Penetration capacity of the wood-decay fungus Physisporinus vitreus
© Fuhr et al.; licensee Springer. 2013
Received: 17 September 2012
Accepted: 30 January 2013
Published: 27 March 2013
Bioincising is a biotechnological process for improving the permeability of refractory wood such as Norway spruce heartwood using the wood-decay fungus Physisporinus vitreus. The degradation of the bordered pit membranes by P. vitreus in its first stage of wood colonization enhances the uptake of preservatives and wood modification substances, whereas the strength of the material is not significantly reduced.
We propose to study bioincising by means of a mathematical model, because many factors affect the growth and effects of P. vitreus in Norway spruce in such a complex way that an evaluation of the optimal incubation conditions (i.e. water activity, temperature or pH) is very expensive or even not possible solely using laboratory experiments.
Using a hyphal growth model we demonstrate here for the first time how to optimize bioincising by linking the microscopic growth behavior of P. vitreus with macroscopic system properties of the wood. Moreover, we propose universal measures of wood-decay fungi, i.e., penetration velocity, penetration work and penetration capacity, which may figure as measures for the efficiency of wood colonization. For example, our simulation shows that an increase of the hyphal growth rate (i.e. changing the incubation conditions) from 1 to 2 μm·d-1 results in an increase of the mycelium’s growth velocity from 0.8 to 1.75 μm·d-1 and an increase of the penetration capacity from 0.5 to 0.6 10-3·mm2·d-1 using a pit degradation rate of 2 μm·d-1.
Information about the penetration velocity, penetration work and penetration capacity is of significance for both its biotechnological use and the study of the colonization strategy of wood-decay fungi in general.
KeywordsFilamentous fungus Fungal colony Mycelia modeling Bioincising Picea abies Bordered pit
Using a discrete modeling approach called the fungal growth model (FGM), in previous studies the metabolism of P. vitreus (Fuhr et al. 2011b) and the effect of the wood tissue on its growth (Fuhr et al. 2011a) have been analyzed, whereas the penetration behavior was not studied in detail until now (Figure 1). Thus, the focus of this work is to study the rule of the bordered pits to obtain a complete modeling framework covering all relevant effects for the optimization of the permeability of bioincised wood sample.
The degradation of the bordered pit membranes in its first stage of Norway spruce (Picea abies (L.) H. Karst.) wood colonization might be the main reason for the significant increase of the permeability of treated wood (Schwarze et al. 2006). This biotechnological process, which is termed bioincising, can be used to improve the uptake of wood preservatives and wood modification substances (Schwarze & Schubert 2009; Schwarze & Schubert 2011). In this context several studies concerning P. vitreus addressed the anatomy of treated Norway spruce wood (Fuhr et al. 2011a; Lehringer et al. 2010; Stührk et al. 2010; Fuhr et al. 2012), the influence of environmental factors to its radial growth rate (Fuhr et al. 2011b; Schubert & Schwarze 2009; Schubert et al. 2010) and the alteration of wood properties (Spycher et al. 2008; Schwarze et al. 2008; Lehringer et al. 2011a; Lehringer et al. 2011b). Despite their potential, the methods mentioned are unable to illustrate the influence of microscopic effects such as the pit degradation rate on the macroscopic behavior of the fungus, because wood is an opaque material and the in vivo observation of processes inside a wood sample has not been possible until now. Therefore, we propose the use of mathematical models to study and optimize the penetration behavior of P. vitreus, since its growth behavior was successfully simulated by FGM, even in complex physical and chemical structured environments (Fuhr et al. 2011a).
The pits are valve-like structures between the voids within the wood (i.e. pores or lumens) and regulate the transport of nutrients in the tree. For example, in the living wood (i.e. sapwood) of Norway spruce the bordered pits are permeable for liquids. Whereas, in the dead part of the tree (i.e. heartwood) they are closed and lignified (Liese & Bauch 1967). It is this closing, called aspiration, of the bordered pits that makes efficient treatment of this wood species impossible without energy- and cost-intensive technical processing.
The degradation of the bordered pit membranes in their first stage of growth appears to be a common strategy of wood-decay fungi to colonize softwoods (Schwarze et al. 2006; Liese & Schmid 1961; Daniel 1994; Green et al. 1995; Green & Highley 1997). The size, structure and distribution of bordered pits is a significant factor for the accessibility of wood tissue both for fluids and fungal hyphae (Rayner & Boddy 1988). The time required by a hypha to penetrate through a bordered pit either by the support of pressure or enzymes (i.e. pit penetration time) obviously influences the ability of the mycelium to colonize a refractory wood such as Norway spruce heartwood.
Pit degradation : Pit degradation rates α c (enzymatic, Eq. 3 ) and α p (pressure, Eq. 7 ) evaluated for the pit penetration times τ = τ c = τ p = 0.5, 1, 1.5 and 2 days
Pit penetration time [d]τ
Pit degradation rate [μm/d]
α c (κ= 0.2)
α p (β1= 0.175, β2= −1.5)
The white-rot basidiomycete Physisporinus vitreus EMPA 642 was cultivated in 9 cm Petri dishes on 2% malt extract agar (MEA) at 23°C and 70% relative humidity (RH). After 2 weeks we placed sterilized (121°C, 20 min and 2 bar vapor pressure) Norway spruce (Picea abies (L.) H. Karst.) samples with a size of approximately 10 mm (longitudinal) × 2 mm (radial) and 10 mm (tangential) on the mycelium. The faces of the samples, with the exception of one radial tangential face, were sealed with a topcoat (Nuvovern ACR Emaillack, Walter Mäder AG, Killwangen, Switzerland) by brushing, so that the P. vitreus colonized the wood via the unsealed side in a longitudinal direction (Figure 2a).
After 10 days of incubation at 23°C and 70% RH we cut thin sections of approximately 30 μm thickness from the wood samples using a microtome as shown in Figure 2b. We stained the fungus with lactophenol blue, took mosaic images with a pixel size of approximately 0.65 μm × 0.65 μm using a Zeiss LSM 510-NLO (Figure 2c) and analyzed the images by digital image processing (Figure 2d).
Hyphal growth model
Model parameters : typical model parameters used throughout this work
[l L , l T , l 0 ]
[2.5, 0.08, 0.04]
Density of nutrient point
Diameter of bordered pit
Mean hyphal growth rate
Mean edge length
Growth cut-off length
Growth cut-off angle
Pit initial nutrient
Pit initial degradation rate
Pit degradation rate
Apical branching threshold
Lateral branching threshold
Initial number of pellet
n k 0
Initial number of tips
n s 0
Initial nutrient concentration
n n 0
Edges, nodes and tips form the mycelium of the fungus, whereby the position of the nodes is restricted to the position of the nutrient points as shown in Figure 7b. The characteristic growth of the fungus P. vitreus, which degrades the initially closed bordered pit membranes in its first stage of wood colonization, is simulated by a pit-to-pit growth of the hyphae. Thereby the mean growth rate of a hypha is given by μ. The evolution of the mycelium is driven by key processes such as the uptake and transport of nutrients, branching and polarization of the hyphae.
At each iteration step m of the algorithm the mycelium may grow by one edge. Thereby the length of the new edge and the angle measured to its predecessor is restricted by the growth cut-off length ξ and the growth cut-off angle θ. The mean edge length is λ. Each extension of the mycelium costs the fungus a specific amount of nutrients depending on the length of the edge. The fungus accumulates these nutrients in the nodes by degrading the pits at each time step initially for m = m 0 by α I and for m > m 0 by α c , where m 0 is the time when a new node is created at a pit. Branching occurs if the amount of nutrients at a node exceeds a certain level β t (at a tip node) and β s (at an interior node). A tip node is a node with one edge, whereas an interior node has more than one edge.
where F j , the amount of nutrients at point (j) and κ ∈ [0,ν], denotes a specific pit opening threshold. Details about the model construction are given in (Fuhr et al. 2011a).
The simulation begins by placing n k 0 starting nodes, called pellets, with an initial nutrient concentration n n 0 on the longitudinal face of the wood specimen (Figure 7a). All pits are initially closed (i.e. F j > κ) and their initial amount of nutients is ν. The unit of the resource that sustains fungal growth, called pit nutrient, is given in micrometers (μm), because we prefer to express the fungal activity (Eq. 1) with a measure, which is observable in laboratory experiments, e.g. holes in the torus of the bordered pits (directly) or a permeability (indirectly). However, the pit nutrient, given in micrometers, can be converted into other quantities of interest. For example, the mass of degraded lignin may be calculated by multiplying the pit nutrient by the degraded area given in μm2 times the density of the lignin given in microgram per volume [μg/μm3].
Analytical growth model
where μ ij is the growth velocity of a hyphae (i.e. hyphal growth rate) within a tracheid measured between the points (i) and (j) (see Figure 7a), l S is the length of the shortest path and τ is the pit penetration time, i.e. the time required for a hypha to grow through a bordered pit. Generally, there are two modes of pit penetration by a hypha. In the first case the torus is eroded by enzymes, e.g. P. vitreus (Schwarze et al. 2006). Whereas, in the second case a hypha breaks through the torus by mechanical pressure, e.g. blue stain fungi (Liese & Schmid 1961), which is typically indicated by cracks in the lignified torus. We indicate the mode of penetration by lower indices, i.e. enzymatic erosion (c) and pressure (p).
where D is the diameter of a bordered pit and κ ∈ [0, 1] is an opening threshold. Thus, D · κ is the diameter of a hole, which is prerequisite for a vegetative hypha to penetrate through the torus. α c is the pit degradation rate, given in μm·d-1, to dissolve the torus.
For example, a hypha bores a hole into a cell wall by α p = 0.25 μm per day. After approximately 2.12 days the diameter of the hole is approximately 0.53 μm (Eq. 4). This hole size corresponds to a penetration time of 2.12 days (inserting d = 0.53 μm into Eq. 5). Thus, the time of fungal activity at the cell wall is equal to the penetration time and therefore the hypha is able to grow through the bored hole. We directly obtain the penetration time τ p of approximately 2.12 days by inserting α p = 0.25 into Eq. 7.
Penetration velocity, work and capacity
Obviously, the penetration capacity of a fungus strongly depends on factors such as temperature, water activity and pH, the microclimate, the presence of wood preservatives and other factors, since wood decay-fungi are sensitive to their environment. The scalar П Q may figure as a measure for the efficiency of a specific fungus to colonize a certain wood tissue.
For simplicity, throughout this work, we use the terms ‘penetration work’ and ‘penetration capacity’ for the specific penetration work and penetration capacity using the total amount of degraded pit nutrients as the quantity of interest.
After 10 days of incubation, we observe that the fungus starting from the unsealed longitudinal face penetrates approximately 10 mm into the wood sample (Figure 2d). This corresponds to a penetration velocity of approximately 1 mm·d-1. The morphology of the growth front is characterized by hyphae growing at different rates (i.e. leading hyphae). The density of the mycelium at the unsealed end is much higher than on the growth front. We measure that a hypha crosses 3–4 tapered ends from the unsealed to the opposite face.
Figure 3 shows the evolution of the mycelium over a time span of 36 hours for κ = 0.5 and 1.0 (see Eq. 1) using the model parameters of Table 2. The system consists of 20 tracheids with 1070 pits in total. The fungus begins growing from the left longitudinal face and fixed boundaries are imposed to all faces. For κ = 1.0 the fungus grows without any resistance by the pit membranes and after approximately 32 hours the first hypha reaches the longitudinal face on the right side, whereas the fungus requires in the second case (i.e. κ = 0.5) approximately 42 hours for the same distance. The total hyphal length of the mycelium is approximately 130 mm for both conditions, whereas the number of tips is approximately 350 and 500 for κ = 1.0 and 0.5 respectively. In addition, the model shows that for κ = 0.5 P. vitreus requires approximately 15 per cent more nutrients to reach the right longitudinal face.
Figure 4 shows the velocity of the mycelium v f (Eq. 8) evaluated for hyphal growth rates between 0.5 and 5 mm·d-1 and pit degradation rates between 1 and 4 μm·d-1 (Eq. 3) using the model parameters of Table 2 and the tracheid framework of Figure 7a. The system consists of 2 (longitudinal) × 10 (tangential) tracheids and fixed boundaries are imposed to all faces. The fungus begins growing from the lower longitudinal face and the velocity is evaluated by measuring the time of the mycelium between points 1 and 3. The numerical results of these experiments are shown in Figure 4 by the symbols ○ (α c =1 μm·d-1), □ (α c = 2 μm·d-1), Δ (α c = 3 μm·d-1) and × (α c = 4 μm·d-1).
We observe that the penetration velocity v f increases with increasing values of μ and α c . For example, at a hyphal growth rate of μ = 0.5 the relative difference between the penetration velocity at α c = 1 and α c = 4 is smaller than 1, whereas at μ = 5 the difference is larger than 2. The influence of the pit degradation rate on the relationship between the hyphal growth rate and the penetration velocity seems to be nonlinear. It would be interesting to know more about this relationship, because the hyphal growth rate depends on environmental factors and may allow us to optimize the process of bioincising. Thus, the next two paragraphs develop such a relationship.
The solid lines in Figure 4 show Eq. 11 using Eq. 12a, 12b, 12c, 12d and N t = 2.65, q=3 and p=0.5. The velocity of 1 mm·d-1 measured from the experiment of Figure 2d corresponds approximately to hyphal growth rates μ (α c ) = 0.66 (4), 0.73 (3), 0.84 (2) and 1.14 (1) mm·d-1. The pit degradation rates α c = 1, 2, 3 and 4 μm·d-1 correspond to pit penetration times τ c = 2, 1, 0.67 and 0.5 days (Eq. 12a) and pit degradation rates by pressure α p = 2.77, 0.87, 0.44 and 0.27 μm·d-1 as shown in Table 1.
Penetration work and penetration capacity
Figure 5 and Figure 6 show the penetration work W N (Eq. 9) and the penetration capacity П N (Eq. 10) of P. vitreus measuring as quantity Q the amount of degraded nutrients given in micrometer. Since we measure the penetration depth in millimeters, the unit of the penetration work and the penetration capacity are 10-3·mm2 and 10-3·mm2·d-1 respectively. A penetration capacity of 1.0 10-3·mm2·d-1 means that the growth front of the mycelium penetrating 1 mm·d-1 into the wood degrades 1 micrometer pit membranes in total. We use the same simulation setup as in Figure 4. We observe that the penetration work decreases with increasing hyphal growth rates, whereas the penetration capacity increases with increasing hyphal growth rates. In addition, higher pit degradation rates result in a higher penetration work and penetration capacity.
The growth of physisporinus vitreus
The penetration behavior of P. vitreus into Norway spruce heartwood is supposed to be characterized by a stepwise capture of wood tissue (Fuhr et al. 2011a), because the aspirated and lignified bordered pits hinder the expansion of the mycelium (Figure 2). Only the degrading of either the bordered pits or the cell wall enables the fungus to grow from one tracheid to another. Thereby the ratio between the velocity of the hypha within the tracheids (i.e. hyphal growth rate) and the pit degradation rate is of interest, because this ratio influences the density of the mycelium, the number of tips in the system and the penetration velocity of the growth front as shown by our simulations (Figures 3 and 4).
Rays are not considered in the model, because they affect fungal growth in radial direction. The present study focuses on the penetration of the mycelium in longitudinal direction as shown in Figure 3.
The FGM assumes that the hyphal growth rate (μ) and the pit degradation rate (α c ) are the key factors for the colonization of Norway spruce wood in its first stage of growth. Using the analytical model (Eq. 11), we are able to quantify the influence of both factors on the penetration velocity of P. vitreus. The results suggest that a doubling of the hyphal growth rate enables P. vitreus to reduce the pit degradation rate by a factor 4 (Figure 4), to reach a penetration velocity of 1 mm·d-1 (Figure 2d). The hyphal growth rate is mainly influenced by the water activity, temperature and pH (Schubert et al. 2010), whereas the effect of environmental factors on the ability of P. vitreus to penetrate the bordered pits is unknown. Thus, changing the incubation conditions offers an optimization of the bioincising process (see next section ‘Optimization of bioincising’).
The measured hyphal growth rates between approximately 0.5 and 1.5 mm d-1 (Figure 4) are in good agreement with in vivo experiment of P. vitreus at standard conditions (Stührk 2011) and therefore confirm our model assumption. We are able to estimate for the first time the pit degradation rate of P. vitreus. Our simulations in combination with laboratory experiments show that the pit degradation rates (α c and α p ) are approximately 1 to 4 and 0.3 – 8 μm d-1 for a penetration either by enzymes or by pressure (Table 1).
The penetration time τ p is based on the of the experiments of Bardage and Daniel (1998). However, the influence of environmental effects such as temperature and pH on the penetration behavior of hyphae of white-rot fungi such as P. vitreus in wood may not covered by the experiments of Bardage and Daniel (Bardage & Daniel 1998) and may limit the extension of our model besides standard conditions. Thus, more quantitative and qualitative experimental studies about the penetration of hyphae through pores are needed.
Optimization of bioincising
We use a discrete modeling approach to study the biotechnological process of bioincising, because such a model provides information about the effects of P. vitreus, e.g. the amount of degraded pits, and therefore enables an optimization of the bioincising process. For example, our simulation shows that an increase of the hyphal growth rate from 1 to 2 μm·d-1 results in an increase of the growth velocity of the mycelium from 0.8 to 1.75 μm·d-1, a decrease of the penetration work from 1 to 0.75 10-3·mm-2 and an increase of the penetration capacity from 0.5 to 0.6 10-3·mm2·d-1 using a pit degradation rate of 2 μm·d-1 (Figures 4, 5 and 6). A penetration work of 1 to 0.75 shows that, for the tracheid framework given in Figure 7a, the growth front of the mycelium penetrating 1 mm into the wood degrades approximately 1 to 0.75 micrometer pit membranes in total (see Figure 5). Thereby, a penetration capacity of 0.5 to 0.6 10-3·mm2·d-1 indicates that the growth front of the mycelium penetrating 1 mm·d-1 into the wood degrades approximately 0.5 to 0.6 micrometer pit membranes in total, which is a measure for the permeability of the wood (Fuhr et al. 2011a). Moreover, the penetration capacity may figure as a measure for the efficiency of wood-decay fungi to colonize wood, since a high pit degradation rate may facilitate the capture of their resource. Thus, it would be interesting to measure and compare various penetration capacities from several wood-decay fungi, e.g. choosing as quantity of interest the biomass, amount of degraded pits or permeability.
The last step would be an optimization of bioincising on a larger scale using the modeling framework as described above. On a macroscopic scale, the influence of the distribution of pellets, which are the inocula on the surface of wood blocks, is of interest because the penetration velocity of P. vitreus in radial (i.e. rays) and longitudinal (i.e. tracheids) direction is much higher than in tangential direction. Thus, combining environmental factors with the amount and distribution of the inocula on the wood surface will help assist designing incubation conditions that are required to induce a certain degree of wood permeability by P. vitreus.
There are no relevant information about the authors for the interpretation of the article.
Swiss federal laboratories for materials and technology
Fungal growth model
Malt extract agar
The authors gratefully acknowledge J. Hehl (ETH Light Microscopy Center) for helpful discussions on image processing and express their gratitude to the Swiss National Science Foundation (SNF No. 205321–121701) for its financial support.
- Bardage SL, Daniel G: The ability of fungi to penetrate micropores: implications for wood surface coatings. Material und Organismen 1998, 31: 233–245.Google Scholar
- Comstock G: Directional permeability of softwoods. Wood and Fiber Science 1970, 1: 283–289.Google Scholar
- Daniel G: Use of electron microscopy for aiding our understanding of wood biodegradation. FEMS Microbiol Rev 1994, 13: 199–233. 10.1111/j.1574-6976.1994.tb00043.xView ArticleGoogle Scholar
- Fuhr MJ, Schubert M, Schwarze FWMR, Herrmann HJ: Modelling the hyphal growth of the wood-decay fungus Physisporinus vitreus. Fungal Biol 2011, 115: 919–932. 10.1016/j.funbio.2011.06.017View ArticleGoogle Scholar
- Fuhr MJ, Stührk C, Schubert M, Schwarze F, Herrmann HJ: Modelling the effect of environmental factors on the hyphal growth of the basidiomycete Physisporinus vitreus. J Basic Microbiol 2011, 52: 523–530.View ArticleGoogle Scholar
- Fuhr MJ, Stührk C, Münch B, Schwarze F, Schubert M: Automated quantification of the impact of the wood-decay fungus physisporinus vitreus on the cell wall structure of norway spruce by tomographic microscopy. Wood Sci Technol 2012, 46: 769–779. 10.1007/s00226-011-0442-yView ArticleGoogle Scholar
- Green F, Highley T: Mechanism of brown-rot decay: paradigm or paradox1. Int Biodeterior Biodegradation 1997, 39: 113–124. 10.1016/S0964-8305(96)00063-7View ArticleGoogle Scholar
- Green F, Tschernitz JL, Kuster TA, Highley TL: Hydrolysis of bordered pits during colonization of conifers by brown-rot fungi. In 26th Annual meeting Helsingør, Denmark 11–16 june 1995. Helsingør: International Research Group on Wood Preservation; 1995.Google Scholar
- Lehringer C, Hillebrand K, Richter K, Arnold M, Schwarze F, Militz H: Anatomy of bioincised Norway spruce wood. Int Biodeter Biodegr 2010, 64: 346–355. 10.1016/j.ibiod.2010.03.005View ArticleGoogle Scholar
- Lehringer C, Koch G, Adusumalli RB, Mook WM, Richter K, Militz H: Effect of physisporinus vitreus on wood properties of norway spruce. Part 1: aspects of delignification and surface hardness. Holzforschung 2011, 65: 711–719.Google Scholar
- Lehringer C, Saake B, Zivkovic V, Richter K, Militz H: Effect of physisporinus vitreus on wood properties of Norway spruce. Part 2: aspects of microtensile strength and chemical changes. Holzforschung 2011, 65: 721–727.Google Scholar
- Liese W, Bauch J: On the closure of bordered pits in conifers. Wood Science and Technology 1967, 1: 1–13.View ArticleGoogle Scholar
- Liese W, Schmid R: Licht- und elektronenmikroskopische Untersuchungen über das Wachstum von Bläuepilzen in Kiefer- und Fichtenholz. Holz als Roh- und Werkstoff 1961, 19: 329–337. 10.1007/BF02603326View ArticleGoogle Scholar
- Plomley NJB: Formation of the colony in the fungus Chaetomium. Aust J Biol Sci 1958, 12: 53–64.Google Scholar
- Rayner ADM, Boddy L: Fungal decomposition of wood: Its biology and ecology. Chichester, UK: John Wiley & Sons; 1988.Google Scholar
- Schubert M, Schwarze F: Response surface analyse (RSM) der wirkung kombinierter parameter auf das wachstum von physisporinus vitreus. Holztechnologie 2009, 50: 16–20.Google Scholar
- Schubert M, Mourad S, Schwarze F: Radial basis function neural networks for modeling growth rates of the basidiomycetes Physisporinus vitreus and Neolentinus lepideus. Appl Microbiol Biotechnol 2010, 85: 703–712. 10.1007/s00253-009-2185-3View ArticleGoogle Scholar
- Schwarze FWMR, Schubert M: Enhance uptake of wood modification agents in 'bioincised' wood. 40th Annual IRG Meeting Beijing, China 2009., IRG/WP 09–40445:Google Scholar
- Schwarze FWMR, Schubert M: Physisporinus vitreus: a versatile white rot fungus for engineering value-added wood products. Appl Microbiol Biotechnol 2011, 92: 431–440. 10.1007/s00253-011-3539-1View ArticleGoogle Scholar
- Schwarze FWMR, Landmesser H, Zgraggen B, Heeb M: Permeability changes in heartwood of Picea abies and Abies alba induced by incubation with Physisporinus vitreus. Holzforschung 2006, 60: 450–454.View ArticleGoogle Scholar
- Schwarze FWMR, Spycher M, Fink S: Superior wood for violins wood decay fungi as a substitute for cold climate. New Phytol 2008, 179: 1095–1104. 10.1111/j.1469-8137.2008.02524.xView ArticleGoogle Scholar
- Siau JF: Transport processes in wood. Verlag Berlin Heidelberg New York: Springer; 1984.View ArticleGoogle Scholar
- Sirviö J, Kärenlampi P: Pits s natural irregularities in softwood fibers. Wood and Fiber Science 1998, 30: 27–39.Google Scholar
- Spycher M, Schwarze F, Steiger R: Assessment of resonance wood quality by comparing its physical and histological properties. Wood Science and Technology 2008, 42: 325–342. 10.1007/s00226-007-0170-5View ArticleGoogle Scholar
- Stührk C: Tomographische visualisierung des hyphensystems von physisporinus vitreus in fichtenholz (picea abies) zur optimierung des bioincising prozesses. Gallen: EMPA St; 2011.Google Scholar
- Stührk C, Fuhr M, Schubert M, Schwarze F: Analyzing hyphal growth of the bioincising fungus Physisporinus vitreus with light-, confocal laser scanning- and, Synchrotron X-ray tomographic microscopy. 41st Annual Meeting Biarritz, France 2010., IRG/WP 10–20438:Google Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.