INTRODUCTION
Dendrochronology and dendroclimatology often require multiple series of tree rings to create a chronology with adequate sample depth. As a result, hundreds of rings need to be pretreated before they are analysed. This makes for a time consuming and laborious task that can create a bottleneck in processing samples leading to reduced efficiency in the laboratory.
Cellulose Extraction in the Past
The average composition of pine wood species is α-cellulose (40–45%), hemicellulose (20–25%), lignin (23–34%), and resins and extractives (<10%) (Rowell et al. Reference Rowell, Pettersen, Han, Rowell and Tshabalala2005). For radiocarbon analysis, α-cellulose is often the preferred compound to extract as it most accurately represents the atmospheric radiocarbon content from the growth year.
Green (Reference Green1963) outlines the commonly used Jayme-Wise method whereby fine wood meal is first treated using a solvent extraction of 2:1 benzene-ethanol followed by 95% ethanol to remove resins. This is followed by treatment with acidified (glacial acetic acid) NaClO2 and heated in a steam bath to 70°C. Acidified NaClO2 is periodically and heated for varying times depending on wood types. A modification of this method by Leavitt and Danzer (Reference Leavitt and Danzer1993) using toluene instead of benzene, has become one of the most common methods used to extract holocellulose.
Since the turn of the 21st century, there have been a few projects with the aim of processing wood samples in strips of wood (laths) rather than as individual ring samples. This is an important concern as the capacity to process samples is often the major limiting factor in analysis as it is both time and labor-intensive.
Loader et al. (Reference Loader, Robertson, Lucke and Helle2002) made one of the first attempts to extract holocellulose before separating out the individual annual rings by soaking cores in acidified NaClO2. This method was unable to produce accurate δ13C results when compared to individually prepared samples. In later years, lath preparation of samples was successfully done by Li et al. (Reference Li, Labbé, Driese and Grissino-Mayer2011) where laths were treated using the standard Jayme-Wise method (Green Reference Green1963). This did however come with difficulties, as laths were fragile and often broke, thus requiring extra support. Kagawa et al. (Reference Kagawa, Sano, Nakatsuka, Ikeda and Kubo2015) successfully created cases made from polytetrafluoroethylene (Teflon) to support wooden lath samples throughout a Jayme-Wise pretreatment to address this problem while maintaining sample quality. In the present study, we use silica webbing tape to support the lath samples.
FTIR and Radiocarbon as Proxies for Contaminant Removal
Testing the effectiveness of different methods required the use of different proxies and carefully selected samples. We chose to use Fourier-transform infrared spectroscopy (FTIR) and radiocarbon to determine the extent of contaminant removal. Radiocarbon results were compared to the IntCal20 and Bomb21 calibration curves (Hua et al. Reference Hua, Turnbull, Santos, Rakowski, Ancapichún, De Pol-Holz, Hammer, Lehman, Levin and Miller2022; Reimer et al. Reference Reimer, Austin, Bard, Bayliss, Blackwell, Ramsey, Butzin, Cheng, Edwards and Friedrich2020). In conjunction, FTIR offers a visual representation of the presence or absence of wood components when compared to untreated wood.
The use of FTIR in the identification of various wood components has been used effectively in many studies ranging from the paper and pulp industry (Bouchard and Douek Reference Bouchard and Douek1993) to similar projects investigating the preparation of wood samples for isotope analysis (e.g. Rinne et al. Reference Rinne, Boettger, Loader, Robertson, Switsur and Waterhouse2005; van der Wal 2021). FTIR has been shown as a powerful tool in understanding wood composition and testing the removal of contaminants when extracting cellulose.
The positions of the relative peak intensities indicate the presence of different functional groups. Wood spectra generally show absorbance around 3300 cm–1 indicating O-H bonds and a slightly smaller peak around 2900 cm–1 indicating the presence of C-H bonds. The region between 2500 cm–1 and 2000 cm–1 generally shows no absorption, as this region indicates the presence of triple bonds (of which are not abundant in most wood components). For this study, wavenumbers between 1800 cm–1 and 1400 cm–1 are of interest, as this region records the absorbance of double bonds (C=O and C=C). These double bonds are present in lignin, resin, and other minor extractives.
In this study, we test the ability of different methods to produce “clean” cellulose in the shortest time by using 14C measurements and Fourier-Transform Infrared Spectroscopy (FTIR) analysis as a proxy for pretreatment efficiency. To do this, we compare four different pretreatment methods on individual pine tree rings (Pinus sylvestris L.) from central Norway from the 1930s to determine the extent of contaminant removal. We then use the best performing methods on thin wood laths containing multiple rings and analyze using FTIR to understand the potential of lath pretreatment.
MATERIALS
To test the different methods, samples were taken from a pine tree which started its growth in AD 1899 around Vassfjellet (close to the city of Trondheim in central Norway). This tree was felled in AD 2018 and these ages were confirmed using dendrochronological cross matching against the central Norway master curve by Thun (Reference Thun2002). At the time of felling, the heartwood-sapwood boundary was around the AD 1974 ring. The tree is ca. 45 cm in diameter with an average ring width of 1.7 mm. A 5cm thick disc was cut from the trunk and was used for sample material in these experiments.
False Bomb Peak
The transition of wood from sapwood to heartwood has been shown to incorporate 14C from the atmosphere at the time of transition (Cain and Suess Reference Cain and Suess1976; Olsson Reference Olsson1980; Stuiver and Quay Reference Stuiver and Quay1981). This becomes important for samples where the conversion from sapwood to heartwood happened during the bomb spike period as these rings would incorporate a higher 14C concentration than that of the original ring cellulose. This effect makes for 14C-enriched tree rings which are good candidates for testing the effectiveness of pretreatment methods. Figure 1 shows the radiocarbon results of 25 tree ring samples (1925–1950) of untreated wood plotted against the NH1 atmospheric 14C bomb curve (Hua et al. Reference Hua, Turnbull, Santos, Rakowski, Ancapichún, De Pol-Holz, Hammer, Lehman, Levin and Miller2022) over 1942–2019 and IntCal20 (Reimer et al. Reference Reimer, Austin, Bard, Bayliss, Blackwell, Ramsey, Butzin, Cheng, Edwards and Friedrich2020) during the period 1850–1941. Our untreated wood samples before the 1930s contain between 3‰ and 15‰ more 14C than the atmosphere during their growing period. This increases in the 1930s with 1933 having the biggest difference between untreated wood and the curve (70‰ difference). This increased Δ14C marks the “false bomb spike” for this tree. It is for this reason that we use tree ring samples for 1933–1937 to test pretreatment methods.
Figure 1 Intcal20 (1850–1941; Reimer et al. Reference Reimer, Austin, Bard, Bayliss, Blackwell, Ramsey, Butzin, Cheng, Edwards and Friedrich2020) and Bomb calibration curve NH1 (1942–2019; Hua et al. Reference Hua, Turnbull, Santos, Rakowski, Ancapichún, De Pol-Holz, Hammer, Lehman, Levin and Miller2022) plotted in gray against the Δ14C results of untreated tree rings from 1925 to 1950 (black).
METHODS
For the pretreatment of individual rings, the earlywood (EW), latewood (LW), and whole ring (WR) samples were cut for each year (1933–1937). The disc was cut into smaller pieces using an electric band saw. Thin shavings were cut using handheld scalpels from these pieces for each year, taking care to keep EW and LW portions separate for pretreatment. These samples were then pretreated using the methods outlined in Table 1 and described below. This resulted in a total of 75 samples including 15 samples that would not be pretreated. Sample weights ranged between 4 mg and 6 mg for 17.5% NaOH and Solvent extraction, and between 10mg and 70mg for BABAB and BABAB+ treatments.
Table 1 Outline of the four pretreatment methods tested: 17.5% NaOH (Rowell et al. Reference Rowell, Pettersen, Han, Rowell and Tshabalala2005), Solvent extraction (Bruhn et al. Reference Bruhn, Duhr, Grootes, Mintrop and Nadeau2001), BABAB (Němec et al. Reference Němec, Wacker, Hajdas and Gäggeler2010), and BABAB+. The amounts and times indicated are those used for individual samples. These were increased for the pretreatment of laths.
17.5% NaOH
The use of a strong base is important for the isolation of α-cellulose from holocellulose (Rowell et al. Reference Rowell, Pettersen, Han, Rowell and Tshabalala2005) as it is insoluble in 17.5% NaOH unlike hemicellulose. We therefore experiment with treating the wholewood with only 17.5% NaOH to test the ability of a strong base in creating a crude fraction with properties similar to cellulose.
Solvent Extraction
Solvent extractions are often the starting point of many pretreatments of wood tissue (Leavitt and Danzer 1993; Loader et al. Reference Loader, Robertson, Barker, Switsur and Waterhouse1997). A common mix of solvents has often included the use of toluene and ethanol to remove resinous material and other extractives. A solvent extraction alone is not adequate as resins and extractives do not make up more than 10% of pine wood samples. However, in the present case, as we are aware that the extractives are enriched in radiocarbon, this method should prove fairly effective in improving the results. The eluotropic sequence used in this project is taken from Bruhn et al. (Reference Bruhn, Duhr, Grootes, Mintrop and Nadeau2001) and includes the use of six different solvents in the following order: tetrahyrofuran, chloroform, petroleum ether, acetone, methanol, and water. This choice of solvents, from non-polar to polar, ensures that each solvent washes out the previous one.
BABAB
This is a holocellulose extraction method from Němec et al. (Reference Němec, Wacker, Hajdas and Gäggeler2010), which combines two common concepts for holocellulose extraction: the acid/base/acid (ABA) pretreatment sequence and an acidified bleach treatment. The ABA sequence is commonly used in pretreatments to remove carbohydrates and, in the case of wood, leaves behind cellulose and lignin (Gaudinski et al. Reference Gaudinski, Dawson, Quideau, Schuur, Roden, Trumbore, Sandquist, Oh and Wasylishen2005). Němec et al. (Reference Němec, Wacker, Hajdas and Gäggeler2010) modified this and preceded this step with a long overnight soak in 4% NaOH, which disrupts the wood structure allowing for a more effective use of the ABA steps. This is then followed by an acidic bleaching step to remove the lignin. The remaining fraction from this method is holocellulose. From start to finish, samples pretreated using the BABAB method require one overnight soak and 8 hours of additional treatment, not including sample cutting and drying times.
BABAB+
This method uses the BABAB holocellulose extraction (described above) followed by a strong base treatment (17.5% NaOH) for 3.5 hours to remove hemicellulose. Degraded samples may require less treatment time. A short 0.4% HCl step to remove atmospheric carbon that dissolved in the alkali solution ends the preparation. Using this method, we expect to extract a pure α-cellulose of sufficiently high quality for precise radiocarbon measurements as opposed to the holocellulose extracted using the BABAB method.
Lath Pretreatment
The lath pretreatment began with the use of an electric band saw to cut 1 mm to 3 mm thick laths from a wood disc (approximately 3 cm thick). Two laths containing 102 rings each were pretreated using BABAB and BABAB+ methods in long sample boats (see Supplementary material, Figure 1). The sample boats are made of borosilicate glass and are 300 mm long, 58 mm wide, and 28 mm deep.
To compensate for the thickness of material being pretreated, the amount of solution and the submerging times were increased to full-day submersion. The laths were pretreated in 100 mL of the solutions for at least double the time outlined in Table 1. It became particularly important to perform the first NaOH step twice, adding fresh solution the second time, as well as performing multiple bleach steps until the whole lath was white. To provide extra support to the sample during the bleaching steps, 30 cm strips of silica webbing tape (2.5 cm wide) were placed beneath the lath to help move the sample in one piece.
While the BABAB treatment could be completed with the lath intact, the strong base step at the end of BABAB+ proved to be too aggressive. The laths had to be cut prior to this last step, which was done on individual rings, thus not completed as an in-tact lath.
FTIR and Radiocarbon Analysis
All samples were left in a drying oven at 65°C until completely dry after pretreatment. Samples were then combusted in an elemental analyzer and graphitized in an automatic system using a H2-Fe reaction (Seiler et al. Reference Seiler, Grootes, Haarsaker, Lélu, Rzadeczka-Juga, Stene, Svarva, Thun, Værnes and Nadeau2019). The graphite was measured at the Trondheim 1MV AMS system following standard procedures (Nadeau et al. Reference Nadeau, Vaernes, Svarva, Larsen, Gulliksen, Klein and Mous2015).
FTIR measurements were done using a PerkinElmer Spectrum 400 FT-IR/FT-NIR Spectrometer. Absorption was measured between 4000 cm–1 and 550 cm–1 in 32 scans per sample. Background measurements were also taken in between each sample. The results were normalized using the Spectragryph (version 1.2.16.1) to allow for easier comparison.
RESULTS AND DISCUSSION
Individual Ring Pretreatments
FTIR
FTIR analysis of the pretreated fractions and untreated wood show a progression of “contaminant” removal between wavenumbers 1400 and 1800 cm–1. This region mostly represents the bending and stretching of double bonds (C=O and C=C) neither of which should be present in α-cellulose. Untreated wood has the highest absorbance in this region due to the presence of lignin and wood extractives. Five peaks were identified in this region (labeled 1–5 in Figure 2). Figure 2 shows the FTIR spectra for the 1935 EW pretreated samples. There was no significant visible difference in the spectra between the years and between earlywood, latewood, and whole wood samples.
Figure 2 FTIR spectra of the different pretreatment methods: No pretreatment (black), 17.5% NaOH (red), solvent extraction (yellow), BABAB (green), and BABAB+ (purple). (Please see online version for color figures.)
Peak 1 (1734 cm–1) typically represents C=O bonds found in esters, ketones, aldehydes, and acids. This peak can be detected in untreated wood as well as the NaOH and solvent extraction samples. This peak has been attributed to the presence of lignin in wood (Pandey and Pitman Reference Pandey and Pitman2003; Rinne et al. Reference Rinne, Boettger, Loader, Robertson, Switsur and Waterhouse2005). We do not expect a solvent extraction to remove lignin, but this peak is reduced in samples treated with solvent extraction. It is therefore possible that absorbance in this peak may also be caused by resin or other extractives.
Peak 2 (1698 cm–1), associated with resins and extractives, is only observed in the untreated wood and the NaOH pretreatment sample although absorption is somewhat reduced. Solvent extraction, BABAB and BABAB+ pretreated samples do not show absorbance of this band. This is to be expected as resins and extractives are secondary components that are relatively easy to remove.
Peak 3 (1641 cm–1) is seen in all fractions. While we did not expect to see this in the BABAB+ pretreated wood fraction (as it suggests the presence of double bonds), this is not uncommon in α-cellulose as it is associated with the extra moisture (Rinne et al. Reference Rinne, Boettger, Loader, Robertson, Switsur and Waterhouse2005; Hajdas et al. Reference Hajdas, Hendriks, Fontana and Monegato2017). Rinne et al. (Reference Rinne, Boettger, Loader, Robertson, Switsur and Waterhouse2005) also tested if the water used during pretreatment could be detected in the δ18O analysis of the cellulose and found that it did not make a significant difference.
Peak 4 (1594 cm–1) was observed in all samples other than BABAB+ pretreatment. This peak highlights the efficiency of the extra 17.5% NaOH after a BABAB procedure and, ultimately, the removal of hemicellulose from the wood. Similar to peak 2, this justifies the need to remove lignin, resins, and extractives for complete cellulose extraction as there was very little reduction in absorption from the sample treated only with 17.5% NaOH.
Peak 5 (1509 cm–1) is only completely removed by BABAB+ pretreatment; however, a BABAB pretreatment removes a large portion of the peak. This peak has been attributed to the presence of lignin (Pandey and Pitman Reference Pandey and Pitman2003), thus suggesting that, in this case, the BABAB pretreatment has not been completely successful in removing lignin. Němec et al. (Reference Němec, Wacker, Hajdas and Gäggeler2010) suggests repeated bleaching steps may be required, this may be necessary for well-preserved woods.
The FTIR spectra obtained from BABAB+ pretreatment is visually similar to spectra obtained from cellulose extracted from a modified Jayme-Wise on Pinus wood Kagawa et al. (Reference Kagawa, Sano, Nakatsuka, Ikeda and Kubo2015). This suggests that a the BABAB+ pretreatment outlined here is capable of producing high quality α-cellulose. This is followed by a BABAB pretreatment that is still effective in removing contaminant components but only produces holocellulose.
Lath Pretreatment
The spectra shown in Figure 2 suggest that to obtain “clean” enough samples we would need to perform BABAB or BABAB+ pretreatments. However, the capacity to perform these pretreatments is limited by time and sample pretreatment capacity. Making precise cuts to separate rings (in some instances making sub-annual cuts) for a whole tree sequence before pretreatment is also time consuming (compared to a few minutes to cut a lath from a disc with a bandsaw or cutting a core in half with a handheld electric mini-saw). With BABAB and BABAB+ being the most effective but time-consuming pretreatments within this project, we decided to alter and adjust these methods to test if they can be used for pretreating a wood lath sample.
Figure 3 shows the comparison of BABAB and BABAB+ when done on individual rings, rings from the lath, and untreated wood. These spectra show that, with time adjustments, a lath pretreatment can produce a good quality cellulose comparable to that of a single ring pretreatment. When comparing the BABAB+ method (Figure 3B), the lath pretreatment shows little absorbance around the untreated peak positions 1, 2, 4, and 5. The amplitude of peak 3 is likely caused by excess water in the sample as they might not have been dried sufficiently. This result gives us confidence in scaling the method for laths. The comparison of the BABAB pretreated samples (Figure 3A) suggest that using the time adjusted BABAB method for a lath results in improved quality of cellulose. Peaks 4 and 5 almost disappear in the lath sample unlike the in the individual ring test. For the individual ring pretreatments, only BABAB+ was able to remove these two peaks. This suggests that extended submersion times can compensate for not using the ultrasonic bath or the addition of a strong base to remove hemicellulose.
Figure 3 A. FTIR spectra of a BABAB lath pretreated ring, an individually pretreated ring and untreated wood sample. B. FTIR spectra of a BABAB+ lath pretreated ring, an individually pretreated ring, and an untreated wood sample.
Ring vs. Lath
The sample boats are relatively compact and can accommodate 25-cm-long laths (usually more than 100 rings). Using two boats, a BABAB pretreatment can produce over 200 samples in five days. Pretreatment of an entire lath comes with its own difficulties and limitations. A major one being the structural integrity of the sample throughout the pretreatment. We found it increasingly difficult to keep the samples intact with each bleaching step. Taking pictures of the lath and easily distinguishable sequences before pretreatment and throughout the process made it easier to determine the ring year. This is important to note when using this method as it requires an attention to detail in order not to lose or add a ring. The very nature of the bleach steps introduces a second problem: the difficulty to distinguish rings. However, with good lighting and photographs of easily identifiable sequences, the rings can still be identified. Making sub-annual cuts was easier at this stage compared to cutting untreated wood. Treating a lath also poses a limit to the type of samples that can be done. In this case, samples cut from a thick slab of wood were available, but it is common in dendro- studies to only have access to cores obtained with a boring device. Cutting these cores into 2mm thick laths may result in narrow rings yielding samples that are too small for analysis. We can also appreciate that the samples chosen in these experiments were selected because their wider rings permit easier identification of ring boundaries. It is often the case that wood samples in climate studies have narrow rings thus making lath pretreatment more difficult.
14C Measurements
Radiocarbon measurements for the pretreated fractions from individual rings are shown in Table 2. The difference between these results and the IntCal20 curve from 1933 to 1937 (Δ14C) is shown in Figure 4. Due to natural variations and regional variation, we expect some deviation from the exact values of the IntCal20 curve but still use the curve as a guide for expected values. The unpretreated wood samples show the highest difference in Δ14C with low accuracy and repeatability. This is reflected in the FTIR results, showing high absorption between 1800 cm–1 and 1400 cm–1. The samples soaked in 17.5% NaOH have a much smaller difference (∼30 ‰ less) in Δ14C compared to untreated wood. This suggests the partial removal of contaminant constituents in the wood; however, these samples are still far from the Intcal20 values. The FTIR results for the NaOH treatment show absorption around Peak 2, which is mostly caused by resin. The large difference between the samples and the Intcal20 values support that Peak 2 records the presence of resins. Solvent extraction pretreatment produced the next best results with more consistency. This is consistent with the FTIR results that show samples treated by solvent extraction exhibit a spectrum closest to those of BABAB and BABAB+. The 1937 and 1934 rings even showed solvent extracted samples performing better than BABAB treated samples. While this was not a consistent trend, it does show the effectiveness of this Soxhlet sequence for these samples. It is important to note that the effectiveness of this method may be biased to this study as it is to our understanding that the resin and extractives which are later incorporated into the wood contain bomb radiocarbon. However, resin and extractives make up a small component of the whole wood. This is clear in the FTIR results (Figure 2) where solvent extraction reduced peaks relating to resins but not lignin.
Table 2 Radiocarbon results of untreated wood samples and the four different pretreatment methods for the years 1933–1937.
Figure 4 Difference in radiocarbon results of pretreated samples from 1933–1937 compared to the Intcal20 calibration curve.
The best performing pretreatment methods were BABAB and BABAB+. Samples pretreated with a BABAB+ method measured the closest to the Intcal20 values compared to BABAB samples. These results show the efficiency of the 17.5% NaOH step after bleaching and the small isotopic differences between holocellulose and α-cellulose and ultimately the importance of isolating α-cellulose for radiocarbon measurements. The results for earlywood, latewood, or whole ring samples do not show statistical differences.
CONCLUSION
We have tested four methods of pretreatment to explore the potential of using less vigorous pretreatment methods as well as the individual capabilities of these methods to remove different wood components. The wood samples were selected to include the “false bomb peak” in which 14C from the bomb spike is incorporated in wood during the sapwood to heartwood transition. In addition to radiocarbon measurements, we have used FTIR to assess the purity of the samples after each pretreatment.
Based on the FTIR spectra there are clear differences in the spectra of more crude pretreatment fractions compared to the BABAB and BABAB+ extracted holo- and α-cellulose. Furthermore, we can identify the peaks affected by the different solvent washes. The eluotropic sequence of solvent extraction is very effective in removing secondary wood components that in this case have a much higher 14C content, but not enough lignin is removed by this procedure.
FTIR is a powerful proxy tool for assessing contaminant removal in cellulose. In this case, where we were aware of the source of “contamination”, we were able to avoid overestimating the effectiveness of a solvent extraction in the samples.
We also highlight that with some adjustments to the BABAB and BABAB+ methods, they can be used to pretreat long laths with multiple rings that are comparable by FTIR to individually processed rings. By increasing the time of submerging and some careful sample handling, lath pretreatment potentially doubles sample output. This is particularly important in creating tree ring chronologies, as it reduces processing time significantly.
As shown in Figure 4, BABAB+ pretreatment produced cellulose whose radiocarbon content was closest to the IntCal20 but the difference between α-cellulose and holocellulose for stable isotope analyses needs to be further investigated.
COMPETING INTEREST DECLARATION
There are no competing interests from any of the authors of this manuscript.
SUPPLEMENTARY MATERIAL
To view supplementary material for this article, please visit https://doi.org/10.1017/RDC.2024.20
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