Introduction

With the decreasing supply of precious wood over the past few decades, fast-growing plantation wood has been widely regarded as an alternative due to its short growth cycle, good permeability, and moderate prices [1,

Materials and methods

Materials

Defect-free fast-growing poplar boards of P. tomentosa Carr. (sapwood) were chosen and conditioned to 10% equilibrium moisture content. The veneer sample dimensions were 100 mm × 100 mm × 1.0 mm. Reactive Brilliant Blue KN-R (C.I. Reactive Blue 19), which belongs to beta sulphuric acid esters of hydroxyethyl sulfone reactive dye commonly used in textile dyeing, was provided by Taopu Dye Plant in Shanghai, China. Sodium chloride, sodium carbonate, sodium silicate and hydrogen peroxide (H2O2) were of analytical grade and provided by Yi **u Bo Gu Company (China). The molecular structure of Reactive Brilliant Blue KN-R is shown in Fig. 1.

Fig. 1
figure 1

Chemical structure of Reactive Brilliant Blue KN-R

Bleaching treatment

The wood samples were bleached to even in tone. The bleached wood samples were prepared at a water bath temperature of 60 °C, a 30% (v/v) H2O2 concentration of 3.0%, with sodium silicate of 5.0 g/L, a treating time of 75 min and a volume ratio of 1:20.

Dyeing method

A ultrasonic-assisted dip-dye method at atmospheric pressure was used for veneer dyeing. Wood veneers were vertically immersed in the dye solution, leaving sufficient space between each veneer so as to ensure the maximization of ultrasonic wave obtained per unit area of the dyeing veneers. A volume ratio of 1:20 (Vveneer:Vsolution) was maintained throughout the experiment. The solution was stirred every 15 min for even penetration. After dyeing, the treated wood samples were rinsed thoroughly with distilled water to wash away the residual dye, and then air-dried to 8% moisture content without light. The reaction mechanism of dye and wood is shown in Fig. 2.

Fig. 2
figure 2

The reaction mechanism of Reactive Brilliant Blue KN-R dye and wood

Associated single experimental factors are shown in Table 1.

Table 1 Single-factor experimental conditions for dyeing poplar wood

Characterization

Measurement of dye uptake

Dye uptake was characterized by absorption of dye from dye bath to wood samples. A UV–visible spectroscopy (721 ApL, China), which found a maximum absorption wavelength (λmax) for Reactive Brilliant Blue KN-R dye at 598 nm, was used to determine the absorption. Dye uptake was calculated based on the following equation [25]:

$${C_{\text{t}}} \ (\% )=\frac{{{A_0} - {A_{\text{t}}}}}{{{A_0}}} \times 100,$$
(1)

where \({A_0}\) and \({A_{\text{t}}}\) are the absorption of the dye solution at λmax before and after wood dyeing, respectively.

Measurement of color

The K/S values were assessed for the dyed wood veneer samples, which determines the color strength of dyed wood by using a color measuring instrument (Dataflash 110 Datacolor, USA) with illumination/observer conditions set at D65/10°. K/S values were calculated from reflectance values using the Kubelka–Munk equation [26],

$$K/S=\frac{{{{(1 - R)}^2}}}{{2R}},$$
(2)

where K is the absorption coefficient, S is the scattering coefficient, and R is the decimal fraction of the reflectance of the dyed wood.

Fourier transform infrared spectroscopy (FTIR) analysis

Fourier transform infrared spectroscopy (Nicolet 6700, Thermo Scientific, USA) was used to analyze the surface chemical structure of the dyed and undyed wood samples. The samples were ground to 200-mesh size and embedded into potassium bromide (KBr) pellets. The pellets were subjected to FTIR spectrophotometry in the range of 4000–400 cm−1 and at a resolution of 4 cm−1 for 32 scans.

Thermogravimetric (TG) analysis

The thermal decomposition studies of the samples were carried out using a Q5000 TGA analyzer (TA Instruments, USA). Approximately 4–6 mg of sample was heated from room temperature to 600 °C at a heating rate of 10°/min under nitrogen atmosphere (100 mL/min).

X-ray diffraction (XRD) analysis

The crystallinity of the dyed and undyed wood samples was evaluated using an XRD instrument: D8 advance diffractometer (Brüker, USA) equipped with a Cu Kα radiation source (λ = 0.154 nm). A 2θ range between 5° and 50° was scanned with a 0.02° step and a scan speed of 2°/min. The crystallinity was measured as the ratio of the intensity difference in the selected peak positions.

The crystallinity index (CI) for wood samples was determined by the following equation:

$$CI\;(\% )=({I_{{\text{Max}}}} - {I_{{\text{Am}}}})/{I_{{\text{Max}}}} \times {\text{1}}00,$$
(3)

where IMax is the maximum intensity of the lattice diffraction peak, and IAm is the intensity scattered by the amorphous fraction of the sample.

Scanning electron microscopy (SEM) analysis

The distribution of reactive dye molecules in wood cells were detected with SEM (Hitachi S-3400N, Japan) at an accelerating voltage of 15 kV. The tangential sections of the samples were fixed on conductive adhesives and then coated with gold.

Grey system theory analysis

Grey system theory analysis is a system engineering discipline based on the mathematical theory. It can be widely applied to various fields, such as agriculture, geology and weather. According to the grey system theory analysis, the results of qualitative analysis and quantitative analysis are always consistent. In this study, we can determine which factors influence the dye uptake and K/S the most by using grey system theory analysis.

It is assumed that,

Y 1, Y2, …, Ys are the systematic characteristics behavior sequences, and X1, X2, …, Xm are the correlation factor behavior sequences. Moreover, Yi = (yi(1), yi(2), yi(3), …, yi(n)), Xj = (xj(1), xj(2), xj(3), …, xj(n)), and the length of Yi (i = 1, 2, …, s) and Xj (j = 1, 2, …, m) is equal. εij is the gray absolute correlation degree of Yi and Xj. Then, the gray absolute correlation matrix can be defined as follows:

$$A=({\varepsilon _{ij}})=\left[ {\begin{array}{*{20}{c}} {{\varepsilon _{11}}}&{{\varepsilon _{12}}}&{\cdot\cdot\cdot}&{{\varepsilon _{1{\text{m}}}}} \\ {{\varepsilon _{21}}}&{{\varepsilon _{22}}}&{\cdot\cdot\cdot}&{{\varepsilon _{2{\text{m}}}}} \\ \vdots & \vdots & \ddots & \vdots \\ {{\varepsilon _{{\text{s}}1}}}&{{\varepsilon _{{\text{s}}2}}}&{\cdot\cdot\cdot}&{{\varepsilon _{{\text{sm}}}}} \end{array}} \right],$$
(4)

where the element in the row i is the gray absolute correlation degree between Yi (i = 1, 2, …, s) and X1, X2, …, Xm; the element in the column j is the gray absolute correlation degree between Y1, Y2, …, Ys and Xj (j = 1, 2, …, m).

Based on the grey correlation theorem, εij can be calculated as following:

  • Step 1: \(Y_{i}^{0}\) = (0, yi(2) − yi(1), yi(3) − yi(1), …, yi(n) − yi(1)),

    \(X_{j}^{0}\) = (0, xj(2) − xj(1), xj(3) − xj(1), …, xj(n) − xj(1)).

  • Step 2: |Yi| = \(\left| {\sum\nolimits_{{k=2}}^{{n - 1}} {y_{i}^{0}} (k)+\frac{1}{2}y_{i}^{0}(n)} \right|\), |Xj| = \(\left| {\mathop \sum \limits_{{k=2}}^{{n - 1}} x_{j}^{0}(k)+\frac{1}{2}x_{j}^{0}(n)} \right|\).

  • Step 3: εij = \(\frac{{1+\left| {{Y_{si}}} \right|+\left| {{X_{sj}}} \right|}}{{1+\left| {{Y_{si}}} \right|+\left| {{X_{sj}}} \right|+\left| {{X_{sj - }}{Y_{si}}} \right|}}\).

Definition 1

If ∃l, j ∈ {1, 2, …, m}, and εil ≥ εij, i = 1, 2, …, s, then, Xl > Xj (the systemic factors Xl is superior to Xj). Further, if ∀j = 1, 2, …, m, j ≠ l, and Xl > Xj, then the systemic factors Xl can be regarded as the optimal factor.

Definition 2

If ∃l, j ∈ {1, 2, …, m}, and \(\sum\nolimits_{{i=1}}^{m} {{\varepsilon _{il}}}\) ≥ \(\sum\nolimits_{{i=1}}^{m} {{\varepsilon _{ij}}}\), then, Xl ≥ Xj (the systemic factors Xl is better or as good as Xj).

Definition 3

If ∃l ∈ {1, 2, …, m}, ∀j = 1, 2, …, m, j ≠ l, and Xl ≥ Xj, then, Xl is the quasi-optimal factor.

Results and discussion

Effect of ultrasonic-assisted temperature on dye uptake and K/S

Figure 3 shows the dye uptake and K/S of the treated wood specimens against ultrasonic-assisted temperature. With increasing temperature, dye uptake initially increased, and then decreased. As the temperature was raised from 20 to 40 °C, the dye uptake increased by 10.8%. When the temperature got to 40 °C, the dye uptake reached maximum value at 25.5%. This result could be attributed to the high-temperature accelerating molecular thermal motion. Moreover, the number of cavitation bubbles formed by ultrasonic vibration reduced due to the irregular movement, resulting in a more homogenous solution [3].

Fig. 3
figure 3

Effect of ultrasonic-assisted temperature on dye uptake and K/S

However, when the temperature exceeded 40 °C, dye uptake decreased and then leveled off. The dye used in this study belongs to a low temperature dye; therefore, the molecule activity of dye was reduced by the relatively high temperature of the solution. In addition, the hydrolysis rate of the dye was higher than the rate of its reaction with wood fiber [4]. K/S demonstrates a similar tend between 20 and 70 °C. The maximum K/S value of 12.28 reached at 60 °C, which was slightly higher than the value (11.30) at 50 °C. Obviously, evaluated temperature promoted adsorption and combination between the dye molecules and the surface wood fiber. However, when the temperature was higher than 60 °C, the dye molecules, which reacted with wood fiber, were hydrolyzed.

Higher dye uptake leads to higher utilization rate of dye. Also, higher K/S value results in better dyeing effect. According to the comprehensive analysis, the optimal temperature is 50 °C.

Effect of ultrasonic-assisted dye concentration on dye uptake and K/S

As shown in Fig. 4, when the dye concentration increased from 0.1 to 2.0%, the dye uptake first increased, and then declined. The dye uptake reached its maximum (29.4%) at 0.5% dye concentration. Under the same ultrasonic power, the higher the dye concentration, the greater the dye uptake, which is because the growing number of dye molecules increases the probability of dye penetrating, diffusing, and adsorbing onto the wood. However, further increasing dye concentration, will cause aggregation of the dye molecules and therefore decrease dye uptake.

Fig. 4
figure 4

Effect of ultrasonic-assisted dye concentration on dye uptake and K/S

K/S value has a tendency to increase with increasing dye concentrations. The K/S increased greatly from 10.94 at dye concentration of 0.1% to 17.45 at 1.0%. With increasing dye concentration, the number of dye molecules increased per unit volume [27]. Thus, the number of dye molecules absorbed on per unit area of the wood surface increased and the K/S value improved.

Considering both factors of dye uptake and K/S, the ideal dye concentration is 0.5%. At that dye concentration, the dye uptake was 29.4% and K/S value was 16.74.

Effect of ultrasonic-assisted power on dye uptake and K/S

Figure 5 shows that dye uptake increased with increased ultrasonic power. Compared to wood samples without application of ultrasonic power, dye uptake significantly increased with sonication. A higher ultrasonic power resulted in a higher dye uptake. When 200 W of ultrasonic power was applied, the dye uptake was maximized to 25.5%. Higher ultrasonic power could improve the permeability of the wood, allowing more dye molecules to penetrate wood and enhancing dye uptake. Moreover, an improvement in the ultrasonic power could contribute to promoting the activation of the dye molecules, which gave rise to a higher proliferation potential.

Fig. 5
figure 5

Effect of ultrasonic-assisted power on dye uptake and K/S

K/S value increased at first and then decreased slightly as ultrasonic power increased. The K/S peaked at 11.02 with an ultrasonic power of 160 W. This behavior could be attributed to the assisting effect of ultrasonic power on the dyeability of wood fiber with Reactive Brilliant Blue KN-R dye. The ultrasound has threefold effects (dispersion, degassing and diffusion) on the dyeing system. First, ultrasonic vibration cavitation produces uniform dispersions in the dye bath. Second, dissolved or entrapped air molecules are expelled from fiber capillaries and interstices at the crossover of fabric into liquid by cavitation, thus facilitating dye-fiber contact. Third, the rate of diffusion of the dye inside the fiber and the chemical reaction between dye and fiber are also accelerated by piercing the insulating layer covering the fiber [28,29,30,31]. From the viewpoint of efficiency and cost, the optimal power for dye uptake and K/S is 160 W.

Effect of ultrasonic-assisted dip** time on dye uptake and K/S

The effects of dyeing time on dye uptake and K/S are illustrated in Fig. 6. Dye uptake rapidly increased from 11.5 to 25.5% with prolonged dip** time, and then decreased slightly after 120 min. This phenomenon may be due to the fact that wood dyeing process is a dynamic sorption and desorption equilibrium process for dye molecules to diffuse and infiltrate the internal structure of wood [32]. In addition, the cavitation and thermal effect generated by ultrasonic waves are also beneficial to the sorption process of dye molecules into the wood. However, the ultrasonic treatment could accelerate the dissolution of extractives within wood. Moreover, with extended time, more dye molecules permeating wood, thus reducing the concentration difference of dye liquid inside wood tissues. Also, the dye molecules had the traces of hydrolysis. All the three factors mentioned above led to the slightly decrease of dye uptake.

Fig. 6
figure 6

Effect of ultrasonic-assisted dyeing time on dye uptake and K/S

K/S value obtained increased as time increased. The peak (11.02) was attained after 180 min of dip** time. With prolongation of dyeing time, the wood fibers had enough time to take up dye molecules and further reacted with them. As the time further increased, the effective flow area of dye solution is smaller due to the triangle adsorption principle of the dye molecules [33]. After 120 min of dyeing, the reaction between wood fibers and dye molecules was almost completed, so the K/S changed a little. Therefore, based on comprehensive consideration, the optimal dyeing time is 120 min.

Effect of ultrasonic-assisted dyeing assistant on dye uptake and K/S

Figure 7 shows the effect of dyeing assistant on the dye uptake and K/S. The dye uptake firstly increased rapidly from 16.7 to 25.5%, and then gradually increased to 28.9%. When the dyeing assistant was up to 50 g/L, the dye uptake decreased to 22.4%. During the dyeing process, the sodium chloride electrolyte could reduce the repulsive force between chromophores of dye and fiber surfaces, and promote the combination of dye molecules and wood fiber. Moreover, with elevated addition of dyeing assistant, the sodium ion concentration increased, and thus improved the activity of reactive dyes. However, the excessive sodium ion might have led to the aggregation and even desorption of the dye molecules, so the dye uptake decreased.

Fig. 7
figure 7

Effect of ultrasonic-assisted dyeing assistant on dye uptake and K/S

K/S value always increased with increased dyeing assistant. The K/S value reached a maximum (13.90) when the dyeing assistant was 50 g/L. Sodium chloride, which belongs to neutral electrolyte, plays an important role in the dyeing process as the leveling agent and dyeing assistant. Therefore, the dye molecules could better adsorb and combine with the wood surface. Besides, the ultrasonic power helps better dyeing in the presence of salt [34]. According to Fig. 7, the optimal dyeing assistant was determined to be 40 g/L.

Effect of ultrasonic-assisted dye-fixing agent on dye uptake and K/S

The alkaline agent selected as fixing agent could enhance dye uptake [35]. Different amount of fixing agent was added, and the results of its effects are presented in Fig. 8. Clearly, dye uptake and K/S value initially increased, and then decreased with increased fixing agent. Dye uptake reached the maximum value at 31.2%, when the fixing agent was increased to 25 g/L. However, the K/S was maximized to 13.00 at 30 g/L. Addition of fixing agent could increase the pH value of dye solution and form more cellulose hydroxy anions, and thus the rate of dye-fixing reaction was accelerated. Moreover, the amount of dye fixed on the wood fiber rapidly increased, so the K/S value increased. However, when addition of fixing agent was further increased, the hydrolysis rate was higher than the reaction rate, so the dye uptake and K/S decreased. Therefore, according to the comprehensive consideration, the better fixing agent was 25 g/L.

Fig. 8
figure 8

Effect of ultrasonic-assisted fixing agent on dye uptake and K/S

Through the above analyses, the idealized process by single-factor experiment uses a temperature of 50 °C, a dye concentration of 0.5%, a ultrasonic power of 160 W, a dyeing time of 120 min, a dyeing assistant of 40 g/L, and a fixing agent of 25 g/L.

Grey system theory analysis

We assume dye uptake (Y1) and K/S (Y2) as the evaluation sequence, and temperature (X1), dye concentration (X2), ultrasonic power (X3), dip** time (X4), dyeing assistant (X5), and dye-fixing agent (X6) as related sequence factors. Table 2 shows the detailed numerical value of systematic characteristics behavior sequences (Y) and correlation factor behavior sequences (X).

Table 2 The values of systematic characteristics behavior sequences (Y) and correlation factor behavior sequences (X)

We calculated the grey absolute correlation degree of Y1 and Y2 with X1, X2, X3, X4, X5 and X6 by the three steps, respectively, and then obtained the gray absolute correlation matrix as follows:

$$~A=\left[ {\begin{array}{*{20}{c}} {{\varepsilon _{11}}}&{{\varepsilon _{12}}}&{{\varepsilon _{13}}}&{{\varepsilon _{14}}}&{{\varepsilon _{15}}}&{{\varepsilon _{16}}} \\ {{\varepsilon _{21}}}&{{\varepsilon _{22}}}&{{\varepsilon _{23}}}&{{\varepsilon _{24}}}&{{\varepsilon _{25}}}&{{\varepsilon _{26}}} \end{array}} \right]=\left[ {\begin{array}{*{20}{c}} {0.5020}&{0.5995}&{0.5030}&{0.5111}&{0.5266}&{0.5353} \\ {0.5007}&{0.7920}&{0.5010}&{0.5038}&{0.5091}&{0.5120} \end{array}} \right].$$

Obviously, εi2 > εi6 > εi5 > εi4 > εi3 > εi1 (i = 1, 2), namely, X2 > X6 > X5 > X4 > X3>X1, meets the Definition 1. It means that dye concentration (X2) had the strongest effect on dye uptake (Y1) and K/S (Y2), and temperature (X1) had the weakest effect on dye uptake (Y1) and K/S (Y2) among these factors. Therefore, this assessment method helps to provide a theoretical reference for ultrasonic-assisted wood dyeing techniques, and the producer could better control the dyeing technology in the actual production.

FTIR analysis

The FTIR spectra of wood samples in the 4000–400 cm−1 region are shown in Fig. 9. The broad peak that occurs at 3400–3200 cm−1 was associated with –OH stretching in hydroxyl groups originating mainly from cellulose [36]. The absorption at 1740 cm−1 was due to C=O stretching of xylan [37]. The peak at 1034 cm−1 was attributed to C–O–C stretching of aliphatic ether bond [4]. In comparison with the undyed wood, the –OH band was broader in the case of dyed wood, which could be caused by different types of inter- and intramolecular hydrogen bonds [38, 39]. Besides, the 1740 cm−1 band declined clearly after the conventional dyeing treatment, suggesting the degradation of hemicellulose [40]. However, the C=O stretching vibration of ultrasonic-assisted dyeing treatment declined more than that of the conventional dyeing treatment, which may be attributed to the cavitation and thermal effects of the ultrasonic waves. The absorbance ratio of 1034 cm−1 was increased after dyeing treatment, indicating the formation of ether bond, which may result from the reaction between wood component and the dye.

Fig. 9
figure 9

FTIR spectra of A undyed, B dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and C dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and 160 W ultrasonic power

TG analysis

Thermal stability of the undyed and dyed wood samples was studied using TG. Figure 10 shows the mass loss and differential TG (DTG) curves of the samples ranging from room temperature to 600 °C. For the undyed wood, the first degradation region from 50 to 120 °C relates to the release of moisture and adsorbed water from the wood [41].The dyed wood had a similar tendency to undyed wood at this stage. The thermal degradation patterns reveal that most of the degradation events occur between 200 and 400 °C, which is consistent with a previous study [42]. At this stage, the residue of undyed wood was 6.52%, while the residues of the conventional dyed wood and ultrasonic-assisted dyed wood were 11.27% and 13.23%, respectively (Table 3). This result can be attributed the dye used in this study reacting with wood component and generating strong ester bond. In addition, due to the assisting effect of ultrasonic power on the dyeability of wood fiber, more ester bonds could be formed and thus increased the thermal stability. Additionally, as can be seen from Fig. 10 and Table 3, the temperature at maximum degradation rate changed obviously. The temperature at the maximum degradation rate of undyed wood was 350 °C, while the temperature at the maximum degradation rate of dyed wood were 297 °C and 287 °C, separately, indicating the dye had a chemical reaction with the wood component.

Fig. 10
figure 10

TG and DTG patterns of A undyed, B dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and C dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and 160 W ultrasonic power

Table 3 Thermogravimetric parameters for thermal degradation of undyed and dyed wood veneer

XRD analysis

Appearing in Fig. 11 are XRD spectra of undyed and dyed wood. The characteristic peaks of poplar wood are at 2θ = 16.0°, 22.0°, and 34.6°, corresponding to the crystal plane diffraction peaks of (101), (002), and (040) in cellulose, respectively. The position of the peaks did not change, indicating that the main crystalline structure of wood was not distinctly influenced by dyeing. The crystallinity of undyed wood was 41.05%, while the conventional dyed wood and ultrasonic-assisted dyed wood were 47.36% and 50.52%, respectively. The increased crystallinity of conventional dyed wood is attributed to the hydrothermal dying process. Compared with the conventional dyed wood, the crystallinity of the ultrasonic-assisted dyed wood increased. The increased crystallinity may be ascribed to the degradation caused by acoustic cavitation, which reduces the amorphous fractions of wood, and enriches the relative crystalline content [43].

Fig. 11
figure 11

XRD curves and relative crystallinity of A undyed, B dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and C dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and 160 W ultrasonic power

SEM analysis

The SEM results are shown in Fig. 12. Empty cell walls and pits were obviously observed in the undyed wood (Fig. 12A), while these empty places were filled with a certain amount of dye molecules (Fig. 12B, C). Compared with the undyed and conventional dyed wood, apparently, the wood vessel walls of ultrasonic-assisted dyed wood appear rough (Fig. 12C). The ultrasonic cavitation and heat effects resulted in sharp moisture vaporization in the wood cell cavity, which caused an outward diffusion of vapor pressure to act on the wood vessel cell wall. This led to some pit membranes to rupture, forming new channels for dye liquor, which increased the dyeability of wood.

Fig. 12
figure 12

Scanning electron micrographs: A undyed, B dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and C dyed at 50 °C, 0.5% dye concentration, 120 min dyeing time, 40 g/L dyeing assistant, 25 g/L fixing agent, and 160 W ultrasonic power

Conclusions

Ultrasonic-assisted dyeing as an environment-friendly and energy-efficient wood dyeing method improved the decorative property of fast-growing poplar wood.

Different ultrasonic-assisted factors affected dye uptake and K/S in different ways. The idealized process by a single-factor experiment in this study used a temperature of 50 °C, a dye concentration of 0.5%, a ultrasonic power of 160 W, a dyeing time of 120 min, a dyeing assistant of 40 g/L, and a fixing agent of 25 g/L.

Through the grey system theory analysis, dye concentration had the strongest effect on dye uptake and K/S, while temperature had the weakest effect on dye uptake and K/S among these factors.

The reactive dye used in the study had chemical reaction with wood component, and formed ester groups. After the ultrasonic-assisted dyeing, the thermal stability and crystallinity of fast-growing poplar wood samples were both increased. Moreover, the dye molecules diffused into the cell cavity, wood vessel, aperture, and part of the wood microstructure such as pit membrane was mechanically damaged, creating new fluid channels for the dye and increasing the dyeability of wood.