- Open Access
The physico-chemical properties and biostimulative activities of humic substances regenerated from lignite
© David et al.; licensee Springer. 2014
- Received: 7 October 2013
- Accepted: 10 February 2014
- Published: 21 March 2014
The positive effect of humic acids on the growth of plant roots is well known, however, the mechanisms and role of their physical structure in these processes have not been fully explained yet. In this work, South-Moravian lignite was oxidized by means of nitric acid and hydrogen peroxide to produce a set of regenerated humic acids. The elemental composition, solid state stability and solution characteristics were determined and correlated in vitro with their biological activity. A modified hydroponic method was applied to determine the effects of their potassium salts on Zea mays seedlings roots with respect to the plant weight, root length, root division, and starch and protein content. The relations between the determined parameters were evaluated through Principal Component Analysis and Pearson’s correlation coefficients. The results indicated that the most important factor determining the biological activity of South-Moravian lignite potassium humates is related to the nature of self-assemblies, while the chemical composition had no direct connection with the root growth of Zea mays seedlings. It was demonstrated a controlled processing that provided humic substances with different chemical and physicochemical properties and variable biological activity.
- Lignite humic substances
- Thermal analysis
- Biological activity
Humic substances (humics, HS) are refractory, dark-colored heterogeneous organic compounds produced in the decay of the total biota in the environment (Stevenson 1994). From the chemical point of view, they are a heterogeneous mixture of fragments of lignins, cellulose, suberins and cutins. Their unique structure makes them a versatile material with applications in industry, medicine, environmental protection, and agriculture. It is becoming clearer, that the presence of humics in soil is necessary for sustainable agriculture, due to their ability to condition the soil, enhance its stability and increase its resistance to erosion (Laker et al. 1993; Spaccini et al. 2002), ensure enhanced biological activity (Canellas et al. 2002; Canellas et al. 2008; Nardi et al. 2000a, b; Zandonadi et al. 2007) and obtain higher crop yields (Antošová et al. 2008; Brownell et al. 1987; Eyheraguibel et al. 2008). In addition, humics have the ability to sequestrate soil pollutants (Evdokimov and von Wandruszka 1998; Sanjay et al. 1999; Senesi and Loffredo 2001; von Wandruszka 2000), and may be used in soil remediation (Fava et al. 2004; Stehlíčková et al. 2009; von Wandruszka 2000).
The biological activity of humics has been recognized in 1917 (Bottomley 1917), while their hormone–like nature was reported later (Canellas et al. 2008; Nardi et al. 2002). Aguirre et al. (2009) noted that the biological activity of humics is based on their ability to promote the expression of selected genes encoding enzymes like FeIII chelate reductase, plasma membrane H+ATPase, and FeII high affinity transporter. Mora et al. (2010) questioned this “hormone-like” idea, since no cytokinins, gibberellins and indolacetic acid were found in humic acid samples. Instead, they hypothesized that humics enhance the activation of root plasma membrane H+ATPase, since this may cause significant changes in the root-to-shoot distribution of NO3– and therefore of cytokinins and polyamines.
Piccolo et al. (1992) showed that the humic fraction with the highest acid functionality and the smallest molecular size had the greatest effect on plant nitrate uptake and hormone-like activity. In contrast, neither the aliphatic nor the aromatic content of the extracts appeared to play a role in the biological activity (Nardi et al. 2000a, b, and 2002) confirmed those observations and concluded that the smaller molecular size fractions can be partially taken up by the plasmolemma of higher plant cells, whereas the larger fractions (> 3.5 kDa) interacted only with the cell walls. In contrast, Canellas et al. (2010) showed that the size fractions of vermicompost humics obtained by preparative HPSEC (High performance size exclusion chromatography) had similar biological activities. In the work of Vlčková et al. (2009), the highest biological activity of humics toward Zea mays (tested by the method of Antošová et al. (2008)), was observed for 35–175 kDa molecular weight fraction.
Lignite, i.e. low rank coal, has been recognized as a valuable source of humics (Kučerík et al. 2003). The content of humics can be increased by regeneration processes with nitric acid, potassium manganate (VII), sulfuric acid, or hydrogen peroxide (Berkowitz 1985, Rausa et al. 1994;Kučerík et al. 2003;Vlčková et al. 2009). However, understanding the influence of lignite regeneration on the physicochemical and biological behavior is still incomplete. The same holds true for optimization of the regeneration processes (e.g. regeneration agent, type and concentration, and regeneration time). Since regeneration is most effective in suspension with nitric acid or hydrogen peroxide (Kučerík et al. 2008a, b), the focus of the study is on these two oxidizing agents.
The aims of this work, therefore, are: (i) to elucidate the pertinent processes in South-Moravian lignite treatment; (ii) to test the obtained products from both chemical and physico-chemical perspectives; and (iii) to assess the influence of regeneration on their biological activity in vitro.
Lignite regeneration; extraction and preparation of humates
All the chemicals were obtained from LachNer Ltd., Neratovice, Penta Ltd., Chrudim, (Czech Republic) and SigmaAldrich Co., Steinheim (Germany). South Moravian lignite (kindly provided by Lignit Hodonín Ltd., Mikulčice, Czech Republic) was regenerated with two oxidizing agents – nitric acid (abbreviated as N) and hydrogen peroxide (abbreviated as P) in concentrations of 10, 20, 30, 40, 50, 65 vol% and 5, 10, 20, 30 vol%, respectively. The lignite:oxidizing agent ratio was 1:10 w/w (50 g of parental lignite in 500 mL of regeneration agent). Lignite was treated for 30 minutes at a temperature around 30°C in a glass beaker. For the 50 and 65 vol% nitric acid treatment a round bottom flask with a reflux Allihn condenser and a cooling bath were used, since the regeneration reactions were strongly exothermic. The mixture was filtered and the filtration cake of treated lignite was used for extraction of regenerated humate. A quantity of 40 g of lignite was subjected to extraction via a slightly modified process published by Swift (1996). It involved an alkaline extraction with a mixture of 0.5 mol L–1 sodium hydroxide and 0.1 mol L–1 sodium pyrophosphate. The lignite:agent ratio was 1:10 w/w. Separation was achieved by centrifugation for 15 min at 15°C and 4000 rpm with Rotina 46 R centrifuge (Andreas Hettich Ltd., Tuttingen, Germany), and precipitation by addition of concentrated hydrochloric acid. Further purification included removal of silicate residues with 5 vol% hydrofluoric acid and dialysis against deionized water through a SpectraPor 1000 Da cutoff dialysis membrane made of regenerated cellulose (Spectrum Labs Inc., Rancho Dominguez, CA, U.S.A.).
Humic acid from parental lignite.
Humic acid from lignite regenerated with nitric acid solution (N), the number means vol% concentration.
Humic acid from lignite regenerated with hydrogen peroxide (P) solution, the number means vol% concentration.
Potassium humate salt from parental lignite.
Potassium humate salt from lignite regenerated with nitric acid solution (N), the number means vol% concentration.
Potassium humate salt from lignite regenerated with hydrogen peroxide (P) solution, the number means vol% concentration.
Solid state analyses of humic acids
Elemental analyses of HA and RHA samples were conducted employing a Perkin Elmer 2400 CHNS/O Elemental Analyzer. The oxygen percentage was calculated as a difference between the sample weight and the C, H, and N content, taking into account the moisture and ash contents determined by thermogravimetry (see below).
The influence of regeneration on the thermooxidative stability of humics products was assessed by thermogravimetry. Prior to the analysis, the samples were dried for two weeks over sodium hydroxide, and then analyzed with a Q5000 IR TGA instrument (TA Instruments Inc., New Castle, DE, U.S.A.). The 100-μL platinum pans of the apparatus were used as sample holders, and the analysis was carried out using a 10°C∙min–1 temperature ramp from room temperature (RT) to 650°C, under a 50 mL∙min–1 flux of dry air.
Fourier transform infrared spectrometry
Infrared spectra were obtained using potassium bromide pellets technique, in which 1 mg of oven dried (105°C, 3 h) humic material (HA and RHA) was mixed with 200 mg of dried FTIR grade KBr. Spectra were measured with a Thermo Nicolet iS10 infrared spectrometer (Thermo Fisher Scientific Inc., Waltham, MA, U.S.A.). The instrument was set up with a resolution of 8 cm–1 and 64 scans per analysis. The spectra were processed using the Nicolet Omnic 8 software.
Liquid state analyses of humates
Dynamic light scattering
Dynamic light scattering measurements were obtained with a N4 Plus Submicron Particle Sizer equipped with He-Ne red laser of wavelength of 632.8 nm (Coulter Corp., Miami, FL, U.S.A.), calibrated using latex beads from the producer. Sample solutions of 250 mg∙L–1 were prepared in water and filtered through GN 0.2 μm filters (Millipore Corp., Billerica, MA). Unimodal Analysis Mode was used with a detection angle of 90°. Measurements were taken in 10 runs of 300 s each, at 25°C in a 1-cm quartz cuvette. Outlying values were excluded according to the Dean-Dixon test (Dean and Dixon 1951).
High performance size exclusion chromatography
High performance size exclusion chromatography (HPSEC) experiments were performed using an Ultimate 3000 Standard Chromatography Station (Dionex Inc., Sunnyvale, CA, U.S.A.), equipped with a BioSep S2000 600 × 7.8 mm column, and a BioSep Guard pre-column with a 0.2-μm stainless steel inlet filter (Phenomenex Inc., Torrance, CA, U.S.A.). The column was thermostated at 25°C, and a diode array detector was employed. The eluent was a 50 mmol∙L–1 solution of NaH2PO4∙H2O in MilliQ water adjusted to pH 7 by means of 1 M NaOH solution. The flow rate was set at 0.6 mL∙min–1. Samples were prepared as 0.6 mg∙mL–1 solutions of potassium humate dissolved in mobile phase, and 100 μL of the sample was injected. The calibration of the column was performed using poly(styrenesulphonate) standards of 194.2, 145, 32.9, 14.9, 6.53 and 0.91 kDa mass (Polymer Standards Service Ltd., Mainz, Germany). Calibration curves and results were obtained using Dionex Chromeleon, Microsoft Excel, and OriginLab software. The weight averaged (MW) and number averaged (MN) molecular weights of the humates were calculated according to the Mori and Barth (1999). For the purpose of comparison, an 1100 Series Chromatography Station (Agilent Inc., Santa Clara, CA, U.S.A.) equipped with quaternary pump and an RI detector was used with the same column and under identical conditions. Calibration was carried out using polysaccharide standards (of 404, 212, 112, 47.3, 5.9, 0.667 kDa mass, same purveyor).
In order to determine the amount of water of hydration bound by the humics, a high resolution ultrasonic spectrometer (HRUS 102, Sonas Technologies Ltd., Dublin, Ireland) was employed. Measurements of ultrasonic velocity for each sample were conducted in two independent quartz cells, stirred at 600 rpm with bottom and top stirrers. The system was kept at 25.00 ± 0.02°C, using a water bath. The instrument was calibrated with deionized water at 25.00 ± 0.02°C. Ultrasonic experiments are based on the determination of difference in ultrasonic velocities in cell 1 (1 mL of sample solution) and cell 2 (1 mL of pure water) (the U12 value). The concentration of the sample (potassium humate) was always 250 mg∙L–1, measurements of ultrasonic velocity were repeated three times at three different frequencies (5478, 7850 and 12196 kHz).
High resolution density measurements were performed for the same solutions, in triplicates, with a DMA 4500 density meter (Anton Paar Ltd., Graz, Austria).
Resulting compressibility (β) and hydration of the humates were calculated according to equations published by Davies et al. (1982), which assumes that the compressibility of hydration water is much lower than that of non-interacting solvent and of the humic substances themselves.
The common maize Zea mays CEKLAD 235 species (Oseva Bzenec Ltd., Czech Republic) was selected in the biological studies as treated seed for its universality, easy availability, high durability, and good germination percentage. The seeds were treated for 5 min in a 50 mM sodium hypochlorite (NaClO) solution and then washed and immersed in deionized water for 4 h to precondition them for germination. The germination was conducted in wet Tork Wiper 430 paper laboratory towels (Thermo Fisher Scientific Ltd., Pardubice, Czech Republic), into which the seeds were rolled, separated by approximately 3 cm gaps. The paper rolls with seeds were put in a glass beaker containing deionized water and left to germinate for 2 days in the dark at 28 ± 2°C, employing a BT-120 Biological Thermostat (Laboratorní přístroje Praha Ltd., Prague, Czech Republic).
Biological activity assessment
The germinated seeds and grown plants were weighed and the differences were recorded in terms of total mass increment. In addition, the lengths of the roots of five marked germs/plants were measured before and after the growing experiment, and the differences in root growth were recorded. The roots of these five plants were also scanned with a Perfection 2480 Photo Scanner (Epson Deutschland Ltd., Meersbuch, Germany) against a black background. The resulting images (300 × 300 dpi) were captured by means of HarFA (Harmonic and Fractal image Analyzer) software (http://www.fch.vutbr.cz/lectures/imagesci) (Zmeškal et al. 2001), which was previously shown to be suitable for the evaluation of images from biological experiments (Tománková et al. 2006) and neuroscience (Wu et al. 2010). The scanned images were saved as bitmaps and subjected to 2D Wavelet Analysis. Overall results of biological activity were assessed by means of R Environment for Statistical Computing software (http://www.R-project.org) (R Development Core Team 2012). The root growth increments for the particular 15 samples were statistically compared using a one-way analysis of variance (ANOVA). Post-hoc multiple comparisons were conducted using Tukey’s HSD (Honestly Significant Difference) test. The assumptions were evaluated using Levene’s test and the Shapiro-Wilk’s test. Slight discrepancies vis-à-vis the normality assumptions were disregarded, as they were considered to have minimal impact on the results.
Rather than plants stress tests, we focused on the determination of sugars and protein in the seedlings. After the image analysis, the seedlings were dried in a laboratory dryer for three days at 60°C. The total dry mass was divided for determination of sugars and proteins. The sugar content was determined polarimetrically using the customary Ewers polarimetric method (Kennedy et al. 1995). The proteins were determined by the Kjeldahl method (McClements 2001) for the determination of total nitrogen. An automatic Kjeldahl analyzer Kjel-Tec™ 2100 (FOSS Inc., Hillerød, Denmark) was used.
Lignite treatment and humate regeneration
Results of solid humic acids analyses
FTIR Relative peak intensity ratios
Solid state analyses of humic acids
Results of the elemental analysis are presented in Table 2. A notable feature of the lignite treatment was the variation in nitrogen content of the regenerated humic acids – especially through treatment with 20–40 vol% HNO3. The increase in nitrogen content in samples RHA20N to RHA40N, and the slight decrease in RHA50N and RHA65N confirmed the previous observation about the concentration effect on the yield (Kučerík et al. 2003). The HNO3 treatment resulted in producing of nitrogen enriched humic substances, with the exception RHA10N. This is in contrast to the results reported previously by Čtvrtníčková et al. (2011) and Vlčková et al. (2009) who reported an N increase in the regenerated products obtained in a similar process. The reason for this discrepancy is not entirely clear; it might be related to variation of humics from batch to batch within the same source. The HNO3 treated samples showed also a higher oxygen content and larger O/C ratio, indicating an increase in the number of oxygen bearing groups. Comparison with humic standards provided by International Humic Substances Society (IHSS 2013) shows that the samples from the nitric acid treated lignite were, in terms of N content, more reminiscent of Elliot Soil HA than of Leonardite HA. HA obtained from H2O2 treated lignite had lower oxygen content and O/C ratio, higher H content and H/C ratio and lower N content. Since the O content was calculated as a difference, the determined value may include traces of S and P.
FTIR spectra of all HA and RHA materials were comparable to those reported in the literature (Stevenson 1994), examples are reported in Figure 2. The incorporating of nitrogen atoms into the humic structure by the HNO3 lignite treatment was confirmed by 1540–1520 cm–1 peaks due to the Ar–NH/NO2 moiety (RHA20N–RHA65N samples). The strong effect of concentrated HNO3 was corroborated by the 1333 cm–1 peak of CO–NH and NO2 (in RHA40N–RHA65N samples). In the RHA20P and RHA30P samples, the 1269 cm–1 peak of aromatic/R–COOR moieties was also present. To distinguish between parental HA and the RHA samples, we calculated the intensity ratio of the 2930 and 1610 cm–1 absorption bands (i.e. aliphatic/aromatic ratio) (Table 2). To assess the lignite modification by HNO3, we determined also the intensity ratios of the absorption bands at 1550–1520 cm–1 (amidic) and 1610 cm–1 (aromatic). All the regenerated samples gave a slightly higher aliphatic/aromatic ratio than parental HA. The highest value was obtained for RHA40N, followed by the samples RHA65N, RHA50N, RHA20N and RHA5P. The lowest aliphatic content (but still higher than the HA sample) appeared in the RHA30P sample.
Liquid state analyses
Results of high performance size exclusion chromatography as detected by DAD and RID
MN(280 nm DAD) [g∙mol–1]
MW(280 nm DAD) [g∙mol–1]
PDI (280 nm DAD) 
PDI (RID) 
Biological activity results of humic samples and AtonikPro (Root growth increment, plant mass increment and root division (Perimeter); averages with respective standard deviations
Root growth increment (2 × 5 roots)
Mass increment (2 × 30 plants)
K[BW] – root division (Perimeter) (2 × 5 roots)
Starch content (30 plants dry mass)
Protein content (30 plants dry mass)
16 ± 3
27 ± 0.01
1524 ± 5
7 ± 1
29 ± 6
1180 ± 6
40 mg L–1
19 ± 2
30 ± 6
2573 ± 6
40 mg L–1
20 ± 3
29 ± 0.4
2158 ± 8
40 mg L–1
20 ± 3
28 ± 5
1881 ± 4
40 mg L–1
20 ± 4
25 ± 2
2792 ± 6
40 mg L–1
18 ± 2
26 ± 0.3
2405 ± 6
40 mg L–1
21 ± 2
26 ± 2
2944 ± 6
40 mg L–1
19 ± 4
29 ± 9
2663 ± 7
40 mg L–1
20 ± 3
31 ± 3
2064 ± 6
40 mg L–1
19 ± 4
27 ± 0.5
2253 ± 9
40 mg L–1
21 ± 3
30 ± 3
2477 ± 8
40 mg L–1
21 ± 2
31 ± 5
2792 ± 7
KRHA10N + AtonikPro
40 mg L–1+ 0.04 vol%
7 ± 1
38 ± 7
1181 ± 3
KRHA30P + AtonikPro
40 mg L–1+ 0.04 vol%
7 ± 2
32 ± 2
1144 ± 3
The root divisions for the 15 samples were statistically compared in the same way and the differences among the samples were again found to be highly significant. The treatments KHA, KRHA30N, KRHA50N, KRHA65N, and KRHA30P lead to significantly larger root divisions (p-values 0.017, <0.001,<0.001, <0.006 and <0.001 respectively) compared to the control group. Furthermore, the results for KRHA30P were only borderline non-significant (p-value 0.051), and could also be included in the previous group. Finally, the same considerations regarding the test results applied here. The results for KHA and other treatments (except for AtonikPro and Control) did not differ significantly, even though the sample means and medians varied. The highest mass increment was observed in the plants grown in the mixture of 40 mg∙L–1 KRHA10N and 0.04 vol% of AtonikPro (sample 13).
The treatment of lignite had an effect on the starch and proteins content of the maize roots. Slightly higher starch contents were found in plants grown in AtonikPro, KHA, KRHA10N and KRHA65N solutions, while the use of AtonikPro, KRHA5P and KRHA10P led to increased protein content (see Table 3 for details).
All of the tested humates exhibited some degree of biological activity with regard to stimulating the growth of maize plants. Materials in both lower and higher molecular weight ranges (e.g. KRHA50N and KRHA30P, respectively) gave statistically significant positive results. Works by Canellas et al. (2002) or Zandonadi et al. (2007) have shown that chemical composition, rather than molecular weight distribution, is the prime factor in growth stimulation by humates. Most of the regenerated humates generally produced higher root growth (Figure 7) and higher root division (Figure 8), than native humate (KHA) extracted from the parental lignite, it should be noted, however, that neither root growth, nor root division showed enhancements that were statistically significant in all ten regenerated materials, as compared to native KHA. This is in line with the prediction by Vlčková et al. (2009) that oxidation of parental lignite leads to higher biological activity of the resulting humate product. Although the details of the oxidative mechanism are not known yet, it may be suggested that the introduction of additional carboxyl, hydroxyl, amino, and nitro groups play a role. As for root division, higher median values (relative to KHA) were observed for KRHA30N, KRHA50N and KRHA30P.
Table 4 shows that humates regenerated from lignite with nitric acid had positive effects on the starch content of the plants, while selected hydrogen peroxide regenerated humates showed increases in protein content. AtonikPro gave positive results in both cases, presumably because of its nitrophenolate nature (Hejnák 2010).
Principal component analysis and correlations
PCA of KRHA samples (data not shown) did not show significant variability in the data, with the first two PC values accounting for only 58% of data variability. The only significant differences were noted for KRHA40N, KRHA50N, and KRHA30P. The KRHA40N sample had the highest M w and PDI (280 nm) values, while KRHA30P and KRHA50N showed more significant growth increments and root division.
The correlation coefficients shown in Table 4 confirmed that in terms of aliphatic, aromatic and amidic groups’ content, the FTIR results correlated well with the results for C, H, O and N content obtained from elemental analysis. The information from thermogravimetry, giving a negative correlation between O/N content and 1st TGA onset temperature, also confirmed that humic acid regeneration reduced the thermal stability of the materials (Gonet and Cieslewicz 1998). Generally, the more H was present in the humic sample, the lower the amount of ash produced in the thermogravimetric analysis became. Interestingly, the average aggregate particle size (AAPS) of the humates measured by DLS appeared to have no correlation with the molecular weights assessed by DAD and RID in the HPSEC separations. Likewise, no significant correlations of density and ultrasonic velocity with other parameters were observed. As for the HPSEC results, the MN values obtained by means of the DAD detector (at 280 nm) were in a good agreement with those obtained by RID (r = 0.844, p < 0.05). Further, there was no correlation between MN and MW values obtained by DAD, while the correlation of both obtained by RID was significant and positive (r = 0.893, p < 0.05). This can be ascribed to the fact that the different detectors were sensitive to different moieties. It should be noted that the results of KRHA40N (mainly the DAD HPSEC MW result) deviated strongly. No explanation is forthcoming for this circumstance, and it should probably be set aside as an artifact.
Inspection of the biological activities revealed that there was no correlation between root division and AAPS or root growth and AAPS. This indicates that these biological parameters were not affected by the aggregate size of the humates dissolved in the growth solution. The molecular weights, in particular MN obtained with the DAD, did show a moderate correlation with root growth (r = 0.617, p < 0.05), while MN values obtained with the RID were similarly correlated with plant mass (r = 0.772, p < 0.05). Positive correlations were also found for MW obtained with the RID (r = 0.627, p < 0.05). The DAD results showed no correlation with mass increment (MN) for the entire set of 30 plants, while slightly negative borderline nonsignificant trend (r = -0.598, p < 0.1, p = 0.052) was found for MW. Positive correlations for molecular weight with root growth increment and plants mass increment were in line with previous findings (Canellas et al. 2010; Nardi et al. 2002). It also appeared that humates containing light absorbing groups induced root growth in Zea mays, with a correlation of r = 0.694, p < 0.05.
Pearson’s correlation coefficients of chemical composition with humates’ biological activity
Elemental analysis [at%]
FTIR relative peak intensity ratios
K[BW] Root division
Pearson’s correlation coefficients of molecular weight distribution fractions (detected by DAD at 280 nm) with humates’ biological activity
> 100 kg∙mol–1
K[BW] Root division
These results are in agreement with the findings by Vlčková et al. (2009) and the results of Canellas et al. (2010). Our findings do not agree with Nardi’s presumption (Nardi et al. 2002), that the greatest biological activity of humates lies with molecular weight fractions up to 3.5 kDa. Our work, however, supports later reports that showed the importance of higher molar weight humates (Canellas et al. 2010; Vlčková et al. 2009; Zandonadi et al. 2007).
Lignite, in particular the South-Moravian lignite, represents a unique source of humic substances, but its exploitation as a raw material for environmental and agricultural scenarios is still limited. As demonstrated in this and earlier work, regeneration presents a way to increase the recovery of humic substances from lignite, and also allows for the tuning of their properties. The cost-benefit analysis was beyond the scope of this paper; however, the regeneration agents may be preferably recycled into the commercial fertilizer production. This may open a pathway to superior results with the use of these materials in agricultural applications. However, full control of these properties and biological activity still remains a challenge.
The Ministry of Education, Youth and Sports of the Czech Republic is acknowledged for funding of this research in terms of the MSM0021630501 research project, as well as for the support of the first author’s internship at the University of Idaho in terms of FreeMovers grant. Dr. Noel E. Palmer (University of Idaho, U.S.A.) and Dr. Karolína Benešová (Research Institute of Brewing and Malting, Czech Republic) are acknowledged for helpful discussions. Authors thank the companies Lignit Ltd. Mikulčice/UVR Mníšek pod Brdy, Inc., Czech Republic (raw lignite), ArystaLifeScience Czech Republic (AtonikPro) and Oseva Bzenec Ltd., Czech Republic (CEKLAD 235 corn) for providing their samples for free.
This study was also supported by the CEP Project LO1211 “Materials Research Centre at FCH BUT – Sustainability and Development” from Ministry of Education, Youth and Sports of the Czech Republic.
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