COMPARING THE STRUCTURE OF SPRUCE WOOD BIODEGRADED BY Trametes versicolor AND Gloeophyllum trabeum AND FURTHER UTILIZATION OF THIS MATERIAL

Development of new materials puts a great emphasis on saving production costs, energy, decreasing the amount and number of chemicals used during the manufacturing process. Bio-based materials can be ecologically produced and recycled after their lifespan, which saves the environment. The recent interest in bio-based materials led to the objective of this work. In this article, the structure of spruce wood ( Picea abies ) biodegraded by the white-rot fungus Trametes versicolor and brown-rot fungus Gloeophyllum trabeum was studied. Structure of the wood was observed macroscopically and microscopically. Classic and unusual stain combinations were used in this work. Ethanol was intentionally omitted in the process of making permanent mounts. It was done to preserve the coherence of the decayed microsections and to keep small fragments from being rinsed away. Results of the observations suggest that spruce wood decayed by these fungi could be used as an insulation material. Wood decaying fungi decrease the density of wood and increase its porosity. A low density and high porosity are important properties for insulation materials. According to the results, spruce wood decayed by Trametes versicolor would be more suitable to be used as an insulating material.


INTRODUCTION
The focus in material development in the recent years has been creating materials, which are ecological, recyclable and have a low or no carbon dioxide emissions. Development of new materials and manufacturing technologies is rapidly going forward. Desired properties of a certain material can be reached by its various modifications. Modifications in material manufacturing can save energy needed for the production, number and amounts of chemical substances used and impact of the production on the environment.
Wood modifications have an abundant history. The three methods used commercially are chemical, thermal, and impregnation modification. Each of these has advantages and disadvantages when it comes to the properties of the modified wood and the complexity of the modification process (Hill 2011). Biomodification of wood with wood decaying fungi is another type of wood modification. During the early 1960s, industrially cultivated white rot fungus (Trametes versicolor) was used in the German Democratic Republic, mainly on beech wood for pencil or ruler production (i.e., "mykowood," Unbehaun et al. 2000, Mai et al. 2004, Schwarze and Schubert 2011. Currently, fungi are widely used in multiple different areas -mycoremedation ecology, cleaning industrial sewerage water, degradation of pesticides, biosorption of heavy metals (Pavlík 2013). Natural processes that occur during fungal biodegradation of wood may be utilized for industrial purposes and have a great potential for the cellulose-producing and wood processing industries (Fackler et al. 2007). Using wood decay fungi for biotechnological applications in the forest products industry has been studied for several decades because the specificity of their enzymes and the mild conditions under which degradation proceeds make them potentially suitable agents for wood modification (Majcherczyk and Hüttermann 1998, Messner et al. 2002, Schwarze 2008).
An interesting application of a controlled use of the degradation pattern of Physisnosporinus vitreus is the production of mycowood with improved acoustic properties to overcome the shortages of natural wood with the superior tonal qualities desired by traditional musical instrument makers (Schwarze and Schubert 2011). Biodegradation of beech wood with Trametes versicolor changed its optical properties; with the amount of lignin removed an increase in the lightness and a change in the biodegraded beech wood color were observed (Solár et al. 2006).
The objective of this work was to compare the structure of spruce wood biodegraded by a white-rot fungus Trametes versicolor and a brown-rot fungus Gloeophyllum trabeum. Structure of the samples was observed on a macroscopic and microscopic level. Because biodegraded wood is very fragile, improving some steps in making permanent mounts process was needed. Discussion of this article explores how changes in structure of biodegraded wood affect its properties. As it was mentioned before, this change in properties can be used in the production processes or new products.
T. versicolor is known for causing both erosive and simultaneous types of decay. First, it creates cavities in S3 layers of cell walls. Cavities are created in the place of direct contact with hyphae and the gradually grow deeper and wider into the cell walls. In moderate stages of decay, certain parts of cell walls are gradually being completely digested in the direction towards the middle lamella. In advanced stages of decay, erosion channels are created (Reinprecht 1998).
Gloephyllum trabeum is a brown-rot fungus. A typical sign of brown-rot decay are cracks running across and parallel to the grain. It is a result of mechanical damage in cell walls. In brown-rot fungi decay processes, the S2 layer is the most accessible and the compound middle lamella is the least accessible to decay. Various brown-rot fungi have different abilities of degrading lignin (Reinprecht 1998).

MATERIALS AND METHODS
Spruce wood (Picea abies L.) samples were used in this experiment. The samples were cut from lumber obtained from a local window frames manufacturer. The obtained lumber was certified window scantlings lumber. The samples were cut and sanded to sizes of L × R × T: 8 mm × 50 mm × 50 mm, 50 mm × 8 mm × 50 mm, 50 mm × 50 mm × 8 mm. The grain was always properly aligned with the general anatomical directions. One part of the samples (48 samples) was intentionally degraded with Trametes versicolor (L. Lloyd), and the other part of the samples (48 samples) was intentionally degraded with Gloeophyllum trabeum (Pers. (Murill)). Reference samples (36 samples) were left undegraded by fungi. The mass losses of the samples were 43,8 % after degradation by Trametes versicolor and 20,9 % after degradation by Gloeophyllum trabeum.
The intentional degradation was performed in the laboratory at the Department of Wood Technology at the Technical University at Zvolen. Kolle flasks and the malt agar soil were prepared according to STN EN 113 (1998). Fungi strains used for the intentional degradation were BAM 116 for T. versicolor and BAM 115 for G. trabeum (Bundesanstalt für Materialforshung und -prüfung, Berlin, Germany). Spruce samples were submerged into re-boiled and cooled distilled water one day prior to placing the samples into prepared Kolle flasks.
Duration of the intentional degradation for T. versicolor was 6 months. For G. trabeum, the degradation time was 4 months. A shorter degradation duration for spruce samples degraded with G. trabeum was chosen, because samples with a longer degradation duration were too brittle to be cut into microsections. After the degradation duration passed, the samples were cleaned off visible mycelium and left to air dry at room tem-perature. The samples were then oven dried, and they were stored in a climatic room at an air temperature 20 °C and air humidity around 50 %.
Three samples from each group (degraded by T. versicolor, G. trabeum, undegraded reference group), nine samples in total were chosen for the macroscopical and microscopical observation. From the degraded spruce sample groups, samples with a mass loss close the average mass loss of the group were chosen. The chosen samples were macroscopically observed under a Leica stereoscope. The results are shown in Figure  After the macroscopical observation was finished, small blocks with the dimensions of 3 mm × 3 mm × 7 mm were carefully cut from the samples. A total of 9 blocks from 9 samples were used for microscopical observation. All sample blocks were embedded in epoxy resin. Embedding the decayed samples was necessary for microtome sectioning, because these samples were very fragile, and it was nearly impossible to cut the microsections. Embedding the wood blocks in epoxy resin made the fragile decayed wood stable enough for microsections cutting.
The wood samples were cut on a sledge microtome (Reichert, Wien, Austria). Thickness of the samples was approximately 15 μm -20 μm. The microsections were put on a microscope slide and each microsection was stained with a different stain or combination of stains.
The main aim for staining microsections was to make T. versicolor and G. trabeum hyphae clearly visible in the structure of the spruce wood. Therefore, stain combinations were used to stain the spruce wood microsections. The stain combinations were made by mixing equal volumes of Toluidine, Astra Blue, Safranin and Fast Green for the TASG stain combination. For the TAS stain combination, equal volumes of Toluidine Blue, Astra Blue and Safranin were mixed. Some microsections were stained with only Toluidine or Safranin. Two more stain combinations were used in this article -the combination of Fast Green with Safranin (later referred to as GS stain combination), and Toluidine mixed with Safranin (later referred to as TS stain combination).
Using a Toluidine Blue stain gives a qualitative determination of lignin and its distribution (Herr 1992, Schwarze et al. 2000a, Schwarze et al. 2000b). Safranin stain is used for a semi-qualitative detection of lignin in cell walls. It is used as a counterstain in some staining protocols, coloring all cell nuclei red (Cartwright 1929, Jensen 1962. A combination of Safranin and Astra Blue is used to detect early stages of white rot, i.e., selective delignification. Safranin stains lignin regardless of whether cellulose is present, whereas Astra Blue stains cellulose only in the absence of lignin Messner 1994, Schwarze andEngels 1998). According to the manufacturer, Fast Green is suitable also for staining protein and starch and it is certified for use in combination with Safranin for plant cells; as a substitute for aniline blue in Gomori's one step tri-chrome procedure. Fast Green is also used as a counterstain in detecting reaction wood. Reaction wood absorbs the green stain whereas opposite wood has a red to yellow color (Kúdela and Čunderlík 2012). Uptake of dye clearly depends on both chemical and physical aspects (Hubbe et al. 2019).
After leaving the stain absorb in the microsections for 5 minutes, the stains or stain combinations were rinsed out with distilled water without using ethanol. Preserving most of the decayed microsection was our objective. After rinsing the microsections with only distilled water without using ethanol, they were left to airdry. The microsections were mounted in Euparal (BioQuip Products Inc., Rancho Dominguez, United States) and covered with cover slips. The permanent microslides were placed on a board from a ferromagnetic material and magnetic weights were applied on the cover slips. The permanent microslides were left to cure at room temperature for two to three weeks.
We intentionally omitted the step of using ethanol for drying microsections. Further rinsing steps could damage the hyphae, and small fragments of the decayed wood could be rinsed away. We also wanted to omit ethanol to avoid using more chemical substances to prepare the fragile microsection. The comparison of leaving the microsections to air-dry without using ethanol and using ethanol to dry the microsection are shown in Figure 1. The microsections shown in Figure 1a were rinsed only with distilled water without using ethanol after staining and they were left to air-dry at room temperature. As the photo shows, these microsections remained stretched out on the microscope slide. Microsections shown in Figure 1b were rinsed with distilled water, subsequently dried with 75 % ethanol and then with 96 % ethanol. It is apparent, that the microsections in Figure  1b are severely damaged and incoherent in comparison to microsections in Figure 1a. The microsections in Figure 1b show also severe cupping. Such cupping makes the microsections difficult to stretch out on the microscope slide.
Wood decayed with fungi is very fragile. It is therefore better to omit ethanol to dry the microsections. Ethanol causes the microsection to dry rapidly and this damages the microsection. Rinsing the microsection only with distilled water without using ethanol and leaving it to air-dry does not cause stress to the microsection. Gradual air-drying of the decayed wood microsection makes better conditions for the finished permanent mount.  The difference between leaving the microsections to air-dry without using ethanol and using ethanol to dry microsections might not be largely visible in Figure  Omitting ethanol in the permanent mount preparation process does not have a bold difference in the final color hue of the microsection. However, it is highly beneficial for coherence of the microsections, which can be seen in Figure 1b.

Results
Comparison and analysis of spruce wood decayed with T. versicolor and G. trabeum was started with a macroscopic observation of differences in the structure of decayed and reference samples. The comparison is documented in Figure 3e1  The transition from earlywood to latewood is clearly visible in Figure 3e2. Both figures show earlywood and latewood. Reference spruce wood was undegraded, it has a typical pale-yellow color of earlywood and light brown color of latewood. Figure 3e3 shows a radial section of reference spruce wood. Pronounced ray parenchyma cells are visible; white arrows are pointing at them in the figure. The transition from earlywood to latewood is clearly visible in the figure. Figure 3e4 shows a tangential section of the reference spruce wood. The picture was taken at the earlywood to latewood transition; therefore, the color appears to be dark yellow to very light brown. Figure 3f1, Figure 3f2, Figure 3f3, Figure 3f4 show spruce wood decayed with T. versicolor. The color change of the decayed wood is apparent. Figure 3f1 and Figure 3f2 show a cross section. A big check running along the latewood is shown in Figure 3f1. The cell walls are separated by this split. White areas visible mostly in earlywood are T. versicolor mycelium. Spruce wood decayed with T. versicolor appears to have a rough surface. In Figure 3f2, earlywood with a large area of mycelium is shown. The transition from earlywood to latewood is harder to recognize, due to the earlywood color change from pale-yellow to brown because of the decay. Earlywood cell walls around the mycelium area appear to be elevated in comparison to the cell walls covered by mycelium. Fine hyphae are also visible in this figure, they are pointed at with yellow arrowheads. Figure 3f3 shows a radial section with exposed ray parenchyma. In comparison to the reference spruce wood radial section in Figure 3e3, the cell walls of spruce wood decayed with T. versicolor are more pronounced and clearly visible even at the magnification of 60 x. This is due to the activity of the fungus, thinning of cell walls made the lumina wider. In some spots, the cell walls can even be missing because they are already mostly or fully digested by the fungus. The white, shiny areas are T. versicolor mycelium. Figure 3f4 shows a tangential section. Like in Figure 3f3, cell walls are more pronounced because of their thinning caused by the fungus. Some cell walls in this figure are mostly or fully digested, and this appears like a check running along the grain in the left part of the figure. White, shiny areas of mycelium are visible also in tangential section.
In Figure 3g1 Figure 3g3. However, the surface in Figure 3g3 appears to be wavy compared to the surface in Figure 3f3. This is because of checks running across the grain, which is another typical sign of brown-rot fungi decay. Checks running across the grain of the spruce wood are visible in the tangential section shown in Figure 3g4, yellow arrows point at the checks.
Hyphae growth and spread throughout the decayed spruce wood was analyzed on radial and tangential microsections shown in Figure 4h1 Figure 4h2 shows a tangential microsection and Figure 4h3 shows a radial microsection, both were stained with Toluidine. Figure 4i1 shows an earlywood cross section stained with TAS stain combination, Figure 4i2 shows a tangential microsection stained with Toluidine and Figure 4i3 shows a radial microsection stained with a combination of Fast Green and Safranin. Arrows point at hyphae and arrowheads point at bore holes. After staining the microsections with Toluidine, hyphae of both fungi appeared in a purple color (Figure 4h3 and Figure 4i2). Staining microsections with GS stain combination stained the hyphae green and the cell walls absorbed Safranin (Figure 4i3). The hyphae of both fungi appeared red when the microsections were stained with the TAS stain combination (Figure 4h1 and Figure 4i1).  (Figure 4h3, Figure 4i3). Because ray parenchyma contains nutrients, the hyphae were located mostly near ray parenchyma (Figure 4h3 and Figure 4i3). Ray parenchyma in samples decay by T. versicolor were often severely decomposed. This is visible v Figure 4h3, in the lower part, where an arrowhead is pointing at the ray parenchyma. Samples decayed by G. trabeum did not show such ray parenchyma decomposition; the ray parenchyma in these samples were undecayed (Figure 4i3). Hyphae grew also through bordered pits; this is visible in Figure 4h2. The bordered pits toruses and poruses in Figure 4h2 are almost completely digested. This was not observed in spruce wood decayed by G. trabeum, only a small amount of the bordered pits toruses were digested. T. versicolor hyphae created numerous bore holes in cell walls, which is presented in Figure 4h3. The bore holes were observed mainly on tangential sections. In this experiment, bore holes in spruce wood decayed by G. trabeum were not observed.    Figure 5k1 and Figure 5k2. These dark spots did not appear in reference spruce wood microsections. The dark spots are known as the beginning point of the degradation process in the cell wall. There is visible thinning of cells walls in Figure 5k2 and Figure 5k3, marked with yellow arrows. Thinning occurred mostly around ray parenchyma area, which agrees with the locations of hyphae. The thinned parts of the cell walls attached to ray parenchyma are visibly thinner than their opposite parts connected to other earlywood tracheids. Figure  5k3 shows an erosion channel in the lower left part of the figure. The cell walls in this part were completely digested. Erosion channels were observed also in Figure 4h1.
Numerous cavities in spruce latewood decayed by G. trabeum are pointed out with white arrowheads in Figure 5l1. A detached cell wall is observed on the right side of the figure, denoted with a white arrowhead. Detached cell walls were not as often in spruce wood decayed by G. trabeum as in spruce wood decayed by T. versicolor. The cell walls in spruce wood decayed by G. trabeum were rather cracked and rough, as observed in Figure 5l2 or very thinned until middle lamella was left, as observed in Figure 5l3. Even though the cell walls in Figure 5l2 are very saturated with the stain combination, the strong saturation enhanced the outlines of the severely cracked the innermost tracheid layers. The location of hyphae and their attachment to the cell walls in Figure 5l2 agrees with the places where the severe cracking in the cell walls occurred. Figure 5l3 shows completely digested cell walls in earlywood with many hyphae present. Most of the cell walls in this figure are very thinned.

DISCUSSION
As observed by Bari et al. (2020), wood species had an important impact on the decay behavior of the studied white-rot fungi. Some white rot fungi have the genetic capacity to produce a wider range of enzymes and radicals, triggered by the chemical composition of cell walls and perhaps local variations in the molecular composition within the cell wall (Bari et al. 2020).
Stages of decay may vary throughout the sample. Even if the mass loss is high, the microsection might not contain any signs of decay or a very early stage of decay. It is therefore important to know, what stage of decay is being observed. Presence of only fine hyphae in wood should indicate an early stage of decay, while a mixture of fine and larger hyphae would suggest a moderate stage of decay (Wilcox 1993). Bari et al. (2020) observed fungal decay by T. versicolor in Norway spruce (Picea abies (L.) H. Karst.). Early stages of decay, in which fungal hyphae and decay zones were detected in the innermost layer of the tracheids. T. versicolor showed more advanced stages of decay for latewood than earlywood (Bari et al. 2020). In the study by Wilcox (1993), the attack by G. trabeum on Douglas fir (Pseudotsuga menziesii (Mirb.) Franco) latewood was not observed until 7 % mass loss and occurred then only at the growth ring boundary; by 15 % mass loss, the attack extended from the transition as well. In white fir (Abies concolor (Gord. & Glend.) Lindl. ex Hildebr.), latewood attack by G. trabeum was not apparent until 25 % mass loss and was observed to come from both the boundary and transition of the growth ring.
In the presented work and results, signs of decay by T. versicolor were observed better and spotted easier in latewood than in earlywood. It is mainly due to the cell wall thickness; cavities especially are observed better in latewood than in earlywood. The decay by G. trabeum was apparent even in areas with an early stage of decay -the number of hyphae present in earlywood lumina was very high (Figure 4i3).
Postia placenta brown rot fungus hyphae were commonly seen moving cell-to-cell by penetrating bordered pits (Schilling et al. 2013). Erosion of the simple and bordered pits caused round or oval openings (Yilgor et al. 2013) in Turkish sweetgum (Liquidambar orientalis Mill.) heartwood decayed by T. versicolor.
Some fungi species penetrate through cell walls by creating bore holes. Hyphal tunnelling through cell walls is another means by which certain fungi may be able to grow through wood in which cell lumina are inaccessible (Daniel et al. 1992, Schwarze et al. 1995, Schwarze et al. 2004, Schwarze and Fink 1997, Schwarze and Fink 1998, Worrall et al. 1997. In our presented results, T. versicolor hyphae created numerous bore holes. The bore holes were observed mostly on tangential sections. G. trabeum did not create any bore holes. Creation of bore holes by T. versicolor was observed in different wood species by various researchers before -in hornbeam wood (Carpinus betulus) (Bari et al. 2019), beech wood (Fagus orientalis Lipsky) (Bari et al. 2015) and Turkish sweetgum (Liquidambar orientalis Mill.) heartwood (Yilgor et al. 2013).
Only a few brown-rot fungi have been observed to grow by hyphal tunneling through cell walls (Duncan 1960, Schwarze et al. 2000a, Kleist and Schmitt 2001. G. trabeum was found to do so in the study by Schwarze and Spycher (2005) and Wilcox (1993). In the study by Wilcox (1993), G. trabeum hyphae created bore holes in Douglas fir (Pseudotsuga menziesii (Mirb.) Franco) and white fir (Abies concolor (Gord. & Glend.) Lindl. ex Hildebr.) wood in the earliest stages of decay. The bore holes were more readily observed in radial sections than in cross sections. The diameter of bore holes increased with progressing decay. Wilcox (1993) also observed that bore holes smaller in diameter than the penetrating hyphae were observed at the earliest stage of decay studied, while the bore holes were considerably larger than the hyphae by the time a moderate stage of decay was reached.
Some studies have reported that parenchyma cells are resistant to brown-rot decay (Worrall et al. 1997, Schwarze et al. 2000a, Schwarze et al. 2003. The results of the study by Yilgor et al. (2013) showed almost the same degree of decomposition in all types of cell walls in Turkish sweetgum (Liquidambar orientalis Mill.) heartwood decayed by Tyromyces palustris. In our study, G. trabeum digested ray parenchyma cells significantly less (Figure 4i3) than T. versicolor. Ray parenchyma cells in spruce wood decayed by T. versicolor were usually severely decomposed, with numerous bore holes in their vicinity (Figure 4h3).
Thinning of cell walls means that not only the fungi are capable of degrading lignin and hemicelluloses, but they can also attack cellulose polymer as well. The decomposition of S2 and S3 layers and the remainder of only a thin middle lamella are the result of the fungi using all cell wall components, which was previously reported (Wilcox 1973, Schwarze et al. 2004, Schmidt 2006, Schwarze 2007, Bari et al. 2018. Cell wall thinning was observed in both T. versicolor and G. trabeum samples in this experiment. The thinning was observed better, and it was apparent in samples decayed by T. versicolor. It was even possible to compare the thickness of the cell wall within one tracheid. One part of the tracheid was visibly thinner than the opposite part of the same tracheid, which is visible in Figure 5k3. Innermost parts of cell walls in samples decayed by G. trabeum were severely cracked and then digested until compound middle lamella was left. In the case of brown rot degradation, cellulose has been removed leaving lignin as the cell wall component. T. versicolor, on the other hand, also degrades lignin so the structure after white rot degradation looks rough (Vaukner Gabrič et al. 2016). Roughness of both T. versicolor and G. trabeum samples is compared in Figure 3f3, Figure 3f4, Figure 3g3, Figure 3g4. The samples decayed by T. versicolor look more coherent and compact in comparison to samples decayed by G. trabeum. The structure of spruce wood decayed with G. trabeum appears to be sponge-like, almost fleecy, especially around areas with checks ( Figure 3g2).
Presence of bore holes, thinned cell walls and erosion channels increase the porosity of decayed wood. Porosity of beech wood (Fagus sylvatica L.) and sessile oak heartwood (Quercus petraea Matt. Liebl.) decayed by T. versicolor was measured and calculated by Slováčková (2021b). The porosity of spruce wood was calculated in the experiment as well, but the result was published in the author´s dissertation thesis. Porosity of decayed beech wood increased by 20 % -30 % and porosity of decayed sessile oak heartwood increased by 10 % -13 % in comparison to healthy wood (Slováčková 2021b), and the porosity of decayed spruce wood increased by 12 % -17 % (Slováčková 2021c). A high porosity is an important property of thermal insulations.
Because decayed wood is more porous, has wider cell lumina and there are bore holes in cell walls, the permeability of wood could be increased. However, research showed the opposite. As observed by Solár et al. (2006) and Slováčková and Mišíková (2021), the permeability of healthy beech wood was higher than permeability of beech wood decayed by T. versicolor.
A low density and high porosity of decayed spruce and beech wood were significant factors influencing the values of thermal conductivity (Slováčková 2021a). Thermal conductivity values of decayed spruce and beech wood were lower than thermal conductivity values of undecayed spruce and beech wood. Thermal conductivity measurements were performed on samples of both decayed and healthy wood conditioned at 60 % ± 5 % relative air humidity and at 20 ºC ± 2 °C air temperature. To compare the decrease in thermal conductivity values, ratios of decayed and undecayed thermal conductivities were presented: longitudinal direction in spruce 0,8; radial direction 0,64; tangential direction 0,54. The ratios for beech wood are as follows: thermal conductivities ratio of degraded and undegraded wood for longitudinal direction 0,82; for radial direction 0,61 and 0,69 for tangential direction (Slováčková 2021a).
Many of the challenges of using wood as an engineering material arise from changes in moisture content or an abundance of moisture with the wood (Glass and Zelinka 2010). Because fungi attack the cell wall components, it is expected that the fungal attack has an impact on equilibrium moisture content of the decayed wood. Bader et al. (2012) observed various properties of Scots pine (Pinus sylvestris) sapwood decayed by T. versicolor and G. trabeum. A higher stage of degradation resulted in a lower equilibrium moisture content (EMC) and the EMC was more strongly affected by G. trabeum than T. versicolor (Bader et al. 2012). Chemical components of the cell wall responsible for moisture uptake are more strongly degraded by G. trabeum than T. versicolor (Bader et al. 2012).

CONCLUSIONS
The main objective of the presented work was to observe differences and similarities in the structure of spruce wood biodegraded by T. versicolor and G. trabeum. The samples were observed macroscopically and microscopically. Both wood decaying fungi caused thinned cell walls, numerous cavities in cell walls and a mass loss. Cutting of the decayed samples on the sledge microtome and manipulation with the microsections was difficult and it was necessary to improve the permanent mount making process. Because rinsing steps can rinse away small fragments of the fragile microsection, we tried to omit rinsing with ethanol. It was possible to rinse microsections with only distilled water and finish the permanent mount in the usual way. Wood decayed by Trametes versicolor could be used as insulating material. These samples had numerous bore holes in cell walls and erosion channels. The wood was very porous, had a low density, which are important properties for insulating materials. Results of this work can be applied in permanent mount preparation, material development as well as in studying effects of fungal decay on spruce wood. Biodegradation of wood is a natural process. There is a possibility of using fewer chemical substances during the production process of biodegraded wood, which can lessen the impact on the environment. hr/archives/72-volume-45-issue-no-3/327-biotechnological-wood-modification-with-selective-white-rot-fungi-and-its-molecular-mechanisms