Abstract
Neem (Melia azedarach) extract has good antibacterial properties, but its bioactivities are easily decomposed. In order to protect the bioactivities of neem extract, melamine urea formaldehyde (MUF) was used as wall material to prepare a wood microcapsule preservative. The size and distribution of microcapsules after treatments at different temperatures were determined by microscopy. These observations showed that increases in temperature caused the microcapsule particles to become smaller and more evenly distributed. The stability of this preservative was studied by use of an environmental factors experiment (ultraviolet light, condensation, and water spray) and a decay test. The results indicated that the microcapsule preservative from neem extract was more stable than the neem extract preservative. The results indicated that the microcapsule preservative from neem extract showed acceptable environmental stability. The water spray resistance of microcapsule preservative from neem extract was the best.
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Preparation and Stability of Microcapsule Wood Preservative from Neem Extract
Luchen Liu and Guoqi Xu *
Neem (Melia azedarach) extract has good antibacterial properties, but its bioactivities are easily decomposed. In order to protect the bioactivities of neem extract, melamine urea formaldehyde (MUF) was used as wall material to prepare a wood microcapsule preservative. The size and distribution of microcapsules after treatments at different temperatures were determined by microscopy. These observations showed that increases in temperature caused the microcapsule particles to become smaller and more evenly distributed. The stability of this preservative was studied by use of an environmental factors experiment (ultraviolet light, condensation, and water spray) and a decay test. The results indicated that the microcapsule preservative from neem extract was more stable than the neem extract preservative. The results indicated that the microcapsule preservative from neem extract showed acceptable environmental stability. The water spray resistance of microcapsule preservative from neem extract was the best.
Keywords: Wood preservatives; Neem extract; Microcapsule; Environmental stability
Contact information: College of Engineering and Technology, Northeast Forestry University, Harbin 150040 China; *Corresponding authors: xuguoqi_2004@126.com
INTRODUCTION
Wood protection has been used since the early days, when people used coatings (such as tung oil and tannin) to protect wood (Lotz and Hollaway 1988). Copper chromium arsenate (CCA), lindane, and sodium pentachlorophenate have been extensively used worldwide. However, due to the toxicity of these preservatives, they have been phased out (Aceto and Fedele 1994). Many companies have developed more environmentally friendly wood preservatives and have applied for patents. Some of these preservatives have been used in practice such as quaternary ammonium copper series (ACQ-C and ACQ-D), CuHDO (Dibis, which stands for copper N-cyclohexane diazene dioxide), and Triazle (Hayoz et al. 2003). However, these types of wood preservatives have problems with the improvement of the anti-corrosion treatment process and the recycling of waste disposal materials (Lebow et al. 2004; Freeman et al.2005; Ung and Cooper 2005; Eller et al. 2018).
Plants produce many metabolic products with bacteriostatic effects in the face of environmental intrusion (Gould 1989; Swain 1997; Teng et al. 2018). Therefore, plant extracts can be used as active ingredients in wood preservatives (Singh and Singh 2012). Extracts from neem (Melia azedarach) have excellent resistance to insect and fungi (Islam et al. 2009). Melia azedarach contains bioactive compounds such as azadirachtin and quercetin. Extremely low concentrations of azadirachtin and quercetin can inhibit the growth of wood-decay fungi (Dhyani and Tripathi 2006, 2008). Although azadirachtin extracts have a strong antibacterial effect, they are sensitive to ultraviolet rays and temperature (Jarvis et al. 1998). This leads to the inactivation of azadirachtin when it is used as a wood preservative, which affects the service life of the wood treated by neem extracts.
Microencapsulation is a promising remedial technique for resolving and addressing the environmental issue of pesticides (Takei et al. 2008; Zhu et al. 2010); this technique has been used for formulation of fenitrothion and methomyl (Knowles 1998). Microencapsulation entraps liquid or solid molecules in a polymeric shell material. It is commonly applied in various fields such as pesticide and medicine (Gao and Qian 2010; Li et al. 2011; Scott et al. 2011). Due to the small size of microcosmic “channels” such as wood vessels and pits (Uphill et al. 2014), the size and diameter of microcapsule granules are important for applying microcapsule technology to wood preservation. When the diameter of the microcapsule is less than 20 µm, it can be pressurized into some species of wood by vacuum impregnation (Hayward et al. 2014). Larger microcapsules are effectively imported by increasing the porosity of wood through microwave expansion and other pretreatment technologies (He et al. 2014). The above research indicates that this technology has certain difficulties in the use of wood preservation. In this study, microcapsule pre-preservative solution was inserted into wood and then solidified into a capsule by controlling the temperature. The air-stability of the preservative was investigated through environmental simulation experiments of sunlight, dew, and rain.
EXPERIMENTAL
Materials
Neem (Azadirachta indica A. Juss) seeds were picked from different trees in September 2017 (Yuanmou County, Yi Autonomous Prefecture of Chuxiong, Yun Nan Province, China (East longitude 101 ° 35 ’06’ – 102 °, 25 ° 23 ‘- 26 ° 06’ north latitude)). The seeds were washed, dried, and crushed through a 20-mesh sieve. Sapwood samples were cut from fresh felled poplar (Populus ussuriensis Kom.) (Dongfanghong Forest Farm, Heilongjiang Province, China). The samples were prepared from a board milled to 20 mm (R) × 20 mm (L) × 10 mm (T). The chemical reagents used in the experiment were anhydrous ethanol, distilled water, and 50% melamine modified urea formaldehyde resin (Research Institute of Wood Industry, Chinese Academy of Forestry).
Preparation of Microcapsule Pre-preservatives
The active ingredients of neem were extracted from seeds using the water-bath method. The extraction temperature was 50 °C. 50% ethanol aqueous solution was used for the extraction. The extracted solvent to material ratio was 16:1 by volume. The extracted mixture was suction-filtered to obtain a filtrate. The filtrate was placed on a rotary evaporator to obtain an extract of the neem seed active ingredient. All mixtures were formulated to contain 10% neem extract and 10% MUF by weight. The mixture treatments were prepared using a 90-4 digital temperature-controlled magnetic stirrer (Shanghai Zhenjie experimental equipment co. LTD, Shanghai, China) at a temperature of 50 °C, a stirring speed of 1200 r/min, and a stirring time of 1 h.
Immersion Treatment of Wood Samples
All wood samples were extracted with purified water to remove impurities. The samples were numbered and sterilized in an autoclave at 120 °C for 1 h. The samples were conditioned to a constant mass at 103 °C in a dryer and weighed. The wood samples were submerged under a given treatment solution and held under a vacuum for 12 h. The treatment solutions were a microcapsule pre-preservative solution, an extract of the neem seed solution, and an MUF solution. The wood samples were removed, the surface solidified liquid was erased, and the mass of the wood was weighed after drying so that the drug loading could be calculated.
Process of Microcapsule Formed Inside Wood Samples
The treated with microcapsule pre-preservative solution samples were placed in an oven and gradually heated. The heating process is shown in Table 1. The control points for each temperature increased from 40 °C to 80 with a 10 °C interval. The heating time of the samples in each stage was 5 h. After drying all of the samples (A, B, C, D, E) at 40 °C for 5 h, a certain amount of samples (A) was taken out. The remaining samples (B, C, D, E) were dried in the next stage at 50 °C for 5 h, and then some samples (B) were taken out. The remaining samples (C, D, E) continued to be heated at 60 °C for 5 h, and the previous steps were repeated. Finally, the final samples (E), at an initial temperature of 80 °C, passed through each stage of heating. With the gradual rise in temperature, the microcapsules gradually formed inside the samples.
Table 1. The Heating Process
Morphology Observations of the Treated Wood Samples
The treated samples were cut into small pieces (8 mm (R) × 8 mm (T) × 1 mm (L)). The small samples were sputter-coated with gold. The morphology was observed by scanning electron microscopy (SEM, Quanta 200, FEI Co., Hillsboro, OR, USA). The acceleration voltage was set to 10 kv to 15 kv, the beam spot was 2 to 3, and the working distance was 10 mm.
Environmental Factors Experimental Design
To evaluate the environmental stability of microcapsule wood preservatives, accelerated ageing tests of the three different treated wood samples (Table 2) were performed in an ultraviolet aging test chamber using ultraviolet rays, condensation, and spray. A UV-A340 lamp and UV-B313 was used to simulate the UV portion of the solar spectrum. The spray and condensation of water was used to simulate rain and dew.
Decay Resistance Test of the Treated Wood Samples before and after Accelerated Ageing Tests
This test used the samples in Table 2. The samples taken before the accelerated ageing tests were treated as the control experiment. The wood samples were tested for resistance to wood-decay fungi using a Chinese standard method of testing wood preservatives (GB/T 13942.1 2009). The treated wood samples were conditioned to a constant mass at 50 °C in dryer and weighed. The treated wood samples were sterilized in an autoclave at 120 °C for 1 h. The samples were cultured in a river sand sawdust medium with brown rot fungi (Gloeophyllum trabeum) for 12 weeks. After 12 weeks, the mycelium on the sample surfaces was scraped, conditioned to a constant mass at 103 °C in a dryer, and weighed. The mass loss rate of the treated samples under various accelerated aging tests was calculated.
Table 2. The Environmental Factors Experimental Design
RESULTS AND DISCUSSION
Observation of the Morphology of the internal Microcapsule in Treated Wood Samples
The morphology of the wood samples that did not undergo the soaking treatment is shown in Fig. 1. The SEM images show the morphologies of the internal microcapsules of the samples under different control temperatures after gradual heating (Figs. 2 to 6). Some tiny particles were visualized to have formed inside the treated wood samples. This indicated that a large number of microcapsules had been formed in the wood cavity after it was impregnated with the microcapsule pre-preservative solution and was heat cured. This kind of microcapsule structure used MUF as the wall material. The neem extracts were wrapped inside as core material and then fixed in the cavity of the samples. During the microcapsule process, the prepolymer condensed to form MUF particles in the aqueous solution, then the particles aggregated and were deposited at the surface of the internal phase (neem extracts). The morphologies of the internal microcapsules in the samples treated at temperatures below 40 °C are shown in Fig. 2, which shows that the microcapsule existed in some places of the samples, while it was not distributed in some other places. The distribution of the microcapsule was very uneven and sparse. The mean diameter of the microcapsules was slightly larger. The morphology of the internal microcapsule in the samples treated at temperatures below 50 °C are shown in Fig. 3. Compared with the microstructure of wood treated below 40 °C, the microcapsule distributions were more uniform, dense, and showed a trend of decreasing of particle size. The morphology of the internal microcapsule in the samples treated at temperatures below 60 °C are shown in Fig. 4. The size of microcapsules decreased and the distribution of microcapsules was more uniform than that of the samples taken under low temperature conditions. The morphology of the internal microcapsule in the treated wood samples under 70 °C are shown in Fig. 5, which indicates that tiny microcapsule particles in the cell wall of the wood gradually formed a microcapsule structure similar to the membrane shape. The microcapsule was attached to the inner wall of the wood pit. The morphology of the internal microcapsule in the samples treated at temperatures below 80 °C were shown in Fig. 6. It was shown that the particle size of the microcapsule further decreased and became more similar to the membrane structure. The average particle size of the microcapsule was about 1 μm. Microcapsules were also the most evenly distributed. Therefore, the temperature of the treatment affected the uniformity and particle size of encapsulation in the wood samples.
Fig. 1. The morphology of wood samples without soaking treatment
Fig. 2. The morphology of the internal microcapsule in treated samples under 40 °C