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Výbohová, E., Geffertová, J., and Geffert, A. (2018). "Impact of steaming on the chemical composition of maple wood," BioRes. 13(3), 5862-5874.

Abstract

Chemical changes resulting from the thermal treatment of maple wood (Acer platanoides L.) through various steaming techniques were evaluated. Main wood components were isolated and characterized from the maple wood samples after steaming. Then, the isolated holocellulose and dioxane lignin were analyzed using ATR-FTIR spectroscopy. The effects of an increase in temperature and extension of the steaming period were seen primarily in the holocellulose and extractives contents, and less in the cellulose and lignin components. Certain steaming methods resulted in an increase in chemical composition, while others saw a decrease. The cellulose content of steamed maple wood was not considerably altered; however, the cellulose crystallinity did increase. The slight changes observed in this study can be attributed to several concurrent effects. While the lignin content in steamed maple wood showed only minimal changes, there were several changes in the structure of the lignin macromolecule. Demethoxylation, the decrease in the ratio of syringyl-propane to guaiacyl-propane units, and the formation of new alpha-C=O bonds were also observed. The hydrothermal treatment of wood also resulted in color changes of wood samples; the intensity of the change depended on the intensity of the treatment.


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Impact of Steaming on the Chemical Composition of Maple Wood

Eva Výbohová, Jarmila Geffertová, and Anton Geffert *

Chemical changes resulting from the thermal treatment of maple wood (Acer platanoides L.) through various steaming techniques were evaluated. Main wood components were isolated and characterized from the maple wood samples after steaming. Then, the isolated holocellulose and dioxane lignin were analyzed using ATR-FTIR spectroscopy. The effects of an increase in temperature and extension of the steaming period were seen primarily in the holocellulose and extractives contents, and less in the cellulose and lignin components. Certain steaming methods resulted in an increase in chemical composition, while others saw a decrease. The cellulose content of steamed maple wood was not considerably altered; however, the cellulose crystallinity did increase. The slight changes observed in this study can be attributed to several concurrent effects. While the lignin content in steamed maple wood showed only minimal changes, there were several changes in the structure of the lignin macromolecule. Demethoxylation, the decrease in the ratio of syringyl-propane to guaiacyl-propane units, and the formation of new -C=O bonds were also observed. The hydrothermal treatment of wood also resulted in color changes of wood samples; the intensity of the change depended on the intensity of the treatment.

Keywords: Maple wood; Steaming; Extractives; Holocellulose; Cellulose; Lignin; FTIR spectroscopy

Contact information: Department of Chemistry and Chemical Technologies, Technical University in Zvolen, T.G. Masaryka 24, 960 53 Zvolen, Slovakia; *Corresponding author: geffert@tuzvo.sk

Introduction

The steaming of wood is a hydrothermal treatment that uses water vapor. It causes structural changes in the wood, as well as changes in the wood’s chemical, physical, and mechanical properties. The wood after hydrothermal treatment is less sticky, with fewer cracks, faster drying, a more pleasant and uniform color, increased durability and strength, and better stability (Melcer et al. 1983). The extent of these changes depends on different variables of the hydrothermal treatment (e.g., temperature, pressure, and duration).

The hydrothermal treatment of wood at low temperatures does not cause marked chemical or physico-chemical changes to the main components of the wood. More notable chemical changes are correlated with an increased duration of hydrothermal treatment (Melcer et al. 1983; Kačík et al. 1989; Solár and Melcer 1990, 1992; Kačík et al. 1993; Laurová et al. 2004). Increasing the temperature of the hydrothermal action above 80 °C increases the chemical and physico-chemical changes throughout the wood. At the same time, its mechanical strength decreases in correlation with the intensity of the treatment (Melcer et al. 1983; Kačík et al. 1989, 1990; Solár and Melcer 1990).

The acidity of the environment during hydrothermal treatment increases gradually because of the splitting-off of acetyl and formyl groups of hemicelluloses. Additionally, the formation of organic acids, such as acetic and formic acid, lowers the pH of the condensate.

This lowering of pH catalyzes various hydrolysis, dehydration, degradation, and condensation reactions of the carbohydrates and their products. Hexose dehydration leads to 5-hydroxymethyl-2-furaldehyde formation. 2-Furaldehyde is formed by degradation of pentoses, and further decomposition of furan derivatives produces levoleic and formic acids (Jönsson et al. 2013).

In native cellulose, monomers of glucose form microfibrils that are stabilized by hydrogen bonds, making the macromolecule highly crystalline and difficult to hydrolyze (Trajano and Wyman 2013). In contrast, hemicelluloses are heteropolysaccharides that have shorter, branched chains of saccharides. Because of their amorphous structures and the presence of acetyl groups, hemicelluloses are the most thermally labile of wood’s polymeric components (Hill 2006).

Degradation of non-cellulosic polysaccharides leads to the loss of holocellulose in hydrothermally treated wood (Kačík et al. 1990, 2001; Laurová et al. 2004). Studies by Mercer et al. (1989) and Kačík et al. (1996) confirm that the hydrothermal treatment of wood first results in a relatively rapid release of hemicelluloses, while the vulnerability to hydrothermal treatment varies between wood species. In general, hardwoods have a higher proportion of hemicelluloses, so they have a higher content of acetyl groups compared with softwoods. Furthermore, hardwood hemicelluloses are richer in pentosans, which are more susceptible to degradation than hexosans. Therefore, hardwoods are less thermally stable than softwoods (Hill 2006).

The main components of maple wood are interconnected to form the “lignin-saccharide complex”. Lignocellulosic materials have chemical bonds especially between lignin and lateral branches of hemicelluloses (Volynets et al. 2017). According to Chen et al.(2010), lignin-free xylan is released during the initial phase of hydrothermal treatment, while lignin-bound xylan is dissolved in the later phase.

The carbohydrate and aromatic components of wood (i.e., lignin) also undergo changes during hydrothermal treatment. The degree of change depends primarily on the temperature and action time. This process demonstrates the presence of syringaldehyde and vanillin in condensates of steaming wood (Laurová et al. 2004).

Relevant works indicate that the intensity of structural changes in the lignin of different wood species treated under approximately the same hydrothermal conditions can vary (Kačík et al. 1989, 1990; Solár and Melcer 1992).

The high temperatures of hydrothermal treatment cause depolymerization of the lignin because of the hydrolysis of the -alkyl-aryl ether linkages. High temperatures and lengthy treatment can also initiate condensation reactions. Hydrothermal treatment causes the formation of new chromophore structures in the lignin, which changes the color of the treated material (Solár 1997). Structural change in the aromatic ring of the lignin macromolecule may occur because of oxidation, condensation, or conjugation of the double-bonded aromatic rings, while the content of carbonyl and carboxyl groups increases (Košíková et al. 1976).

This study sought to evaluate the various chemical changes that maple wood undergoes during a variety of steaming treatments. Conventional analytical methods were used to isolate the wood components to determine their chemical composition. The isolated holocellulose and dioxane lignin were analyzed using ATR-FTIR spectroscopy. The spectral analysis of individual wood components is critical for understanding the behavior of wood species during steam treatments.

Experimental

The samples of maple wood (Acer platanoides L.) supplied from an industrial plant Sundermann Ltd. (Banská Štiavnica, Slovakia) were used to investigate chemical changes that occurred in different steaming treatments.

Each maple wood sample had the dimensions 30 X 75 X 510 mm. These samples were thermally treated by the steam in a pressure autoclave APDZ 240 (Dzurenda 2018). Treatment temperature and duration for the maple wood samples are given in Fig. 1. The temperature of the steam and duration of the processes are shown in Table 1.

The fraction of sawdust from 0.5 mm to 1.0 mm from completely disintegrated boards of the original maple wood and wood after steaming (including surface and center part) were used to monitor the chemical changes.

Fig. 1. Modification of maple wood samples with steam (according to Dzurenda 2018)

Table 1. Thermal Treatment of Maple Wood

Select chemical characteristics were measured in the samples before steam treatment and after the various steam treatments. These characteristics are listed in Table 2.

Table 2. Select Chemical Characteristics

The isolated holocellulose and dioxane lignin were analyzed using ATR-FTIR spectroscopy. The measurements were carried out using a Nicolet iS10 FTIR spectrometer equipped with a Smart iTR attenuated total reflectance (ATR) sampling accessory with a diamond crystal (Thermo Fisher Scientific, Madison, WI). The resolution was set at 4 cm− 1 for 32 scans for each steaming technique and following analysis. The wavenumber range varied from 4000 cm− 1 to 650 cm− 1. Six analyses were performed per sample. OMNIC 8.0 software (Thermo Fisher Scientific, Madison, WI) was used to evaluate the spectra.

Results and discussion

The chemical composition of maple wood varies depending on the species of wood, the locality, and the methods of determination. Holocellulose content ranges from 79% to 86.9%, cellulose from 38.3% to 47.4%, lignin from 20.7% to 25.3%, and extractives from 1.9% to 2.9% (Fengel and Wegener 1984; Baloghová and Kačík 1996; Kačík et al. 1996). According to the results of Baloghová and Kačík (1996), maple wood holocellulose is composed primarily of D-glucose and D-xylose, while other carbohydrates (e.g., L-rhamnose, L-fucose, L-arabinose, D-mannose) are present in small amounts.

The results of the chemical analysis of the samples of the original maple wood and post-treated wood for each technique are shown in Fig. 2.

Fig. 2. Chemical characteristics of maple wood before and after steaming. Note that “0” signifies wood before steam treatment

Based on the chemical characteristics, it can be concluded that the increased intensity of the treatment was reflected primarily in the changes in holocellulose and extractives contents, and less in the contents of cellulose and lignin.

The content of extractives slightly decreased with increasing temperature and extended steaming period for modes I and II, resulting in their release or decomposition. In the most extreme steaming treatment (mode III), when temperature increased from 130 °C to 140 °C, the content of extractives increased by 33% compared with the original content and by 53% relative to the mode II conditions. This increase has previously been shown to be related to the extraction of decomposition products of other wood components (hemicelluloses, water soluble lignin, and amorphous cellulose). Baloghová and Kačík (1996) reported increased extractives in maple wood during prehydrolysis for 6 h at 160 °C, rising from 2.92% to 16.25%.

The average polysaccharide content in maple wood decreased slightly in modes I and II compared with untreated wood, and the decrease in mode III was more dramatic, reaching approximately 8%.

The FTIR analysis of isolated holocellulose was performed to characterize the changes in polysaccharides in the maple wood after hydrothermal treatment. Characteristic absorption bands of both cellulose and hemicellulose were found in the obtained spectra and assigned according to the literature, as shown in Table 3 (Hon and Shiraishi 2001; Pandey and Pittman 2003). The results are further depicted in Fig. 3.

Table 3. Spectral Records of Examined Holocellulose Samples

Fig. 3. Spectra of holocellulose samples isolated from maple wood

From the evaluation of the obtained spectral records, it can be stated that during the hydrothermal treatment of maple wood, the degradation of more labile hemicelluloses was observed. This is evident from the decrease in the intensity of absorption bands at 1732 and 1243 cm-1 (Fig. 4). This decrease is 15.1% and 10.7%, respectively, of the original intensity of said absorption bands.

Fig. 4. The decrease in intensity of absorption bands at 1732 and 1243 cm-1

According to Fengel (1966), temperature influences first the partial degradation of long hemicellulose chains into shorter ones and then the degradation through monosaccharides to volatile products. At the same time, ongoing deacetylation affects the thermal stability of hemicelluloses.

Cellulose is the most stable against hydrothermal action in the range of given temperatures. The cellulose content in maple wood under the influence of steaming did not change considerably (Fig. 2), and its slight variation in individual modes is the result of several concurrent effects: degradation of hemicelluloses or amorphous cellulose, or condensation reactions.

The results of Melcer et al. (1989) confirmed that during the hydrothermal treatment of the wood, there is first a relatively rapid release of hemicelluloses, then the slower release of the water-soluble part of the lignin, and later part of the amorphous cellulose.

Some authors reported a relative increase in cellulose with a prolonged hydrothermal treatment at a temperature range of 80 °C to 140 °C, caused by the loss of hemicellulose and lignin components (Melcer et al. 1989; Solár and Melcer 1990). According to the results of Kačík (1997), the content of cellulose in hydrothermally treated wood did not usually change at temperatures up to 100 °C, but above 100 °C it increased because of the degradation of hemicelluloses, which in maple wood were mostly D-xylose and D-glucose.

From comparison of the FTIR spectra of holocellulose (Fig. 3), a decrease in the ratio of intensities of absorption bands A1333/A1316was observed (Fig. 5). According to Colom et al. (2003), the decrease in this ratio signifies an increase in the cellulose crystallinity. These changes may result from the faster degradation of the amorphous cellulose regions, but also from the reorganization of the quasi-crystalline cellulose regions at higher temperatures (Bhuiyan et al.2000).

Fig. 5. Change in the ratio of A1333/A1316

The resulting average values of lignin content in steamed maple wood show only minimal changes (Fig. 2). Solár (1997) stated that depolymerization, reduction in the degree of lignin crosslinking, and the disappearance of bonds in the lignin-polysaccharide system predominate in the early stages of hydrothermal wood treatment. Laurová et al. (2004) showed the presence of syringaldehyde and vanillin in the condensates of the steamed wood, which indicates the ongoing change of the aromatic part of wood lignin.

Figure 6 shows a comparison of ATR-FTIR spectra of dioxane lignin isolated from original and hydrothermally treated (mode III) wood samples. It reflects changes in lignin structure caused by treatment under extreme conditions.

Fig. 6. Comparison of ATR-FTIR spectra of dioxane lignin

A decrease in the intensity of absorption bands can be observed in the region 3040 cm-1 to 2760 cm-1. These bands are attributed to symmetric and asymmetric stretching vibrations of C-H in -OCH3and –CH2 (Hon and Shiraishi 2001; Karmanov and Derkacheva 2013). The decrease in intensity is caused by demethoxylation of the lignin macromolecule during hydrothermal treatment. Furthermore, after treatment, a decrease in the ratio of syringyl-propane to guaiacyl-propane units was observed (Fig. 7). The partial removal of –OCH3 groups and the preferential removal of syringyl to guaiacyl units in various hardwood species during autohydrolysis and steam explosion, respectively, were discussed in other works (Chua and Wayman 1979; Martin-Sampedro et al. 2011).

Fig. 7. Change in the ratio of syringyl and guajacyl units

Other findings from the comparison of the FTIR spectra of lignin include the shift of the maximum absorption band, which is attributed to unconjugated C=O bonds, to a lower wavenumber as a result of treatment, i.e., from 1724 cm-1 to 1718 cm-1. According to Chen et al. (2012), this result suggests the formation of new -C=O bonds in lignin’s structure, which can contribute to the darkening of treated wood.

Fig. 8. Color changes in the original maple wood (0) after various steaming modes

The hydrothermal treatment of wood also resulted in color changes in the wood samples. The intensity of the color change depended on the severity of the treatment conditions. The photo of the disintegrated samples in Fig. 8 shows the color changes of the original and post-treated maple wood samples.

The mechanism of color change is complex, and many overlapping reactions of the basic components of wood and their decomposing products are involved (Solár 1997). Color changes are related to reactions of polysaccharide degradation products such as oxidation, dehydration, and condensation (oxidation of 2-furaldehyde, carbohydrates, and pectin reactions). They are also related to the chemical changes in lignin (quinone methide structures; free radicals; formation of new chromophoric groups; increase in phenolic hydroxyl groups) and extractives (color complexes of extracts of phenolic nature).

Similar color changes have been documented by many authors in their works on the hydrothermal treatment of various tree species by steaming or prehydrolysis (Melcer et al. 1983; 1989; Kačík 1997; Solár 1997; Dzurenda 2014; 2018; Barcík et al. 2015; Kučerová et al.2016; Geffert et al. 2017).

Conclusions

  1. Increases in temperature and duration of the steaming treatment primarily affected the holocellulose and extractives contents, and less so the contents of cellulose and lignin.
  2. The decreased extractives content from steaming treatments modes I and II was a result of their release into the condensate or decomposition. However, after the mode III steam treatment, the extractives content increased by 33% compared with the original content and by 53% relative to the mode II conditions. This increase is already related to the extraction of decomposition products of other wood components.
  3. The average polysaccharide ratio in maple wood decreased slightly after modes I and II treatments compared with the original sample, and decreased more sharply after mode III, by approximately 8%. The decrease in content of polysaccharides was due to the degradation of more labile hemicelluloses.
  4. Cellulose is the most stable against hydrothermal action in the range of given temperatures, as its content did not change considerably after steam treatment. The cellulose crystallinity did increase during steaming.
  5. The lignin content in steamed maple wood showed only minimal changes because depolymerization, or the reduction in the degree of lignin crosslinking and the disappearance of bonds in the lignin-polysaccharide system, predominate in the early stages of hydrothermal wood treatment. However, there were several changes in the structure of the lignin macromolecule. Demethoxylation, the decrease in the ratio of syringyl-propane to guaiacyl-propane units, and the formation of new -C=O bonds were observed.
  6. The hydrothermal treatment of wood also resulted in color changes in the wood samples, relative to the severity of the treatment conditions.

ACKNOWLEDGMENTS

This work was supported by the Slovak Scientific Grant Agency VEGA under contract No: 1/0563/16.

References CITED

ASTM Standard D 1106 – 96 (1998). “Standard test method for acid insoluble lignin in wood,” ASTM International, West Conshohocken, PA (TAPPI T T-13m-54).

ASTM Standard D 1107 – 96 (Re-approved 2001). “Standard test method for ethanol-toluene solubility of wood,” ASTM International, West Conshohocken, PA (TAPPI T 204 os-76).

Baloghová, D., and Kačík, F. (1996). “Zmeny sacharidického podielu javorového dreva pri predhydrolýze [Changes in saccharide content of maple wood in pre-hydrolysis],” in: Selected Processes in the Chemical Processing of Wood, Technical University in Zvolen, Zvolen, Slovakia, pp. 187-192.

Barcík, Š., Gašparík, M., and Razumov, E. Y. (2015). “Effect of thermal modification on the colour changes of oak wood,” Wood Res.60(3), 385-396.

Bhuiyan, T. R., Hirai, N., and Sobue, N. (2000). “Changes of crystallinity in wood cellulose by heat treatment under dried and moist conditions,” J. Wood Sci. 46(6), 431-436. DOI: 10.1007/BF00765800

Chen, X., Lawoko, M., and Heiningen, A. (2010). “Kinetics and mechanism of autohydrolysis of hardwoods,” Bioresource Technol. 101(20), 7812-7819. DOI: 10.1016/j.biortech.2010.05.006

Chen, Y., Gao, J., Fan, Y., Tshabalala, M. A., and Stark, N. M. (2012). “Heat-induced chemical and color changes of extractive-free black locust (Robinia pseudoacacia) wood,” BioResources 7(2), 2236-2248. DOI: 10.15376/biores.7.2.2236-2248

Chua, M. G. S., and Wayman, M. (1979). “Characterization of autohydrolysis aspen (P. tremuloides) lignins. Part 1. Composition and molecular weight distribution of extracted autohydrolysis lignin,” Can. J. Chem. 57(10), 1141-1149. DOI: 10.1139/v79-187

Colom, X., Carrilo, F., Nogués, F., and Carriga, P. (2003). “Structural analysis of photodegraded wood by means of FTIR spectroscopy,” Polym. Degrad. Stabil. 80(3), 543-549. DOI: 10.1016/S0141-3910(03)00051-X

Dzurenda, L. (2014). “Sfarbenie bukového dreva v procese termickej úpravy sýtou vodnou parou [The colour of beechwood in the process of thermal treatment with water vapor],” Acta Facultatis Xylologiae56(1), 13-22.

Dzurenda, L. (2018). “The shades of color of Quercus robur L. wood obtained through the processes of thermal treatment with saturated water vapor,” BioResources 13(1), 1525-1533. DOI: 10.15376/biores.13.1.1525-1533

Fengel, D. (1966). “Über die Veränderungen des Holzes und seiner Komponenten im Temperaturbereich bis 200 °C – Zweite Mitteilung: Die Hemicellulosen in unbehandeltem and in thermisch behandeltem Fichtenholz [About changes in wood and its components in the temperature range up to 200 °C- Second communication: Hemicelluloses in untreated and thermally treated spruce wood],” Holz als Roh- und Werkstoff 24(3), 98-109. DOI: 10.1007/BF02608355

Fengel, D., and Wegener, G. (1984). Wood: Chemistry, Ultrastructure, Reactions, Walter de Gruyter, Berlin, Germany.

Geffert, A., Výbohová, E., and Geffertová, J. (2017). “Characterization of the changes of colour and some wood components on the surface of steamed beech wood,” Acta Facultati Xylologiae 59(1), 49-57. DOI: 10.17423/afx.2017.59.1.05

Hill, C. A. S. (2006). Wood Modification: Chemical, Thermal, and Other Processes, John Wiley & Sons, Chichester, United Kingdom.

Hon, D. N., and Shiraishi, N. (2001). Wood and Cellulosic Chemistry,Marcel Dekker, New York, NY.

Jönsson, L. J., Alriksson, B., and Nilvebrant, N. O. (2013). “Bioconversion of lignocellulose: Inhibitors and detoxification,” Biotechnol. Biofuels 6(1). DOI: 10.1186/1754-6834-6-16

Kačík, F. (1997). Vplyv teploty a vlhkosti na zmeny sacharidov [The influence of temperature and humidity on carbohydrate changes], Technical University in Zvolen, Zvolen, Slovakia.

Kačík, F. (2001). Tvorba a chemické zloženie hydrolyzátov v systéme drevo – voda – teplo [Creation and chemical composition of hydrolysates in the wood – water – heat system], Technical University in Zvolen, Zvolen, Slovakia.

Kačík, F., and Solár, R. (2000). Analytická chémia dreva [Analytical Chemistry of Wood], Technical University in Zvolen, Zvolen, Slovakia.

Kačík, F., Solár, R., and Melcer, I. (1989). “Štúdium hydrolyzátu po hydrotermickej úprave bukového dreva (Fagus silvatica L.), I. časť [Study of hydrolysate after hydrothermal treatment of beech wood (Fagus silvatica L.), Part I],” in: Zborník vedeckých prác Drevárskej fakulty [Proceedings of the Scientific Works of the Faculty of Wood Sciences and Technology], Technical University in Zvolen, Zvolen, Slovakia, pp. 35-45.

Kačík, F., Solár, R., and Melcer, I. (1990). “Štúdium hydrolyzátu po hydrotermickej úprave bukového dreva (Fagus silvatica L.), II. časť [Study of hydrolysate after hydrothermal treatment of beech wood (Fagus silvatica L.), Part II],” in: Zborník vedeckých prác Drevárskej fakulty [Proceedings of the Scientific Works of the Faculty of Wood Sciences and Technology], Technical University in Zvolen, Zvolen, Slovakia, pp. 45-56.

Kačík, F., Solár, R., and Melcer, I. (1993). “Stanovenie monosacharidov v dreve a drevných materiáloch metódou plynovej chromatografie [Determination of monosaccharides in wood and wood materials by gas chromatography],” in: Zborník vedeckých prác Drevárskej fakulty [Proceedings of the Scientific Works of the Faculty of Wood Sciences and Technology], Technical University in Zvolen, Zvolen, Slovakia, pp. 99-103.

Kačík, F., Solár, R., and Baloghová, D. (1996). “Zmeny lignínu javorového dreva (Acer pseudoplatnus L.) vplyvom predhydrolýzy [Changes in lignin of maple wood (Acer pseudoplatnus L.) due to pre-hydrolysis],” in: Selected Processes in the Chemical Processing of Wood, Technical University in Zvolen, Zvolen, Slovakia, pp. 173-178.

Karmanov, A. P., and Derkacheva, O. Y. (2013). “Application of Fourier transform infrared spectroscopy for the study of lignins of herbaceous plants,” Russian Journal of Bioorganic Chemistry 39(7), 677-685. DOI: 10.1134/S1068162013070066

Košíková, B., Joniak, D., Tomáš, M., and Košík, M. (1976). “Sledovanie niektorých chemických reakcií pri hydrotermickej úprave dreva. Časť II. Reakcie modelových látok lignín-sacharidových komplexov [Monitoring of some chemical reactions in hydrothermal treatment of wood. Part II. Reactions of model substances of lignin-saccharide complexes],” Wood Research 21(3), 161-169.

Kučerová, V., Lagaňa, R., Výbohová, E., and Hýrošová, T. (2016). “The effect of chemical changes during heat treatment on the color and mechanical properties of fir wood,” BioResources 11(4), 9079-9094. DOI: 10.15376/biores.11.4.9079-9094

Laurová, M., Mamoňová, M., and Kučerová, V. (2004). Proces parciálnej hydrolýzy bukového dreva (Fagus sylvatica L.) parením a varením [Process of partial hydrolysis of beech wood (Fagus sylvatica L.) by steaming and cooking], Technical University in Zvolen, Zvolen, Slovakia.

Martin-Sampedro, R., Capanema, E. A., Hoeger I., Villar, J. C., and Rojas, O. J. (2011). “Lignin changes after steam explosion and laccase-mediator treatment of eucalyptus wood chips,” J. Agr. Food Chem. 59(16), 8761-8769. DOI: 10.1021/jf20160f

Melcer, I., Melcerová, A., Solár, R., and Gajdoš, E. (1983). „Porovnávacia charakteristika zmien jaseňového dreva (Fraxinus excelsior L.) po jeho hydrotermickej úprave varením a parením [Comparative characterization of changes in ash common wood (Fraxinus excelsior L.) after its hydrothermal treatment by cooking and steaming],“ Wood Research 28(1), 37-56.

Melcer, I., Melcerová, A., Solár, R., and Kačík, F. (1989). Chemizmus hydrotermickej úpravy listnatých drevín [Chemistry of hydrothermal treatment of hardwood species], University of Forestry and Wood Technology in Zvolen, Zvolen, Slovakia.

Pandey, K. K., and Pitman, A. J. (2003). “FTIR studies of the changes in wood chemistry following decay by brown-rot and white-rot fungi,” Int. Biodeterior. Biodegr. 52(3), 151-160. DOI: 10.1016/S0964-8305(03)00052-0

Solár, R. (1997). Zmeny lignínu v procesoch hydrotermickej úpravy dreva [Changes in lignin in hydrothermal wood treatment processes],Technical University in Zvolen, Zvolen, Slovakia.

Solár, R., and Melcer, I. (1990). “Chemical changes of the polysaccharidic part of hydrothermally treated oak wood their reflection in its mechanical properties,” in: Zborník vedeckých prác Drevárskej fakulty (Proceedings of the scientific works of the Faculty of Wood Sciences and Technology], University of Forestry and Wood Technology in Zvolen, Zvolen, Slovakia, pp. 15-26.

Solár, R., and Melcer, I. (1992). “Structural land chemical alterations of lignin in the proces of oak wood hydrothermal treatment,” Wood Research 12(3), 11-23.

Trajano, H. L., and Wyman, C. E. (2013). “Fundamentals of biomass pretreatment at low pH,” in: Aqueous Pretreatment of Plant Biomass for Biological and Chemical Conversion to Fuels and Chemicals, C. E. Wyman (ed.), John Wiley & Sons, Medford, MA, pp.103-128. DOI: 10.1002/9780470975831.ch6

Volynets, B., Ein-Mozaffari, F., and Dahman, Y. (2017). “Biomass processing into ethanol: Pretreatment, enzymatic hydrolysis, fermentation, rheology, and mixing,” Green Process. Synth. 6(1), 1-22. DOI: 10.1515/gps-2016-0017

Article submitted: April 11, 2018; Peer review completed: May 19, 2018; Revised version received and accepted: June 1, 2018; Published: June 13, 2018.

DOI: 10.15376/biores.13.3.5862-5874