Kun Liabc,
Hua Zheng*abc,
Hong Zhangabc,
Wen-wen Zhangab,
Kai Liab and
Juan Xuab
aResearch Institute of Resources Insects, Chinese Academy of Forestry, Kunming, 650224, People's Republic of China. E-mail: riricaf@163.com; Tel: +86-871-63860021
bResearch Center of Engineering and Technology on Forest Resources with Characteristics, State Forestry Administration, Kunming, Yunnan 650224, People's Republic of China
cKey Laboratory of Cultivation and Utilization of Resource Insects, State Forestry Administration, Kunming, Yunnan 650224, People's Republic of China
First published on 6th June 2016
This study made use of a novel totally chlorine-free (TCF) bleaching approach to prepare bleached shellac. Some single factor experiments were employed to investigate the effects of the main factors in the H2O2 bleaching method. A new chlorine-free bleached shellac resin was obtained in the Box–Behnken design responsive surface optimal experimental conditions (pH, 9.0–11.0; 1.33 mL g−1, concentration of 30% hydrogen peroxide; 2.0 h, dropping time of hydrogen peroxide; 7.2 h, bleaching time; 90 °C, temperature). The yield and color index of the bleached shellac obtained under the optimal experimental conditions were 80.84% and 0.5675 respectively. The result of the physicochemical property test, IR spectrum and DSC characterization indicate that the properties of H2O2 bleached shellac are similar to commercially refined shellac resin. Moreover, it is noteworthy that the H2O2 bleached shellac was remarkable in alcohol solubility and thermal lifetime tests. It had a higher acid value and a lower softening point compared with commercially refined shellac resin, which can be applied safely in many fields including food and medical industries without chlorine residues.
Therefore, the fabrication of bleached shellac by the TCF bleaching method is very important and provides opportunities for the shellac industry. Hydrogen peroxide, a green (environmentally friendly) bleaching agent, has high reactivity and meets the requirement34–37 of being totally free from chlorine. However, there is a problem: the bleaching reaction that occurs under alkaline condition and acidulous hydrogen peroxide is easily neutralized by alkali in the bleaching solution. So, with the occurrence of neutralization reaction, the bleaching reaction may easily fail because the bleaching efficiency of hydrogen peroxide is reduced quickly and shellac is separated out from the bleaching solution. In view of this, the pH of the bleaching liquor may be the key factor. It needs to be controlled during the bleaching process to make sure that the bleaching reaction is performed under optimal pH conditions.
Therefore, the TCF bleaching technique of making shellac resin can be processed and optimized by single factor experiments and the Box–Behnken design responsive surface optimal experiment. Meanwhile, the physical and chemical properties of the obtained chlorine-free bleached shellac have been characterized to provide data for the application of bleached shellac.
The stabilizers made from the mixture of Na2SiO3 and MgSO4 in the ratio of 4:1 (w:w), namely 0.6 g and 0.15 g, were added to the solvent, and 30% H2O2 solution (volume 20, 30, 40, 50 and 60 mL; equivalent concentration 0.667, 1.00, 1.33, 1.67 and 2.00 mL g−1) was injected into the solvent at different times (2, 3, 4, 5 and 6 h). Finally, the bleaching procedure was carried out at varying times (3, 4, 5, 6, 7, 8, and 9 h) and temperatures (50 °C, 60 °C, 70 °C, 80 °C and 90 °C).
After the bleaching procedure was completed, the liquor was cooled down and filtered by adding diatomite. After acidification with 5% sulfuric acid, washing and freeze drying, the bleached shellac was weighed to measure the moisture content. The yield and color index of the bleached shellac was calculated by using the method in the section above.
The yield of the bleached shellac is calculated as:
The color index of the bleached shellac was determined using the ultraviolet spectrophotometric procedure (UV, DU800, Beckman, United States) as the method provided by Chinese national GB standard (GB/T8143-2008).38
Independent variable | Coding level | |||
---|---|---|---|---|
−1 | 0 | 1 | ||
A | H2O2 | 1.00 mL g−1 | 1.33 mL g−1 | 1.67 mL g−1 |
B | Bleaching time | 4 h | 6 h | 8 h |
C | Bleaching temperature | 70 °C | 80 °C | 90 °C |
As shown in Fig. 4a, within a certain range, as the H2O2 increased, the color index of the bleached shellac decreased and the bleaching effect tended to be preferable, while the bleaching yield reduced at the same time. When the concentration of H2O2 was 1.33 mL g−1, the bleaching yield curve tended to be balanced and the color index was close to 1.0. However, when the concentration of H2O2 increased to 2.00 mL g−1, the color index of the bleached shellac continuously decreased to 0.48 (less than 1.0). To optimize the concentration of H2O2, the maximum bleaching yield was expected to be found on the premise that the color index of bleached shellac could meet the standard. Thus, the range of 1.00–1.67 mL g−1 could be selected as the optimization range of the variable for the next optimal experiment.
In Fig. 4b, when the dropping time of H2O2 was longer than 2.0 h, the bleaching yield and color index showed little change under the conditions proposed in this paper. In the range of 2 to 6 h, all the corresponding color indexes were less than 1.0, meeting the standard of refined bleached shellac Grade I in GB/T8140-2009. Besides, the change in the bleaching yield was only by ±4%. The influence of the dropping time was insignificant. Hence, there was no need to optimize the factor except in choosing the dropping time of H2O2 as 2 h. This indicates that the adsorption of H2O2 by the stabilizer was very likely to be saturated because of high dropping speed of H2O2. This made the bleaching reaction difficult to control and unsafe. Therefore, the dropping time of 2 h was proved to be more suitable.
Fig. 4c showed that within the given range of the bleaching time, the yield of shellac bleaching changed slightly and peaked at 5–7 h of bleaching reaction. Meanwhile, the color index kept decreasing with the bleaching reaction and tended to be generally stable after 7 h. This shows that it met the prescribed requirements for refined bleached shellac Grade I according to GB/T8140-2009. After 3 h of reaction, prolonging the bleaching time had no significant influence on the bleaching effect. On the condition that the color index meets the standard, maximizing the yield of shellac bleaching can expand the optimization range of the bleaching time. Thus, taking the change of color index and yield into account, the optimization of the variable ranging from 4 to 8 h was the best choice.
In the range of 50 °C to 90 °C, the color index of the bleached shellac decreased with rising temperature under the same condition (see Fig. 4d). It was obvious that the higher temperature was conducive for shellac bleaching. However, the yield of the bleached shellac declined with increasing temperature, which demonstrates that it is essential to find the balance between the yield and color index of the bleached shellac. Therefore, the bleaching temperature needs to be optimized. Owing to the high color (>2.0) index at higher temperatures (>70 °C), it is better to set the optimization range in the range of 70 °C to 90 °C for the next optimal experiment.
Run order | A, H2O2, mL | B, bleaching time, h | C, bleaching temperature, °C | Bleaching yield/% | Color index |
---|---|---|---|---|---|
1 | 1 | −1 | 0 | 68.26 | 0.8576 |
2 | 1 | 1 | 0 | 63.51 | 0.8953 |
3 | 1 | 0 | −1 | 82.14 | 1.6975 |
4 | 0 | −1 | −1 | 91.93 | 2.4222 |
5 | 0 | −1 | 1 | 72.15 | 0.7474 |
6 | −1 | 1 | 0 | 75.56 | 1.7709 |
7 | 1 | 0 | 1 | 63.61 | 0.3998 |
8 | −1 | 0 | 1 | 77.54 | 0.8002 |
9 | 0 | 0 | 0 | 54.99 | 0.9692 |
10 | −1 | −1 | 0 | 77.65 | 1.7254 |
11 | 0 | 1 | 1 | 75.46 | 0.5432 |
12 | 0 | 0 | 0 | 55.86 | 1.0017 |
13 | 0 | 1 | −1 | 87.96 | 2.6854 |
14 | −1 | 0 | −1 | 92.9 | 5.4639 |
15 | 0 | 0 | 0 | 60.68 | 0.9913 |
The acquired coefficients of the predictive equation and the variance are presented in Table 3. The influence of each factor was judged by P value, i.e., when the P value was less than or equal to 0.05, the influence of the factor was significant.42 As indicated in Table 3a, for the linear terms, the influences of bleaching temperature and the concentration of H2O2 reached significant levels. The degree of influence is as follows: bleaching temperature > the concentration of H2O2 > bleaching time. For the interaction terms, only the interactive influence of the concentration of H2O2 and the bleaching time was significant, and the degree of influence indicate a descending order as follows: AB > BC > AC. The bleaching yield was significantly impacted by all quadratic terms in the order of C2 >B2 > A2. By analyzing the degree of influence of the optimizing factors selected in Table 3 on the response values, it can be shown that the independent variables and the ranges were able to reflect the variation of the bleaching yield with the change in the factors mentioned using this model. Among the parameters, the lack of fit was 0.8715 (much higher than 0.05), which suggests that the lack of fit was insignificant. Meanwhile, the regression coefficient of the model was R2Adj = 0.9662, which indicates that the fitting degree of the regression equation was favorable.43,44
(a) Bleaching yield as response value | (b) Color index as response value | ||
---|---|---|---|
Source | P value | Source | P value |
Model | 0.0003 | Model | <0.0001 |
A | 0.0008 | A | <0.0001 |
B | 0.2907 | B | 0.0399 |
C | 0.0001 | C | <0.0001 |
AB | 0.0001 | AB | 0.8044 |
AC | 0.5118 | AC | <0.0001 |
BC | 0.1659 | BC | 0.0005 |
A2 | 0.0048 | A2 | <0.0001 |
B2 | 0.0008 | B2 | 0.0016 |
C2 | <0.0001 | C2 | <0.0001 |
— | — | A2C | <0.0001 |
— | — | AB2 | <0.0001 |
Lack of fit | 0.8715 | Lack of fit | 0.6575 |
R2 = 0.9880 R2Adj = 0.9662 | R2 = 0.9999 R2Adj = 0.9999 |
Table 3b shows that the influence of the bleaching kinetics model, with the concentration of H2O2, bleaching time and bleaching temperature as influencing factors on the color index of bleached shellac, achieved an extremely significant level. For the linear terms, the influences of the concentration of H2O2 and bleaching temperature were extremely significant, while that of bleaching time was significant. Among the interaction terms, the interactive influence of the concentration of H2O2 and bleaching temperature (AC), and the bleaching time and bleaching temperature (BC) were extremely significant, while that of the concentration of H2O2 and bleaching time (AB) was below the significant level. Besides, all quadratic terms showed extremely significant levels including the correction terms A2C and AB2. Taking all the model parameters into account, the lack of fit was 0.6575, which was greater than 0.05, and the fitting coefficient of the model equation was R2Adj = 0.9999, suggesting that the regression equation exhibited preferable fitting degree.43
3D surface and contour analysis diagrams for the influence of each group of interactive parameters on the yield and color index of bleached shellac were generated according to the regression equation, as shown in Fig. 5.
Fig. 5 3D surfaces and contours of RSM for the interactive influences of each factor on bleaching yield and color index. |
From the 3D response surface plots of the yield of bleached shellac and each factor in Fig. 5a, it can be seen that the concentration of H2O2, bleaching temperature and bleaching time were the key factors influencing the yield of bleached shellac. In addition, all the yield bleaching curves revealed a tendency to form an inverse parabola under the interactive influence of each factor, which means that the influences of the three factors should be comprehensively considered to find the optimum balance point for the yield of the bleached shellac. However, since the yield of the bleached shellac was not the only indicator to be considered in the model, it was essential to ensure that the color index of the bleached shellac could meet China's national standard while maximizing the yield of the bleached shellac. Therefore, the model needed to be further optimized with color index as the response value.
Fig. 5b revealed that the influence of the interaction factors on the color index of the bleached shellac was in a monotonous trend. This was attributed to the mode of influence of each factor on the bleaching effect. For example, the concentration of H2O2 and the bleaching temperature were directly proportional to the color index of the bleached shellac, while the influence of the bleaching time was closely associated with the concentration of H2O2 and the bleaching temperature.
As shown in Fig. 8, based on infrared spectrogram, the main molecular framework of H2O2 bleached shellac is consistent with commercially refined shellac resin. This demonstrates that H2O2 bleached shellac is one of the new species of shellac resin. However, there are differences in the main absorption peaks between the two shellac resins: 1565 cm−1 in commercially refined shellac and 1415 cm−1 in H2O2 bleached shellac.46 Firstly, the peaks at 1565 cm−1 are CC stretching vibration absorption peaks of aromatic hydrocarbons carbon framework. Also, the aromatic hydrocarbon in alkaline extracted shellac resin is anthraquinone chromogenic material. Evidently, the disappearance of this peak in H2O2 bleached shellac shows that a bleaching reaction assuredly occurred in the process. To an extent, it supports the theory that the main colored constituents of shellac are laccaic acids47,48 (pigments in shellac resin, as shown in Fig. 9). Secondly, a new absorption peak, 1415 cm−1, was found in H2O2 bleached shellac. It is O–H bond deformation vibration absorption peak of carboxylic acid. Therefore, a new carboxylic acid was generated in the bleaching process of shellac. The hydroxyl or aldehyde of shellac resin was simultaneously oxidized when hydrogen peroxide attacked the chromophore of anthraquinones. Other absorption peaks were assigned as follows:49 stretching vibration absorption peak of hydroxyl at 3425 cm−1, stretching vibration absorption peak of the hydroxyl C–O bond at 1042 cm−1, C–H stretching vibration absorption peaks of methyl and methylene at 2932 cm−1 and 2857 cm−1, deformation vibration absorption peak of olefin in C–H bond surface at 1042 cm−1, stretching vibration absorption peak of carbonyl at 1718 cm−1, O–H bond deformation vibration absorption peak of carboxylic acid at 1411 cm−1 and stretching vibration absorption peak of C–O bond of aromatic oxide bond at 1146 cm−1 and 1254 cm−1.
DSC curves of H2O2 bleached shellac and commercially refined shellac are shown in Fig. 10. By analyzing these curves, it was discovered that the glass transition of these two kinds of shellac occurred at the temperature range of −20 °C to 50 °C. The glass transition temperature of commercially refined shellac was 32.23 °C, which is higher than that of bleached shellac, with a glass transition temperature of 26.50 °C. Thus, stress relaxation of intermolecular rearrangement was more likely to happen in H2O2 bleached shellac than in commercially refined shellac.39 It also suggests that H2O2 bleached shellac has higher requirements regarding storage conditions. As for the melting process, there were significant differences between H2O2 bleached shellac and bleaching materials. There were two relatively obvious melting and endothermic processes, at 0–100 °C and 150–350 °C within the test range of 0–400 °C. The first endothermic peak of commercially refined shellac was obvious and sharp with initial, final and peak temperatures of 60.1 °C, 74.7 °C and 68.3 °C respectively, while the temperature range of the second one was greater in a smooth peak shape with initial and final temperatures of 182.8 °C and 380.2 °C respectively, but without a clear peak value. The thermal absorption characteristics of H2O2 bleached shellac were opposite those of commercially refined shellac. In other words, the first endothermic peak was smooth with initial and final temperatures of 19.1 °C and 119.5 °C respectively. Its peak value temperature was 68.4 °C, which is close to that of commercially refined shellac. However, the second peak was sharper than the first one, with initial, final and peak temperatures of 121.4 °C, 224.3 °C and 222.5 °C respectively. Based on the results, it can be said that the components of high melting point in H2O2 bleached shellac increased, and at the same time, the thermal response temperature of the components of low melting point decreased greatly (with initial melting temperature of 19.1 °C) compared with that of commercially refined shellac. The result is consistent with that of IR spectrum, which shows that the amount of carboxyl increased. This suggests that shellac resin was oxidized during the H2O2 bleaching process.
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