the coal into cleaner fuel or creating a base for production of complex aromatic compounds (Igbinigie et al. 2008; Sekhohola et al. 2013). Apart from expensive and energy-demanding chemical methods several biological methods of coal solubilization are under investigation. The idea is to apply microorganisms (bacteria or fungi) or solubilizing agents produced by them (alkali substances, biosurfactants, chelators, enzymes) to degrade the polymer (Fakoussa and Hofrichter 1999; Gokcay et al. 2001; Wang et al. 2016). Trametes versicolor, Trichoderma reesei, Bacillus mycoides and Gordonia alkanivorans are few from the list of brown coal biosolubilizing microorganisms.
The products of biosolubilization are a mixture of humic, fulvic acids and other organic compounds. The chemical structure of the products enables their usage as excellent sorbents, for example in biosorption of various pollutants, especially heavy metals. Moreover, humic and fulvic acids may be used as mediators for biogeochemical reactions as they may perform function of oxidants or reducers. Brown coal has been proposed before as fertilizer and a component in soil remediation process (Sekhohola et al. 2013). Furthermore, high content of organic substances suggests application of liquefied coal in production of methane. The process of biosolubilization may be an initial step for methanogenesis. Addition of laccase will lead to further degradation of lignite which would result in easier methane production (Haider et al. 2013; Stephen and Park 2015). Liquefied brown coal may also be used as a raw material for production of various chemicals—alcohols, aromatic compounds, fatty acids, etc. The desired substances could be obtained by further chemical or enzymatic process or by application of microorganisms with specific metabolic abilities.
Fusarium oxysporum is an ascomycete reported as an excellent microorganism for brown coal biosolubilisation (Strzelecki et al. 2015). F. oxysporum possesses three genes that may encode for extracellular laccases (Kwiatos et al. 2015). Laccases have been enlisted as potential solubilising agents and also lignin degrading enzymes (Sekhohola et al. 2014; Wang et al. 2015; Munk et al. 2015; Ortner et al. 2015; Hämäläinen et al. 2018). It catalyzes oxidation of phenolic substrates with water as only by-product. Moreover, laccases are able to oxidize non-phenolic compounds indirectly, with help of redox mediators. In laccase mediator system (LMS) the enzyme oxidizes low molecular weight phenolic compound—mediator—and a very reactive intermediate product is formed. Next, it leaves the laccase active site and oxidizes other substrates which could not enter the enzyme active site on their own. The mediators are either synthetic ones like 2,2′-azino-bis(3-ethylbenzothiazoline-6-sulfonic acid) diammonium salt (ABTS), 1-hydroxybenzotriazole (HBT) or natural ones—lignin derivatives, such as sinapic acid, 2,6-dimethoxyphenol or p-coumaric acid. Laccases are enzymes useful in various fields—food and textile industry, biomedical diagnostics, biofuel production, organic synthesis and bioremediation (Pollegioni et al. 2015; Kaczmarek et al. 2017; Hilgers et al. 2018). Moreover, laccases have also potential in lignin valorization (Wang et al. 2015; Coconi Linares et al. 2018; Ghatge et al. 2018). In the study, we report heterologous expression of a new laccase from F. oxysporum for the first time and its assessment as a brown coal biosolubilizing agent.
Materials and methods
All chemicals used in the study were analytical grade and bought from Sigma (Saint Louis, USA) or Chempur (Piekary Śląskie, Poland). The brown coal used in the study was obtained from Bełchatów Brown Coal Mine (Poland). Coal particles with a diameter of 1–2 mm were subjected to pretreatment with 8M HNO3 as described earlier (Romanowska et al. 2015) and then subjected to microbial solubilization.
The microorganism used in the study was F. oxysporum LOCK 1134 (Centre of Industrial Microorganisms Collection—LOCK, WDCM105), strain isolated from brown coal from Bełchatów Brown Coal Mine, currently in pure culture collection at the Institute of Technical Biochemistry, Lodz University of Technology. Pichia pastoris KM71H from Invitrogen (Carlsbad, USA) was used for protein expression and Escherichia coli top10f’ (Invitrogen, Carlsbad, USA) for standard cloning procedures. pJET1.2 plasmid (Thermo Fisher Scientific, Walthman, USA) was used for basic molecular manipulations and pPICZαA vector (Invitrogen, Carlsbad, USA) was used for enzyme expression.
Construction of expression vector
All sequences encoding for Gr2 laccase with native signal sequence and without introns found on Fusarium Comparative Project website were aligned using Clustal W program (Kwiatos et al. 2015). The consensus sequence was subjected to codon optimization for P. pastoris expression. The resulting sequence (GeneBank accession number MH351668) was synthesized by GeneArt (Thermo Fisher Scientific, Regensburg, Germany) with Eco721 restriction site of 5′ end of the sequence and NotI on 3′ end of the sequence. The amplified with high fidelity polymerase DNA sequence was cloned to pJET vector. Having multiplied the vector by standard E. coli procedures (Evans 1990) the sequence was cut out by Eco721 and NotI restriction enzymes and ligated with pPICZα A with T4 DNA Ligase (5 U/µL) (Thermo Fisher Scientfic). The resulting vector was cut with SacI restriction enzyme (Thermo Fisher Scientific) and transformed to electrocompetent P. pastoris KM71H according to the Invitrogen Easy Select Pichia Expression protocol. Positive transformants were selected on YPD plates (2% peptone from casein, 1% yeast extract, 0.4% dextrose, 1.5% agar) with zeocine (100 µg/mL). Then, the clones were cultivated in 96-deep well plates according to the procedure explained elsewhere (Weis et al. 2004). The clone producing the highest laccase activity in culture supernatant was chosen for further cultivations.
Production of recombinant F. oxysporum laccase in P. pastoris
The recombinant P. pastoris KM71H was cultivated in Sixfors fermenter (InFors-HT, Bottmingen, Switzerland) of maximal volume of 500 mL according to Pichia Fermentation Process Guidelines with minor modifications. The fermentation basal salt medium was supplemented with 0.2 mM CuSO4. The fermentation started with inoculation with 20 mL preculture of OD600 3 (10% initial volume). For the first 24 h the cultivation was at glycerol batch phase, when the oxygen spike appeared the glycerol fed-batch phase (18 mL/h/L of 50% glycerol with 12 mL/L pTM1 salt) begun and last for 4 h. The induction of protein expression started with the methanol fed-batch phase. The methanol was added gradually from 0 to 3 mL/h/L for 4 h and then the feed was constant till the end of the fermentation. Sampled were taken for measurements of laccase activity, protein concentration and wet biomass. The cultivation was stopped after 167 h from inoculation, the biomass was separated from supernatant with centrifugation (15 min, 4 °C, 8000×g). The protein was concentrated to the volumetric activity of 70 U/L (laccase preparation) on 30 kDa Tangential Flow Filtration Membrane Cassettes (Sartorius).
Laccase activity was measured at 25 °C by monitoring oxidation of 1 mM ABTS at 420 nm (ε420 = 36,000 M−1 cm−1) in McIlvaine buffer at pH 3.5. One unit of enzyme activity was defined as the amount of enzyme required to obtain 1 µmol of product per minute. Each sample was measured in duplicate.
Plate screening for brown coal biosolubilization potential
Fusarium oxysporum LOCK 1134 was cultivated for 7 days at 30 °C on solid modified Czapek-Dox medium: glucose (10.0 g/L), sodium glutamate (2.0 g/L), NaNO3 (3.0 g/L), K2PO4 (2.0 g/L), MgSO4 (0.5 g/L), KCl (0.5 g/L), agar (15 g/L). The pH of the medium was set to 7 with 1M HCl before autoclaving. Small parts of brown coal pretreated with HNO3 were situated on fungi mycelium and incubated for 2 days at 30 °C.
Brown coal biosolubilization by F. oxysporum LOCK 1134
Fusarium oxysporum LOCK 1134 was cultivated for 7 days at 30 °C on solid modified Czapek-Dox medium. The fungi were transferred from Petri dish to 500 mL flat-bottomed flasks with 100 mL liquid modified Czapek-Dox with 0.1% sterile coal powder as an inducer. F. oxysporum was cultivated for 3 days at 30 °C and 180 rpm. Next, 10 mL of obtained pre-culture was transferred to 100 mL of fresh medium. The fungus was cultivated in the same conditions for next 3 days. 5 g (5% w/v) of sterile pretreated coal was added to the prepared 3 days old culture. The experiment was conducted for 14 days at 30 °C and 180 rpm. Sterile medium with coal subjected to the same conditions was considered as a control. Having finished the incubation the biomass was centrifuged at 7740×g for 15 min and the obtained supernatant (liquefied coal) was further analyzed.
The fraction of solid coal and liquefied coal, were subjected to analysis. In order to assess the amount of produced humic and fulvic acids, the absorbance at 450 nm and 650 nm were measured accordingly with T80 + UV/VIS PG Instruments Ltd spectrophotometer. The amount of mercury in coal was determined by atomic absorption spectroscopy CV AAS and other elements were measured with EuroVector 3018.
Liquified coal treatment with recombinant laccase
The liquefied coal was subjected to further degradation by recombinant enzyme preparation. 0.5 mL of solubilized coal (containing 15.2 mg/mL dry coal) was mixed with 0.5 mL of laccase preparation (0.035 U) with or without mediators and placed in 2 mL eppendorf tubes. The tubes were put on a rack and incubated in a shaking incubator (100 rpm, 40 °C) for 24 h. The following variants were assessed:
0.5 mL of liquefied coal (pH 4.2) and 0.5 mL of laccase preparation
0.5 mL of liquefied coal (pH 3) and 0.5 mL of laccase preparation
0.5 mL of liquefied coal (pH 4.2), 0.5 mL of laccase preparation and 1 mM ABTS
0.5 mL of liquefied coal (pH 4.2), 0.5 mL of laccase preparation and 5 mM ABTS
0.5 mL of liquefied coal (pH 4.2), 0.5 mL of laccase preparation and 1 mM sinapic acid (SA)
0.5 mL of liquefied coal (pH 4.2), 0.5 mL of laccase preparation and 5 mM sinapic acid.
All variants were prepared in triplicates. Every sample has its own control (instead of enzyme sterile water was added), also in triplicate.
Analysis of the biodegradation process
Absorbance at 650 nm (fulvic acids) and 450 nm (humic acids) were measured after 1 h and 24 h by Multiskan™ GO Microplate Spectrophotometer (Thermo Scientific) in order to assess the amount of released acids. Fourier Transform Infrared Spectroscopy (FTIR) was used to determine the specific chemical groups of atoms in the structure of coal and its biosolubilization products. The FTIR analysis was performed using a Thermo Nicolet AVATAR 330 at the transmission range from 4400 to 400 cm− 1 after 24 h of incubation. Prior to FTIR analysis the samples were lyophilized.
Expression and production of F. oxysporum laccase coding sequence in P. pastoris
One of the potential F. oxysporum laccase coding sequences described before was synthesized with codon optimized for expression in P. pastoris. The 90 positive colonies that grew on YPD with zeocin were picked and cultivated in 96-deep well plate as explained previously (Weis et al. 2004). At the end of the cultivation the supernatant was harvested and subjected to ABTS assay to determine the laccase activity. The activities varied from well to well and the maximal reached 7 U/L while the average activity was 2.6 U/L. The best clone was picked and was produced by recombinant P. pastoris KM71H in 500 mL bioreactor according to the standard procedure. The samples were taken twice a day for wet biomass and laccase activity measurements. Laccase activity was detectable after 95 h from the inoculation and the fermentation was stopped when the activity in culture supernatant started to decrease. The maximum activity was 22 U/L reached in the culture stationary phase (Fig. 1). The laccase preparation was obtained by biomass separation and supernatant concentration.
Plate screening for brown coal biosolubilization potential
Fusarium oxysporum LOCK 1134 converts solid brown coal into dark liquid droplets after 2 days incubation at 30 °C. The experiment is presented in Fig. 2, in Additional file 1: Movie S1) a movie showing F. oxysporum LOCK 1134 solubilizing brown coal is presented.
Brown coal biosolubilization by F. oxysporum LOCK 1134 and coal analysis
The brown coal was solubilized by F. oxysporum LOCK 1134 during the submerged cultivation of the fungi. Almost no humic and fulvic acids were formed in control sample (medium with coal), while the amount of humic acids formed by F. oxysporum solubilization reached 1474 mg/g in culture supernatant.
The elemental analysis revealed carbon content decrease in liquefied coal and increase in oxygen content (Table 1). Because of that we observe 50% decrease in calorific value of coal [calculated with Dulong equation (Yin et al. 2009)]. Coal biosolubilization led to significant decrease of sulfur and mercury content in liquefied products.
Liquid coal treatment with laccase preparation
Humic and fulvic acids release
The biotransformation of liquid coal by recombinant laccase was done with and without presence of redox mediators. Humic and fulvic acids are released from lignite during the process for all six variants, which indicates that laccase took effective role in coal degradation. The most significant changes occur with presence of natural laccase mediator—sinapic acid, when its concentration is high (5 mM—variant F). On the other hand, the presence of ABTS does not benefit the reaction (variant C and D) (Figs. 3, 4).
The release of humic and fulvic acids for all 6 variants is caused by similar events (Fig. 5). The lack of picks at 900 cm−1 and lower wavenumbers for all samples but control suggests the degradation of aromatic compounds. Moreover, higher transmittance at 1058 cm−1 signifies formation of ether bonds, while high transmittance at 1343 cm−1 formation of C–O bonds (in carboxylic groups), probably due to introduction of oxygen into coal structure. Other proves of oxidation of lignite by laccase is visible at wavenumbers around 1600—the increase of picks in this area suggests formation of esters, carboxylic groups or lactons. The differences in picks around 2360 cm−1 comes from various distribution of C=N bonds.
Fusarium oxysporum LOCK 1134 is a strain effectively solubilizing brown coal (Fig. 2). The amount of humic acids formed by F. oxysporum solubilization reached 1474 mg/g in culture supernatant. To compare, in compost average amount of humic substances, which are responsible for soil enrichment, reaches only 182 mg/g (Gusiatin and Kulikowska 2012). Recently, lignite derived humic acids were reported as an excellent fertilizer, that increase vegetable and wheat yield and soil quality index (Ahmad et al. 2015; Ciarkowska et al. 2017). Moreover, our results also supports these studies, showing that liquefied coal stimulates germination of seed and growth of plant roots (data not published yet).
The elemental analysis suggests that F. oxysporum metabolizes the carbon from coal—the amount of carbon decreases from 44 to 32%. The solubilization of lignite implies introduction of oxygen into coal structure to loosen the hard structure and make it more susceptible to other chemical changes. The biosolubilization by F. oxysporum LOCK 1134 ends with 10% increase in oxygen content in lignite (Table 1).
The maximal calorific value of coal (18 MJ/kg) and solubilization products (9.2 MJ/kg) was calculated with Dulong equation (Yin et al. 2009) (Table 1). The calorific value of coal is within the range of cited values (Höök et al. 2010). The biosolubilization of coal leads to 50% decrease in calorific value; mainly due to decrease in carbon and oxygen content. However, the product of coal solubilization could find an alternative of its application in energy production. Co-fermentation is applied for improvement of methane fermentation by dilution of the main substrate with addition of another organic matter. It is designed in the way that a proper carbon:nitrogen:phosphorous ratio is preserved (Sosnowski et al. 2008).
Biosolubilization aims to reduce impurities in coal, clear out lignite from mercury and sulfur or nitrogen that may form harmful oxides during the combustion of the material. Biosolubilization goes together with biodesulfurization—F. oxysporum LOCK 1134 is able to reduce sulfur content in almost 50% (Table 1). Comparing the results with previously published studies of biological biosolubilization with bacteria indicates that F. oxysporum more effectively dispose sulfur than Gordonia alkanivorans S7 and Bacillus mycoides NS1020 (Romanowska et al. 2015). S7 leaves 80% and NS1020 73% of sulfur content after solubilization in liquefied product, while F. oxysporum just 59%. Another benefit from biological liquefaction by F. oxysporum is reduction of mercury content in coal—it decreases from 164.62 µg/kg in pretreated coal to only 0.59 µg/kg in liquefied product. It is estimated that 1900 ton of mercury was emitted to the environment in 2010 all over the world by combustion of fossil fuels (Jozwik et al. 2014). Our results indicates that properly designed biosolubilization process has a great impact on reduction of harmfulness of exhausted gases.
The fungi possesses in its genome genes that encode laccases, however till now it was not known if extracellular laccases have an impact on lignite biosolubilization. The conducted research used F. oxysporum recombinant laccase expressed in P. pastoris to visualize the effect of the enzyme on coal structure. The study confirmed the ability of the laccase to improve the biodegradation process. The most optimum action of the enzyme is obtained if laccase-mediator system is in use and natural lignin mediators seem to be a better choice than synthetic ones. Nevertheless, many researches prove the benefit of enzyme engineering towards its specificity and optimal conditions to profit the processes conducted by them (Macellaro et al. 2014; Scheiblbrandner et al. 2017).
It is widely discussed if laccase can catalyze bond cleavage in lignin by itself (Munk et al. 2015; Tonin et al. 2016; Hilgers et al. 2018). Most scientists conclude that it is not possible due to the size of substrate binding pocket. The lignin either cannot enter the active site or cannot leave it inhibiting the laccase catalytic action. However, as the results suggests, the recombinant laccase from F. oxysporum is able to introduce changes in liquid coal structure without the addition of a mediator (40% less fluvic acids than with SA) (Fig. 3). The liquid coal is firstly partially degraded by fungus due to action of various agents, such as biosurfactants, alkali substances, chelators and enzymes. It is possible that in the liquid coal there are already smaller lignin parts that are little enough to act as mediators. They may be oxidized by laccase and then proceed and oxidize bigger molecules further. Another hypothesis is that while lignin is activated laccase leads to cleavage of the weakest bonds, for example the ether bonds (Munk et al. 2015).
For the changes in lignin structure to occur, one electron should be removed from lignin molecule. Then the surface becomes more reactive, which will lead to various changes: bond cleavage and depolymerization, change in functional groups (acetylation or demethylation) or coupling. Low molecular weight compounds like mediators may attach to lignin by radical coupling. The event may succeed in two ways: either in spreading of the mediator on the surface (grafting) or in continuation of radical polymerization which ends with lignin polymerization (Barneto et al. 2012; Munk et al. 2015). Grafting may promote solubilization of lignin, which is of interest for clean coal technologies techniques. The mechanism of polymerization may explain the formation of higher molecular weight compounds—humic acids (Figs. 3 and 4). Fulvic acids are formed during all the 6 processes; the highest amount is released when high concentration of sinapic acid is present. However, sole laccase also leads to formation of considerable amount of higher weight compounds—polymerization abilities of laccase are commonly acknowledged (Mikolasch and Schauer 2009; Munk et al. 2015; Pollegioni et al. 2015).
The recombinant laccase has its optimum at pH 3.5 and 40 °C. The experiment was conducted at 40 °C and pH 4.2—the pH of liquefied coal, except for variant B—the pH of liquefied coal was adjusted to pH 3 by 1M HCl. The release of humic acids are almost identical for variant A (laccase without mediators, pH 4.2) and variant B (laccase without mediators, pH 3), while the amount of produced fulvic acids are 13% higher for variant B (Fig. 3). This suggests that if the reaction took place for the variant with sinapic acid (E, F), probably the results would be even better. As it would not have industrial sense to change the pH of coal, the solution would be to engineer the enzyme to shift its pH optimum towards pH 4.2. The research on laccase directed evolution towards changes of its optimum reaction conditions have been done successfully in the past (Pardo et al. 2012; Mate et al. 2013).
The second bottleneck of the application that could be overcome by protein engineering is the stability of the enzyme in the most optimum conditions. As Fig. 3 presents the difference between the amount of fulvic acids released after 1 h of the experiment and 24 h is around 10% for all cases. Probably the enzyme is deactivated by too high temperature and too low pH after couple of hours; however the mediators may act even longer.
Heterologous expression of fungal laccases is a complex topic that brings many challenges. It is often necessary to optimize the cultivation conditions in order to obtain detectable level of laccase expression. The duration, oxidation of culture, pH of medium, concentration of copper ions and ethanol that could enhance the permeability of membrane and enhance secretion are only few to mention in long process of expression optimization. It is often required to enhance the secretion and expression levels by protein engineering. For example Pycnoporus cinnabarinus laccase was heterologously expressed in Saccharomyces cerevisiae at level of 0.003 U/L and then due to medium optimization and cost-intensive directed evolution enhanced 8000 fold to 24 U/L (Camarero et al. 2012). Trametes versicolor LCC1 was expressed in P. pastoris and its activity in 7-day culture supernatant was 2 U/L, when it reached 173 U/L after the optimization of culture conditions (Colao et al. 2006). F. oxysporum laccase was expressed in P. pastoris with maximal level of 7 U/L in 96 deep-well format, while cultivated in bioreactor, the expression of laccase was increased over threefold (Fig. 1).
Although, it is still unknown in which extend the extracellular laccases help the fungi in biosolubilization process, the addition of adequately tailored biocatalyst may be of interest for many industrial applications. Clean coal technologies are of essential value, especially in Europe, were coal is the national wealth and other energy sources like crude oil are not available.
2,2′-azino-bis(3-ethylbenzothiazoline-6-sulfonic acid) diammonium salt
Ahmad I, Ali S, Khan KS, Hassan ul F, Bashir K (2015) Use of coal derived humic acid as soil conditioner to improve soil physical properties and wheat yield. Int J Plant Soil Sci 5:268–275
Barneto AG, Aracri E, Andreu G, Vidal T (2012) Investigating the structure—effect relationships of various natural phenols used as laccase mediators in the biobleaching of kenaf and sisal pulps. Bioresour Technol 112:327–335. https://doi.org/10.1016/j.biortech.2012.02.136
Camarero S, Pardo I, Cañas AI, Molina P, Record E, Martínez AT, Martínez MJ, Alcalde M (2012) Engineering platforms for directed evolution of Laccase from Pycnoporus cinnabarinus. Appl Environ Microbiol 78:1370–1384. https://doi.org/10.1128/AEM.07530-11
Ciarkowska K, Sołek-Podwika K, Filipek-Mazur B, Tabak M (2017) Comparative effects of lignite-derived humic acids and FYM on soil properties and vegetable yield. Geoderma 303:85–92. https://doi.org/10.1016/j.geoderma.2017.05.022
Coconi Linares N, Fernández F, Loske AM, Gómez-Lim MA (2018) Enhanced delignification of lignocellulosic biomass by recombinant fungus Phanerochaete chrysosporium overexpressing laccases and peroxidases. J Mol Microbiol Biotechnol 28:1–13. https://doi.org/10.1159/000485976
Colao MC, Lupino S, Garzillo AM, Buonocore V, Ruzzi M (2006) Heterologous expression of lcc1 gene from Trametes trogii in Pichia pastoris and characterization of the recombinant enzyme. Microb Cell Factories 5:31. https://doi.org/10.1186/1475-2859-5-31
Evans GA (1990) Molecular cloning: A laboratory manual, 2nd edition, vols 1, 2, and 3. Current protocols in molecular biology. Vols 1 and 2: By Sambrook J, Fritsch EF, Maniatis T. Cold Spring Harbor: Cold Spring Harbor Laboratory Press. (1989), p 1626. $115.00. Edited by Ausubel FM, Brent R, Kingston RE, Moore DD, Seidman JG, Smith JA, Struhl K. New York: Greene Publishing Associates and John Wiley & Sons. (1989), p 1120. $255.00. Cell 61:17–18. https://doi.org/10.1016/0092-8674(90)90210-6
Fakoussa RM, Hofrichter M (1999) Biotechnology and microbiology of coal degradation. Appl Microbiol Biotechnol 52:25–40
Ghatge S, Yang Y, Song W-Y, Kim T-Y, Hur H-G (2018) A novel laccase from thermoalkaliphilic bacterium Caldalkalibacillus thermarum strain TA2.A1 able to catalyze dimerization of a lignin model compound. Appl Microbiol. https://doi.org/10.1007/s00253-018-8898-4
Gokcay CF, Kolankaya N, Dilek FB (2001) Microbial solubilization of lignites. Fuel 80:1421–1433. https://doi.org/10.1016/S0016-2361(01)00010-2
Gusiatin ZM, Kulikowska D (2012) Przemiany substancji humusowych, azotu oraz form metali ciężkich w osadach ściekowych kompostowanych w mieszaninie z odpadami lignocelulozowymi. Inż Ekol 28:81–93
Haider R, Ghauri MA, SanFilipo JR, Jones EJ, Orem WH, Tatu CA, Akhtar K, Akhtar N (2013) Fungal degradation of coal as a pretreatment for methane production. Fuel 104:717–725. https://doi.org/10.1016/j.fuel.2012.05.015
Hämäläinen V, Grönroos T, Suonpää A, Heikkilä MW, Romein B, Ihalainen P, Malandra S, Birikh KR (2018) Enzymatic processes to unlock the lignin value. Front Bioeng Biotechnol. https://doi.org/10.3389/fbioe.2018.00020
Hilgers R, Vincken J-P, Gruppen H, Kabel MA (2018) Laccase/mediator systems: their reactivity toward phenolic lignin structures. ACS Sustain Chem Eng 6:2037–2046. https://doi.org/10.1021/acssuschemeng.7b03451
Höök M, Zittel W, Schindler J, Aleklett K (2010) Global coal production outlooks based on a logistic model. Fuel 89:3546–3558. https://doi.org/10.1016/j.fuel.2010.06.013
Igbinigie EE, Aktins S, van Breugel Y, van Dyke S, Davies-Coleman MT, Rose PD (2008) Fungal biodegradation of hard coal by a newly reported isolate, Neosartorya fischeri. Biotechnol J 3:1407–1416. https://doi.org/10.1002/biot.200800227
Jozwik K, Szynkowska M, Kula PJ, Niedzielski P, Pietrasik R, Goralski J (2014) A new concept for limitation of the mercury emission from exhaust gases from power station units Nowa koncepcja ograniczenia emisji rtęci z gazów wylotowych bloków energetycznych. Przemysl Chem 93:1339–1342
Kaczmarek MB, Kwiatos N, Szczęsna-Antczak M, Bielecki S (2017) Laccases—enzymes with an unlimited potential. Biotechnol Food Sci 81:41–70
Kwiatos N, Ryngajłło M, Bielecki S (2015) Diversity of laccase-coding genes in Fusarium oxysporum genomes. Fungi Their Interact. https://doi.org/10.3389/fmicb.2015.00933
Macellaro G, Baratto MC, Piscitelli A, Pezzella C, Fabrizi de Biani F, Palmese A, Piumi F, Record E, Basosi R, Sannia G (2014) Effective mutations in a high redox potential laccase from Pleurotus ostreatus. Appl Microbiol Biotechnol 98:4949–4961. https://doi.org/10.1007/s00253-013-5491-8
Mate DM, Gonzalez-Perez D, Falk M, Kittl R, Pita M, De Lacey AL, Ludwig R, Shleev S, Alcalde M (2013) Blood tolerant laccase by directed evolution. Chem Biol 20:223–231. https://doi.org/10.1016/j.chembiol.2013.01.001
Mikolasch A, Schauer F (2009) Fungal laccases as tools for the synthesis of new hybrid molecules and biomaterials. Appl Microbiol Biotechnol 82:605–624. https://doi.org/10.1007/s00253-009-1869-z
Munk L, Sitarz AK, Kalyani DC, Mikkelsen JD, Meyer AS (2015) Can laccases catalyze bond cleavage in lignin? Biotechnol Adv 33:13–24. https://doi.org/10.1016/j.biotechadv.2014.12.008
Ortner A, Huber D, Haske-Cornelius O, Weber HK, Hofer K, Bauer W, Nyanhongo GS, Guebitz GM (2015) Laccase mediated oxidation of industrial lignins: is oxygen limiting? Process Biochem 50:1277–1283. https://doi.org/10.1016/j.procbio.2015.05.003
Pardo I, Vicente AI, Mate DM, Alcalde M, Camarero S (2012) Development of chimeric laccases by directed evolution. Biotechnol Bioeng 109:2978–2986. https://doi.org/10.1002/bit.24588
Pollegioni L, Tonin F, Rosini E (2015) Lignin-degrading enzymes. FEBS J 282:1190–1213. https://doi.org/10.1111/febs.13224
Romanowska I, Strzelecki B, Bielecki S (2015) Biosolubilization of Polish brown coal by Gordonia alkanivorans S7 and Bacillus mycoides NS1020. Fuel Process Technol 131:430–436. https://doi.org/10.1016/j.fuproc.2014.12.019
Scheiblbrandner S, Breslmayr E, Csarman F, Paukner R, Führer J, Herzog PL, Shleev SV, Osipov EM, Tikhonova TV, Popov VO, Haltrich D, Ludwig R, Kittl R (2017) Evolving stability and pH-dependent activity of the high redox potential Botrytis aclada laccase for enzymatic fuel cells. Sci Rep 7:13688. https://doi.org/10.1038/s41598-017-13734-0
Sekhohola LM, Igbinigie EE, Cowan AK (2013) Biological degradation and solubilisation of coal. Biodegradation 24:305–318. https://doi.org/10.1007/s10532-012-9594-1
Sekhohola LM, Isaacs ML, Cowan AK (2014) Fungal colonization and enzyme-mediated metabolism of waste coal by Neosartorya fischeri strain ECCN 84. Biosci Biotechnol Biochem 78:1797–1802. https://doi.org/10.1080/09168451.2014.930325
Sosnowski P, Klepacz-Smolka A, Kaczorek K, Ledakowicz S (2008) Kinetic investigations of methane co-fermentation of sewage sludge and organic fraction of municipal solid wastes. Bioresour Technol 99:5731–5737. https://doi.org/10.1016/j.biortech.2007.10.019
Stephen Y, Park YL (2015) Biogenic methane production from coal: a review on recent research and development on microbially enhanced coalbed methane (MECBM). Fuel. https://doi.org/10.1016/j.fuel.2015.10.121
Strzelecki B, Kwiatos N, Bielecki S (2015) Effect of coal pretreatment on brown coal biosolubilisation by Fusarium oxysporum 1101. PhD Interdiscip J 1(2015):125–132
Tonin F, Melis R, Cordes A, Sanchez-Amat A, Pollegioni L, Rosini E (2016) Comparison of different microbial laccases as tools for industrial uses. New Biotechnol 33:387–398. https://doi.org/10.1016/j.nbt.2016.01.007
Wang J, Feng J, Jia W, Chang S, Li S, Li Y (2015) Lignin engineering through laccase modification: a promising field for energy plant improvement. Biotechnol Biofuels 8:145. https://doi.org/10.1186/s13068-015-0331-y
Wang L, Nie Y, Tang Y-Q, Song X-M, Cao K, Sun L-Z, Wang Z-J, Wu X-L (2016) Diverse bacteria with lignin degrading potentials isolated from two ranks of coal. Front Microbiol. https://doi.org/10.3389/fmicb.2016.01428
Weis R, Luiten R, Skranc W, Schwab H, Wubbolts M, Glieder A (2004) Reliable high-throughput screening with Pichia pastoris by limiting yeast cell death phenomena. FEMS Yeast Res 5:179–189. https://doi.org/10.1016/j.femsyr.2004.06.016
Yin S, Tao X, Shi K, Tan Z (2009) Biosolubilisation of Chinese lignite. Energy 34:775–781. https://doi.org/10.1016/j.energy.2009.02.009
NK performed the experiments concerning laccase, analyzed the data and prepared the manuscript, MJK helped with data analysis and manuscript preparation; BS performed the experiments with F. oxysporum, SB initiated the project and supervised the work. All authors read and approved the final manuscript.
We would like to thank Dr. Irena Romanowska and Dr. Manu de Groeve for the introduction to brown coal biosolubilization topic and for scientific discussions.
The authors declare that they have no competing interests.
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This video shows a time lapse movie of the solubilization of Polish brown coal (lignite) by Fusarium oxysporum LOCK 1134. Brown coal pieces were placed on the mycelium of a fungus and incubated for several days at room temperature. The video was made by automatically taking a picture of the petri dish every 10 minutes. Author: Manu de Groeve.
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Kwiatos, N., Jędrzejczak-Krzepkowska, M., Strzelecki, B. et al. Improvement of efficiency of brown coal biosolubilization by novel recombinant Fusarium oxysporum laccase. AMB Expr 8, 133 (2018). https://doi.org/10.1186/s13568-018-0669-1
- Brown coal
- Laccase mediator system