Next Article in Journal
Plasticizers Derived from Biomass Resources: A Short Review
Previous Article in Journal
Block Copolymer of Flexible and Semi-Flexible Block Confined in Nanopost Array
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Comparison and Optimization of Reactive Dyes and Coating Performance on Fraxinus mandshurica Veneer

1
Co-Innovation Center of Efficient Processing and Utilization of Forest Resources, Nanjing Forestry University, Nanjing 210037, China
2
College of Furnishings and Industrial Design, Nanjing Forestry University, Nanjing 210037, China
3
Department of Industrial Chemistry, School of Science and Technology, Meiji University, 1-1-1 Higashi-Mita, Tama-ku, Kawasaki-shi 214-8571, Japan
*
Author to whom correspondence should be addressed.
Polymers 2018, 10(12), 1302; https://doi.org/10.3390/polym10121302
Submission received: 20 September 2018 / Revised: 20 November 2018 / Accepted: 21 November 2018 / Published: 24 November 2018

Abstract

:
In this study, Fraxinus mandshurica veneer was dyed with reactive brilliant red X-3B, black KN-B and blue K-3R dyes. The dye concentration, bath ratio and dyeing time were selected for an orthogonal experiment. Analysis of variance showed that the dye concentration had the greatest effect on the dye uptake of F. mandshurica veneer. In the independent experiments, dye uptake increased at first and then decreased with increasing dye concentration; the chromatic aberration increased with the dye concentration and then remained steady. The infrared spectra were used to examine the dyeing behaviors before and after dyeing and the binding form between reactive dyes and F. mandshurica veneer was analyzed. Based on the optimization of process parameters, the optimal dyeing condition was considered to be 75 °C, the dye concentration to be 0.5–1.0%, the dyeing time to be 60 min and the bath ratio to be 20:1. The dye uptakes of reactive brilliant red X-3B, black KN-B and blue K-3R dyes were 75.0–75.4%, 50.0–64.6% and 32.0–66.0%, respectively. The chromatic aberration of F. mandshurica veneer dyed with reactive brilliant red X-3B, black KN-B and blue K-3R dyes was 53.0–59.0, which was a significant increase. After dyeing, the hardness and impact strength of the waterborne coating on the dyed F. mandshurica increased but adhesion was reduced. The coating films produced a matte glossiness.

Graphical Abstract

1. Introduction

There are various kinds of dyes for wood, acid, alkaline, reactive, direct, natural biological, etc. [1]. Among them, acid dyes, which mainly color wood lignin, are most widely used [2]. However, they have defects such as easy fading and poor water resistance. The related research showed that the adsorption of dye molecules to wood was a physical adsorption when acid dyes were used [3]. When reactive dyes were used, they penetrated the interior of the wood and reacted with the wood components to form a covalent bond [4]. Therefore, compared with acid dyes, the stability of wood dyed with reactive dyes was higher [5]. In the dyeing process, changes in different factors such as dyeing time, bath ratio and dye concentration usually produced different effects [6]. High concentrations of dye molecules in liquid increased the viscosity, thus affecting the adsorption and permeability.
Waterborne coatings are widely used in many industries because of their green, non-polluting characteristics [7]. Due to the advantages of containing few volatiles, no pollution and high safety, waterborne coatings for wood are the main research object. High gloss can have a negative effect on people’s eyesight, making the low gloss of waterborne wood coatings increasingly popular [8]. So far, many researchers have studied the dyeing process of poplar [9] but fewer have studied the effects of dyeing on subsequent finishing processes. Although Fraxinus mandshurica is a material commonly used for the veneer of high-grade furniture [10], there are few studies on reactive dyeing and waterborne finishing of Fraxinus mandshurica. In this paper, the dyeing properties of three kinds of reactive dyes including reactive brilliant red, reactive blue and reactive black dyes on F. mandshurica were examined by an orthogonal test and independent experiments. Based on the results of the dye uptake and chromatic aberration, the effects of different reactive dyes on the properties of waterborne coatings on the F. mandshurica were evaluated and optimized and a preliminary discussion on the chemical and physical properties of dyeing veneers was also carried out.

2. Materials and Methods

2.1. Materials

F. mandshurica veneer (uniform material color, 40 mm × 40 mm × 3 mm) came from Yihua Lifestyle Technology Co. Ltd., Shantou, China. Reactive brilliant red X-3B dye, reactive black KN-B dye, reactive blue K-3R dye, sodium sulfate (Na2SO4) and sodium carbonate (Na2CO3) were supplied by Jiangsu Zhengyang Dyestuff Technology Co. Ltd., Wuxi, China. The structures of the reactive brilliant red X-3B, reactive black KN-B and reactive blue K-3R dyes are shown in Figure 1 where distilled water was used as the solvent for these dyes. Waterborne coatings were supplied by Yihua Lifestyle Technology Co. Ltd., Shantou, China. Waterborne coatings consisted of acrylic copolymers supported by water (the content was 90.0%), dipropylene glycol methyl ether (the content was 2.0%) and dipropylene glycol butyl ether (the content was 8.0%).

2.2. Dyeing and Coating Test

The experimental process was as follows: ash veneer → immersion in dyeing solution → constant temperature heating → dyeing → veneer fixing treatment → repeated distilled water washes until no fading → veneer drying → coating three times.
Because the dye concentration, dyeing time and bath ratio were the main factors effecting dyeing in this study, they were selected as the three parameters. A three-factor, two-level L4 (23) orthogonal test scheme was designed and is summarized in Table 1. The first level of the dye concentration was 1.0% and the second was 5.0%. The first level of the bath ratio was 20:1 and the second was 30:1. The first level of dyeing time was 60 min and the second was 120 min. According to the requirements of the liquor ratio, Na2SO4 and Na2CO3 concentrations were fixed at 2.0% and the temperature of dyeing was controlled at 75 °C. It was reported that high temperatures are usually recommended for best dye penetration and dyeing effect. The controlled temperature, 75 °C, did not lead to hydration of functional groups in reactive dyes [11]. According to the requirements of the dyes, Na2SO4 and distilled water were mixed to the desired concentrations. The bath ratio was the weight ratio of the dye liquor to the dyeing specimen. The weight of the F. mandshurica veneer for each time dyed was about 3.5 g. According to the bath ratio, the quantity of the dye liquor was about 70–105 g. The F. mandshurica veneers were placed in the heated dye liquor and Na2CO3 was added after the stipulated dyeing time to solidify color processing. The dyeing solution was cooled to 60 °C and kept at a constant temperature. The fixing agent Na2CO3 was added, stirred evenly and placed for 30 min before the veneer fixing treatment was finished. After fixing the color, the dyed F. mandshurica veneer was removed from the thermostat water tank and the specimen was cleaned with distilled water until the water had no discoloration. Then, the stained specimens were placed in the oven at 80 °C for 15 min to dry. The wash water solution was added to the dyeing wastewater to the same quantity as before dyeing (70–105 g) for determination of the dye uptake. The results of the orthogonal test were analyzed, calculating for range and variance and independent experiments were carried out with the most important factors.
The waterborne coatings were sprayed onto the dyed veneer of F. mandshurica by an airbrush (Guangzhou Zhongtian Electrical Equipment Co. Ltd., Guangzhou, China). The coating was naturally dried for 3 h and then, using 1000 grit sandpaper, the waterborne coating was sanded and a dry cloth was used to wipe off the dust. The spray process needed to be repeated three times. The thickness of the waterborne coating was about 40 μm.

2.3. Characterization

The dye uptake was determined by the spectrophotometric method [12]. The specific method was as follows: The absorbance of dye liquor before dyeing (A0) and the mixed liquor of waste liquid and cleaning liquid after dyeing (A1) were measured using a 752N type UV-Vis spectrophotometer and calculated according to the following formula:
C (%) = (A0 − A1)/A0 × 100%
In Formula (1), C is dye uptake. The higher the dye uptake, the more dye wood absorbed in the process of dyeing. The HP-2136 chromatic aberration meter was used to directly measure the lab value of the specimen before and after dyeing. The chromatic aberration was measured at three points and the average value was obtained. The differences in color before and after dyeing were represented by ΔL, Δa and Δb, where ΔL is the difference in brightness, Δa is the red and green index difference and Δb is the yellow and blue index difference. Therefore, the chromatic aberration (ΔE) was calculated according to the following formula [13]:
Δ E = ( Δ L ) 2 + ( Δ a ) 2 + ( Δ b ) 2
The greater the chromatic aberration, the better the dyeing effect. The greater the ΔL was, the more the lightness decreased. The greater the Δa was the more red color the dyed material presented. A greater Δb indicates that the dyed material tended to be yellow. The infrared spectrum before and after dyeing was tested using a VERTEX 80V infrared spectrum analyzer (Bruker, Germany). The strength of the waterborne coatings on the dyed veneer of F. mandshurica was measured by a QCJ impactor. A QFZ-II coating adhesion tester was used to test the adhesion of the coating on the dyed veneer. Both the impactor and adhesion tester were produced by Tianjin Jingkelian Material Testing Machine Co. Ltd., Tianjin, China. The 6H–6B pencil test was used to test the hardness of the coating on the dyed veneer of F. mandshurica. For this test, the angle between the pencil and the coating was 45° and the pencil scratched under 1.0 kg load. The hardness of the pencil (6H, 5H, 4H, 3H, 2H, 1H, HB, 1B, 2B, 3B, 4B, 5B and 6B) was used to determine the hardness of the coating when there was initial scaring on the coating. A BGD512-60° gloss meter, produced by Suzhou Essen Instrument Equipment Co. Ltd., Suzhou, China, was used to measure the gloss of the waterborne coatings on the dyed veneer of F. mandshurica. A cone hole with a top angle of 120° was drilled on the coatings. The cone hole was drilled in the field of view of the microscope and the wall of the hole was imaged with the microscope magnified 40 times. The coating part of the bus bar perpendicular to the microscope’s main axis was read out. The length of the coating part of the bus bar was measured. According to the trigonometric function relation, it was evident that the thickness of the coating was half of the length of the coating part of the bus bar. The arithmetic mean of three points was used to evaluate the waterborne coating thickness.

3. Results and Discussion

3.1. Orthogonal Test

The dye uptake and chromatic aberration of the dyeing veneer of F. mandshurica were affected by three factors, dye concentration, dyeing time and bath ratio, and the effects on the dye uptake were obvious according to the comparative analysis of range. The effects of the above three factors on the dye uptake of dyed veneers are summarized in Table 1. The range values and variances corresponding to the same factors are calculated in each column in Table 1, the greater the range value and variance, the more significant the effect of the factor. In comparison with range value and variance, dye concentration had the most significant impact on the dye uptake of the dyeing veneer of F. mandshurica, while the effect of the other two factors was small. After optimization, the dye uptake and chromatic aberration of dyed veneer were optimized. Based on Table 1, it was obvious that the dye uptake of samples 1Red, 1Black and 1Blue were higher than those of other dye samples. Therefore, in the next optimization experiment the dyeing time was fixed at 60 min and the bath ratio was fixed at 20:1.
Based on the results from Table 1, chromatic aberrations of four sample sets were tested in orthogonal experiments. This is summarized in Table 2, Table 3 and Table 4. The parameters L, a and b are the color values of the F. mandshurica veneer before being dyeing. The parameters L’, a’ and b’ are the color value parameters of F. mandshurica veneer after dyeing. The different colors of F. mandshurica veneer before and after dyeing with the reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dyes are represented as ΔL, Δa and Δb. Chromatic aberration of F. mandshurica veneer before and after dyeing is represented as ΔE. Table 2, Table 3 and Table 4 demonstrate that after dyeing with reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye, a great change of chromatic aberration of F. mandshurica was observed. The values of chromatic aberration were large, 54–60, suggesting that the veneers of F. mandshurica after dyeing with the reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye were all obviously stained. The negative ΔL (Table 2, Table 3 and Table 4) indicated that the lightness decreased. Table 2 shows that the Δa was positive, indicating that the color of dyed F. mandshurica veneer was red. Table 3 and Table 4 show the Δa as being negative, indicating that the color of dyed F. mandshurica veneer was green.

3.2. Effects of Dye Concentration

According to the orthogonal test, the bath ratio was 20:1 and the dyeing time was 60 min. Based on the orthogonal experiment design, the dye concentrations were 0%, 0.5%, 1.0%, 1.5%, 2.0%, 2.5% and 3.0%, respectively, in the independent experiments to evaluate the dye uptake and chromatic aberration. Figure 2 shows the concentration of reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye on the dye uptake of dyed F. mandshurica veneers. It can be seen in the dyeing experiments of the above three kinds of dyes that dye uptake of the dyed veneer first increased and then decreased with the increase in dye concentration. When the concentration of reactive red dye increased from 0 to 1.0%, the dye uptake increased from 0 to about 75.0%. This is because when the dye concentration increased, the number of dye molecules in the liquid increased, thus increasing the contact force of veneer of F. mandshurica fiber surface adsorption [14]. However, when the reactive brilliant red X-3B dye concentration increased from 1.0% to 3.0%, the adsorption of dye molecules on fibers of F. mandshurica veneer would gradually reach saturation and, therefore, the dye uptake would decline [15]. Figure 2 shows that the dye uptake was improved in the dyeing process when the concentration of reactive brilliant red X-3B dye was 0.5–1.0%.
When the concentration of reactive black KN-B dye increased from 0 to 0.5%, the dye uptake was the highest. When the concentration of the reactive black dye was 0.5–2.0%, the dye uptake decreased. With the increase of reactive black dye concentration, the contact probability of reactive black dye and veneer of F. mandshurica fibers increased when the reactive black dye concentration increases. The solution was too viscous when the concentration of reactive black dye increased to 0.5%; this reduced the penetration of dye molecules so the dye uptake was reduced. When the reactive black dye concentration was further increased to 3.0%, the dye uptake increased slightly but remained at a lower value. When the concentration of the reactive black dye was 0.5–1.0%, the dye uptake of reactive black KN-B was improved.
When the concentration of the reactive blue K-3R dye was 0.5–1.0%, the dye uptake rose. However, the dye uptake decreased with further increases in the reactive blue K-3R dye concentration. This was because with the increase in reactive blue K-3R dye concentration, the reactive blue K-3R dye molecules aggregated in the F. mandshurica veneer, resulting in reduced liquidity, which plugged the wood cell walls of the hole and reduced the permeability of reactive blue K-3R dye [16]. Therefore, the dye uptake was improved in the reactive blue K-3R dyeing process when the reactive blue K-3R dye concentration was 1.0–1.5%.
Figure 3 shows a trend of chromatic aberration with the three kinds of dye. In the dyeing experiments of the above three dyes, with the dye concentration increased from 0 to 1.0%, the chromatic aberration value of F. mandshurica veneer increased sharply from 0 to about 60. Then, when the reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye concentration increased from 1.0% to 3.0%, the veneer chromatic aberration values increased slowly and tended towards stable values. Considering the production cost and energy consumption, the optimal concentration of three kinds of dyes is 0.5–1.0%.

3.3. Infrared Spectrum Analysis of Dye Concentration on Properties of F. mandshurica Veneer

Figure 4 shows the infrared spectrum of unstained F. mandshurica veneer and dyed F. mandshurica veneer of 0.5% and 3.0% concentration of reactive red dye, respectively. The assignment of peaks is summarized in Table 5. The band at 3380 cm−1 is the –OH stretching vibration of F. mandshurica. It can be seen that when the dye concentration was 0.5%, it showed a similar 3380 cm−1 band in both dyed and undyed samples, indicating that when the dye concentration was 0.5% the combination of reactive dyes and F. mandshurica was in the form of physical adsorption [17]. The peak at 3380 cm−1 slightly decreased suggesting that a chemical reaction of –OH and dye molecules occurred between the dye liquor and F. mandshurica in the dyeing process [18]. In the 3.0% reactive brilliant red X-3B staining of F. mandshurica the –OH stretching vibration at 3380 cm−1 disappeared, possibly due to reactive brilliant red dye coverage of the –OH group in the F. mandshurica or due to the reaction of reactive brilliant red and –OH. When the F. mandshurica was dyed by a 3.0% concentration of reactive brilliant red X-3B, a new peak 2360 cm−1 was produced for the –CN stretching vibration [19]. After the dye treatment, N–H–O absorption at 1658 cm−1 of F. mandshurica decreased. After the 3.0% dye concentration treatment, the C–O–C bond (1171 cm−1) absorption band was enhanced, indicating that the dehydration reaction between the –OH group reactive brilliant red and the hydroxyl groups in F. mandshurica had occurred and formed a C–O–C covalent bond [20]. Therefore, the combination of reactive brilliant red dye and F. mandshurica was in two forms in the dyeing process, physical combination and chemical reaction, and that in the test concentration (0–3.0%) range, with the increase of reactive brilliant red dye concentration, the chemical reaction between the reactive brilliant red dye and F. mandshurica was more obvious. This indicated a better combination [21]. With the increase of the reactive brilliant red concentration (Figure 5), the reactive brilliant red had a very uniform coverage of F. mandshurica and the reactive brilliant red was basically filled in the fibrous tissue of F. mandshurica.
Figure 6 is the infrared spectra peak graph of unstained F. mandshurica, 0.5% and 3.0% reactive black KN-B dye concentration stain samples. The attribution of the infrared spectra band is summarized in Table 5. When the reactive black KN-B dye concentration was 0.5%, there was a gentle peak in the band at 1300–1500 cm−1 and a new band at 2360 cm−1 of the –CN stretching vibration was produced. This was formed by the reaction of carbonyl groups in F. mandshurica and –NH2 groups in reactive black dye [22,23]. When the reactive black KN-B dye concentration was 3.0%, it was obvious that the absorption band of absorption of N–H at 3324 cm−1 was weakened and that the carbonyl groups at 1730 cm−1 had disappeared due to the reaction of carbonyl groups in F. mandshurica and –NH2 groups in reactive black dye. With the increased concentration of reactive black KN-B dye, the reaction between the dye and F. mandshurica was more obvious, indicating that the combination was firmer.
Figure 7 is a graph of the infrared spectra peak of unstained processing F. mandshurica and the dyeing samples with 0.5% and 3.0% reactive blue K-3R dye concentration. As can be seen from Figure 7, when the dye concentration was 0.5% and 3.0%, the peaks at 1658 cm−1 and 3324 cm−1 tended to be gentle and a new peak at 2360 cm−1 was produced. This showed that there was a chemical bond of –CN due to the reaction of carbonyl groups in F. mandshurica and –NH2 groups in reactive blue K-3R dye molecules [23,24].

3.4. Properties of Waterborne Coating on Surface of Dyed F. mandshurica Veneer

The changes of different mechanical properties of the waterborne coating on the surface of dyed F. mandshurica veneer are shown in Figure 8, Figure 9, Figure 10 and Figure 11. It can be seen that when the concentration of reactive red dye increased from 0 to 2.0%, the waterborne coating hardness increased from B to 3H, the adhesion decreased from level 1 to level 3, the impact strength increased from 5.0 kg·cm to 35.0 kg·cm and the gloss of waterborne coating decreased from 88.0% to 11.4%. When the active black dye concentration increased from 0 to 1.0%, the waterborne coating hardness increased from B to 2H, the adhesion decreased from level 1 to 3, the impact strength increased to 35 kg·cm and the gloss of waterborne coating decreased from 88.0% to 24.3%. When the activated blue dye concentration increased from 0 to 1.0%, the waterborne coating hardness increased from B to 3H, the adhesion decreased from level 1 to level 2, the impact strength increased to 40 kg·cm and the gloss of waterborne coating decreased from 88.0% to 25.1%. According to the general requirements of the national standard for wooden furniture [25], the gloss of the waterborne coating on the surface of dyed F. mandshurica veneer is matte [26]. With further increases in the concentration of reactive dyes, changes in hardness, adhesion and impact resistance changed very little. Compared with undyed F. mandshurica veneer, the hardness of the waterborne coating increased, the adhesion decreased and the impact strength increased. This may be due to the reaction between F. mandshurica veneer and reactive dyes that changed the characteristics of the substrate and changed the performance of surface waterborne coatings.

4. Conclusions

The properties of the reactive brilliant red X-3B, black KN-B and blue K-3R dyes for dyeing of F. mandshurica veneer depend largely on the dye concentration. The dye uptake and chromatic aberration of F. mandshurica veneer showed that the concentration of 0.5–1.0% was better. The chromatic aberration showed improved color when the dye concentration was 0.5–2.5%. After combining the dye uptake and chromatic aberration, 0.5–1.0% was considered the better value. Therefore, the optimum conditions in the orthogonal test showed that the dyeing parameters of the reactive brilliant red X-3B, black KN-B and blue K-3R dyes for F. mandshurica veneer were temperatures of 75 °C, a dye concentration of 0.5%–1.0%, a dyeing time of 60 min and bath ratio of 20:1. The dye uptake of brilliant red X-3B dye was 75.0–75.4%, which was higher than that of the other two dyes. The chromatic aberration was 53–59, which was larger and looked more obviously dyed. During the dyeing process of the reactive brilliant red X-3B, reactive black KN-B and reactive blue K-3R dyes for F. mandshurica veneer, the physical and chemical reactions were included in two forms and when the dye concentration was increased in the experimental test range, the reaction between the reactive dye and F. mandshurica veneer was more obvious. After dyeing with reactive brilliant red X-3B, reactive black KN-B and reactive blue K-3R, the hardness of the waterborne coating on the surface of F. mandshurica veneer was increased, adhesion was decreased, impact strength was improved and gloss decreased to the matte level, all positive indications concerning the application of waterborne coating on the surface of dyed F. mandshurica veneer.

Author Contributions

Data curation, X.Y.; Investigation, X.Q.; Writing—original draft, R.L.; Writing—review & editing, T.M.

Acknowledgments

This project was partly supported by the Natural Science Foundation of Jiangsu Province (BK20150887), Youth Science and Technology Innovation Fund of Nanjing Forestry University (CX2016018) and Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD).

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Radaei, E.; Moghaddam, M.R.A.; Arami, M. Application of artificial neural network on modeling of reactive blue 19 removal by modified pomegranate residual. Environ. Eng. Manag. J. 2017, 16, 2113–2122. [Google Scholar]
  2. Pan, Y.; Hurren, C.-J.; Li, Q. Effect of sonochemical scouring on the surface morphologies, mechanical properties, and dyeing abilities of wool fibres. Ultrason. Sonochem. 2018, 41, 227–233. [Google Scholar] [CrossRef] [PubMed]
  3. Was-Gubala, J.; Starczak, R. UV-Vis microspectrophotometry as a method of differentiation between cotton fibre evidence coloured with reactive dyes. Spectrochim. Acta A 2015, 142, 118–125. [Google Scholar] [CrossRef] [PubMed]
  4. Ratnamala, G.-M.; Deshannavar, U.-B.; Munyal, S.; Tashildar, K.; Patil, S.; Shinde, A. Adsorption of reactive blue dye from aqueous solutions using sawdust as adsorbent: Optimization, kinetic, and equilibrium studies. Arab. J. Sci. Eng. 2016, 41, 333–344. [Google Scholar] [CrossRef]
  5. Khadijeh, A.; Habib-Allah, T. Adaptive neuro-fuzzy inference system analysis on adsorption studies of reactive red 198 from aqueous solution by SBA-15/CTAB composite. Spectrochim. Acta A 2017, 171, 439–448. [Google Scholar]
  6. Ageetha, V.; Bhumika, C.; Padmaja, P. Adsorption of reactive blue 21 and reactive red 141 from aqueous solutions onto hydrotalcite. J. Environ. Chem. Eng. 2016, 4, 2617–2627. [Google Scholar]
  7. Yan, X.-X.; Qian, X.-Y.; Lu, R.; Miyakoshi, T. Synergistic effect of addition of fillers on properties of interior waterborne UV-curing wood coatings. Coatings 2018, 8, 9. [Google Scholar] [CrossRef]
  8. Yan, X.-X.; Cai, Y.-T.; Lu, R.; Miyakoshi, T. Development and characterization of new coating material of blended epoxy-lacquer with aluminum. Int. J. Polym. Sci. 2017, 2017, 5017356. [Google Scholar] [CrossRef]
  9. Sun, D.-L.; Sun, D.-B.; Yu, X.-C. Ultrasonic-assisted dyeing of poplar veneer. Wood Fiber Sci. 2011, 43, 442–448. [Google Scholar]
  10. Xiong, X.-Q.; Guo, W.-J.; Fang, L.; Zhang, M.; Wu, Z.-H.; Lu, R.; Miyakoshi, T. Current state and development trend of Chinese furniture industry. J. Wood Sci. 2017, 63, 433–444. [Google Scholar] [CrossRef]
  11. Siddiqua, U.-H.; Ali, S.; Iqbal, M.; Hussain, T. Relationship between structure and dyeing properties of reactive dyes for cotton dyeing. J. Mol. Liq. 2017, 241, 839–844. [Google Scholar] [CrossRef]
  12. Starczak, R.; Was-Gubala, J. UV-Vis microspectrophotometric study of wool and polyamide fibres dyed with analogous gryfalan dyes. Dyes Pigments 2016, 132, 58–63. [Google Scholar] [CrossRef]
  13. Hiromitsu, K.; Ryuta, T.; Yoshiro, K.; Daisuke, K.; Yuka, O.; Yuki, B.; Hiroyuki, S.; Tatsuhiro, G.; Yoshiyasu, K.; Ko, M.; et al. Linked color imaging (LCI), a novel image-enhanced endoscopy technology, emphasizes the color of early gastric cancer. Endosc. Int. Open 2017, 5, E1005–E1013. [Google Scholar] [Green Version]
  14. Najafpoor, A.; Alidadi, H.; Esmaeili, H.; Hadilou, T.; Dolatabadi, M.; Hosseinzadeh, A.; Davoudi, M. Optimization of anionic dye adsorption onto Melia azedarach sawdust in aqueous solutions: Effect of calcium cations. Asia-Pac. J. Chem. Eng. 2016, 29, 258–270. [Google Scholar] [CrossRef]
  15. Lu, X.-J.; Yang, B.; Chen, J.-H.; Sun, R. Treatment of wastewater containing azo dye reactive brilliant red X-3B using sequential ozonation and upflow biological aerated filter. J. Hazard. Mater. 2009, 161, 241–245. [Google Scholar] [CrossRef] [PubMed]
  16. Tissera, N.-D.; Wijesena, R.-N.; de Silva, K.-M.-N. Ultrasound energy to accelerate dye uptake and dye-fiber interaction of reactive dye on knitted cotton fabric at low temperatures. Ultrason. Sonochem. 2016, 29, 270–278. [Google Scholar] [CrossRef] [PubMed]
  17. Mahmoud, M.-E.; Nabil, G.-M.; E-l Mallah, N.-M.; Bassiouny, H.-I.; Kumar, S.; Abdel-Fattah, T.-M. Kinetics, isotherm, and thermodynamic studies of the adsorption of reactive red 195 A dye from water by modified Switchgrass Biochar adsorbent. J. Ind. Eng. Chem. 2016, 37, 156–167. [Google Scholar] [CrossRef]
  18. Hu, L.-L.; Wang, Q.; Qian, H.-F.; Fan, X.-R. Reactivity and stability of CI reactive red 120 at high temperature. Fibers Polym. 2014, 15, 2515–2524. [Google Scholar] [CrossRef]
  19. Rizk, H.-F.; Ibrahim, S.-A.; El-Borai, M.-A. Synthesis, fastness properties, color assessment and antimicrobial activity of some azo reactive dyes having pyrazole moiety. Dyes Pigments 2015, 112, 86–92. [Google Scholar] [CrossRef]
  20. Xiao, H.; Zhao, T.; Li, C.-H.; Li, M.-Y. Eco-friendly approaches for dyeing multiple type of fabrics with cationic reactive dyes. J. Clean. Prod. 2017, 165, 1499–1507. [Google Scholar] [CrossRef]
  21. Wu, X.-B.; Wu, D.-C.; Fu, R.-W. Studies on the adsorption of reactive brilliant red X-3B dye on organic and carbon aerogels. J. Hazard. Mater. 2007, 147, 1028–1036. [Google Scholar] [CrossRef] [PubMed]
  22. Xiao, J.-Q.; Zhang, S.-F.; Yang, J.-Z.; Huang, Q. Study on chemical bonding of polycarboxylic acid black on cotton and its dyeing and finishing properties. Dyes Pigments 2007, 73, 111–117. [Google Scholar] [CrossRef]
  23. Yan, X.-X.; Xu, G.-Y. Influence of silane coupling agent on corrosion-resistant property in low infrared emissivity Cu/polyurethane coating. Prog. Org. Coat. 2012, 73, 232–238. [Google Scholar] [CrossRef]
  24. Chen, T.-Y.; Kao, C.-M.; Hong, A.; Lin, C.-E.; Liang, S.-H. Application of ozone on the decolorization of reactive dyes-Orange-13 and Blue-19. Desalination 2009, 249, 1238–1242. [Google Scholar] [CrossRef]
  25. GB/T3324-2008 Wooden Furniture-General Technical Requirements; Standardization Administration of the Peoples’s Republic of China: Beijing, China, 2008; pp. 1–16. (In Chinese)
  26. Toscani, M.; Valsecchi, M.; Gegenfurtner, K.-R. Lightness perception for matte and glossy complex shapes. Vis. Res. 2017, 131, 82–95. [Google Scholar] [CrossRef] [PubMed]
Figure 1. The structures of (A) reactive brilliant red X-3B dye, (B) reactive black KN-B dye and (C) reactive blue K-3R dye.
Figure 1. The structures of (A) reactive brilliant red X-3B dye, (B) reactive black KN-B dye and (C) reactive blue K-3R dye.
Polymers 10 01302 g001
Figure 2. Effects of reactive brilliant red X-3B, black KN-B and blue K-3R dye concentrations on dye uptake.
Figure 2. Effects of reactive brilliant red X-3B, black KN-B and blue K-3R dye concentrations on dye uptake.
Polymers 10 01302 g002
Figure 3. Effect of reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye concentrations on chromatic aberration.
Figure 3. Effect of reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye concentrations on chromatic aberration.
Polymers 10 01302 g003
Figure 4. IR spectra of F. mandshurica veneer after dyeing with different concentrations of reactive red.
Figure 4. IR spectra of F. mandshurica veneer after dyeing with different concentrations of reactive red.
Polymers 10 01302 g004
Figure 5. Side SEM of F. mandshurica veneer after reactive red dyeing at different concentrations of (A) 0.5% and (B) 3.0%.
Figure 5. Side SEM of F. mandshurica veneer after reactive red dyeing at different concentrations of (A) 0.5% and (B) 3.0%.
Polymers 10 01302 g005
Figure 6. IR spectra of F. mandshurica veneer after dyeing with different concentrations of reactive black.
Figure 6. IR spectra of F. mandshurica veneer after dyeing with different concentrations of reactive black.
Polymers 10 01302 g006
Figure 7. IR spectra of F. mandshurica veneer after dyeing with different concentrations of reactive blue.
Figure 7. IR spectra of F. mandshurica veneer after dyeing with different concentrations of reactive blue.
Polymers 10 01302 g007
Figure 8. Variation trend of waterborne coating hardness on the F. mandshurica veneer after dyeing.
Figure 8. Variation trend of waterborne coating hardness on the F. mandshurica veneer after dyeing.
Polymers 10 01302 g008
Figure 9. Variation trend of waterborne coating adhesion on the F. mandshurica veneer after dyeing.
Figure 9. Variation trend of waterborne coating adhesion on the F. mandshurica veneer after dyeing.
Polymers 10 01302 g009
Figure 10. Variation trend of waterborne coating impact strength on the F. mandshurica veneer after dyeing.
Figure 10. Variation trend of waterborne coating impact strength on the F. mandshurica veneer after dyeing.
Polymers 10 01302 g010
Figure 11. Variation trends of gloss of waterborne coating on the F. mandshurica veneer after dyeing.
Figure 11. Variation trends of gloss of waterborne coating on the F. mandshurica veneer after dyeing.
Polymers 10 01302 g011
Table 1. L4 (23) results of dye uptake by F. mandshurica veneer.
Table 1. L4 (23) results of dye uptake by F. mandshurica veneer.
SampleDye concentration (%)Bath ratioDyeing time (min)Dye uptakeRed (%)Dye uptakeBlack (%)Dye uptakeBlue (%)
1Red, 1Black, 1Blue1.020:16075.050.066.0
2Red, 2Black, 2Blue1.030:112053.036.044.0
3Red, 3Black, 3Blue5.020:11208.422.042.0
4Red, 4Black, 4Blue5.030:1603.61.833.0
RangeRed58.013.48.6
RangeBlack31.117.13.1
RangeBlue17.515.56.5
VarianceRed3364.0179.674.0
VarianceBlack967.2292.49.6
VarianceBlue306.3240.342.3
1Red, 2Red, 3Red and 4Red refer to the 1–4 samples of reactive brilliant red X-3B dye. 1Black, 2Black, 3Black and 4Black refer to 1–4 samples of reactive black KN-B dye. 1Blue, 2Blue, 3Blue and 4Blue refer to 1–4 samples of reactive blue K-3R dye. RangeRed, RangeBlack and RangeBlue are the range of reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye, respectively. VarianceRed, VarianceBlack and VarianceBlue are the variance of reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye, respectively. Dye uptakeRed, Dye uptakeBlack and Dye uptakeBlue are the dye uptake of reactive brilliant red X-3B dye, reactive black KN-B dye and reactive blue K-3R dye, respectively.
Table 2. L4 (23) orthogonal test of chromatic aberration with reactive brilliant red.
Table 2. L4 (23) orthogonal test of chromatic aberration with reactive brilliant red.
SampleLabL’a’b’ΔLΔaΔbΔE
1Red75.45+5.79+20.8637.08+45.75+8.39−38.37+39.96−12.4756.79
2Red76.77+5.35+20.1133.09+41.59+13.26−43.68+36.24−6.8557.17
3Red74.30+5.97+21.1530.33+36.21+12.97−43.97+30.24−8.1853.99
4Red75.14+5.95+19.9230.87+38.00+13.71−44.27+32.05−6.2155.01
Table 3. L4 (23) orthogonal test of chromatic aberration with reactive black.
Table 3. L4 (23) orthogonal test of chromatic aberration with reactive black.
SampleLabL’a’b’ΔLΔaΔbΔE
1Black75.79+6.15+21.0120.82+1.73−2.57−54.97−4.42−23.5859.98
2Black74.61+5.99+20.4922.41+1.28−2.65−52.20−4.71−23.1457.29
3Black74.90+5.87+20.0620.29+4.29−0.36−54.61−1.58−20.4258.32
4Black74.46+5.70+20.0720.45+4.03−0.61−54.01−1.67−20.6857.86
Table 4. L4 (23) orthogonal test of chromatic aberration with reactive blue.
Table 4. L4 (23) orthogonal test of chromatic aberration with reactive blue.
SampleLabL’a’b’ΔLΔaΔbΔE
1Blue75.29+5.99+21.6123.08+1.26−5.91−52.21−4.73−27.5259.21
2Blue74.46+5.97+20.0722.98+1.23−5.44−51.48−4.74−25.5157.65
3Blue74.91+6.03+20.8319.84+1.93−3.40−55.07−4.10−24.2360.30
4Blue75.71+5.81+21.7121.04+2.21−3.64−54.67−3.60−25.3560.37
Table 5. Assignment of peaks.
Table 5. Assignment of peaks.
Peak (cm−1)Assignment
3380–OH stretching vibration
2360–CN stretching vibration
1658N–H–O absorption
1171C–O–C bond absorption
3324absorption of N–H
1730carbonyl groups

Share and Cite

MDPI and ACS Style

Yan, X.; Qian, X.; Lu, R.; Miyakoshi, T. Comparison and Optimization of Reactive Dyes and Coating Performance on Fraxinus mandshurica Veneer. Polymers 2018, 10, 1302. https://doi.org/10.3390/polym10121302

AMA Style

Yan X, Qian X, Lu R, Miyakoshi T. Comparison and Optimization of Reactive Dyes and Coating Performance on Fraxinus mandshurica Veneer. Polymers. 2018; 10(12):1302. https://doi.org/10.3390/polym10121302

Chicago/Turabian Style

Yan, Xiaoxing, Xingyu Qian, Rong Lu, and Tetsuo Miyakoshi. 2018. "Comparison and Optimization of Reactive Dyes and Coating Performance on Fraxinus mandshurica Veneer" Polymers 10, no. 12: 1302. https://doi.org/10.3390/polym10121302

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

Article Metrics

Back to TopTop