# Effect of Ammonia Fumigation Treatment on Wood Color and Chemical Composition

Authors: Weigang Zhang; Minzhen Bao; Weisheng Sun; Lei Huang; Liang Cheng
Journal: International Journal of Polymer Science
 (2021)

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## Abstract

Betula alnoides was used as a test material to study the effect of ammonia fumigation treatment on wood color and chemical composition. The effects of concentration, temperature, and duration of ammonia fumigation on wood color were studied. The properties of the material were studied using contact angle measurements, X-ray diffraction, Fourier-transform infrared spectroscopy, and dynamic thermomechanical analysis. In general, the color difference of the wood increased with the concentration of ammonia used in the fumigation process, treatment temperature, and treatment duration. After ammonia fumigation treatment, the chemical composition of hydroxyl and carboxyl groups in the wood was reduced. We concluded that ammonia fumigation treatment decreased material wettability and dynamic mechanical rigidity and increased the degree of crystallinity in wood.


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## Body

## 1. Introduction

Owing to its natural appearance, esthetically pleasing color, and excellent material properties, wood is widely used in decorative building applications, particularly for flooring [1, 2]. Economic development and improved quality of life have increased the demand for more abundant colors and varieties of wood flooring. Antique wood is artistically designed and chemically toned to produce a rich and stable color, strong layering, and visual appeal. The surface is processed in an old-fashioned style [3]. Since the 1970s, European and American countries have used chemical toning to achieve antique-style wood flooring and furniture. Chinese flooring companies began to produce antique flooring in the 1990s. Their products quickly captured the domestic market, resulting in the rapid development of antique flooring manufacturing methods.The ammonia fumigation process uses ammonia and ammonia solution to naturally change the color of the wood surface in a confined space under certain environmental conditions [4]. Pawlak and Pawlak [5] studied the chemical reaction between liquid ammonia and wood and found that there may be three chemical reactions between liquid ammonia and wood: (1) ammonia reacts with the carboxyl group to form an amide, (2) ammonia reacts with aldehydes and ketones to form imines, and (3) the ester group reacts with the amide. Research by Weigl et al. [6] showed that ammonia fumigation is effective for preventing the aging of wood and maintaining the color. Weigl also studied the effect of ammonia fumigation on the color of 38 kinds of wood and found that the color change of wood after ammonia fumigation was due to the change of wood chemical composition. Miklečić et al. [7] studied the effect of ammonia on the color change of oak, maple, spruce, and larch wood. All of these woods experienced obvious blackening after exposure to ammonia. Ammonia chemical coloring can reduce unevenness in the color of composite wood in the in-plane and thickness directions and can make the wood texture more prominent and esthetically pleasing. Wood subjected to ammonia fumigation acquires a unique color, which enriches the style of the wood and makes full use of wood materials.Herein,Betula alnoides was used as a raw material to carry out ammonia fumigation treatment. A single factor experiment was used to study the influence of ammonia fumigation on wood color at different temperatures and concentrations for different durations. Subsequently, the contact angle, crystallinity, and functional groups of the treated material were analyzed. In addition, the dynamic viscoelasticity of the treated material was studied. This research provides a theoretical reference for determining suitable processing and utilization conditions of ammonia fumigation treatment, with the aim of improving wood product quality.


## 2. Materials and Methods

### 2.1. Preparation of Materials

B. alnoides air-dried sawn timber of good quality and with no obvious defects (cracking, discoloration, or decay) was used as the test material. After planning on all sides, the timber was cut into test pieces with dimensions of 200×40×20mm. Diluting 28% ammonia solution with deionized water to obtain 22% and 16% ammonia solution. Then, 50 mL of ammonia solution (16%, 22%, or 28%) was placed in a glass dish at the bottom of a container. The test pieces were stacked in the glass dish so as to maximize the contact area between the wood and ammonia. The reaction vessel was then sealed and placed in a blast drying box set to a temperature of 25, 30, or 35°C. The test conditions were as follows: ammonia concentrations of 16%, 22%, or 28% at a fixed temperature of 30°C; and temperatures of 25, 30, or 35°C at a fixed ammonia concentration of 28%. For each condition, 15 wood samples were removed on days 1, 3, and 5 to test their performance.


### 2.2. Color Determination

An automatic colorimeter was used to measure and record the colorimetric parameters of the samples before and after processing. The sample color was measured and calculated based on theL∗a∗b∗ chromaticity space color system of CIE (International Illumination Standards Committee). According to the L∗a∗b∗ system, the color difference (ΔE) between two specimens (e.g., before and after processing) is calculated as
(1)ΔE=ΔL∗2+Δa∗2+Δb∗2,where ∆L∗, ∆a∗, and ∆b∗ represent the total changes in L∗, a∗, and b∗ after the ammonia fumigation treatment, respectively.


### 2.3. Surface Wettability Analysis

The static drop method was used to measure the contact angle of the wood surface. Distilled water was used as a test liquid. The sample was injected directly during the test. In this experiment, a photograph was taken within 1 to 2 s of droplet injection, and then the surface contact angle of the wood was measured using the tangent method. Each measurement was repeated 6 times, and the results were averaged.


### 2.4. X-Ray Diffraction (XRD) Analysis

XRD patterns of the specimens were determined using a Bruker D8 Advance diffractometer with Cu Kα radiation (λ=1.5404Å) at a scanning rate of 2° min−1 in the range of 10–80°. Segal et al.’s [8] empirical method was used to calculate the crystallinity. The diffraction intensity of wood fiber has a maximum value of I002 when 2θ=22° and a minimum value of Iam when 2θ=18°. These intensity values were used to calculate the diffraction scattering intensity of the amorphous area in the wood fiber. The cellulose crystallinity was calculated as
(2)Cr=I002−IamI002×100%.


### 2.5. Dynamic Mechanical Analysis (DMA)

Test samples with dimensions of35×12×2mm were prepared for DMA. A test temperature range of 30–260°C, heating rate of 2°C/min, constant strain of 0.02%, and amplitude of 20 μm were used. The sample was fixed to a double 35 mm cantilever beam. The temperature of the sample environment was raised from room temperature to 30°C, followed by an isothermal hold for 5 min. Subsequently, the temperature program measurement was started. The storage modulus and loss modulus were used as parameters to characterize the dynamic mechanical properties of the material.


### 2.6. Fourier-Transform Infrared (FTIR) Analysis

Infrared spectra of the samples were obtained from a KBr disk containing 1% finely ground samples using a Fourier-transform infrared (FTIR) spectrometer (Vertex 70, Bruker, Japan). Each spectrum was recorded over the wavenumber range of 4000 to 400 cm−1 with an average of 32 scans at a spectral resolution of 4 cm−1.


## 2.1. Preparation of Materials

B. alnoides air-dried sawn timber of good quality and with no obvious defects (cracking, discoloration, or decay) was used as the test material. After planning on all sides, the timber was cut into test pieces with dimensions of 200×40×20mm. Diluting 28% ammonia solution with deionized water to obtain 22% and 16% ammonia solution. Then, 50 mL of ammonia solution (16%, 22%, or 28%) was placed in a glass dish at the bottom of a container. The test pieces were stacked in the glass dish so as to maximize the contact area between the wood and ammonia. The reaction vessel was then sealed and placed in a blast drying box set to a temperature of 25, 30, or 35°C. The test conditions were as follows: ammonia concentrations of 16%, 22%, or 28% at a fixed temperature of 30°C; and temperatures of 25, 30, or 35°C at a fixed ammonia concentration of 28%. For each condition, 15 wood samples were removed on days 1, 3, and 5 to test their performance.


## 2.2. Color Determination

An automatic colorimeter was used to measure and record the colorimetric parameters of the samples before and after processing. The sample color was measured and calculated based on theL∗a∗b∗ chromaticity space color system of CIE (International Illumination Standards Committee). According to the L∗a∗b∗ system, the color difference (ΔE) between two specimens (e.g., before and after processing) is calculated as
(1)ΔE=ΔL∗2+Δa∗2+Δb∗2,where ∆L∗, ∆a∗, and ∆b∗ represent the total changes in L∗, a∗, and b∗ after the ammonia fumigation treatment, respectively.


## 2.3. Surface Wettability Analysis

The static drop method was used to measure the contact angle of the wood surface. Distilled water was used as a test liquid. The sample was injected directly during the test. In this experiment, a photograph was taken within 1 to 2 s of droplet injection, and then the surface contact angle of the wood was measured using the tangent method. Each measurement was repeated 6 times, and the results were averaged.


## 2.4. X-Ray Diffraction (XRD) Analysis

XRD patterns of the specimens were determined using a Bruker D8 Advance diffractometer with Cu Kα radiation (λ=1.5404Å) at a scanning rate of 2° min−1 in the range of 10–80°. Segal et al.’s [8] empirical method was used to calculate the crystallinity. The diffraction intensity of wood fiber has a maximum value of I002 when 2θ=22° and a minimum value of Iam when 2θ=18°. These intensity values were used to calculate the diffraction scattering intensity of the amorphous area in the wood fiber. The cellulose crystallinity was calculated as
(2)Cr=I002−IamI002×100%.


## 2.5. Dynamic Mechanical Analysis (DMA)

Test samples with dimensions of35×12×2mm were prepared for DMA. A test temperature range of 30–260°C, heating rate of 2°C/min, constant strain of 0.02%, and amplitude of 20 μm were used. The sample was fixed to a double 35 mm cantilever beam. The temperature of the sample environment was raised from room temperature to 30°C, followed by an isothermal hold for 5 min. Subsequently, the temperature program measurement was started. The storage modulus and loss modulus were used as parameters to characterize the dynamic mechanical properties of the material.


## 2.6. Fourier-Transform Infrared (FTIR) Analysis

Infrared spectra of the samples were obtained from a KBr disk containing 1% finely ground samples using a Fourier-transform infrared (FTIR) spectrometer (Vertex 70, Bruker, Japan). Each spectrum was recorded over the wavenumber range of 4000 to 400 cm−1 with an average of 32 scans at a spectral resolution of 4 cm−1.


## 3. Results and Discussion

### 3.1. Color Change

Figures1 and 2 showed the appearance of the ammonia-fumigated wood under different treatment conditions. With the increase of the ammonia concentration and the fumigation temperature, the color of treated samples gradually deepened.Figure 1
The appearance of the ammonia-fumigated sample at different ammonia concentrations.Figure 2
The appearance of the ammonia-fumigated samples at different temperatures.Figure3(a) shows the variation in ΔE of ammonia-fumigated samples depending on the ammonia concentration and treatment duration at a temperature of 30°C, and Figure 3(b) shows the variation in color difference depending on the fumigation temperature and treatment duration at 28% ammonia solution. As shown in Figure 3, the chromatic aberration of the treated samples increased significantly as the treatment duration increased. The chromatic aberration increased significantly between the first and third days and slightly between the third and fifth days. When the treatment temperature was 30°C, the ΔE increased with increasing ammonia concentration. The ΔE between the samples fumigated in ammonia solution of different concentrations indicated that the ammonia concentration helps to improve the effect of ammonia fumigation. When the ammonia concentration was 28%, the ΔE increased with increasing temperature. However, the ΔE at different temperatures indicated that the temperature has a low effect on the color of the ammonia-fumigated wood. The color of wood is mainly derived from the chromophore groups in lignin; in addition, the pigment, tannin, resin, and other substances in the extract also have a significant effect on the color of the wood. According to existing research, the main chemical cause of wood discoloration is the oxidative condensation reaction of tannins, pigments, alkaloids, sugars, phenols, and other organic substances in wood [9]. Under the action of ammonia, the resins, tannins, polyphenols, and anthocyanins in the wood undergo chemical reactions to deepen the color of the wood.Figure 3
Total color change (ΔE) of wood samples. (a) ΔE of wood samples fumigated at different ammonia concentrations (16–28%) for different durations (1–5 days); (b) ΔE of wood samples fumigated at different temperatures (25–35°C) for different durations (1–5 days).
(a)(b)


### 3.2. Surface Wettability

Figure4 shows the variation in water contact angle of the samples treated at 30°C with different ammonia concentrations and treatment durations. Compared with that of the control wood, the contact angle of the ammonia-fumigated samples increased with increasing ammonia concentration and treatment duration. The difference in the contact angle of wood treated with different ammonia concentrations decreased with increasing treatment duration, with a contact angle of approximately 77° after 5 days of treatment. An increase in contact angle corresponds to a decrease in wettability. The change in contact angle is mainly related to the change of chemical components of the wood after ammonia fumigation. Free radicals on the wood surface react during the ammonia fumigation process. The crystallinity of the ammonia-fumigated wood increases, and the amount of amorphous cellulose and free hydroxyl groups decreases accordingly [10]. Therefore, its surface wettability decreases, resulting in the measured increase in contact angle.Figure 4
Contact angle of ammonia-fumigated wood samples.


### 3.3. XRD Analysis

As shown in Figure5, the positions of the XRD peaks of the wood crystal planes were not significantly different after the ammonia fumigation process. In addition, the width of the crystalline zone did not change significantly; that is, the ammonia fumigation treatment did not change the wood cellulose crystal structure. Ammonia can enter the amorphous regions of cellulose to cause swelling by increasing the distance between the molecular chains, which increases the crystallinity of the wood [11]. Table 1 demonstrates that treatment duration had an obvious effect on the crystallinity. When the other treatment conditions were constant, the crystallinity increased with extension in treatment duration. When treated at the same temperature for the same duration, the crystallinity of the wood samples increased slightly with an increase in ammonia concentration. Finally, under treatment with the same ammonia concentration for the same duration, the crystallinity of the ammonia-fumigated samples increased with increasing temperature. Overall, ammonia fumigation treatment increased the crystallinity of the treated wood, indicating that ammonia causes a positive degree of crystallinity.Figure 5
XRD curves of treated wood samples. (a) Durations (1–5 days); (b) ammonia concentrations (16–28%); (c) temperatures (25–35°C).
(a)(b)(c)Table 1
Crystallinity of treated wood samples.
SamplesConcentration/%Temperature/°CDuration/dayCrystallinity/%Ammonia-fumigated samples2230154.981630346.63223055.49283055.60282554.38283556.582230556.21Control samples———46.30


### 3.4. DMA Analysis

Figure6 shows the measured storage modulus and loss modulus of the wood samples treated with different temperatures and ammonia concentrations for different durations. Figure 6(a) shows that the storage modulus of the samples treated at different temperatures in 28% ammonia solution decreased with increasing treatment temperature. This is because the kinetic energy of the wood molecules is low under low-temperature conditions. When external force is applied, various functional groups such as side groups, branching chains, and main chains can move. Therefore, the storage modulus is large [12]. When the temperature rises, the molecular motion gradually increases, and the storage modulus gradually decreases. The storage modulus of the ammonia-fumigated wood was lower than that of the control wood. The main reason for this is that polar ammonia molecules swell the noncrystalline areas of the wood cellulose, hemicellulose, and lignin during ammonia fumigation treatment. This increases the free movement space of the molecules. At the same time, the increase in temperature provides the molecules with enough energy to promote the glass transition of hemicellulose and lignin, thereby enhancing the movement of wood molecules.Figure 6
DMA curves of treated samples. (a) Storage modulus and (b) loss modulus of samples fumigated at different temperatures (25–35°C); (c) storage modulus and (d) loss modulus of samples fumigated with different ammonia concentrations (16–28%); (e) storage modulus and (f) loss modulus of samples fumigated for different durations (1–5 days).
(a)(b)(c)(d)(e)(f)The loss modulus of the wood samples decreased with increasing treatment temperature. Compared with that of the control samples, the loss modulus of the ammonia-fumigated samples was reduced. The plasticity of the wood decreased upon ammonia fumigation treatment, while thermal softening of the lignin and hemicellulose molecules occurred, causing viscoelastic changes to the wood. This demonstrates that ammonia fumigation has an effect on the chemical composition of wood. Anα relaxation peak appears in the loss modulus at a temperature of 30–60°C. After ammonia fumigation treatment, the relaxation peak of the material gradually occurs at a lower temperature (from 73 to 32.5–55.6°C), while the intensity of the relaxation peak increases. This indicates that the internal binding force in the amorphous region of the material decreases, and the reduction of the intermolecular force is prone to relaxation [13]. Figures 6(c)–6(f) show that as the ammonia concentration and fumigation duration increased, the storage modulus reduced, the loss modulus increased, the plasticity increased, and the elasticity decreased. These changes are beneficial for improving the dimensional stability of the wood.


### 3.5. FTIR Spectroscopy

Figure7 shows the FTIR spectra of the ammonia-fumigated wood samples treated at 25, 30, or 35°C with an ammonia concentration of 28% and treatment duration of 3 days, whereas Figure 8 shows the FTIR spectra of samples treated at 30°C with an ammonia concentration of 22% and treatment duration of 1, 3, or 5 days.Figure 7
FTIR spectra of ammonia-fumigated samples treated at different temperatures.Figure 8
FTIR spectra of ammonia-fumigated samples treated for different durations.As shown in Figure7, the absorption peak at 3,443 cm−1 of the ammonia-fumigated wood treated at different temperatures was reduced compared with that of the control wood. This indicates that the ammonia fumigation treatment reduces the hydroxyl content of the wood. The number of free hydroxyl groups in the amorphous cellulose region decreases and the crystallinity of the wood increases [5]. The 2,250–2,340 cm−1 band of the ammonia-fumigated material indicated that it might be a compound containing triple bonds or cumulative double bonds. The absorption peak at 2,120 cm−1 corresponds to the external standard, potassium bromide [14]. The intensity of the absorption peak of the nonconjugated carbonyl group at 1,500–1,735 cm−1 decreased, characterizing the relative decrease in hemicellulose content, and the absorption peak of the alcoholic hydroxyl group at 1,271 cm−1 reduced. Thus, the numbers of hydroxyl and carboxyl groups on the main chain and side chain of hemicellulose were reduced. Therefore, there was a reaction between ammonia and hemicellulose that reduced the hemicellulose content. The lignin benzene ring structure vibration at 1,602 cm−1 was significantly reduced, indicating that the lignin content decreased. The peak at 1,086 cm−1 corresponded to the C − O stretching vibration of secondary lignin alcohols and aliphatic ethers. Carbonyl, carboxyl, and hydroxyl groups, as well as carbon–carbon double bonds, are the main chromophoric groups and auxochromic groups in wood, which are present in lignin and extracts. Therefore, ammonia gas may react with wood extracts [15]. From the analysis of the absorption peak absorbance, it was clear that the intensity of the absorption peaks decreased as the temperature of the ammonia fumigation treatment increased. This might be due to the increase in moisture in the air due to the increase in temperature, which reduced the density of ammonia molecules and the wood ammonia fumigation effect.Figure8 shows that the intensity of the characteristic peak at 3,000–3,750 cm−1 decreased slightly with the ammonia fumigation duration. This is due to multiple factors, including the low concentration of ammonia fumigation and ammonia fumigation water molecules. The reduction in hydroxyl groups was reduced, indicating that treatment duration had little effect on the performance of the ammonia fumigation. Nevertheless, the ammonia fumigation treatment duration had a significant effect on the 2,250–2,340 cm−1 region band.In summary, after ammonia fumigation treatment, the content of carbonyl and hydroxyl groups in the wood decreased, and the number of hydrophilic hydroxyl and carbonyl groups decreased. This reduced the surface wettability and increased the contact angle. As the ammonia fumigation temperature increased, the reaction between the ammonia gas and hemicellulose or lignin increased.


## 3.1. Color Change

Figures1 and 2 showed the appearance of the ammonia-fumigated wood under different treatment conditions. With the increase of the ammonia concentration and the fumigation temperature, the color of treated samples gradually deepened.Figure 1
The appearance of the ammonia-fumigated sample at different ammonia concentrations.Figure 2
The appearance of the ammonia-fumigated samples at different temperatures.Figure3(a) shows the variation in ΔE of ammonia-fumigated samples depending on the ammonia concentration and treatment duration at a temperature of 30°C, and Figure 3(b) shows the variation in color difference depending on the fumigation temperature and treatment duration at 28% ammonia solution. As shown in Figure 3, the chromatic aberration of the treated samples increased significantly as the treatment duration increased. The chromatic aberration increased significantly between the first and third days and slightly between the third and fifth days. When the treatment temperature was 30°C, the ΔE increased with increasing ammonia concentration. The ΔE between the samples fumigated in ammonia solution of different concentrations indicated that the ammonia concentration helps to improve the effect of ammonia fumigation. When the ammonia concentration was 28%, the ΔE increased with increasing temperature. However, the ΔE at different temperatures indicated that the temperature has a low effect on the color of the ammonia-fumigated wood. The color of wood is mainly derived from the chromophore groups in lignin; in addition, the pigment, tannin, resin, and other substances in the extract also have a significant effect on the color of the wood. According to existing research, the main chemical cause of wood discoloration is the oxidative condensation reaction of tannins, pigments, alkaloids, sugars, phenols, and other organic substances in wood [9]. Under the action of ammonia, the resins, tannins, polyphenols, and anthocyanins in the wood undergo chemical reactions to deepen the color of the wood.Figure 3
Total color change (ΔE) of wood samples. (a) ΔE of wood samples fumigated at different ammonia concentrations (16–28%) for different durations (1–5 days); (b) ΔE of wood samples fumigated at different temperatures (25–35°C) for different durations (1–5 days).
(a)(b)


## 3.2. Surface Wettability

Figure4 shows the variation in water contact angle of the samples treated at 30°C with different ammonia concentrations and treatment durations. Compared with that of the control wood, the contact angle of the ammonia-fumigated samples increased with increasing ammonia concentration and treatment duration. The difference in the contact angle of wood treated with different ammonia concentrations decreased with increasing treatment duration, with a contact angle of approximately 77° after 5 days of treatment. An increase in contact angle corresponds to a decrease in wettability. The change in contact angle is mainly related to the change of chemical components of the wood after ammonia fumigation. Free radicals on the wood surface react during the ammonia fumigation process. The crystallinity of the ammonia-fumigated wood increases, and the amount of amorphous cellulose and free hydroxyl groups decreases accordingly [10]. Therefore, its surface wettability decreases, resulting in the measured increase in contact angle.Figure 4
Contact angle of ammonia-fumigated wood samples.


## 3.3. XRD Analysis

As shown in Figure5, the positions of the XRD peaks of the wood crystal planes were not significantly different after the ammonia fumigation process. In addition, the width of the crystalline zone did not change significantly; that is, the ammonia fumigation treatment did not change the wood cellulose crystal structure. Ammonia can enter the amorphous regions of cellulose to cause swelling by increasing the distance between the molecular chains, which increases the crystallinity of the wood [11]. Table 1 demonstrates that treatment duration had an obvious effect on the crystallinity. When the other treatment conditions were constant, the crystallinity increased with extension in treatment duration. When treated at the same temperature for the same duration, the crystallinity of the wood samples increased slightly with an increase in ammonia concentration. Finally, under treatment with the same ammonia concentration for the same duration, the crystallinity of the ammonia-fumigated samples increased with increasing temperature. Overall, ammonia fumigation treatment increased the crystallinity of the treated wood, indicating that ammonia causes a positive degree of crystallinity.Figure 5
XRD curves of treated wood samples. (a) Durations (1–5 days); (b) ammonia concentrations (16–28%); (c) temperatures (25–35°C).
(a)(b)(c)Table 1
Crystallinity of treated wood samples.
SamplesConcentration/%Temperature/°CDuration/dayCrystallinity/%Ammonia-fumigated samples2230154.981630346.63223055.49283055.60282554.38283556.582230556.21Control samples———46.30


## 3.4. DMA Analysis

Figure6 shows the measured storage modulus and loss modulus of the wood samples treated with different temperatures and ammonia concentrations for different durations. Figure 6(a) shows that the storage modulus of the samples treated at different temperatures in 28% ammonia solution decreased with increasing treatment temperature. This is because the kinetic energy of the wood molecules is low under low-temperature conditions. When external force is applied, various functional groups such as side groups, branching chains, and main chains can move. Therefore, the storage modulus is large [12]. When the temperature rises, the molecular motion gradually increases, and the storage modulus gradually decreases. The storage modulus of the ammonia-fumigated wood was lower than that of the control wood. The main reason for this is that polar ammonia molecules swell the noncrystalline areas of the wood cellulose, hemicellulose, and lignin during ammonia fumigation treatment. This increases the free movement space of the molecules. At the same time, the increase in temperature provides the molecules with enough energy to promote the glass transition of hemicellulose and lignin, thereby enhancing the movement of wood molecules.Figure 6
DMA curves of treated samples. (a) Storage modulus and (b) loss modulus of samples fumigated at different temperatures (25–35°C); (c) storage modulus and (d) loss modulus of samples fumigated with different ammonia concentrations (16–28%); (e) storage modulus and (f) loss modulus of samples fumigated for different durations (1–5 days).
(a)(b)(c)(d)(e)(f)The loss modulus of the wood samples decreased with increasing treatment temperature. Compared with that of the control samples, the loss modulus of the ammonia-fumigated samples was reduced. The plasticity of the wood decreased upon ammonia fumigation treatment, while thermal softening of the lignin and hemicellulose molecules occurred, causing viscoelastic changes to the wood. This demonstrates that ammonia fumigation has an effect on the chemical composition of wood. Anα relaxation peak appears in the loss modulus at a temperature of 30–60°C. After ammonia fumigation treatment, the relaxation peak of the material gradually occurs at a lower temperature (from 73 to 32.5–55.6°C), while the intensity of the relaxation peak increases. This indicates that the internal binding force in the amorphous region of the material decreases, and the reduction of the intermolecular force is prone to relaxation [13]. Figures 6(c)–6(f) show that as the ammonia concentration and fumigation duration increased, the storage modulus reduced, the loss modulus increased, the plasticity increased, and the elasticity decreased. These changes are beneficial for improving the dimensional stability of the wood.


## 3.5. FTIR Spectroscopy

Figure7 shows the FTIR spectra of the ammonia-fumigated wood samples treated at 25, 30, or 35°C with an ammonia concentration of 28% and treatment duration of 3 days, whereas Figure 8 shows the FTIR spectra of samples treated at 30°C with an ammonia concentration of 22% and treatment duration of 1, 3, or 5 days.Figure 7
FTIR spectra of ammonia-fumigated samples treated at different temperatures.Figure 8
FTIR spectra of ammonia-fumigated samples treated for different durations.As shown in Figure7, the absorption peak at 3,443 cm−1 of the ammonia-fumigated wood treated at different temperatures was reduced compared with that of the control wood. This indicates that the ammonia fumigation treatment reduces the hydroxyl content of the wood. The number of free hydroxyl groups in the amorphous cellulose region decreases and the crystallinity of the wood increases [5]. The 2,250–2,340 cm−1 band of the ammonia-fumigated material indicated that it might be a compound containing triple bonds or cumulative double bonds. The absorption peak at 2,120 cm−1 corresponds to the external standard, potassium bromide [14]. The intensity of the absorption peak of the nonconjugated carbonyl group at 1,500–1,735 cm−1 decreased, characterizing the relative decrease in hemicellulose content, and the absorption peak of the alcoholic hydroxyl group at 1,271 cm−1 reduced. Thus, the numbers of hydroxyl and carboxyl groups on the main chain and side chain of hemicellulose were reduced. Therefore, there was a reaction between ammonia and hemicellulose that reduced the hemicellulose content. The lignin benzene ring structure vibration at 1,602 cm−1 was significantly reduced, indicating that the lignin content decreased. The peak at 1,086 cm−1 corresponded to the C − O stretching vibration of secondary lignin alcohols and aliphatic ethers. Carbonyl, carboxyl, and hydroxyl groups, as well as carbon–carbon double bonds, are the main chromophoric groups and auxochromic groups in wood, which are present in lignin and extracts. Therefore, ammonia gas may react with wood extracts [15]. From the analysis of the absorption peak absorbance, it was clear that the intensity of the absorption peaks decreased as the temperature of the ammonia fumigation treatment increased. This might be due to the increase in moisture in the air due to the increase in temperature, which reduced the density of ammonia molecules and the wood ammonia fumigation effect.Figure8 shows that the intensity of the characteristic peak at 3,000–3,750 cm−1 decreased slightly with the ammonia fumigation duration. This is due to multiple factors, including the low concentration of ammonia fumigation and ammonia fumigation water molecules. The reduction in hydroxyl groups was reduced, indicating that treatment duration had little effect on the performance of the ammonia fumigation. Nevertheless, the ammonia fumigation treatment duration had a significant effect on the 2,250–2,340 cm−1 region band.In summary, after ammonia fumigation treatment, the content of carbonyl and hydroxyl groups in the wood decreased, and the number of hydrophilic hydroxyl and carbonyl groups decreased. This reduced the surface wettability and increased the contact angle. As the ammonia fumigation temperature increased, the reaction between the ammonia gas and hemicellulose or lignin increased.


## 4. Conclusions

In this study, a single factor experiment was used to determine the effect of the ammonia concentration, fumigation temperature, and fumigation duration on the color, surface wettability, dynamic viscoelasticity, and chemical composition ofB. alnoides wood samples. The main conclusions are as follows:
(1)
Compared with control wood, the color of the ammonia-fumigated wood changed significantly. The color difference increased with the treatment duration, ammonia concentration, and treatment temperature. Among them, the influence of ammonia concentration on color difference is more significant than that of treatment temperature(2)
With an increase in the ammonia concentration and treatment duration, the surface contact angle of the ammonia-fumigated samples increased. The longer the treatment, the smaller the difference in contact angle. After 5 days of ammonia fumigation, the contact angle was approximately 77°(3)
Compared with control wood, the crystallinity of wood increased after ammonia fumigation treatment. The crystallinity of wood increased with the treatment duration, while the ammonia concentration and treatment temperature had a negligible influence on crystallinity(4)
The storage modulus and loss modulus of ammonia-fumigated samples decreased with increasing measurement temperature. The storage modulus and loss modulus were both lower than those of the control sample, indicating that the ammonia fumigation treatment has an impact on the chemical composition of the wood. The greater the ammonia concentration during fumigation and the longer the treatment duration, the smaller the storage modulus of the ammonia-fumigated material, and the greater the loss modulus(5)
FTIR spectroscopy demonstrated that there was a reduction in hydrophilic groups such as hydroxyl and carboxyl groups in the ammonia-fumigated samples compared with the control sample. Chemical reactions occur between the ammonia and lignin and extracts in the wood during the ammonia fumigation process. The chromophoric and auxochromic groups, such as carbonyl, carboxyl, and hydroxyl groups, are also affected by the fumigation process



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