The invention relates to a method for producing a mineralized wood or mineralized cellulosic materials.

More particularly, the invention relates to mineralized wood , wooden material and other cellulosic material suitable for indoor and outdoor use and methods for making such materials. Various attempts have been heretofore made to protect wood , wooden material and other cellulosic material against fungi and to improve its fire resistance/reaction to fire.

Many of the methods developed were either too costly to be economically feasible or not environmentally safe. The chemical protection of wood against wood destroying fungi is divided into two different approaches: a ) the prevention of the colonization and b) the killing of fungi after they have already colonized wood . According to this, different chemicals are used. In the following , only the application of active agents which can prevent a colonization of wood will be discussed . In general wood preservatives have to meet certain requirements. They have to be efficient against the target organism and the active agents need to be fixed and stabilized in the wood in order to avoid a leaching and evaporation . The ecological impact needs to be as small as possible and its effect should not be a risk for the environment and humans.

The known products can be divided into three groups: i) water based salts, ii ) solvent based formulations, and iii ) creosotes. Basically, water solved metal salts are not stable in wood and are therefore only used for indoor applications. Apart from some essential additives they consist of 80- 1 00% of the active agent. They are easily washed out and already after one rain fall, the whole effect of the substance can be lost if the application was done by brushing or dipping. The main substances are fluoride, silicate or borate. The different salt formulations can further be differentiated by the solubility and penetration behavior.

For outdoor uses the above mentioned salt formulations need to be fixed with chrome. Within 4-6 weeks after the application chrome salts react with certain wood components. Thereby leaching can be significantly reduced. The fixation of chrome salts in wood is based on the reduction of chrome (VI ) to chrome ( I I I ). With chrome ( I I I ) the fluorine or copper salts react to insoluble chemical combinations and become very weather resistant. Parallel to the fixation of the salts the color of the wood changes as well from yellow-orange to olive-green. The chrome functions mainly as fixing agent. Certain chrome compounds (chrome (VI ), for example zinc chromate) are very toxic to animals and humans.

The addition of copper in the salt formulations provides additional protection against soft rot. These salts can be used for impregnation of wood in very wet conditions and in soil contact. The expected rates of leaching for copper-chrome combinations are about 5 % . Common water soluble metal salts are: Chrome-fluoride-salts, Chrome-fluoride-boron-salts, Chrome-copper-salts, Chrome- copper-boron salts and Chrome-copper-fluoride salts.

The use of creosotes is restricted to special applications. Railway sleepers represent the main field for impregnation with creosotes. The efficiency of the creosotes depends on their composition . Products with high concentrations of polycyclic aromatic compounds with 4-6 rings show the best efficiency. A coating of creosote treated wood is not possible. Depending on certain circumstances creosotes can migrate and pollute the surface. Creosote impregnated parts need to be treated as hazardous waste after their lifetime.

Solvent based preservative formulations are used for indoor and outdoor applications with no ground contact. The common fields of application are usually class of utilization 1 - 3 (regarding EN 335, for example class 3 windows and doors). The basic components are organic solvents, biocide active substances, binders and pigments. These products are mainly water stable and can not be leached out but they do not show the necessary performance in earth contact. The concentration of the active substances is normally between 0.5 - 5 % because they are highly efficient. The active agents in solvent based preservatives belong to the same groups like the biocide agents in herbicides, but they differ in certain points significantly. The aspects of special interest for this type of wood preservatives are: penetration depth , low evaporation of the active agent, no crystallization at the surface, smelling behavior, binder and pigment concentration . Frequently used organic biocide systems are: Permethrin, Deltamethrin , Dichlofluanid , Propiconzol and Tebuconazol.

All of the above mentioned agents exhibit a certain protection behavior, however they all transform the wood into a toxic material.

Beside the degradation via fungi wood can also be destroyed by fire. Therefore a comprehensive fire protection is necessary and becomes more and more important especially for multi-story houses made from wood. To influence the fire resistance wood can be treated with different systems of fire retardants.

A treatment with these substances results in delayed ignition , reduced heat release rate and slower spread of flames. They act on different levels, most of the time combined : promotion of char formation at lower temperature than wood usually degrades, free- radicals trapping in the flame, dilution of combustible gases coming from wood with non- combustible gases, reduction of heat content of the volatile gases, or coating protection of the wood surface. The most commonly used fire retardants for wood products are inorganic salts, of which some can absorb moisture promoting decay and destruction of metal joints. Because these salts are typically water soluble and easily leached out of wood, water-insoluble organic fire retardants have been developed, which are mainly based on amino resin systems polymerized after impregnation into wood [2]. Unfortunately, fire retardants, despite reducing the combustion potential of wood, can also unfavorably affect following properties of wood: mechanical strength, hygroscopicity, stability, toxicity, adhesive and mechanical properties, and receptivity to coatings. Moreover, they are used in relatively large doses, which impacts the cost of the structure. The smoke emissions, together with carbon monoxide increased concentration during fire might happen as well, as it is the case with the widely used monoammonium phosphate [4]. Intumescent coatings are easier to apply and less costly but their susceptibility to cracks, abrasion and wear results in the loss of efficiency.

It is therefore an objective of the present invention to overcome these and other disadvantages characterizing the prior art and provide an environmentally friendly and non-toxic method to protect wood, wood containing materials and other cellulosic material against fungi and to improve their fire resistance. Summary of the Invention

The purpose of this invention is to provide a method for protecting wood, wooden material and other cellulosic material by mineralization . Due to the novel mineralization method, the water soluble reactants penetrate the material stepwise and water insoluble salts, preferably in crystalline form, are generated in situ within the cells themselves, in the cell walls, in the pits and in the middle lamellas.

A further purpose of this invention is to provide mineralized products, i.e. wood, wooden material and other cellulosic material, in such a way as to allow their intended functions while also providing one or more of the following properties or functions: i) protection against fungi, ii ) improving their biological resistance, iii ) improving moisture and weather resistance, iv) reducing flammability, v) improved fire resistance.

Detailed Description of the Invention

The purpose of this invention is to provide an improved method for mineralization of wood, wooden material, for example materials containing wood, such as windows, tables and doors, and other cellulosic material, the method comprising: i) a first impregnation step, comprising a first impregnation of wood, wooden material or other cellulosic material with an aqueous solution of potassium methyl siliconate or potassium oxalate, ii) a first drying step, comprising drying of the wood, wooden material or other cellulosic material, iii ) a second impregnation step, comprising a second impregnation of wood, wooden material or other cellulosic material with an aqueous solution of calcium chloride or C0 ₂ (gaseous or fluidic) and iv) a second drying step, comprising drying of the wood , wooden material or other cellulosic material.

Typically, the concentration of potassium methyl siliconate or potassium oxalate dissolved in the solution is 1 00% of their saturation concentration . Additionally, the concentration of calcium chloride dissolved in the solution may be 1 00% of its saturation concentration . It is preferred that the first and/or the second impregnation comprises a phase of overpressure during which the pressure is selected in the range of 5 - 1 0x 1 0 ⁵ Pa ( 5- 1 0 bar) and the temperature in the range of 1 5 to 50°C. According to a further preferred embodiment, the duration of the phase of overpressure in the first and/or the second impregnation step is≥ 1 hour, typically 1 - 24 h, preferably 4-8 h . According to a further preferred embodiment, the first and/or the second impregnation is preceded by a vacuum phase, during which the wood , wooden material or other cellulosic material is exposed to underpressure, preferably for 30 minutes at 40 to 60 °C and preferably to an underpressure of 1 - 3x 1 0 ⁴ Pa ( 1 00-300 mbar).

According to a further preferred embodiment the wood, wooden material or other cellulosic material is dried above the fiber saturation level of 28-35 %, preferably 30% in the first drying step. A fiber saturation level of 1 00% (fiber saturation point) is the point in the drying process at which only water bound in the cell walls remains and all other water having been removed from the cell cavities.

The first drying step comprises preferably a vacuum phase, during which the wood, wooden material or other cellulosic material is exposed to underpressure, preferably for 30 minutes at 40 to 60 °C and preferably at an underpressure of 1 - 3x 1 0 ⁴ Pa ( 1 00-300 mbar).

Typically, the wood , wooden material or other cellulosic material is dried to a wood moisture, preferably a wood moisture of 1 2 to 1 6 % in the second drying step. The wood moisture is calculated by the formula (m _s -md)/md * 1 00, wherein m _s is the mass of the sample and irid is the mass of the sample after drying in an oven at 1 03 °C until mass constancy.

Wood, wooden material or other cellulosic material which is mineralized in a method according to the present invention is characterized in that calcium methyl siliconate or calcium oxalate or polymethyl silicic acid of low or no solubility in water is deposited in the wood, wooden material or other cellulosic material, preferably in crystalline form. Preferably the untreated wood, wooden material or other cellulosic material gains 30 - 40% weight by mineralization with calcium methyl siliconate, 40 - 50 %, by mineralization with calcium oxalate and 20-30% by mineralization with polymethyl silicic acid.

The mineralization with calcium methyl siliconate is also based on two impregnation steps. In the first step, the material is impregnated in an aqueous solution with potassium methyl siliconate CH ₃ Si (OH ) ₂ OK. After impregnation with the anion, the material is dried and then impregnated with calcium chloride CaCI ₂ (cation ) in aqueous solution . The potassium methyl siliconate already present as anion in the material to be mineralized and the calcium chloride provided in the second impregnation step form calcium methyl siliconate {[CH ₃ Si (OH )20]2Ca} _S oiid, preferably in crystalline form, which is practically not soluble in water, and KCI.

In this reaction, the molar ratio between both reactive compounds is 2: 1 . For the reactive compounds preferably solutions of 2: 1 molar content are prepared. The molecular weight of CH ₃ Si (OH ) ₂ OK is 1 32.23 g/mol, the water solubility 51 .5 g/ 1 OOg H ₂ 0. The molecular weight of CaCI ₂ ^« 6H ₂ 0 is 21 9.08 g/mol, the water solubility 81 .3 g/ 1 00g H ₂ 0. For 2: 1 solutions 587. 1 0 g potassium methyl siliconate is dissolved per 1 L H ₂ 0 and 485.5 g calcium chloride per 1 L H ₂ 0.

M ineralization with calcium oxalate

The mineralization with calcium oxalate is also based on two impregnation steps. In the first step, the material is impregnated in an aqueous solution with potassium oxalate C ₂ 0 ₄ K ₂ . After impregnation with the anion , the material is dried and then impregnated with calcium chloride CaCI ₂ (cation ). The potassium oxalate already present as anion in the material to be mineralized and the calcium chloride form calcium oxalate {C ₂ 0 ₄ Ca} _SO iid, preferably in crystalline form, which is practically not soluble in water, and KCI. In this reaction, the molar ratio between both reactive compounds is 1 : 1 . For each reactive compound preferably a solution of equimolar content is prepared. The molecular weight of C ₂ 0 ₄ K ₂ - H ₂ 0 is 1 84.23 g/mol, the water solubility 38.7 g/ 1 00g H ₂ 0. The molecular weight of CaCI ₂ - 6H ₂ 0 is 21 9.08 g/mol, the water solubility 81 .3 g/ 1 00g H ₂ 0. For equimolar solutions 387 g potassium oxalate is dissolved per 1 L H ₂ 0 and 460 g calcium chloride per 1 L H ₂ 0.

The mineralization with polymethyl silicic acid is also based on two impregnation steps. In the first step, the material is impregnated in an aqueous solution with potassium methyl siliconate CH ₃ Si (OH ) ₂ OK. After impregnation with the anion, the material is impregnated with C0 ₂ either in the fluidic or the gaseous state. The potassium methyl siliconate already present as anion in the material to be mineralized and the C0 ₂ provided in the second impregnation step form polymethyl silicic acid {[CH ₃ Si (OH ) ₂ 0-] _n }soiid, which is practically not soluble in water, and K ₂ C0 ₃ .

Calcium chloride (CaCI ₂ ) Calcium chloride is an ionic halide in solid state at room temperature. CaCI ₂ is a hygroscopic compound and forms solutions in water dissociating in calcium and chloride ions. It can be commercially found in pure state, but more commonly as hyd rated compound for example as mentioned above as CaCI ₂ - 6H ₂ 0, or as CaCI ₂ -4H ₂ 0, CaCI ₂ - 2 H ₂ O or CaCI ₂ - H ₂ 0. Properties will evidently depend on its hydration degree. For the tests performed CaCI ₂ - 6H ₂ 0 was employed .

From the safety and environmental side, calcium chloride and its solutions represent the same risks as other common non-toxic chlorides, e.g. NaCI, LiCI and KCI. Therefore its solutions can be considered as harmless to plants and soil, hence environmentally friendly for wood impregnation , if some residues of this compound remain. Potassium oxalate (C ₂ 0 ₄ K ₂ )

Potassium oxalate is a salt of oxalic acid. Its appearance is that of transparent and colorless crystals. In aqueous solutions it can dissociate to form oxalate and potassium ions. Oxalate ions can be combined with calcium, magnesium, and iron ions to form less water-soluble or insoluble salts. Potassium oxalate is commercially available as anhydrous and monohydrate salt. In the current experiments, the monohydrate (C ₂ 0 ₄ K ₂ - H ₂ 0) was used . Once the oxalate anion has reacted with the cation from the calcium chloride solution it forms an insoluble salt (C ₂ 0 ₄ Ca ) that is retained in wood, providing the protection effect.

Potassium methyl siliconate (CH ₃ Si (OH ) ₂ OK) Potassium methyl siliconate is commercially available as an aqueous solution and it is commonly used in diluted form for water-repellent applications. Aqueous solutions may be highly alkaline and therefore care must be taken during handling .

Wood, wooden material and other cellulosic material .

Two wood species commonly used in construction are beech ( Fagus sylvatica ) and pine ( Pinus sylvestris ). They are representative species of European hardwood and softwood and grow in important volume in Switzerland and other central European countries. Furthermore, they are listed as suggested species in the norm EN 1 1 3 , for biological tests of impregnated wood. These two wood species were used in the experiments described below. Beech ( Fagus sylvatica ) is a hardwood belonging to the division of angiosperms. As it is characteristic for hardwoods, beech is composed by vessel elements, fibers (tracheids), parenchyma and ray cells. Vessels are arranged in a non -specific pattern , resulting in a semi-porous to diffuse porous distribution. Growth ring limits are demarked by dark colored late wood . Density varies from 0.48 - 0.68 - 0.88 g/cm ³ .

Pine ( Pinus sylvestris ) is a softwood belonging to the division of conifers. Pine is mainly composed by tracheids, as is characteristic for softwoods and has well differentiated thick walls in late wood and thin walls in early wood. Density varies from 0.3 - 0.49 - 0.86 g/cm ³ (in the early zone).

Further types of wood preferably used in the method according to the invention are: silver fir, maple, cotton wood and alder.

Wood which fulfils the requirements for wood according to the norm EN 1 1 3 is preferably used and mineralized in the method according to the present invention . The main requirements of the norm EN 1 1 3 are: a ) Wood quality: wood should have straig ht grains and no knots. Pine should be exclusively of sapwood and poor in resin . Beech should not have red heart. b) The number of annual rings in the width direction must be 2.5 - 8 per cm for pine, and 2 - 6 per cm for beech. c) The direction of the rings in the cross section could have any direction but should not be tangential to the width direction of the cross section . d ) The proportion of latewood in the cross section should not be more than

30% . e) Moisture content in wood should be 1 2 %. f) Wood must not have floated in water, not have been dried over 60°C and neither have been chemically treated . g ) The density of samples must not vary more than ± 1 0 % from the mean value for samples that will be treated and not more than ± 20% for samples that will be used for control. h ) The stated size of specimens is 50x25x 1 5 mm ³ . Leaching : brief description of the EN84 procedure

In order to evaluate and quantify the mineralization process (i.e. the retention of impregnated insoluble material in treated specimens) leaching tests were per-formed . The description of the leaching process can be found in the standard EN84. A summary of the main points to be considered for the current tests is presented below. a ) Specimens to be leached include untreated samples (control ) besid

ones that are mineralized . b) Every material species and treatment must be separated in different leaching baths. The quantity of deionized water is l OOmL per sample of

50x25x 1 2mm ³ . As for impregnation , specimens need to be completely covered and weights need to be added to avoid samples to float. c) First, specimens submerged into the deionized water bath undergo a vacuum (40 mbar) during 20 min. Then, they stay at atmospheric pressure during 2 hours. Afterwards this first water bath is poured and changed . d ) Samples are then transferred to a room at 20 ± 2 °C and 65 ± 5 % RH .

Here, samples remain during 1 4 days, and water is changed 9 times. The first change must be done after 1 day and the following after 2 and 3 days. Biological tests

The biological tests were done on the basis of the European Standard EN 1 1 3 ( European Standard , 1 996 ) with some modifications in order to allow accelerated tests. Two series of biological tests have been carried out in order to evaluate the resistance of the mineralized woods, wooden materials and other cellulosic materials against fungi and biological deg radation .

According to the literature ( Bravery and Dickinson , 1 978) it is possible to employ smaller wooden blocks in order to accelerate the duration of the test to 6 to 1 0 weeks, depending on the size of the samples ( EN 1 1 3 incubation time is 1 6 weeks). This method has been used for the present tests.

Fungi used in the tests were Coniophora puteana, Coriolus versicolore and Poria placenta .

For characterization two methods were employed . For gravimetry the weight of wood specimens was measured at several points of the experimental process. Since the reactives/products of impregnation/mineralization have a significant weight and concentration , the gained weights in wood and other specimens treated were perfectly measureable. Obviously, specimens with bigger sizes give more accurate results than small ones, since the volume of samples and absorbed materials are already more representative. For microscopy (as the second method ) analysis were done with raster electron microscope, H itachi TM 1 000 with a Wolfram Cathode (Voltage: 1 5kV) as electron source and a backscattering electron detector with a magnification of 20- 1 0 ^' OOO. The samples were prepared in several different ways. For each mineralization type, samples were boiled or simply humidified on the surface. With this approach it was possible to estimate stability against leaching . The cutting was done with a sliding microtome and single use knifes. To understand the changes due to the impregnation procedure and due to the degradation by fungi, reference samples were prepared as well.

Evaluation of treatment efficiency

The weight loss percentages of mineralized samples was determined after attack with different fungi according to EN 1 1 3 and before leaching .

In all treatments, impregnated samples suffered less weight loss after fungi attack ( not higher than 4% for the majority of treated samples) than control samples that were placed in the same fungi infested petri dishes.

Fire tests

The fire tests were performed according to EN ISO 1 1 925- 2. The samples are placed vertically into the holding device and the burner is installed in front of the sample tilted 45°. The distance of the burner from the unprotected edge of the sample is 1 6mm. The flame has a length of 20mm. With this experimental set up the samples get flame treated for a fixed time depending on the material. Then the burner with the flame gets removed. The evaluation of the burn ing test is done via the time the sample burns after removing the flame and the dimension of the burning pattern on the surface.

Brief Description of the Figures

Fig. 1 shows a schematic flow chart of the mineralization method according to the present invention ; Fig. 2 shows a schematic flow chart of an preferred embodiment of the mineralization method according to the present invention comprising vacuum phases preceding the first and the second impregnation ;

Fig. 3 compares the solid content of Pine and Beech samples treated by methods T1 , T2 and T3 before and after leaching, (T1 calcium oxalate, T2 calcium methylsiliconate,

T3 _gas polymethyl silicic acid polymerized with pressurized C0 ₂ , T3 I iq polymethyl silicic acid polymerized with liquid C0 ₂ );

Fig. 4 shows the weight loss of samples mineralized with calcium oxalate and control samples after exposure to fungi (following EN 1 1 3 ) before leaching , illustrating a clear trend showing that impregnated samples provide a protection effect of wood against fungi attack. Furthermore, Fig, 4 shows that Coniophora puteana cultures are more active than Coriolus versicolor cultures. P-T1 -CN ( Pine Calcium oxalate Coniophora puteana ), P-T1 -CR ( Pine Calcium oxalate Coriolus versicolor), B-T1 - CN ( Beech Calcium oxalate Coniophora puteana ), B-T1 -CR ( Beech Calcium oxalate Coriolus versicolor);

Fig. 5 shows the weight loss of samples mineralized with Calcium methyl siliconate and control samples after exposure to fungi (following EN 1 1 3 ) before leaching . Fig. 5 illustrates a clear trend showing that impregnated samples provide a significant protection effect of wood against fungi attack. P-T2-CN Pine Calcium methyl siliconate Coniophora puteana, P-T2-CR Pine Calcium methyl siliconate Coriolus versicolor, B-T2-CN Beech Calcium methyl siliconate Coniophora puteana, B-T2- CR Beech Calcium methyl siliconate Coriolus versicolor;

Fig 6 shows burn ing time after removal of the flame for different mineralized wood samples of fir and beech, following EN ISO 1 1 925- 2 (treatment 1 calcium oxalate, treatment 2 Calcium methyl siliconate, treatment 3 polymethyl silicic acid ). As can be seen , all treatments 1 -3 significantly improve the fire resistance of the wooden samples;

Fig. 7 to Fig. 1 1 show pine and beech samples mineralized with Calcium methyl siliconate and Calcium oxalate and polymethyl silicic acid .

Fig 7 shows REM images of an untreated reference beech sample before (a ) and after

(c) fungi attack as well as of untreated reference pine sample before (b) and after

(d ) fungi attack (Coniophora puteana ). In beech the deg radation caused by Coniophora puteana (c) becomes obvious by the holes between the cells, in pine, (d ) the deg radation by the same fungi leads to cracking of the cell walls.

Fig 8 shows REM images of beech treated with calcium chloride and potassium oxalate after leaching for 9 days and boiling for 4 hours ( 1 1 7°C). Calcium oxalate crystals are produced in the lumen of the cells. Mainly the vessels are filled with calcium oxalate (a, c), but also in the lumen of the fibers and parenchyma cells (b) Oxalate crystals are present. The reaction product not always fills the whole cell lumen but it covers the cell wall surface (a, d ).

Fig 9 shows REM images of pine treated with calcium chloride and Potassium oxalate after leaching for 9 days. The oxalate crystals can be detected in the late and early wood tracheids (a,b). Mainly the cell walls (e) are covered but sometimes the whole lumen is filled (c,d). A high concentration of reaction product is present in the bordered pits (f ). As the REM samples were taken from the center of the wood piece, and the calcium oxalate is distributed over the whole sample, Figure 9 demonstrates that the impregnation takes place in the whole sample and in almost every cell. Fig 1 0 shows REM images of beech treated with calcium chloride and potassium methyl siliconate after leaching for 9 days and boiling 4 hours ( 1 1 7°C). The lumen of the cells and the fibers are filled , the crystals form a solid bloc (a, b). The cell wall layer is also infiltrated and intensively covered with the reaction product (c (leached and boiled ), d (only leached ) ). The cavities of the radial parenchyma cells are less filled in comparison to the bigger lumen of the vessels (e).

Fig 1 1 shows REM images of pine treated with calcium chloride and potassium methyl siliconate after leaching for 9 days. Siliconates are visible in the early and late wood tracheids (a ). Some of the cells are completely filled with the siliconate crystals ( b) and sometimes the cell wall is covered by a layer of these crystals (e). The membranes of the bordered pits are often infiltrated and mineralized by the impregnation products (c, d ) .

The following parag raph describes the process steps of mineralization at an industrial level for facade claddings according to one embodiment of the present invention . The procedure can be applied for the mineralization with calcium oxalate and calcium methyl siliconate. To guarantee the process safety the industrial application of this specific mineralization will be done in two autoclaves with systems to monitor the vacuum-pressure cycle.

1 . Supply of the wood material: dimensions 1 20x20x2500mm (moisture content between 1 2 - 1 6% )

2. Filling the first autoclave with the wood material (beech or pine),

3. Filling the autoclave with the solution of the anion ( Potassium methyl siliconate or Potassium oxalate)

4. Application of vacuum of ca. 1 00 mbar for 2 h 5. Application of pressure of ca. 8 bar for ca. 4 h and temperature in the range of 1 5

-25 °C

6. Empty the autoclave and transport the wood material to the dryer

7. Drying the wood in a conventional kiln to a moisture content of ca. 30 %

8 Filling the second autoclave with the dried wood material

9. Filling the second autoclave with the cation solution (Calcium chloride)

1 0. Application of vacuum of ca. 1 0Ombar for 2h

1 1 . Application of pressure of ca. 8bar for ca. 4h and temperature in the range of 1 5 - 25 °C

1 2. Drying the mineralized wood to 1 2- 1 6%

The following parag raph describes the process steps of mineralization at an industrial level for facade claddings according to a further embodiment of the invention . The procedure can be applied for the mineralization with polymethyl silicic acid. The industrial application of the mineralization will be done in one autoclave with a system to monitor the vacuum- pressure cycle.

1 . Supply of the wood material : dimensions 1 20x20x2500mm ( moisture content between 1 2 - 1 6 % )

2 Filling the autoclave with the wood material ( beech or pine),

3 the autoclave with the solution of the anion ( Potassium methyl siliconate)

4 Application of vacuum of ca. 1 00 mbar for 2h Application of pressure of ca. 8 bar for ca. 4h and temperature in the range of 1 5 - 25 °C Empty the autoclave and remove the wood material to the dryer Drying the wood in a conventional kiln to a moisture content of about 30% Filling the autoclave with the dried wood material Application of C0 ₂ in gaseous state with ca. 2 bar for 1 0 h. and temperature in the range of 1 5 -25 °C