Next Article in Journal
Predicting Changes in Forest Growing Season (FGS) in the Transitional Climate of Poland on the Basis of Current Grid Datasets
Previous Article in Journal
Analysis of Plant Trait Data of Host Plants of Lycorma delicatula in the US Suggests Evidence for Ecological Fitting
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Exploratory Pressure Impregnation Process Using Supercritical CO2, Co-Solvents, and Multi-Cycle Implementation

New Zealand Forest Research Institute (Scion), 49 Sala Street, Private Bag 3020, Rotorua 3046, New Zealand
*
Author to whom correspondence should be addressed.
Forests 2022, 13(12), 2018; https://doi.org/10.3390/f13122018
Submission received: 25 October 2022 / Revised: 21 November 2022 / Accepted: 25 November 2022 / Published: 29 November 2022
(This article belongs to the Section Wood Science and Forest Products)

Abstract

:
Supercritical carbon dioxide (scCO2) is extensively used for extracting chemicals from materials, but the impregnation of materials with chemicals using scCO2 has received little attention in comparison. To the best of our knowledge, most technologies described in the literature operate by the principle of diffusion, where impregnation yield is limited by solubility. The objective of this exploratory study is to prove the feasibility of an scCO2 impregnation process that can extract solutes from one material and release them into another material through a single extraction/impregnation stage that can be applied in cycles to increase the yield. The feasibility of the concept was proven in the laboratory using radiata pine bark wax as the solute and radiata pine wood as the impregnated material. Extraction/impregnation tests were performed at temperatures between 40 and 60 °C, pressures between 12 and 16 MPa, and with the addition of ethanol and acetone as co-solvents. The study demonstrated the feasibility of multi-cycle scCO2 impregnation of wax into wood, where the novelty of the concept is the implementation as traditional pressure impregnation methods.

1. Introduction

Bark protects trees from the external environment [1]. Bark cells contain relatively large amounts of specialized biomacromolecules such as suberin, extractives, and lipids that play a major role in the hydrophobicity and low permeability of bark [1]. Nature seems to have created a complex material that provides extreme repellence to water, and at the same time has high affinity for hydrophilic wood cells [2]. These materials can be extracted from plants using organic solvents such as heptane, ethanol, diethyl ether, 2-methyl tetrahydrofuran, acetone, toluene, ethyl acetate, propanol, butan-2-ol, dimethyl carbonate and methanol [3].
It was reported that extractives from radiata pine bark were highly hydrophobic and had wax-like film-forming properties [2]. The extractives showed a remarkable affinity for wood as revealed by the high degree of resistance to water penetration and wetting of wax treated wood, even after several wetting/drying cycles [2]. Since bark is a residue from timber manufacturing, there is the research question of whether the same wax that protects living trees from the environment could be used to protect timber products in service.
Impregnation of timber with oils and waxes is common for increasing water repellence and improving outdoor performance properties such as dimensional stability, photostability, and resistance against decay fungi and termites [4]. Impregnation has been performed by pressure treatment with melted wax and wax emulsion [4]. For example, timber was impregnated with melted esterified montan acids, modified plant wax, amid wax, paraffin and montan ester wax at 100 °C and 120 °C [5]. Montan wax in aqueous emulsion was also impregnated in wood by pressure treatment [6].
Pressure impregnation with solvents is a practical method depending on the permeability of timber [7], but it requires drying twice. First to remove water from the fresh timber and then again to remove the solvent. Using supercritical carbon dioxide (scCO2) as solvent is an option since CO2 is gas at ambient conditions, thus evaporates spontaneously leaving no solvent behind. scCO2 can also extract hydrophobic waxes from bark [8]; thus, scCO2 could be used for both extraction and impregnating perhaps in a single process. Figure 1 show a conceptual representation of a such hypothetical process.
Scion investigated scCO2 impregnation extensively in the past, and the consensus was that it is not practical for timber. Anecdotical evidence suggested that solubility of waxes in scCO2 is very low; thus, impregnation was almost negligible in comparison to what it is required for timber protection. To increase the amount of wax impregnated in timber, the process would need to be implemented in cycles, but this has never been tried before with scCO2 as far as the authors know.
This study revisits the idea of scCO2 impregnation of waxes in wood. First a literature review was carried out to confirm that multi-cycle scCO2 impregnation of wax in wood has not been investigated before. Then, a single-cycle scCO2 impregnation process was tested for different conditions to confirm that wax impregnation is very low in timber. Finally, two options for multi-cycle scCO2 impregnation were proposed and validated at an exploratory level.

2. Literature Review

2.1. Supercritical CO2 Extraction

scCO2 is extensively used for the extraction of chemical compounds that have low volatility and are susceptible to thermal degradation, especially if there are restrictions for solvents such as in food and pharmaceutical applications [9]. scCO2 extraction is common for natural oils, such as sunflower, tomato, coriander, grape, and peanut seed oils. Solubilities were reported between 2 and 15 mg/g at pressures from 20 to 55 MPa and temperatures from 25 to 50 °C [10].
Other examples are extraction of cottonseed oil at pressures from 35 to 55 MPa and temperatures from 60 to 80 °C [11], and extraction of flaxseed oil at pressures from 21 to 55 MPa and temperatures from 50 to 70 °C [12]. Solubility of flaxseed oil in scCO2 increased from 2.3 mg/g at 21 MPa to 11.3 mg/g at 55 MPa, while corn, soybean, and canola oils reported solubilities between 7.3 and 12 mg/g [12].
scCO2 extraction was also applied to reduce the amount of oil contained in nuts, such as hazelnut, almond, peanut, pecan, and pistachio [13]. Hazelnut oil was extracted at pressures from 15 to 60 MPa and temperatures from 40 to 60 °C. It was found that the solubility increased from 1.0 mg/g at 15 MPa to 28.8 mg/g at 60 MPa [13]. It has been applied to extract natural compounds such as nimbin (which is believed to have insecticidal activity) from neem seeds at 35 °C and 23 MPa [14], alkadienes, carotenoids, β-carotene and γ-linolenic acid from microalgae at temperatures from 40 to 60 °C and pressures up to 35 MPa [15], and lycopene and b-carotene from tomato sauce at temperatures from 35 to 65 °C and pressures from 20 to 30 MPa [16]. The addition of 5% ethanol in scCO2 increased b-carotene and lycopene recovery by, respectively 50 and 55% [16].
The extraction of unsaturated fatty acids from bark with scCO2 was also reported in the literature [8]. It was found that increasing the pressure increases the recovery of wax and sterol esters, while increasing the temperature enhances resin acids solubility. Adding polar organic solvents such as methanol, ethanol and acetone in small amounts achieves higher yields of phenolics, lignans and flavonoids compounds [8]. In summary, scCO2 extraction is a well-known process with many commercial applications that can be used to extract wax from bark.

2.2. Supercritical CO2 Impregnation

scCO2 impregnation of solids has been proven feasible, but there is only a handful of commercial applications [17]. These include the impregnation of wood with biocides [18], dyeing of textiles [19], and reactive tanning of leather [20]. All these technologies operate by the principle of diffusion: a material is first pressurized with scCO2 and then a solute is let to diffuse through the scCO2 into the material. To impregnate wood with biocides, scCO2 at temperatures between 40 and 60 °C was first pressurized to 15 MPa and then recirculated through a small mixing vessel to add fungicide [21]. Treatment times were from 1.5 to 5 h.
Dyeing of textiles was implemented in a flow-type cylindrical vessel [22], in which the dye and the fabric were placed in a vessel, and then scCO2 was introduced at a flow rate that assured saturation with the dye. For impregnation of polyester textiles with mango leaf extract, 5% of methanol was added. Temperatures from 35 to 55 °C and pressures from 40 to 50 MPa were used, and treatment times from 15 to 24 h were recommended to maximize impregnation yield [23]. Dying of textiles with scCO2 has been also reported for temperatures from 40 to 160 °C, pressures from 5 to 140 MPa, process times from 5 to 1620 min, and a range of different co-solvents including water, acetone, and alcohol [24].
Impregnation by diffusion tends asymptotically to equilibrium conditions that are determined by the concentration of a solute in a solvent (Darcy’s law of diffusion). If the solubility in scCO2 is low, then diffusion is slow and limited to transfer small concentrations of solutes. As far as the authors could confirm, scCO2 impregnation has never been applied as traditional pressure impregnation process. This is a recurring theme in this study because impregnation by diffusion is limited to a maximum determined by the solubility of a solute in scCO2. In this study “traditional pressure impregnation” means that the wax will be dissolved in the scCO2 before it is pushed into the wood by pressure, so that the same cycle can be repeated more than once to increase the impregnation yield. The closest example found in the literature was reactive tanning of leather, in which a tanning solution was deposited on the surface of leather, and then scCO2 was used to push the tanning inside the leather by pressure [17].

2.3. Solubility of Fatty Acids in scCO2

A main challenge for implementing scCO2 impregnation as a traditional pressure treatment, is the complex relationship between pressure, temperature, and solubility in scCO2. Selected pressure vs. density isotherms for CO2 are shown in Figure 2, as calculated with an equation of state [25]. The red dot indicates the critical point at approximately 31 °C and 7.4 MPa. Below the critical pressure, there is a range of densities that cannot be realized in normal conditions, where CO2 separates into liquid and gas. The dotted lines in Figure 2 show gas and liquid densities in equilibrium at the same pressure (connected by blue horizontal lines). Above the critical point the CO2 never separates into liquid and gas.
Density and temperature are the main parameters affecting the solubility of lipids in scCO2. There are a series of semiempirical models for determining the solubility of solids in supercritical fluids [26]. It is claimed that the “Chrastil model” is the first one [27]. It is based on the theory of chemical association and expressed as shown in Equation (1):
l n ( S ) = A 1 + A 2 T + A 3   l n ( ρ )
where S = solubility in a supercritical fluid [kg/m3], ρ = density of the supercritical fluid [kg/m3], T = temperature [K], A1 = empirical parameter (function of the molar mass of the solute), A2 = empirical parameter (function of the enthalpy of solvation and enthalpy of vaporization), and A3 = empirical parameter (association number).
Experimental data of lipids solubility in scCO2 were compiled to calculate the Chrastil model parameters [28]. The compilation included fatty acids, monoglycerides, diglycerides, triglycerides, methyl esters, and methyl esters. For lauric, myristic, palmitic, stearic, oleic and linoleic fatty acids, A1 ranged from 12.0 to −46.3, A2 ranged from −2853 to −15,890, and A3 ranged from 5.81 to 9.71. Figure 3 shows an example of solubility calculated using average parameters for the six previous fatty acids (A1 = −21.7, A2 = −8211, A3 = 7.48):
Figure 3 shows that at constant temperature the solubility in scCO2 increases proportionally to pressure, but at constant pressure the effect of temperature is ambiguous. At higher pressures (such as 20 MPa) the solubility increases with temperature, but at lower pressures (such as 10 MPa) the solubility reduces with temperature. The phenomenon is referred as crossover in the scientific literature, and it has been confirmed experimentally [29].
A main challenge to impregnate wood using scCO2 as solvent is that solubility rapidly reduces at low pressures. For example, Figure 3 shows that below 9 MPa the concertation of fatty acids in scCO2 is almost negligible at 40 °C. This means that it is not efficient to dissolve fatty acids in scCO2 at low pressure and then raise the pressure to push the scCO2 into the wood. The scCO2 needs to be pressurized first to dissolve fatty acids at high pressure, and then pushed into the wood. This study proposes a method to implement such process in practice and validates it at an exploratory level.

3. Materials and Methods

3.1. Experimental Set Up

The process tested in this study is described schematically in Figure 4. There are two pressure vessels at controlled temperature referred as extraction and impregnation vessels. The solute (Pinus radiata wax in this study) was placed in the extraction vessel together with a liquid co-solvent when applicable. The wood sample was placed in the impregnation vessel. There were 3 valves controlling the flow of CO2 into (valve 1), between (valve 2) and out of the vessels (valve 3). Valve 1 connected the extraction vessel to a pump (Supercritical Fluid Technologies Inc., Honolulu, HI, USA, SFT-10 CO) that supplied CO2 at controlled flow rate until reaching set-point pressure.
The extraction vessel was an approximately 150 mm long by 30 mm internal diameter stainless steel cylinder (100 mL nominal volume) heated with an external electric jacket. The impregnation vessel was an approximately 159.5 mm long by 14.15 mm internal diameter stainless steel pipe (25 mL nominal volume) submerged in a water bath at controlled temperature. A picture of the actual experimental set-up is shown in Figure 5. The extraction vessel’s output and input valves (7 and 8) are both connected to the top of the vessel, but there is an internal 5 mm diameter pipe inside the extraction vessel that discharges the input CO2 at the bottom.
The wood samples were purchased in a local store. The wood product was a 3 m long by 12 mm diameter stick labelled non-treated kiln-dried radiata pine. The sticks were cut into 150 mm long cylinders to fit in the impregnation vessel. Four 3 m long sticks were purchased and cut into four groups of 14 matched wood cylinders for testing. Figure 6 shows an example of a wood sample as it is removed from the impregnation vessel.

3.2. Process Implementation

The scCO2 extraction/impregnation process depicted in Figure 4 was implemented according to the following steps:
Step 1: Wax was placed in the 100 mL extraction vessel
Step 2: With valve 1 = open and valve 2 = closed, the extraction vessel was pressurized to the set point pressure by pumping liquid CO2
Step 3: With valve 1 = closed and valve 2 = closed, the extraction vessel was left to stabilize for approximately 1 h at controlled temperature
Step 4: A wood sample was placed in the 25 mL impregnation vessel
Step 5: With valve 1 = closed and valve 3 = closed, valve 2 was opened to connect the two vessels. This step is referred as “pressure drop” in this study
Step 6: With valve 2 = open and valve 3 = closed, valve 1 was opened to repressurise the two vessels to the set point by pumping additional liquid CO2
Step 7: With all valves = closed, the impregnation vessel was let to stabilize for approximately 10 min at controlled temperature
Step 8: With valve 1 = closed and valve 2 = closed, valve 3 was open to depressurize the extraction vessel
Step 9: Depending on the test, a new wood sample was placed in the impregnation vessel (back to step 4), or valve 3 was closed to start another impregnation cycle (back to step 5)
Since the solubility of organic compounds are expected to reduce with density (based on the Chrastil model), some solutes were expected to separate when the supercritical fluid expanded in Step 5 from the extraction to the impregnation vessels (pressure drop). However, solutes that separate inside the impregnation vessel should dissolve later when the supercritical fluid is recompressed to the set point pressure.
The main assumption for the proposed process is that the average density at which scCO2 saturated with wax leaves the extraction vessel (Step 5) is higher than the average density at which scCO2 leaves the impregnation vessel (Step 8). Under this condition, there will be more wax entering the impregnation vessel than leaving the impregnation vessel.

3.3. Process Conditions

Two process temperatures were tested in this study: 40 and 60 °C. The first was selected to be slightly higher than the critical CO2 temperature (31.04 °C), and the second was selected to be slightly higher than the wax melting point as determined in this study. The process pressure was selected to ensure that the pressure did not drop below the critical point of an scCO2 + ethanol mixture during Step 5. The pressure drop was estimated theoretically with the CO2 equation of state [25] for a volume expansion from 100 to 125 mL. Theoretical pressures after pressure drops from 12 and 16 MPa are shown in Table 1.
The critical pressures for a CO2 + ethanol mixture were estimated from phase diagrams published in the literature [30]. Estimated critical pressures were 8 and 11 MPa at, respectively 40 and 60 °C. This means that pressure in the 60 °C/12 MPa condition would have likely dropped below the critical point for a CO2 + ethanol mixture; thus, it was not tested in this study. The 40 °C/12 MPa, 40 °C/16 MPa, and 60 °C/16 MPa conditions were tested in this exploratory study.
Tests were performed with scCO2 + wax, scCO2 + ethanol, scCO2 + ethanol + wax, and scCO2 + acetone + wax for comparison. All tests were performed in triplicate with matched wood samples. The extraction vessel was filled with wax and co-solvent before the first replicate; thus, subsequent replicates used wax and co-solvent remaining from the previous step. Triplicates for all tests were treated in the same order.
Tests were also designed to have enough wax and co-solvent to complete all cycles without opening the extraction chamber. It was assumed that during impregnation the fluid distributes uniformly between the 100 mL and 25 mL vessels, and then 25 mL was removed during depressurization. For example, 30 g of ethanol should reduce to 12.3 g after four cycles according to the assumption. Experimental tests confirmed that 30 g of ethanol reduced to approximately 12 g after four cycles.

3.4. Wax Characterization

It was stated in the introduction the aim of this study was to assess the feasibility of a combined extraction/impregnation scCO2 process that takes wax from pine bark and impregnates it into pine wood. To reduce uncertainty, however, this exploratory study used wax that was already extracted from radiata pine bark using scCO2 extraction equipment at 50 °C and pressures between 10 and 30 MPa.
Chemical composition of the wax was measured as trimethylsilyl ester derivative using gas chromatography–mass spectrometry (GC-MS). A sample was accurately weighed and dissolved in chloroform to give a concentration of around 1 mg/mL. 50 μL of dibromoanthracene (DBA) in pyridine (1 mg/mL) was added as an internal standard. All hydroxyl groups in each compound were derivatised to trimethyl silyl esters by addition of 100 μL of BSTFA:TMCS 9:1 (v/v) followed by vortexing and heating at 70 °C for 1 h. Samples were immediately transferred to GC-MS for measuring.
The thermal stability of the wax was measured by thermogravimetric analysis (TGA) with a Discovery TGA (TA instruments, New Castle, DE, USA). About 10 mg of the samples were placed in a platinum sample pan under nitrogen atmosphere (10 mL/min). Temperature was ramped from ambient to 800 °C at 10 °C/min and then maintained for 10 min. Five replicates were measured.
The melting point of the wax was determined with a differential scanning calorimeter (DSC) DSC 214 Polyma (TA instruments, New Castle, DE, USA). For the crude wax, two main state transitions were characterised by DSC, namely, endothermic and exothermic. The endothermic and exothermic transition represents the amount of heat exchanged to, respectively melt and crystalize the sample. No obvious glass transition was observed. Due to peak superimposition related to the numerous components present in the wax, only the total melting and crystallization enthalpiesa were calculated. It was not possible to associate the peaks to specific components.

3.5. Oven-Dried Tests

Before and after impregnation, the wood was dried with air at 103 °C for 24 h to determine oven-dry (OD) weight. Since weight gains were expected to be very low, the accuracy of the measurements was assessed at the beginning of the study. The balance was a Mettler Toledo NewClassic ML104/01 (Mettler Toledo Ltd., Greifensee, Switzerland) which provided four decimals on 1.0000 g. All 150 mm long wood samples were oven-dried for 1, 2, 3 and 4 consecutive days to measure OD weight at four different instances. The OD weight was calculated as the average of the four instances, and the measurement error was calculated as the difference between individual measurements and the average.

4. Results

4.1. Wax Chemical Composition

The main chemical components detected in the wax are reported in Table 2. Chemical composition was measured because the process could have been predicted if Chrastil model parameters were available for the wax components. Unfortunately, stearic acid was the only component for which average Chrastil parameters were available in the reviewed literature [28].

4.2. Wax Thermal Behaviour

The measured degradation ranges and temperatures of melting and crystallization are reported, respectively in Table 3 and Table 4. Table 3 shows that the first degradation transition occurs between 62.4 °C and 75.5 °C with a mass loss of 2.8%. To avoid wax degradation, the higher scCO2 temperature tested in this study was 60 °C. Table 4 reports three endothermic and exothermic transitions peaks. Peak 3 was dominant; thus, the melting point was assumed 49.2 °C. To compare solid and melted wax the scCO2 temperatures tested in this study were 40 °C and 60 °C.

4.3. Experimental Error

The results of measuring OD weight at four different instances (1, 2, 3 and 4 days) are summarized in Table 5. The table shows that the average OD weight of all wood samples was 8.02 g, and the experimental error ranged between +0.1% and −0.1%. Errors in the order of +/−0.05% (one standard deviation) should be expected with the implemented experimental set-up.

4.4. Single-Cycle scCO2 Tests

Table 6 shows a summary of the average weight gain measured in triplicate for single-cycle extraction/impregnation tests, including scCO2 + wax (W), scCO2 + ethanol (Et), scCO2 + ethanol + wax (Et + W), and scCO2 + acetone + wax (Ac + W). The table shows the initial weight of the samples, weight gain immediately after impregnation (in which wood samples still contained solvent and CO2), and weight gain after oven-drying. Tests with only scCO2 + ethanol (without wax) were performed because the wood contained resins and extractives that could be dissolved by ethanol. Tests with only scCO2 where not included because differences could not be discerned from measurement error. Tests with acetone as co-solvent were performed only as reference since ethanol is the preferred solvent in practice.

4.5. Multi-Cycle scCO2 Tests without Co-Solvent

To test the possibility of implementing the process in cycles, the 40 °C/16 MPa condition was selected. All wood samples were cut from the same 3 m long radiata pine stick (thus, they were all matched samples). The first set of multi-cycle tests were performed without co-solvent. Approximately 3 g of wax was placed in the extraction chamber and let to dissolve in scCO2 for approximate 1 h. Then, three matched samples were exposed to one, three and six successive extraction/impregnation cycles.
The pressure in the vessels was measured visually with an analogic manometer with resolution of +/−0.5 MPa. The pressure dropped in average from 16 MPa to 10.1 MPa during Step 5, which agreed with the pressure drop estimated theoretically in Table 1. After a total of 10 impregnation cycles, the extraction vessel was opened to confirm that most of the wax was still available in the extraction chamber.
The results are shown in Figure 7. Based on a linear fitting, the wood samples gained approximately 0.064% of their OD weight in wax per cycle. The linear fitting also shows that the first cycle added an additional 0.12% weight gain with respect to the subsequent cycles. Since the extraction vessel was let to stabilize for approximately 1 h before the tests, it was thought initially that this could be the reason for having higher weight gain in the first cycle. However, it was later concluded that this could not be the only reason.

4.6. Multi-Cycle scCO2 Tests with Co-Solvent

A second set of multi-cycle tests was performed at 40 °C/16 MPa, with 30 g of ethanol and 1.5 g of wax. Three matched samples were treated, respectively for one, three, and six cycles. Since ethanol is consumed cycle by cycle, then weight gain per cycle could potentially change after one, three and six successive cycles. For this reason, a control sample was treated for one cycle after the sample treated for three cycles, and another control sample was treated for one cycle after the sample treated for six cycles. To minimize the effect of ethanol consumption even further, tests were divided in two groups starting both with 30 g of ethanol and 1.5 g of wax. Results are summarized in Figure 8.
Figure 8 shows that weight gain immediately after impregnation (which still retains ethanol and CO2) and weight gain after oven-drying (which only retains wax) are not considerably affected by the number of cycles. It is apparent from Figure 8 that there is an approximately fixed amount of co-solvent and wax that could be retained inside the wood regardless of the number of cycles. For this reason, a final exploratory test incorporated drying between cycles.
The same five matched samples that were treated in Figure 8, were exposed to three more cycles starting with the same process conditions (40 °C, 16 MPa, 30 g ethanol and 1.5 g wax). The difference was that the samples were oven-dried between cycles. The results are shown in Figure 9. Based on a linear fitting the samples gained approximately 0.30% of their OD weight in wax per cycle. The linear fitting also shows that the first cycle added an additional 0.42% weight gain.

5. Discussion

5.1. Singe-Cycle scCO2 Impregnation

The average weight gain reported in Table 6 with scCO2 + wax (without co-solvent) ranged between 0.06% and 0.09%. Those percentages are in the same order of magnitude than the experimental error. However, individual weight gains ranged between 0.14% (maximum) and −0.04% (minimum), which was clearly shifted to the positive side of the scale (only 1 out of 9 individual weight gains was negative). The averages therefore were treated as empirical evidence of wax impregnation.
A similar trend was observed with scCO2 + ethanol (without wax) but in the opposite direction. The results showed average weight losses between −0.06% and −0.11% with a maximum/minimum range between −0.01% and −0.17%. This was considered empirical evidence that resin and other extractives were removed from the wood during treatment. Treatments with scCO2 + wax + co-solvent (ethanol or acetone) showed weight gains beyond experimental error. The average weight gain was between 0.45% and 0.56% with ethanol and between 0.34% and 0.37% with acetone.
Summing up, single-cycle impregnation tests produced weight gains below 0.1% without co-solvent and below 0.6% with co-solvents. For comparison, impregnation of wood with paraffin wax emulsion was reported in the literature for 300 mm long by 20 mm wide by 20 mm thick loblolly and Scots pine [4]. Paraffin emulsions were diluted to 2% (w/w) solid contents with distilled water and impregnated by pressure treatment at 2.0 MPa for 90 min. The study reports average weight gains of 3.5% and 2.6% for, respectively loblolly and Scots pine. This supports the conclusion that the process needs to be implemented in more than one cycle to achieve impregnation levels comparable to traditional pressure treatment.
A conclusion from Table 6 is that wood retained considerably co-solvent and CO2 immediately after treatment. It was found that wood treated without co-solvent retained between 3.5% and 3.7% of their OD weight in CO2, while wood treated with co-solvents retained between 9.9% and 16.7% and between 4.8% and 13.7% of their OD weight in both CO2 and, respectively ethanol and acetone. Further research based on this observation is discussed in Section 5.3 Future research.

5.2. Multi-Cycle scCO2 Impregnation

Figure 7 shows that multi-cycle scCO2 impregnation without co-solvent produced approximately 0.064% weight gain per cycle. If a rounded 3% benchmark is used to compare with traditional pressure treatment, then 45 cycles are required to reach similar impregnation levels. Although exploratory, this suggests that scCO2 impregnation without co-solvent may only be efficient if small amount of wax causes a significant improvement in wood performance.
Figure 8 shows that multi-cycle scCO2 impregnation with co-solvent did not increase weight gain in comparison with a single cycle. One possible explanation is that the solvent separated into an ethanol rich liquid phase during decompression, which was then pushed out from the wood by generation of CO2 gas bubbles. This phenomenon is known as scCO2 dewatering [31].
Evidence of separation is provided by the pressure measured during impregnation. Figure 10 reproduces experimental data of CO2 + ethanol phase equilibrium at 40 °C reported in the literature [30]. Figure 10 also includes the range of pressures measured after pressure drop (Step 5) when vessels were connected, starting with 7 mPa in the first cycle and increasing gradually towards 8 mPa cycle by cycle. Based on the phase equilibrium data for a CO2 + ethanol mixture, at 7 to 8 mPa a liquid phase should separate containing theoretically 50% to 20% ethanol in molar basis.
Because of the dewatering effect during scCO2 decompression (Step 8), each cycle left approximately the same amount of co-solvent and wax inside the wood. To circumvent that limitation the wood was oven-dried between cycles. The assumption was that dewatering removes liquid solvent from the cell lumens but not absorbed solvent from the cell walls. Oven-drying leaves the cell walls available to absorb more solvent in the next cycle.
Figure 9 shows that multi-cycle scCO2 impregnation with co-solvent and drying between cycles added approximately 0.30% weight gain per cycle. If a rounded 3% benchmark is used to compare with traditional pressure treatment, then 9 cycles are required to reach similar impregnation levels. An interesting observation was that the first cycle impregnated more wax than subsequent cycles. Since all cycles in the last exploratory tests started exactly with the same conditions, then it was concluded that untreated wood has higher capacity to retain wax than wood that has been already impregnated with wax.
To support that conclusion treated and untreated samples were inspected with confocal microscope (Leica TCS SP5). Figure 11 shows an image of untreated wood under the microscope, and Figure 12 shows an image of wood treated for four cycles with scCO2 + ethanol and drying between cycles. The green fluorescence in both images is assumed to be caused by oven-dried lignin in cell walls [32], but the brighter yellowish fluorescence mainly appears in the wax impregnated wood. Figure 12 shows ray cells and small cavities that are filled with yellowish fluorescent material, and an image close-up (top left corner) shows yellowish fluorescent material deposited inside cell pits. Since there are only limited pits in cell walls, then this would explain why there is more wax retained in the first cycle.

5.3. Further Research

This study demonstrated that it is possible to impregnate wax in wood using scCO2 cycles, but the number of cycles required to achieve levels comparable to traditional pressure impregnation is high at first glance. Further research would require measuring wax penetration into the wood and using fresh bark instead of wax extracted from bark, but a technoeconomic analysis should be performed first based on the preliminary data collected in this study.
It seems apparent (without a technoeconomic analysis) that multi-cycle scCO2 impregnation may only be efficient if small amounts of wax cause a significant improvement in wood performance. In that regard, the finding that wax tends to deposit inside cell wall pits offers opportunities for further research. This should be investigated further because pits plugged with wax may reduce permeability, and consequently prevent timber from absorbing liquid water in service.
A second interesting observation (that was not anticipated before the study) is that scCO2 impregnation with co-solvents retained a considerably amount of solvent after CO2 decompression. The assumption is that dewatering removes liquid solvent from the cell lumens but not absorbed solvent from the cell walls. This could be further investigated as an opportunity for targeted cell wall modification using a co-solvent that can also react with wood, such as furfuryl alcohol for example [33].

6. Conclusions

This exploratory study demonstrated that it is possible to impregnate solid wood with bark wax using scCO2 as the solvent. The novelty is that the process was designed to work as traditional pressure impregnation, in which solutes dissolved in a liquid solvent are pushed into the wood by pressure. As far as it was confirmed from the scientific literature, this differs from previously reported scCO2 impregnation methods based on diffusion.
In addition, the study demonstrated at an exploratory level that the proposed process can be implemented in cycles. The results showed that without co-solvent, radiata pine wood samples gained approximately 0.064% of their OD weight in wax per cycle, with the first cycle adding additional 0.12% weight gain.
When ethanol was added as co-solvent, it was found that successive extraction/impregnation cycles did not increase weight gain in comparison with a single cycle, probably because a liquid phase containing ethanol and wax was pushed out of the wood by formation of CO2 bubbles.
The study showed that this limitation can be circumvented by drying the solvent between cycles. After incorporating drying between cycles, samples gain approximately 0.30% of their OD weight in wax per cycle, with the first cycle adding an additional 0.42% weight gain with respect to subsequent cycles.

Author Contributions

D.E.: Experimental plan, data analysis and paper writing. L.R. and R.R.: Material properties and chemical analysis. L.D.: Microscopy analysis. M.J.L.G.: Funding and supervision. All authors have read and agreed to the published version of the manuscript.

Funding

New Zealand Ministry of Business Innovation and Employment (MBIE) grant number C04X1802 Bark Biorefinery.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

Claire Mayer from France’s National Research Institute for Agriculture, Food and Environment (INRAe) for her suggestions and feedback.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Graça, J. Suberin: The biopolyester at the frontier of plants. Front. Chem. 2015, 3, 62. [Google Scholar] [CrossRef]
  2. Borgin, K.; Corbertt, K. The hydrophobic properties of bark extractives. Wood Sci. Technol. 1971, 5, 190–199. [Google Scholar] [CrossRef]
  3. Sin, E.H. The Extraction and Fractionation of Waxes from Biomass. Ph.D. Thesis, University of York, York, UK, 2012. [Google Scholar]
  4. Wang, W.; Huang, Y.; Cao, J.; Zhu, Y. Penetration and distribution of paraffin wax in wood of loblolly pine and Scots pine studied by time domain NMR spectroscopy. Holzforschung 2018, 72, 125–131. [Google Scholar] [CrossRef]
  5. Scholz, G.; Krause, A.; Militz, H. Exploratory study on the impregnation of Scots pine sapwood (Pinus sylvestris L.) and European beech (Fagus sylvatica L.) with different hot melting waxes. Wood Sci. Technol. 2010, 44, 379–388. [Google Scholar] [CrossRef] [Green Version]
  6. Lesar, B.; Straže, A.; Humar, M. Sorption properties of wood impregnated with aqueous solution of boric acid and montan wax emulsion. J. Appl. Polym. Sci. 2011, 120, 1337–1345. [Google Scholar] [CrossRef]
  7. Pendlebury, A.; Sorfa, E.; Coetzee, J.; Botha, A. A new technique to determine solvent penetration in wood. Holzforschung 1991, 45, 205–208. [Google Scholar] [CrossRef]
  8. Barbini, S.; Jaxel, J.; Karlström, K.; Rosenau, T.; Potthast, A. Multistage fractionation of pine bark by liquid and supercritical carbon dioxide. Bioresour. Technol. 2021, 341, 125862. [Google Scholar] [CrossRef]
  9. Raventós, M.; Duarte, S.; Alarcón, R. Application and possibilities of supercritical CO2 extraction in food processing industry: An overview. Food Sci. Technol. Int. 2002, 8, 269–284. [Google Scholar] [CrossRef]
  10. Reverchon, E.; Marrone, C. Modeling and simulation of the supercritical CO2 extraction of vegetable oils. J. Supercrit. Fluids 2001, 19, 161–175. [Google Scholar] [CrossRef]
  11. Bhattacharjee, P.; Singhal, R.S.; Tiwari, S.R. Supercritical carbon dioxide extraction of cottonseed oil. J. Food Eng. 2007, 79, 892–898. [Google Scholar] [CrossRef]
  12. Bozan, B.; Temelli, F. Supercritical CO2 extraction of flaxseed. J. Am. Oil Chem. Soc. 2002, 79, 231–235. [Google Scholar] [CrossRef]
  13. Özkal, S.G.; Salgın, U.; Yener, M.E. Supercritical carbon dioxide extraction of hazelnut oil. J. Food Eng. 2005, 69, 217–223. [Google Scholar] [CrossRef]
  14. Tonthubthimthong, P.; Chuaprasert, S.; Douglas, P.; Luewisutthichat, W. Supercritical CO2 extraction of nimbin from neem seeds–an experimental study. J. Food Eng. 2001, 47, 289–293. [Google Scholar] [CrossRef]
  15. Mendes, R.L.; Nobre, B.P.; Cardoso, M.T.; Pereira, A.P.; Palavra, A.F. Supercritical carbon dioxide extraction of compounds with pharmaceutical importance from microalgae. Inorg. Chim. Acta 2003, 356, 328–334. [Google Scholar] [CrossRef]
  16. Baysal, T.; Ersus, S.; Starmans, D. Supercritical CO2 extraction of β-carotene and lycopene from tomato paste waste. J. Agric. Food Chem. 2000, 48, 5507–5511. [Google Scholar] [CrossRef]
  17. Weidner, E. Impregnation via supercritical CO2–What we know and what we need to know. J. Supercrit. Fluids 2018, 134, 220–227. [Google Scholar] [CrossRef]
  18. Kjellow, A.W.; Henriksen, O. Supercritical wood impregnation. J. Supercrit. Fluids 2009, 50, 297–304. [Google Scholar] [CrossRef] [Green Version]
  19. Bach, E.; Cleve, E.; Schollmeyer, E. Past, present and future of supercritical fluid dyeing technology–an overview. Rev. Prog. Color. Relat. Top. 2002, 32, 88–102. [Google Scholar] [CrossRef]
  20. Geihsler, H.; Weidner, E. Verfahren zur Zurichtung von tierischen Häuten oder. Fellen. Patent DE19507572A1, 9 December 1996. [Google Scholar]
  21. Iversen, S.B.; Larsen, T.; Henriksen, O.; Felsvang, K. The world’s first commercial supercritical wood treatment plant. In Proceedings of the 6th International Symposium on Supercritical Fluids, Versailles, France, 28–30 April 2003; pp. 445–450. [Google Scholar]
  22. Park, M.-W.; Bae, H.-K. Dye distribution in supercritical dyeing with carbon dioxide. J. Supercrit. Fluids 2002, 22, 65–73. [Google Scholar] [CrossRef]
  23. Sanchez-Sanchez, J.; Fernández-Ponce, M.; Casas, L.; Mantell, C.; de la Ossa, E.M. Impregnation of mango leaf extract into a polyester textile using supercritical carbon dioxide. J. Supercrit. Fluids 2017, 128, 208–217. [Google Scholar] [CrossRef]
  24. Goñi, M.L.; Gañán, N.A.; Martini, R.E. Supercritical CO2-assisted dyeing and functionalization of polymeric materials: A review of recent advances (2015–2020). J. CO2 Util. 2021, 54, 101760. [Google Scholar] [CrossRef]
  25. Huang, F.-H.; Li, M.-H.; Lee, L.L.; Starling, K.E.; Chung, F.T. An accurate equation of state for carbon dioxide. J. Chem. Eng. Jpn. 1985, 18, 490–496. [Google Scholar] [CrossRef] [Green Version]
  26. Rad, H.B.; Sabet, J.K.; Varaminian, F. Study of solubility in supercritical fluids: Thermodynamic concepts and measurement methods-a review. Braz. J. Chem. Eng. 2020, 36, 1367–1392. [Google Scholar] [CrossRef] [Green Version]
  27. Chrastil, J. Solubility of solids and liquids in supercritical gases. J. Phys. Chem. 1982, 86, 3016–3021. [Google Scholar] [CrossRef]
  28. Güçlü-Üstündaǧ, Ö.; Temelli, F. Correlating the solubility behavior of fatty acids, mono-, di-, and triglycerides, and fatty acid esters in supercritical carbon dioxide. Ind. Eng. Chem. Res. 2000, 39, 4756–4766. [Google Scholar] [CrossRef]
  29. Foster, N.R.; Gurdial, G.S.; Yun, J.S.; Liong, K.K.; Tilly, K.D.; Ting, S.S.; Singh, H.; Lee, J.H. Significance of the crossover pressure in solid-supercritical fluid phase equilibria. Ind. Eng. Chem. Res. 1991, 30, 1955–1964. [Google Scholar] [CrossRef]
  30. Tochigi, K.; Namae, T.; Suga, T.; Matsuda, H.; Kurihara, K.; dos Ramos, M.C.; McCabe, C. Measurement and prediction of high-pressure vapor–liquid equilibria for binary mixtures of carbon dioxide+ n-octane, methanol, ethanol, and perfluorohexane. J. Supercrit. Fluids 2010, 55, 682–689. [Google Scholar] [CrossRef]
  31. Asafu-Adjaye, O.; Via, B.; Sastri, B.; Banerjee, S. Mechanism of dewatering porous structures with supercritical carbon dioxide. Case Stud. Chem. Environ. Eng. 2021, 4, 100128. [Google Scholar] [CrossRef]
  32. Donaldson, L. Autofluorescence in plants. Molecules 2020, 25, 2393. [Google Scholar] [CrossRef]
  33. Lande, S.; Westin, M.; Schneider, M. Properties of furfurylated wood. Scand. J. For. Res. 2004, 19, 22–30. [Google Scholar] [CrossRef]
Figure 1. Conceptual representation of a hypothetical scCO2 process that extracts wax from bark and impregnates it in timber.
Figure 1. Conceptual representation of a hypothetical scCO2 process that extracts wax from bark and impregnates it in timber.
Forests 13 02018 g001
Figure 2. Selected pressure vs. density isotherms for carbon dioxide calculated with a published equation of state [25].
Figure 2. Selected pressure vs. density isotherms for carbon dioxide calculated with a published equation of state [25].
Forests 13 02018 g002
Figure 3. Example of solubility in scCO2 calculated using average parameters for six fatty acids (A1 = −21.7, A2 = −8211, A3 = 7.48).
Figure 3. Example of solubility in scCO2 calculated using average parameters for six fatty acids (A1 = −21.7, A2 = −8211, A3 = 7.48).
Forests 13 02018 g003
Figure 4. Schematic diagram of the scCO2 extraction/impregnation process tested in this study.
Figure 4. Schematic diagram of the scCO2 extraction/impregnation process tested in this study.
Forests 13 02018 g004
Figure 5. Picture of the actual experimental set set-up used in this study.
Figure 5. Picture of the actual experimental set set-up used in this study.
Forests 13 02018 g005
Figure 6. Picture of wood sample as it is removed from the impregnation vessel.
Figure 6. Picture of wood sample as it is removed from the impregnation vessel.
Forests 13 02018 g006
Figure 7. Weight gain after 1, 3 and 6 successive extraction/impregnation cycles with supercritical CO2 without co-solvent.
Figure 7. Weight gain after 1, 3 and 6 successive extraction/impregnation cycles with supercritical CO2 without co-solvent.
Forests 13 02018 g007
Figure 8. Weight gain measured after successive extraction/impregnation cycles. Weight gain is shown as fraction immediately after impregnation and % after oven-drying.
Figure 8. Weight gain measured after successive extraction/impregnation cycles. Weight gain is shown as fraction immediately after impregnation and % after oven-drying.
Forests 13 02018 g008
Figure 9. Weight gain after successive extraction/impregnation cycles with CO2, ethanol and oven-drying between cycles.
Figure 9. Weight gain after successive extraction/impregnation cycles with CO2, ethanol and oven-drying between cycles.
Forests 13 02018 g009
Figure 10. Published experimental data of CO2 + ethanol phase equilibrium at 40 °C [30], and pressures measured during multi-cycle impregnation tests.
Figure 10. Published experimental data of CO2 + ethanol phase equilibrium at 40 °C [30], and pressures measured during multi-cycle impregnation tests.
Forests 13 02018 g010
Figure 11. Autofluorescence of untreated wood cells under optical microscope.
Figure 11. Autofluorescence of untreated wood cells under optical microscope.
Forests 13 02018 g011
Figure 12. Autofluorescence of wax impregnated wood cells under an optical microscope.
Figure 12. Autofluorescence of wax impregnated wood cells under an optical microscope.
Forests 13 02018 g012
Table 1. Theoretical pressures after expanding scCO2 at 12 and 16 MPa from 100 to 125 mL.
Table 1. Theoretical pressures after expanding scCO2 at 12 and 16 MPa from 100 to 125 mL.
TemperatureBefore ExpansionAfter Expansion
(°C)(MPa)(MPa)
40129.5
401610.1
601210.1
601613.0
Table 2. Chemical composition of principal components detected in the wax.
Table 2. Chemical composition of principal components detected in the wax.
ComponentRelative %
Dehydroabietic acid15.83
Docosanoic acid11.78
Tetracosanoic acid9.17
Tetracosan-1-ol6.41
Palustric acid6.08
Abietic acid5.87
B-Sitosterol5.03
Sandaracopimaric acid4.68
1-Docosanol3.51
Eicosanoic acid3.46
Unknown 12.85
Isopimaric acid2.66
Neoabietic acid2.64
Stearic acid (F18:0)2.31
Unknown 22.10
Unknown 31.65
alpha-Terpineol1.22
Unknown 41.02
Table 3. Degradation transition temperatures and associated mass loss (SD between brackets).
Table 3. Degradation transition temperatures and associated mass loss (SD between brackets).
Transition 1Transition 2Transition 3
Onset (°C)62.4 (4.9)244.1 (13.7)357.1 (18.1)
End of transition (°C)75.5 (4.8)304.4 (17.5)419.3 (16.8)
Mass loss (%)2.8 (0.7)44.4 (1.2)48.8 (2.7)
Table 4. Endothermic and exothermic transitions peaks and total enthalpy (SD between brackets).
Table 4. Endothermic and exothermic transitions peaks and total enthalpy (SD between brackets).
Peak 1
(°C)
Peak 2
(°C)
Peak 3
(°C)
Total Enthalpy
(kJ/kg)
Endothermic22.93 (0.27)29.59 (0.12)49.23 (0.34)70.19 (1.90)
Exothermic20.41 (0.28)44.70 (0.38)52.76 (0.86)62.19 (3.52)
Table 5. Average oven-dried weight (OD), standard deviation (SD) and random measurement error.
Table 5. Average oven-dried weight (OD), standard deviation (SD) and random measurement error.
Wood SamplesMeasurement Errors
OD Weight
(g)
SD
(g)
SD
(%)
Maximum
(%)
Minimum
(%)
8.020.350.050.10−0.09
Table 6. Summary of average weight gain measured in triplicate for each treatment.
Table 6. Summary of average weight gain measured in triplicate for each treatment.
TestProcess ConditionsInitial Weight 1Weight Gain after Impregnation 1Weight Gain after Oven-Drying 2
g%%
W-140 °C/12 MPa8.1 (0.3)3.7 (1.2)0.06 (0.14/−0.04)
W-240 °C/16 MPa8.1 (0.2)3.5 (0.9)0.09 (0.14/0.03)
W-360 °C/16 MPa7.9 (0.1)0.7 (0.6)0.09 (0.12/0.04)
Et-140 °C/12 MPa8.1 (0.2)11.1 (0.7)−0.06 (−0.01/−0.16)
Et-240 °C/16 MPa8 (0.3)12.9 (2.5)−0.1 (−0.05/−0.17)
Et-360 °C/16 MPa8.1 (0.2)8.7 (0.5)−0.11 (−0.07/−0.14)
Et + W-140 °C/12 MPa8 (0.3)13.2 (2.7)0.45 (0.67/0.25)
Et + W-240 °C/16 MPa7.9 (0.7)16.7 (3.3)0.56 (0.81/0.41)
Et + W-360 °C/16 MPa7.9 (0.3)9.9 (1.2)0.32 (0.51/0.22)
Ac + W-140 °C/12 MPa7.8 (0.3)13.3 (5.5)0.37 (0.43/0.31)
Ac + W-240 °C/16 MPa8.1 (0.6)11.6 (5.2)0.34 (0.38/0.3)
Ac + W-360 °C/16 MPa8.1 (0.5)4.8 (1)0.26 (0.32/0.21)
1 Standard deviation between brackets. 2 Maximum and minimum values between brackets.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Elustondo, D.; Raymond, L.; Risani, R.; Donaldson, L.; Le Guen, M.J. Exploratory Pressure Impregnation Process Using Supercritical CO2, Co-Solvents, and Multi-Cycle Implementation. Forests 2022, 13, 2018. https://doi.org/10.3390/f13122018

AMA Style

Elustondo D, Raymond L, Risani R, Donaldson L, Le Guen MJ. Exploratory Pressure Impregnation Process Using Supercritical CO2, Co-Solvents, and Multi-Cycle Implementation. Forests. 2022; 13(12):2018. https://doi.org/10.3390/f13122018

Chicago/Turabian Style

Elustondo, Diego, Laura Raymond, Regis Risani, Lloyd Donaldson, and Marie Joo Le Guen. 2022. "Exploratory Pressure Impregnation Process Using Supercritical CO2, Co-Solvents, and Multi-Cycle Implementation" Forests 13, no. 12: 2018. https://doi.org/10.3390/f13122018

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop