Zum Hauptinhalt springen
Artikel Open Access

Fractionation of beech wood pyrolysis liquids with supercritical and gaseous CO2

  • EMAIL logo und
Veröffentlicht/Copyright: 29. Dezember 2025

Abstract

The utilization of slow pyrolysis liquids occurring during charcoal production is limited due to their high content of acids (e.g., acetic acid) and high molecular weight substances. Supercritical carbon dioxide (scCO2) extraction is an effective method to separate low and high molecular weight substances. Gaseous CO2 is capable of removing acetic acid, which is present in significant quantities in slow pyrolysis liquids of wood. In this study, a two-step process was applied to upgrade beech wood slow pyrolysis liquid by removing high molecular weight substances and acids. First, high molecular weight substances and sugars were separated from the beech wood pyrolysis liquid using scCO2 extraction. Then, the contents of acids and ketones in the scCO2 pyrolysis liquid extract were reduced through treatment with gaseous CO2. This method led to the production of an extract with a low content of acids (1.2 wt. %) and a high content of monomeric phenolic compounds (33.7 wt. %). This upgraded extract has the potential to serve as a promising bio-based raw material for the production of phenolic resins, which are extensively utilized in the wood product industry.

1 Introduction

During industrial production of charcoal, approximately 30 wt. % of the dry wood mass is converted into slow pyrolysis liquid (SPL) (Hofbauer et al. 2016). SPL contains various substances, such as phenols, syringols, guaiacols, acids, furans, and ketones (Feng and Meier 2015). The acidic fraction largely consists of acetic acid and propionic acid (Feng and Meier 2015; Möck et al. 2023) and contains a high proportion of high molecular weight substances, which are formed during the slow pyrolysis process (Baumbach et al. 2016). Feng and Meier (2015) characterized a beechwood SPL with gas chromatography using a mass spectrometer and flame ionization detector (GC/MS-FID) and Karl Fischer titration. The SPL had a water content of 1.13 wt. %, and 51 wt. % were detectable by GC/MS-FID. The uncharacterized portion was assumed to consist of high molecular weight substances. The main components of the characterized SPL were acids (6.6 wt. %), ketones (22.2 wt. %), and monomeric phenolic substances (12.6 wt. %).

Despite its many components, the utilization of SPL is currently limited to burning for energy production or using it as a smoke flavoring (Feng 2018). New research indicates that SPL components could have more promising applications. The monomeric phenolic substances, in particular, seem to be interesting for the wood products industry because they can be used to produce phenolic resins (Karthäuser et al. 2024; Sukhbaatar et al. 2009) as well as for wood preservation (Lourençon et al. 2016). However, processing pyrolysis liquids is complicated. The high proportion of high molecular weight components can lead to high viscosity (Meier 2016), and the high acid content can cause corrosion issues. Pyrolysis liquids are also thermolabile, complicating processing, distillation and storage at high temperatures (Czernik et al. 1994). Therefore, separating high molecular weight substances and acids is advisable for further processing.

Pyrolysis liquids have been fractionated by using liquid-liquid extraction (Amen-Chen et al. 1997; Feng and Meier 2016; Wei et al. 2014) and distillation (Capunitan and Capareda 2013; Guo et al. 2010; Zheng and Wei 2011). A suitable alternative for separating high molecular weight substances is extraction with supercritical CO2 (scCO2). When the critical point (7.38 MPa, 304.15 K) (Gupta and Shim 2007) is exceeded, CO2 enters a supercritical state. It acquires a viscosity similar to that of a gas, and its density can reach that of a liquid. Density is the main factor for the solvation power, and in general, scCO2 has the polarity of a non-polar solvent. However, depending on the parameter, it can shift to the polarity of a weakly polar solvent (Clifford 1999). Non-polar, low molecular weight organic substances exhibit high solubility in scCO2, with solubility generally decreasing with increasing molecular weight. The majority of organic substances with a high molecular weight demonstrate minimal solubility in scCO2 (Mukhopadhyay 2000).

Pyrolysis liquids have been extracted with scCO2 in numerous studies (Chan et al. 2018; Cheng et al. 2016; Feng and Meier 2015, 2016, 2017; Möck et al. 2023, 2024; Mudraboyina et al. 2015; Naik et al. 2010; Rout et al. 2009; Wang et al. 2010). There, an enrichment of monomeric phenolic substances, ketones and acids was observed in the extract (Feng and Meier 2015; Möck et al. 2023). The non-polar and high molecular weight substances remained in the residue. One study reported solid, black, tar-like residues (Möck et al. 2023). Another study found that the acid content increased from 6.6 wt. % in the pyrolysis liquid to 9.5 wt. % in the extract (Feng and Meier 2015). Additionally, the extracts darkened during storage, indicating instability.

Sometimes significant losses were observed during the scCO2 extraction of pyrolysis liquids and oils from hydrothermal liquefaction (Feng and Meier 2015, 2016, 2017; Montesantos et al. 2019). These losses are assumed to be due to the entrainment of the atomized extract during pressure release and due to the high solubility of some volatile substances in gaseous CO2 (Möck et al. 2023). Examining the solubility curves of two typical components of pyrolysis liquids, guaiacol and acetic acid (Figure 1), reveals that acetic acid has a significantly higher solubility in gaseous CO2 compared to guaiacol at 353.15 K. Its solubility increases as density decreases. This is attributed to the decrease in pressure that occurs during the reduction of density in the gaseous state. At lower pressures, the solubility of substances is primarily determined by their vapor pressure (Foster et al. 1991).

Figure 1: 
Solubility of acetic acid and guaiacol in function of CO2 at densities between 0 and 500 kg/m3 and 353.15 K (1 = based on data from Bamberger et al. 2000; 2 = based on data from Lee et al. 1999).
Figure 1:

Solubility of acetic acid and guaiacol in function of CO2 at densities between 0 and 500 kg/m3 and 353.15 K (1 = based on data from Bamberger et al. 2000; 2 = based on data from Lee et al. 1999).

The solubility of volatile substances in the gaseous state increases with rising temperatures. Therefore, using hot gaseous CO2 might potentially be feasible for separating substances with high solubility from substances with low solubility. This approach would be similar to distillation, and when combined with scCO2 extraction, it could offer the advantage of separating disruptive, high molecular weight substances. Furthermore, it could be easily integrated into an scCO2 extraction plant. Despite these promising prospects, hot gaseous CO2 in combination with supercritical CO2 extraction has not yet been utilized for the fractionation of pyrolysis liquids.

This study aimed first of all to extract a slow pyrolysis liquid with scCO2 in order to separate high molecular weight substances. In the second step, the content of substances highly soluble in gaseous CO2 should be reduced by hot gaseous CO2, while substances less soluble in gaseous CO2 should be enriched in the extract. Therefore, fractionation was investigated by using two experimental setups. In the first setup, beech wood SPL was extracted with scCO2, and the decompression valve was heated during pressure release. This allowed temperatures of up to 333.15 K in the gaseous CO2. The second setup involved dosing a previously produced scCO2 SPL extract into hot gaseous CO2 and gradually cooling it from 353.15 K to 283.15 K in five vials. Fractionation was investigated by characterizing the composition of the extracts and the SPL via GC/MS-FID. Also, density, viscosity, and water content were determined.

2 Materials and methods

2.1 Materials

The beech wood SPL (Figure 2) used in setup 1 was supplied by proFagus GmbH (Bodenfelde, Germany). The extract used in setup 2 was obtained from the same SPL and produced as described in Möck et al. (2023) (chapter 3.4) with a scCO2 density of 724 kg/m3. There, a single extract was collected during the extraction process. The extraction conditions were as follows: 20 MPa, 333.15 K, flow = 5 g scCO2/min, 25 g SPL, 4 h.

Figure 2: 
Beech wood SPL used for scCO2 extraction in setup 1.
Figure 2:

Beech wood SPL used for scCO2 extraction in setup 1.

2.2 Setup 1: supercritical CO2 extraction with different off-gas temperatures

Off-gas is a mixture of gaseous CO2 and the extract formed during depressurization after scCO2 extraction. The influence of off-gas temperature on extract composition and loss was investigated. For this, a scCO2 extraction system from HDT Sigmar Mothes GmbH (Wildau, Germany) (setup 1) was used. The system is illustrated schematically in Figure 3. Liquid CO2 was compressed by using a high-pressure pump (Figure 3; 2) and heating (Figure 3; 5) brought it into the supercritical state. Then the scCO2 flowed through the extraction vessel (Figure 3; 6), which was filled with liquid SPL, and was depressurized via the heated back pressure regulator valve (Figure 3; 7). The extraction vessel had a volume of 185 cm3. A second heated valve (Figure 3; 8) distributed the cooling during decompression, allowing the off-gas to be heated up to 333.15 K. The off-gas flowed into an insulated vial (60 cm3) (Figure 3; 11) filled with 2 mm glass beads to collect the extract. A thermocouple located in the vial (Figure 3; 10) controlled the heating of the second valve, which allowed the temperature of the off-gas to be adjusted. The extraction plant had been used in previous studies with modified configurations (Feng and Meier 2015, 2016, 2017; Möck et al. 2023, 2024). A more detailed description can be found in Möck et al. (2023).

Figure 3: 
Flow diagram of the scCO2 extraction system used for SPL extraction in setup 1 (extraction parameters: 12.5 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 4 h, flow = 5 g scCO2/min, 25 g SPL).
Figure 3:

Flow diagram of the scCO2 extraction system used for SPL extraction in setup 1 (extraction parameters: 12.5 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 4 h, flow = 5 g scCO2/min, 25 g SPL).

Extractions were carried out at three different off-gas temperatures (333.15 K, 313.15 K, 293.15 K). The extraction parameters were as follows: 12 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 25 g SPL, flow = 5 g scCO2/min, 4 h. Extractions were carried out in duplicate and the system’s leak-tightness was verified using a Gas Alert Micro 5 IR (Honeywell International Inc., Charlotte, USA).

2.3 Setup 2: fractionation of SPL extract with hot gaseous CO2

Setup 2 used five tempered vials (353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K) for fractionating the SPL extract with gaseous CO2. Figure 4 shows a scheme and Figure 5 an image of setup 2. The SPL extract, produced by scCO2 extraction, was pumped at a rate of 0.025 g/min into a heated (353.15 K) gaseous CO2 flow of 2.5 g/min. A syringe pump (Teledyne ISCO, Model 500 D, Lincoln, USA) and two connected 24 ml syringes were used for pumping (Figure 5, C). The syringe pump filled the first syringe with ethanol, which pressed the SPL extract out of the second syringe. The SPL extract was not pumped directly by the pump because the use of syringes made it possible to easily weigh the amount of SPL extract pumped. In order to maximize the contact surface area between the CO2 and the SPL extract, the SPL extract was pumped into a tube filled with cotton. Preheated CO2 (353.15 K) flowed through the cotton-filled tube and then through five vials containing 2 mm glass beads, gradually reducing the temperature of the mixture of CO2 and SPL extract from 353.15 K to 283.15 K. The vials were immersed in either a heated or cooled water bath, and thermocouples measured the temperature of the water and the CO2 inside the vials. The first three vials were heated using magnetic stirrers with hotplates. The fourth vial was cooled with water, and the fifth vial with crushed ice and water. The tubes between the vials were isolated with aluminum foil. Prior to pumping the SPL extract, the vials and CO2 flow were heated at the target temperature for 30 min. Four hours were allotted for pumping SPL extract into the CO2 flow, during which 6 g of extract were pumped into 600 g of CO2 (ratio 1:100). Then, the vials and the syringe filled with SPL extract were weighed using a VWR LPW-2103i (d = 1 mg, max 2,100 g) (Avantor Inc., Radnor, USA) scale. Fractionation was carried out in duplicate, and the leak-tightness of setup 2 was verified using a Gas Alert Micro 5 IR (Honeywell International Inc., Charlotte, USA).

Figure 4: 
Flow diagram of the gaseous fractionation system in setup 2 used for the fractionation of the SPL scCO2 extract at different temperatures (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min; T= thermocouple, MFC = mass flow controller).
Figure 4:

Flow diagram of the gaseous fractionation system in setup 2 used for the fractionation of the SPL scCO2 extract at different temperatures (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min; T= thermocouple, MFC = mass flow controller).

Figure 5: 
Images of the gaseous fractionation system (setup 2) used for fractionation of the SPL scCO2 extract at different temperatures (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min: (A) assembled setup 2; (B) vial with glass beads and thermocouple; (C) syringes for extract pumping).
Figure 5:

Images of the gaseous fractionation system (setup 2) used for fractionation of the SPL scCO2 extract at different temperatures (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min: (A) assembled setup 2; (B) vial with glass beads and thermocouple; (C) syringes for extract pumping).

2.4 GC-MS/FID

The SPL and the extracts were analyzed by GC-MS/FID. The setup consisted of an Agilent HP6890 gas chromatograph (Agilent Technologies. Inc., California, USA) equipped with a flame ionization detector (FID) and an Agilent HP5972 mass spectrometer (MS). Helium was used as the carrier gas at a flow rate of 2 ml/min. A silica-fused column (Varian VF-1701 ms, 60 m x 0.25 mm x 0.25 µm) was used for separation. The temperature program was as follows: 318 K constant for 4 min, heating to 553 K (3 K/min), constant for 20 min at 553 K. Fluoranthene in acetone (ß=203 μg/ml) was used as the internal standard because it is not present in the SPL. Additionally, the retention time of fluoranthene does not overlap with those of other compounds contained in the SPL, thus preventing peak interference. The proportion of the sample to acetone with internal standard solution was 50 mg of sample per ml of internal standard solution. To achieve this, 150 mg of the sample was weighed into a 7 ml vial by using a Gilson Microman pipette with M100 tip (Gilson Inc., Middleton, USA) and an XSE205 Dualrange balance (Mettler-Toledo International Inc., Columbus, USA). Then, 3 ml of the internal standard solution were pipetted with a Microman pipette with M1000 tip (Gilson Inc., Middleton, USA). The sample was dissolved by shaking. One milliliter of the solution was withdrawn with a disposable syringe and transferred through a 0.45 µm regenerated cellulose filter into a 2 ml GC vial. One microliter was injected with a split ratio of 1:15 and an injection temperature of 523.15 K. Based on the MS signal the substances were qualified with Mass Finder 4 and the FID signal was used for quantification. In the SPL, 117 substances were detected, some in small amounts. Therefore, the chromatogram was evaluated only for the 44 substances with the highest proportions. These 44 substances represent approximately 90 % of the GC-detectable portion of the SPL, and 33 of these substances were calibrated against standards. The remaining substances were evaluated using an estimated response factor based on chemically similar substances. This method has been used in two previous studies (Möck et al. 2023, 2024). There was a strong overlap of peak areas for the substances syringol, 4-allyl-, and syringol, 4-propyl-. Since these substances have the same response factor, they were reported together. In cases of minor overlap of peak areas, the course of the peak was estimated for integration. The chromatograms of the SPL and the scCO2 extract are provided in the Supplementary Material. Additional information on the standards used including concentration range, calibration points, R-squared values, producer, purity, and CAS number is provided based on Möck et al. (2023).

2.5 Water content

The water content of the SPL and the scCO2 extract used was measured by Karl Fischer titration as described in Möck et al. (2024). For this, a Titroline Alpha titrator (Schott AG, Mainz, Germany) was used. Forty milligrams of the sample were dissolved under stirring in anhydrous Hydranal Methanol Rapid (Honeywell Fluka™, Seelze, Germany). Then, Hydranal Composite 2 (Honeywell Fluka™, Seelze, Germany) was automatically dosed until all the water present in the sample was consumed. Each ml of water required 0.5 ml of Hydranal Composite 2 (Honeywell Fluka™, Seelze, Germany). The amount of water in the sample was calculated based on the titrated volume of Hydranal Composite 2. The titration endpoint was determined using a double platinum electrode.

2.6 Kinematic viscosity

The kinematic viscosity of the SPL and the scCO2 extract used was determined at 298.15 K using an automatic lead time measuring system from Schott Geräte GmbH (CT62, AVS 350, AVS/S) (Mainz, Germany) in accordance with DIN 51 562 (Deutsches Institut für Normung e.V. 1999). The Ubbelohde viscometer MII/1050741 was used to measure the SPL, and the Ubbelohde viscometer MIc/1033959 was used to measure the scCO2 extract.

2.7 Density

The density of the SPL and scCO2 extract was measured using a 10 ml Isolab Boro 3.3 pycnometer (Isolab Laborgeräte GmbH, Eschau, Germany) and a METTLER AT261 DeltaRange analytical scale (Mettler Toledo, Columbus, USA) at 293.15 K. To determine the density of the sample, the exact volume of the pycnometer was measured using water, and its empty mass was weighed. Then the pycnometer was filled with the sample and weighed again. The density was calculated by dividing the mass of the sample by the volume of the pycnometer.

2.8 Calculation of the vapor phase loading

Vapor phase loading (VPL) indicates the number of grams of the extract dissolved in one kilogram of CO2. The VPL was calculated for gaseous and supercritical CO2 using the following equation:

VPL = m ex . m CO 2

VPL = vapor phase loading  g kg

m ex . = mass of extract  g

m CO 2 = mass of gaseous or supercritical  CO 2 kg

3 Results and discussion

3.1 Characterization of the SPL and scCO2 extract used for setup 2

The SPL used in setup 1 was dark black, had a high kinematic viscosity of 1,101 mm2/s at 293.15 K and a water content of 4.09 %. Its density was 1,204 kg/m3 at 293.15 K. The SPL scCO2 extract used in setup 2 had a kinematic viscosity of 21.6 mm2/s at 293.15 K and a density of 1,117 kg/m3 at 293.15 K. The water content of the scCO2 extract was only 1.67 %. The colour of the scCO2 extract was dark red. Table 1 shows the GC-detectable composition of the SPL and the scCO2 extract used in setup 2.

Table 1:

GC-detectable composition of the SPL used in setup 1 and the scCO2 extract used setup 2.

Substance SPL (wt. %) ScCO2 extract (wt. %) used for setup 2
Acids 5.9 10.0

Acetic acid 4.1 7.0
Propionic acid 1.8 2.9

Nonaromatic ketones 4.0 9.0

Acetol (hydroxypropanone) 1.4 3.0
Butanone, 1-hydroxy-2- 0.3 0.9
Propan-2-one, 1-acetyloxy- 0.2 0.7
Butan-2-one, 1-(acetyloxy)-(NIST MQ 92) 0.1 0.3
Cyclopenten-1-one, 3-methyl-2- 0.1 0.4
Cyclopenten-1-one, 2-hydroxy-3-methyl-2- 1.3 2.6
Cyclopenten-1-one, 3-ethyl-2-hydroxy-2- 0.5 1.0

Furans 1.6 4.2

Furanone, 2(5H)- 0.4 0.9
Furaldehyde, 2- 0.4 1.0
Furaldehyde, 5-(hydroxymethyl)-, 2- 0.2 0.4
Furan-2-one, 2,5-dihydro-3,5-dimethyl- 0.2 0.7
Butyrolactone, γ- 0.4 1.3
Lactone derivative (unspecific spectrum) 0.3 0.3

Pyrans 0.4 0.7

Maltol (pyran-4-one, 3-hydroxy-2-methyl-4H-) 0.4 0.7

Lignin derived phenols 1.1 1.6

Phenol 0.3 0.5
Cresol, o- 0.1 0.5
Cresol, m- 0.7 0.6

Guaiacols (methoxy phenols) 3.5 9.3

Guaiacol 0.8 2.4
Guaiacol, 4-methyl- 0.8 2.3
Guaiacol, 4-ethyl- 0.6 1.7
Guaiacol, 4-propyl- 0.1 0.5
Guaiacol, 4-propenyl-cis (Isoeugenol) 0.2 0.4
Guaiacol, 4-propenyl-(trans) (Isoeugenol) 0.6 1.5
Ethanone, 1-(4-hydroxy-3-methoxyphenyl)-(acetoguaiacone) 0.2 0.1
Guaiacyl acetone 0.2 0.3

Syringols (dimethoxy phenols) 10.5 19.4

Syringol 3.0 5.8
Syringol, 4-methyl- 2.2 4.5
Syringol, 4-ethyl- 1.5 3.2
Syringol, 4-allyl- and syringol, 4-propyl- 1.1 2.5
Syringol, 4-(1-propenyl)-, cis 0.3 0.6
Syringol, 4-(1-propenyl)-, trans 1.3 2.0
Syringaldehyde 0.2 0.1
Acetosyringone 0.2 0.2
Propiosyringone 0.1 0.1
Syringyl acetone 0.5 0.4

Sugars 10.1 2.4

Anhydrosugar unknown (unspecific spectrum) 4.8 1.2
Anhydro-ß-d-glucopyranose, 1,6-(levoglucosan) 3.3 0.0
Anhydrosugar unknown (unspecific spectrum) 0.6 0.0
Anhydrosugar unknown (unspecific spectrum) 0.5 0.0
Dianhydro-α-d-glucopyranose, 1,4:3,6- 1.0 1.2

Nonaromatic alcohols 0.1

Ethylene glycol 0.1

Total 37.2 56.6

With GC-MS/FID it was possible to characterize 37.2 wt. % of the SPL and 56.6 wt. % of the scCO2 extract. Since most high molecular weight substances are poorly soluble in scCO2 (Mukhopadhyay 2000), the majority of these were separated during the extraction, thereby enriching the low molecular weight substances in the scCO2 extract. For instance, the proportion of acids increased from 5.9 wt. % to 10.0 wt. %, non-aromatic ketones from 4.0 wt. % to 9.0 wt. % and syringols from 10.5 wt. % to 19.4 wt. %, respectively. Since scCO2 is a non-polar solvent, the sugar content decreased from 10.1 wt. % in SPL to 2.4 wt. % in the scCO2 extract.

3.2 Extraction with different CO2 off-gas temperatures (experimental setup 1)

In order to investigate how different off-gas temperatures influence the losses and compositions of the extracts during decompression to atmospheric pressure, SPL (25 g) was extracted with supercritical CO2 (flow = 5 g/min, 1,200 g) at three off-gas temperatures (293.15 K, 313.15 K, 333.15 K). A mass loss was observed when comparing the initial mass to the mass of extracts and residues. The losses consist of small amounts of extract remaining in the valves and tubing of the extraction system, and of substances that are not separated in the separator and are carried out with the gaseous CO2. Figure 6 shows the mass balances as the mean of the duplicates, with the error bars indicating the range.

Figure 6: 
Influence of off-gas temperature on losses during scCO2 extraction of SPL in setup 1 (extraction parameters: 12.5 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 4 h, flow = 5 g scCO2/min, 25 g SPL).
Figure 6:

Influence of off-gas temperature on losses during scCO2 extraction of SPL in setup 1 (extraction parameters: 12.5 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 4 h, flow = 5 g scCO2/min, 25 g SPL).

The loss at 293.15 K was 9.5 wt. %. As the off-gas temperature increased, the loss raised with 15.3 wt. % at 313.15 K and 27.2 wt. % at 333.15 K. Due to the increased loss, the amount of collected extract decreased from 29.6 wt. % (at 293.15 K) to 11.1 wt. % (at 333.15 K). The residues ranged between 61.0 wt. % and 62.6 wt. %. Based on the residues, the VPL without losses was calculated between 7.8 and 8.1 g extract/kg scCO2. The VPL is highly dependent on the feed used and on the extraction parameters. In a review the range of VPLs for the extraction of bio-oils varied widely, from 0.7 to 99.7 g extract/kg of scCO2 (Montesantos and Maschietti 2020). According to Montesantos and Maschietti (2020), the VPL can be increased by raising both the density of scCO2 and the temperature at constant density. This is also supported by the solubility curves of acetic acid and guaiacol (see Figure 1). Due to the strong dependence of the VPL on process parameters and feed material, it is advisable to make comparisons under similar extraction conditions. A similar VPL of 10.6 g extract/kg scCO2 for the extraction of SPL at the same extraction temperature and pressure but with a lower solvent-to-feed ratio of 24 was reported (Möck et al. 2023). In the experiments conducted with setup 1, the solvent-to-feed ratio was 48. The slightly lower VPL observed in setup 1 suggests that increasing the solvent-to-feed ratio results in a reduction of the overall yield. This can be attributed to the decreasing amount of easily soluble compounds in the feed during extraction, so that toward the end of the process, the scCO2 no longer provides such a high extraction efficiency. Using the loss values, the amount of extract remaining in the heated off-gas after depressurisation (VPL of the off-gases) was calculated as 2.9 g extract/kg CO2 at 293.15 K, 3.2 g extract/kg CO2 at 313.15 K and 5.7 g extract/kg CO2 at 333.15 K. This indicates that, as the off-gas temperature increased, the solubility of the extract in the gaseous CO2 increased. A previous study shows that the losses were reduced to less than 5 wt. % by cooling the off-gas temperature to 273 K, which corresponded to a VPL of the off-gases of less than 2 g extract/kg scCO2 (Möck et al. 2023). The VPL in the experiments conducted with setup 1 was 2.9 g extract/kg scCO2. It can therefore be assumed that a further decrease in the off-gas temperature would lead to an even lower VPL, thereby reducing the losses caused by extract components dissolved in the off-gas. Furthermore, cooled water baths were used in other studies to cool the collection vessels and thereby reduced losses (Montesantos et al. 2019, 2020).

The SPL, the residue and the extracts produced at different off-gas temperatures were characterized using GC-MS/FID to investigate the effect of off-gas temperature on the extract composition. Figure 7 shows the composition as the mean of duplicates, with error bars indicating the range. As not all compounds are detectable by GC, the columns do not sum up to 100 wt. %.

Figure 7: 
GC-detectable composition of the residues, the SPL and the scCO2 extracts obtained at different off-gas temperatures in setup 1 (extraction parameters: 12.5 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 4 h, flow = 5 g scCO2/min, 25 g SPL).
Figure 7:

GC-detectable composition of the residues, the SPL and the scCO2 extracts obtained at different off-gas temperatures in setup 1 (extraction parameters: 12.5 MPa, 313.15 K, ρscCO2 = 731 kg/m3, 4 h, flow = 5 g scCO2/min, 25 g SPL).

The scCO2 extraction enriched the extracts with syringols, guaiacols, ketones, acids, furans, phenols, and pyrans. By increasing the off-gas temperature the amount of substances detectable by GC decreased. Whereas at 293.15 K, the content was 57.7 wt. %, it was 44.7 wt. % at 333.15 K. This suggests that in gaseous CO2 well-soluble substances were removed from the extract, resulting in an enrichment of non-detectable or high molecular weight substances in the scCO2 extract. Poorly soluble sugars and high molecular weight substances largely remained in the residue. The high proportion of residues can be attributed to the fact that slow pyrolysis produces large amounts of high molecular weight substances (Baumbach et al. 2016), which are poorly soluble in scCO2 (Mukhopadhyay 2000). Possible applications for the high molecular weight components of the residue include the production of activated carbon or energetic use. The sugars present in significant amount in the residue, especially levoglucosan, which is a platform chemical in the chemical industry could also be utilized for the production of biopolymers, biofuels, surfactants, and pharmaceuticals (Itabaiana Jr et al. 2020).

Increasing the off-gas temperature particularly affected the content of acids and ketones. At an off-gas temperature of 293.15 K, the extract consisted of 6.8 wt. % acids and 8.1 wt. % ketones. As the off-gas temperature increased, the acid content decreased to 2.9 wt. % at 313.15 K, dropping further to 1.8 wt. % at 333.15 K. The ketone content decreased from 8.1 wt. % at 293.15 K to 5.9 wt. % at 313.15 K and then to 3.2 wt. % at 333.15 K. In contrast, the syringol content first increased with the rise in off-gas temperature and then decreased slightly. It was 22.7 wt. % at 293.15 K, 26.7 wt. % at 313.15 K and 26.4 wt. % at 333.15 K. This is due to the reduction in acids and ketones, which increased the mass fraction of syringols. A similar behavior was observed for guaiacols. Their content decreased significantly from 10.1 wt. % at 313.15 K to 7.1 wt. % at 333.15 K off-gas temperature. The shift in extract composition was due to different solubilities in gaseous CO2. For example, acetic acid has a solubility of 44.5 g/kg in gaseous CO2 at 0.21 MPa and 353.15 K (based on data from Bamberger et al. 2000). Guaiacol, on the other hand, has a solubility of only 2.3 g/kg under similar conditions (353.15 k, 0.20 MPa) (based on data from Lee et al. 1999).

Using supercritical CO2 extraction in combination with a hot off-gas temperature reduced the proportions of acids and ketones in the extract. Because these extracts contain high proportions of monomeric phenolic compounds, they are promising for the production of phenol resins and for wood preservation (Karthäuser et al. 2024; Lourençon et al. 2016; Sukhbaatar et al. 2009).

In order to capture as much of the extract as possible, it was essential to maintain the off-gas temperature as low as feasible. In industrial processes, scCO2 is not usually expanded to atmospheric pressure, but rather depressurized into the subcritical state in a pressure separator. This allows CO2 to be recycled with reduced compression work. Future work would benefit from using a pressure separator to decrease pressure only to the CO2 density at which the solubility of the contained substances is minimized. For acetic acid, this CO2 density is approximately 100 kg/m3 (based on data from Bamberger et al. 2000; see Figure 1). The extract obtained under these conditions would still contain a high proportion of acids and ketones. To further reduce the content of acids and ketones, the extract collected in the pressure separator could be transferred into a hot CO2 gas stream, where the solubility of acids and ketones is maximized. This would enable their separation as demonstrated in experimental setup 2.

3.3 Fractionation of SPL extract with hot gaseous CO2 (experimental setup 2)

Setup 1 showed that especially the content of acids and ketones in the extract can be reduced by using higher temperatures during the depressurization of the CO2. Setup 2 investigated whether the extract could be fractionated by adding it to a hot, gaseous CO2 stream at atmospheric pressure and using separators at different temperatures. For this, an SPL scCO2 extract was pumped (0.025 g/min) into a hot CO2 stream (2.5 g/min) and passed through five vials. The temperature in the vials gradually decreased from 353.15 K to 283.15 K, and five different fractions were collected. The colors of the fractions ranged from dark red (353.15 K) to orange (333.15 K) to shiny yellow (313.15 K, 293.15 K) to almost colorless (283.15 K). Figure 8 shows the extract and its different fractions. Figure 9 shows the amount of extract collected in the five vials as the average of the duplicates, with error bars indicating the range.

Figure 8: 
Image of the scCO2 extract and the five fractions obtained during subsequent gaseous CO2 fractionation at different temperatures in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).
Figure 8:

Image of the scCO2 extract and the five fractions obtained during subsequent gaseous CO2 fractionation at different temperatures in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).

Figure 9: 
Yield of the five SPL scCO2 extracts obtained during subsequent gaseous CO2 fractionation at different temperatures in the vials in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).
Figure 9:

Yield of the five SPL scCO2 extracts obtained during subsequent gaseous CO2 fractionation at different temperatures in the vials in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).

The majority of the extract was collected in the first vial (353.15 K), accounting for 60.2 wt. % of the feed. At 333.15 K, 9.3 wt. % was collected in the second vial and at 313.15 K, 7.0 wt. % was collected in the third vial. Upon further cooling, 9.1 wt. % was collected in the fourth vial (293.15 K), and an additionally 4.2 wt. % was collected in the fifth vial at 283.15 K. The total loss was 10.3 wt. %. Therefore, it can be assumed, that at a CO2 temperature of 283.15 K, some volatile substances were carried out by the CO2 gas stream.

Subtracting the cumulative yield from the amount of pumped extract gives the amount of extract in the CO2 gas stream at each temperature. Furthermore, using this value and the amount of used CO2 (600 g), the VPL of the gaseous CO2 was calculated (Table 2).

Table 2:

Cumulative yield, extract amounts in the gaseous CO2 and VPL in the five vials during subsequent CO2 fractionation of the SPL scCO2 extract at different temperatures in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).

Vial 1 2 3 4 5
Temperature 353.15 K 333.15 K 313.15 K 298.15 K 283.15 K
Cumulative yield in the vials (g) 3.6 4.2 4.6 5.1 5.4
Amount of extract in gaseous CO2 (g) 2.4 1.8 1.4 0.9 0.6
VPL (g extract/kg CO2) 4.0 3.1 2.4 1.4 1.0

The amount of extract in the gaseous CO2 decreased as the temperature in the five vials decreased. The amount varied from 2.4 g at 353.15 K to 0.6 g at 283.15 K. Consequently, 2.4 g of extract dissolved in 0.6 kg hot gaseous CO2 at 353.15 K. This corresponded to a VPL of 4.0 g extract/kg CO2. When cooled to 333.15 K, 30.5 wt. % (1.8 g extract) of the SPL extract remained dissolved in the CO2, yielding a VPL of 3.1 g extract/kg CO2. As the temperature decreased further, the amount of extract dissolved in the gaseous CO2 decreased to a VPL of 1 g extract/kg CO2 at 283.15 K. Compared to setup 1, the VPL at 333.15 K in setup 2 was significantly lower (setup 1: 5.7 g extract/kg CO2; setup 2: 3.1 g extract/kg CO2). During decompression in setup 1, there was an atomization of the extract leading to the assumption that either the atomized extract was carried out or the extract dissolved better in the gaseous CO2 due to the atomization. Moreover, in setup 2, extract separation occurred in the first vial, indicating that the gaseous CO2 was no longer fully saturated in the second vial. The five different fractions in the vials were analyzed by GC-MS/FID. Figure 10 shows the composition of the scCO2 extract, the five fractions and the SPL as the mean of duplicates, with error bars indicating the range. As not all compounds are detectable by GC, the columns do not sum up to 100 wt. %.

Figure 10: 
GC-detectable composition of SPL, the scCO2 SPL extract, and the five SPL scCO2 extracts obtained during subsequent gaseous CO2 fractionation at different temperatures in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).
Figure 10:

GC-detectable composition of SPL, the scCO2 SPL extract, and the five SPL scCO2 extracts obtained during subsequent gaseous CO2 fractionation at different temperatures in setup 2 (fractionation parameters: 353.15 K, 333.15 K, 313.15 K, 293.15 K, 283.15 K, 4 h, flow = 2.5 g CO2/min and 0.025 g extract/min).

During scCO2 extraction, the main part of the high molecular weight substances and sugars contained in the SPL were not extracted. This resulted in an enrichment of syringols (19.4 wt. %), guaiacols (9.3 wt. %), ketones (9.0 wt. %), acids (10.0 wt. %), and furans (4.2 wt. %) in the scCO2 extract. The total proportion of GC-detectable substances was 37.2 wt. % in the SPL and 56.6 wt. % in the scCO2 extract. In the first vial (353.15 K), the GC-detectable amount was only 42.8 wt. %, which is lower than in the scCO2 extract. This decrease is attributed to the removal of substances that are highly soluble in gaseous CO2, which increased the proportion of high molecular weight substances that are not GC-detectable but still soluble in scCO2. In subsequent vials, the amount of GC-detectable substances increased, which indicates a lower proportion of non-detectable high molecular weight substances.

Through fractionation with heated gaseous CO2, the amount of acids was reduced to 1.2 wt. % in the first vial (353.15 K). The amount of ketones decreased to 2.7 wt. %, while the amount of syringols increased to 25.5 wt. %. As the gaseous CO2 in the vials was cooled further, the syringol content gradually decreased while the content of ketones, acids, and furans increased. No syringols were detected in the extract of the last vial (283.15 K). However, high amounts of ketones (25.2 wt. %), acids (15.8 wt. %), and furans (14.7 wt. %) were present. Initially, the guaiacol content increased before decreasing, reaching its highest concentration (19.2 wt. %) in the extract of the third vial at 313.15 K. The overall content of monomeric phenolic substances (guaiacols, syringols, phenols) was 15.1 wt. % in the SPL and 30.3 wt. % in the scCO2 extract. The content of monomeric phenolic substances in the five vials varied between 33.7 wt. % (353.15 K) and 4.7 wt. % (283.15 K). Fractionation with hot gaseous CO2 slightly increased the content of monomeric phenolic substances while drastically reducing the content of acids and ketones in the extract. Another study produced scCO2 extracts with up to 41.1 wt. % monomeric phenolic substances using pressure separators (Möck et al. 2024). However, the content of acids was 4.3 wt. %, and the content of ketones was 8.0 wt. %. Extracts with low acid and ketone content could be promising for producing phenol resins and preserving wood (Karthäuser et al. 2024; Lourençon et al. 2016; Sukhbaatar et al. 2009). Further purification processes, such as distillation, can be used to obtain bio-based platform chemicals from extracts with high levels of acids and ketones. These chemicals can be used to produce biopolymers, etching agents, or solvents (Murali et al. 2017).

3.4 Limitations and outlook

Due to the limited heating capacity, the temperature of the off-gas in setup 1 was restricted to 333.15 K, and the temperature of the gaseous CO2 in setup 2 was restricted to 353.15 K. Higher temperatures showed to improve the separation of acids and ketones. Therefore, future research should explore using higher temperatures to enhance separation efficiency. Setup 2 experienced losses amounting to 10.8 wt. %, they are suspected to be due to volatile substances carried away with the gaseous CO2. Since the cooling capacity was limited to 283.15 K, applying colder cooling stages could reduce these losses and facilitate further investigation. In setup 1, the ratio of CO2 to extract could not be controlled or varied. Setup 2 tested a ratio of 1:100 (extract to CO2). Future studies should vary this ratio and examine its influence on fractionation to provide valuable insights. Additionally, the extract in setup 2 remained in the vials throughout the experiment, thus allowing for prolonged contact with CO2. It would be beneficial to investigate whether effective fractionation can be achieved with short contact times between the extract and hot, gaseous CO2. Furthermore, combining pressure separators with hot CO2 fractionation appears promising for producing extracts with high concentrations of monomeric phenolic substances and low concentrations of ketones and acids. These extracts could be valuable to the adhesive industry as an alternative to petrochemical, phenol-based fractions. One possible applications of the residue could be the production of activated carbon, while sugars could be utilized as bio-based platform chemicals. Additional processing of fractions rich in acids and ketones may be employed to convert them into viable bio-based platform chemicals.

4 Conclusions

ScCO2 extraction of SPL effectively separates high molecular weight substances and yields extracts with high concentrations of acids, ketones, and monomeric phenolic substances. This study investigated two setups to further fractionate the extracts obtained from scCO2 extraction using gaseous CO2. In setup 1, gaseous CO2 was heated directly during the depressurization of the scCO2, connecting the fractionation step with the extraction process. The specific temperature of the gaseous CO2 influenced the amount of losses and the composition of the extract. As the temperature increased, so did the loss, and the amount of substances that were well soluble in gaseous CO2 decreased. Losses reached 27.2 wt. % at a CO2 temperature of 333.15 K. Through additional fractionation with hot gaseous CO2, the proportion of acids and ketones in the extract decreased drastically, while the content of monomeric phenolic substances increased slightly.

In setup 2, the scCO2 extraction was separated from the fractionation using gaseous CO2. A previously obtained SPL extract was pumped into hot gaseous CO2 and subsequently cooled down in five vials. This process yielded an extract containing 33.7 wt. % monomeric phenolic compounds, with only 1.2 wt. % acids and 2.7 wt. % ketones. Reducing the amount of acids and ketones is an important step fora further utilization of the extracts. The monomeric phenolic substances, in particular, could be of interest to the adhesive industry because they offer the potential to replace petrochemical phenol in widely used phenol-formaldehyde resins. Future work, plans to integrate fractionation with hot, gaseous CO2 into an scCO2 extraction plant connected with a pressure separator. This integration aims to produce extracts with higher concentrations of monomeric phenolic substances and lower amounts of acids and ketones.


Corresponding author: Dennis Marvin Janek Möck, Johann Heinrich von Thünen Institute, Federal Research Institute for Rural Areas, Forestry and Fisheries, Institute of Wood Research, Haidkrugsweg 1, 22885 Barsbüttel, Germany, E-mail:

Award Identifier / Grant number: 2220HV017C

Acknowledgments

Thanks go to proFagus GmbH for providing the slow pyrolysis liquid. Special thanks to Christiane Riegert and Silke Radtke for technical support.

  1. Research ethics: Not applicable.

  2. Informed consent: Not applicable.

  3. Author contributions: The authors have accepted responsibility for the entire content of this manuscript and approved its submission.

  4. Use of Large Language Models, AI and Machine Learning Tools: ChatGPT 3.5 and DeepL were used to improve language.

  5. Conflict of interest: The authors state no conflict of interest.

  6. Research funding: This research was funded by the Fachagentur Nachwachsende Rohstoffe e. V. (Federal Ministry of Food and Agriculture, grant number: 2220HV017C).

  7. Data availability: The raw data can be obtained on request from the corresponding author.

References

Amen-Chen, C., Pakdel, H., and Roy, C. (1997). Separation of phenols from Eucalyptus wood tar. Biomass Bioenergy 13: 25–37, https://doi.org/10.1016/S0961-9534(97)00021-4.Suche in Google Scholar

Bamberger, A., Sieder, G., and Maurer, G. (2000). High-pressure (vapor + liquid) equilibrium in binary mixtures of (carbon dioxide+water or acetic acid) at temperatures from 313 to 353 K. J. Supercrit. Fluids 17: 97–110, https://doi.org/10.1016/S0896-8446(99)00054-6.Suche in Google Scholar

Baumbach, G., Hartmann, H., Höfer, I., Hofbauer, H., Hülsmann, T., Kaltschmitt, M., Lenz, V., Neuling, U., Nussbaumer, T., Obernberger, I., et al.. (2016). Grundlagen der thermo-chemischen Umwandlung biogener Festbrennstoffe. In: Kaltschmitt, M., Hartmann, H., and HofbauerIII, H. (Eds.). Energie aus Biomasse, Grundlagen, Techniken und Verfahren. 3. aktualisierte und erweiterte Auflage. Springer-Verlag, Berlin, Heidelberg, New York, pp. 579–814.10.1007/978-3-662-47438-9_11Suche in Google Scholar

Capunitan, J.A. and Capareda, S.C. (2013). Characterization and separation of corn stover bio-oil by fractional distillation. Fuel 112: 60–73, https://doi.org/10.1016/j.fuel.2013.04.079.Suche in Google Scholar

Chan, Y.H., Yusup, S., Quitain, A.T., Chai, Y.H., Uemura, Y., and Loh, S.K. (2018). Extraction of palm kernel shell derived pyrolysis oil by supercritical carbon dioxide: evaluation and modeling of phenol solubility. Biomass Bioenergy 116: 106–112, https://doi.org/10.1016/j.biombioe.2018.06.009.Suche in Google Scholar

Cheng, T., Han, Y., Zhang, Y., and Xu, C. (2016). Molecular composition of oxygenated compounds in fast pyrolysis bio-oil and its supercritical fluid extracts. Fuel 172: 49–57, https://doi.org/10.1016/j.fuel.2015.12.075.Suche in Google Scholar

Clifford, T. (1999). Fundamentals of supercritical fluids. Oxford University Press, Oxford.10.1093/oso/9780198501374.001.0001Suche in Google Scholar

Czernik, S., Johnson, D.K., and Black, S. (1994). Stability of wood fast pyrolysis oil. Biomass Bioenergy 7: 187–192, https://doi.org/10.1016/0961-9534(94)00058-2.Suche in Google Scholar

Deutsches Institut für Normung e.V (1999). Messung der kinematischen Viskosität mit dem Ubbelohde-Viskosimeter Teil 1: Bauform und Druchführung de Messung, (DIN 51562-1).Suche in Google Scholar

Feng, Y. (2018). Fractionation of pyrolysis liquids with supercritical carbon dioxide, Doctoral thesis. University of Hamburg, Hamburg.Suche in Google Scholar

Feng, Y. and Meier, D. (2015). Extraction of value-added chemicals from pyrolysis liquids with supercritical carbon dioxide. J. Anal. Appl. Pyrolysis 113: 174–185, https://doi.org/10.1016/j.jaap.2014.12.009.Suche in Google Scholar

Feng, Y. and Meier, D. (2016). Comparison of supercritical CO2, liquid CO2, and solvent extraction of chemicals from a commercial slow pyrolysis liquid of beech wood. Biomass Bioenergy 85: 346–354, https://doi.org/10.1016/j.biombioe.2015.12.027.Suche in Google Scholar

Feng, Y. and Meier, D. (2017). Supercritical carbon dioxide extraction of fast pyrolysis oil from softwood. J. Supercrit. Fluids 128: 6–17, https://doi.org/10.1016/j.supflu.2017.04.010.Suche in Google Scholar

Foster, N.R., Gurdial, G.S., Yun, J.S.L., Liong, K.K., Tilly, K.D., Ting, S.S.T., Singh, H., and Lee, J.H. (1991). Significance of the crossover pressure in solid-supercritical fluid phase equilibria. Ind. Eng. Chem. Res. 30: 1955–1964, https://doi.org/10.1021/ie00056a044.Suche in Google Scholar

Guo, X.J., Wang, S.R., Guo, Z.G., Liu, Q.A., Luo, Z.Y., and Cen, K.F. (2010). Pyrolysis characteristics of bio-oil fractions separated by molecular distillation. Appl. Energy 87: 2892–2898, https://doi.org/10.1016/j.apenergy.2009.10.004.Suche in Google Scholar

Gupta, R.B. and Shim, J.-J. (2007). Solubility in supercritical carbon dioxide. CRC Press, Boca Raton.10.1201/9781420005998Suche in Google Scholar

Hofbauer, H., Kaltschmidt, M., Keil, F., Meier, D., and Welling, J. (2016). Pyrolyse. In: Kaltschmitt, M., Hartmann, H., and HofbauerIII, H. (Eds.). Energie aus Biomasse, Grundlagen, Techniken und Verfahren. 3. aktualisierte und erweiterte Auflage. Springer-Verlag, Berlin, Heidelberg, New York, pp. 1183–1265.10.1007/978-3-662-47438-9_14Suche in Google Scholar

Itabaiana Jr, I., do Nascimento, M.A., de Souza, R.O.M.A., Dufour, A., and Wojcieszak, R. (2020). Levoglucosan: a promising platform molecule? Green Chem. 22: 5859–5880, https://doi.org/10.1039/D0GC01490G.Suche in Google Scholar

Karthäuser, J., Raskop, S., Slabohm, M., and Militz, H. (2024). Modification of plywood with phenol–formaldehyde resin: substitution of phenol by pyrolysis cleavage products of softwood kraft lignin. Eur. J. Wood Wood Prod. 82: 309–319, https://doi.org/10.1007/s00107-023-02029-z.Suche in Google Scholar

Lee, M.J., Kou, C.-F., Cheng, J.-W., and Lin, H.-M. (1999). Vapor–liquid equilibria for binary mixtures of carbon dioxide with 1,2-dimethoxybenzene, 2-methoxyphenol, or p-cresol at elevated pressures. Fluid Phase Equilib. 162: 211–224, https://doi.org/10.1016/S0378-3812(99)00183-1.Suche in Google Scholar

Lourençon, T.V., Mattos, B.D., Cademartori, P.H.G., and Magalhães, W.L.E. (2016). Bio-oil from a fast pyrolysis pilot plant as antifungal and hydrophobic agent for wood preservation. J. Anal. Appl. Pyrolysis 122: 1–6, https://doi.org/10.1016/j.jaap.2016.11.004.Suche in Google Scholar

Meier, D. (2016). Schnelle pyrolyse. In: Kaltschmitt, M., Hartmann, H., and Hofbauer III, H. (Eds.). Energie aus Biomasse, Grundlagen, Techniken und Verfahren. 3. aktualisierte und erweiterte Auflage. Springer-Verlag, Berlin, Heidelberg, New York, pp. 1196–1223.Suche in Google Scholar

Möck, D.M.J., Riegert, C., Radtke, S., and Appelt, J. (2023). Process optimization and extraction of acids, syringols, guaiacols, phenols and ketones from beech wood slow pyrolysis liquids with supercritical carbon dioxide at different densities. J. Supercrit. Fluids 199: 105937, https://doi.org/10.1016/j.supflu.2023.105937.Suche in Google Scholar

Möck, D.M.J., Radtke, S., Riegert, C., and Appelt, J. (2024). Production of phenolic-rich slow pyrolysis liquid extracts by supercritical carbon dioxide fractionation. Holzforschung 78: 657–672, https://doi.org/10.1515/hf-2024-0039.Suche in Google Scholar

Montesantos, N. and Maschietti, M. (2020). Supercritical carbon dioxide extraction of lignocellulosic bio-oils: the potential of fuel upgrading and chemical recovery. Energies 13: 1600, https://doi.org/10.3390/en13071600.Suche in Google Scholar

Montesantos, N., Pedersen, T.H., Nielsen, R.P., Rosendahl, L.A., and Maschietti, M. (2019). Supercritical carbon dioxide fractionation of bio-crude produced by hydrothermal liquefaction of pinewood. J. Supercrit. Fluids 149: 97–109, https://doi.org/10.1016/j.supflu.2019.04.001.Suche in Google Scholar

Montesantos, N., Nielsen, R.P., and Maschietti, M. (2020). Upgrading of nondewatered nondemetallized lignocellulosic biocrude from hydrothermal liquefaction using supercritical carbon dioxide. Ind. Eng. Chem. Res. 59: 6141–6153, https://doi.org/10.1021/acs.iecr.9b06889.Suche in Google Scholar

Mudraboyina, B.P., Fu, D., and Jessop, P.G. (2015). Supercritical fluid rectification of lignin microwave-pyrolysis oil. Green Chem. 17: 169–172, https://doi.org/10.1039/c4gc01433b.Suche in Google Scholar

Mukhopadhyay, M. (2000). Natural extracts using supercritical carbon dioxide. CRC Press, Boca Raton.10.1201/9781420041699Suche in Google Scholar

Murali, N., Srinivas, K., and Ahring, B.K. (2017). Biochemical production and separation of carboxylic acids for biorefinery applications. Fermentation 3: 22, https://doi.org/10.3390/fermentation3020022.Suche in Google Scholar

Naik, S., Goud, V.V., Rout, P.K., and Dalai, A.K. (2010). Supercritical CO2 fractionation of bio-oil produced from wheat–hemlock biomass. Bioresour. Technol. 101: 7605–7613, https://doi.org/10.1016/j.biortech.2010.04.024.Suche in Google Scholar PubMed

Rout, P.K., Naik, M.K., Naik, S.N., Goud, V.V., Das, L.M., and Dalai, A.K. (2009). Supercritical CO2 fractionation of bio-oil produced from mixed biomass of wheat and wood sawdust. Energy Fuel. 23: 6181–6188, https://doi.org/10.1021/ef900663a.Suche in Google Scholar

Sukhbaatar, B., Steele, P.H., and Kim, M.G. (2009). Use of lignin separated from bio-oil in oriented strand board binder phenol-formaldehyde resins. Bioresources 4: 789–804, https://doi.org/10.15376/biores.4.2.789-804.Suche in Google Scholar

Wang, J., Cui, H., Wie, S., Zhuo, S., Wang, L., Li, Z., and Yi, W. (2010). Separation of biomass pyrolysis oil by supercritical CO2 extraction. SGRE 1: 98–107, https://doi.org/10.4236/sgre.2010.12015.Suche in Google Scholar

Wei, Y., Lei, H., Wang, L., Zhu, L., Zhang, X., Liu, Y., Chen, S., and Ahring, B. (2014). Liquid–liquid extraction of biomass pyrolysis bio-oil. Energy Fuel. 28: 1207–1212, https://doi.org/10.1021/ef402490s.Suche in Google Scholar

Zheng, J.L. and Wie, Q. (2011). Improving the quality of fast pyrolysis bio-oil by reduced pressure distillation. Biomass Bioenergy 35: 1804–1810, https://doi.org/10.1016/j.biombioe.2011.01.006.Suche in Google Scholar


Supplementary Material

This article contains supplementary material (https://doi.org/10.1515/hf-2025-0088).


Received: 2025-07-10
Accepted: 2025-12-04
Published Online: 2025-12-29
Published in Print: 2026-02-24

© 2025 the author(s), published by De Gruyter, Berlin/Boston

This work is licensed under the Creative Commons Attribution 4.0 International License.

Heruntergeladen am 8.5.2026 von https://www.degruyterbrill.com/document/doi/10.1515/hf-2025-0088/html?lang=de
Button zum nach oben scrollen