Effects of rosin sizing agent on the fixation of boron in Styrax tonkinensis wood

The aim of this study was to evaluate the effect of rosin sizing agent upon fixing boron in Styrax tonkinensis (Piere) wood treated with mixtures of 3% boric acid and 1% rosin sizing agent. After treatment, wood samples were also analyzed by scanning electron microscope observation and energy-Dispersive X-ray spectroscopy (SEM-EDX). The results showed that all boron-rosin formulations impregnated Styrax tonkinensis wood evenly penetrated into the wood blocks. Boron-rosin treatment decreased by 16% the amount of boron leaching from treated wood samples compared with those from the samples treated with boric acid alone. The SEM-EDX analysis proved that the boron element was still in the cell lumens of boron-rosin treated wood blocks after leaching. Results indicated that rosin emulsion sizing agent can have an effect on the fixation of boron in wood. This signifies that using of rosin as fixing agents may contribute to lead to wood treated with boron based preservatives being more widely used

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Effects of rosin sizing agent on the fixation of boron in Styrax tonkinensis wood
 weight differences of the chosen blocks did not 
 JOURNAL OF FORESTRY SCIENCE AND TECHNOLOGY NO. 5 - 2017 133
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exceed 0.5 g. retention of each block. And the percentage of 
 The anionic rosin emulsion sizing agent (R) actual retention to the theory retention was 
was an industrial product and was supplied by regarded as the treatability of each preservative 
Guangxi Wuzhou Arakawa Chemical formulation. 
Industries Co., Ltd. In this study, it was used to 2.3. Leaching treated wood blocks 
impregnate into wood at the concentration of Leaching of boron was determined 
1%. And 3% Boric acid (H3BO3) was provided according to the standard of the American 
by Tianjin Kermel Chemical Reagent Co., Ltd., Wood Preservers’ Association E11 (AWPA 
was used as a preservative salts. It was also E11 2007). Twelve blocks per treatment were 
combined with the rosin emulsion sizing agent air-dried, then immersed in beakers of distilled 
to impregnate wood. water over which a vacuum was applied for 30 
2.2. Treating wood blocks min. Then the vacuum was released and the 
 Before treatment, all sapwood blocks were wood blocks were immersed in the distilled 
oven-dried at 103oC overnight, weighed to the water. After 6 h, 24 h, 48 h, and 48-h intervals 
nearest 0.01 g and recorded as W1. The blocks the leaching water was removed and replaced 
were then vacuum-treated with the treatment with an equal amount of fresh distilled water. 
solution. The vacuum was applied for 30 min Leaching was carried out for a total of 14 days. 
at 0.1 MPa before supplying the solution into All leachates were collected and kept for boron 
the chamber. After the application another 30 analysis. 
min at 0.1 MPa vacuum diffusion period 2.4. Boron analysis 
followed. Then, the blocks were kept in the In order to measure the contents of boron 
treatment solution at ambient conditions until leached from the treated wood blocks, the 
complete saturation. The blocks were then leachates were analyzed by using the 
individually removed from the solution, wiped azomethine-H method described by John et al. 
lightly to remove solution from the wood (1975) and following American Wood 
surface, and immediately weighed to the Preservers’ Association standard method 
nearest 0.01 g to determine the mass after AWPA A2-07. 
impregnation (W2). The theory retention of 2.5. Microscopic observation 
each block was calculated using the following Small samples of dimensions 10 × 10 × 1 
formula: mm were cut from the untreated control and 
 GC the treated wood blocks, and located 3 mm 
 Theory retention, kg/m 3 = 10 (1) 
 V from each radial, tangential, and transverse 
 Where G = W2-W1 is the weight in grams of surface of the wood block. Each sample was 
the treating solution absorbed by the block, C mounted on a metal stub with adhesive, and 
is the weight (g) of preservative in 100 grams then they were placed under vacuum and were 
of treating solution, and V is the volume of the sputter-coated with a thin layer (approximately 
block in cubic centimeters. 20 nm thick) of gold. The samples were then 
 After calculating the retention, the treated observed with a scanning electron microscope 
samples were air-dried for 48 hours, and oven- (SEM, FEI Quanta 200, USA) at an 
dried at 103 °C overnight, and then weighed to accelerating voltage of 20 kV. Random 
determine the dry weights of the wood blocks observations were made on different structures 
after treatment. The difference between the dry to identify the existence of boron in the 
weights before and after treatment is the actual anatomical structure of the samples. The 
134 JOURNAL OF FORESTRY SCIENCE AND TECHNOLOGY NO. 5 - 2017 
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element compositionwas determined by rosin sizing agent alone or boron-rosin 
regional analysis using an energy dispersive X- preservative was very close to theory retention. 
ray spectrometer (EDX) combined with the The actual percent retention of preservative 
SEM. solution containing rosin only or containing 
III. RESULTS AND DISCUSSION boric acid was 92.97% and 97.74%, 
3.1. Retention results respectively. However, when rosin sizing agent 
 Retention levels of Styrax tonkinensis combined with boric acid to impregnate wood, 
wood samples treated with boron-rosin the actual percent retention of presevative 
solutions (as kilograms per cubic meter) and solution was 96.41%. Results indicate that the 
the actual percent retention of preservative concentration of the solutions considered to 
formulations in wood blocks are recorded in impregnate Styrax tonkinensis wood using the 
Table 1. Total uptake of the treating solution in impregnation method described did not 
Styrax tonkinensis wood, including both rosin influence the penetration of the preservative 
alone and in combination with boron, were complexes into the wood blocks. Which could 
relatively uniform. The actual retention of the be proved by SEM analysis. 
 Table 1. Retention levels and treatability of wood samples treated with boron-rosin solutions 
 Theory Retention Actual Retention Treatabilitya 
 Abbreviation Concentrations 
 (kg/m3) (kg/m3) (%) 
 b
 1 1% R + 3% H3BO3 26.15 (1.07) 25.20 (2.77) 96.41 (10.31) 
 2 3% H3BO3 17.12 (0.97) 16.74 (1.66) 97.74 (7.71) 
 3 1% R 6.47 (0.47) 6.01 (0.68) 92.97 (9.59) 
 Note:aTreatability refers to the percentage of actual retention to the theory retention. 
 b All results are means of 24 samples. Standard deviations are in brackets. 
 Figure 1. Boron released from the treated wood samples at different time intervals 
 (BA: boric acid (H3BO3), R: rosin sizing agent) 
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3.2. Boron leaching These results suggest that the rosin can 
 The amount of boron ions released from the contribute to improving boron fixation in wood. 
wood samples treated with boric acid solution This was probably due to the hydrophobic 
alone or in combination with rosin at different property of rosin. After having penetrated into 
time intervals are presented in Figure 1. The the wood blocks, the rosin molecules present in 
results show that a large amount of boron ions the cell lumen and forming an adhesive lm 
was leached out from the wood samples treated that covers the boron crystals (Nguyen et al., 
with boric acid alone. After 14 days of 2013). During the leaching process, the rosin 
leaching, 1338 mg of boron was leached out acted as a barrier that slowed down boron 
from the samples. However, after 1% rosin release from deep inside of the samples, which 
sizing agent was added, the observed leaching resulted in the reduction of the boron ion 
of the boron was 1122 mg, in comparison to diffusing from wood during the leaching 
the treated samples with boric acid alone, the process. 
extent of boron leaching reduced was 16%. 
 a) b) 
 c) d) 
 Figure 2. SEM images of tangential section of control wood block (a) and boric acid alone (b), 
 rosin alone (c) and boron-rosin treated wood samples (d) 
136 JOURNAL OF FORESTRY SCIENCE AND TECHNOLOGY NO. 5 - 2017 
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3.3. Microscopic observation The spectrum obtained from the spot analysis 
 Figure 2 shows the SEM images of the confirmed that these agglomerates contained 
wood sample before and after treatment. the element B and they had a lower B content 
untreated control and wood samples treated in comparison to that observed in the crystal 
with boron-rosin solutions. It can be clearly particles (Fig. 3cd). This signifies easily 
seen that surface of wood cell wall of the penetrated into the wood blocks. 
control sample was extremely smooth and no Figure 4 shows SEM images corresponding 
preservative complexes was detected in any spectrum of tangential sections of treated wood 
part of the untreaed control wood blocks (Fig. blocks after leaching. For wood blocks treated 
2a). When the wood blocks treated with only with boric acid alone, after leaching no crystal 
boric acid were observed, various crystal particles was detected by SEM observation 
particles were found in the cell lumens (Fig. (Fig. 4a). This revealed that after leaching, 
2b). The spot analysis using SEM-EDX proved boric acid seemed to be completely leached out 
that these particles contained B (Fig. 3ab). from treated wood. However, when the leached 
When the wood blocks treated with rosin alone, wood blocks treated with boron-rosin were 
various spherical agglomerates were easily observed, the spherical agglomerates were still 
detected in the cell lumen (Fig. 2c). However, detected in the cell lumens (Fig. 4b). In 
unlike the crystals in Figure 2b or spherical addition, the spot analysis using SEM-EDX 
agglomerates in Figure 2c, various spherical proved that these agglomerates contained the 
agglomerates were easily detected in the cell element B (Fig. 4cd). This signi es that the 
lumen of the wood blocks treated with boron- rosin formed an adhesive lm to cover the 
rosin formulation, these agglomerates were boron crystals and the resulting boron was 
tightly adhered to the wood cell wall (Fig. 2d). xed into the wood blocks. 
 a) b) 
 c) d) 
 Figure 3. SEM images (left) and corresponding spectrum (right) of tangential section of unleached 
 wood blocks treated with boric acid alone (a,b) and boron-rosin solution (c,d) 
 JOURNAL OF FORESTRY SCIENCE AND TECHNOLOGY NO. 5 - 2017 137
 Forest Industry 
 a) b) 
 Element Wt% 
 BK 01.16 
 CK 61.66 
 OK 37.18 
 c) d) 
 Figure 4. SEM images and corresponding spectrum of tangential section of leached wood blocks 
 treated with boron alone (a) and boron-rosin solution (b, c, d). 
IV. CONCLUSIONS complexes containing B still existed in the cell 
 This study evaluated the effect of rosin lumens of wood, even after leaching. The use 
sizing agent on the fixation of boron in styrax of rosin as fixing agents may contribute to lead 
tonkinensis wood. The results showed that to wood treated with boron based preservatives 
using rosin alone or in combination with boric being more widely used. 
acid solution to impregnated Styrax tonkinensis Acknowledgements 
wood by the impregnation method described The authors are grateful for the support of 
did not influence the penetration of the the Vietnam National University of Forestry. 
preservative complexes into the wood blocks. REFERENCES 
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 ẢNH HƯỞNG CỦA KEO NHỰA THÔNG 
 ĐẾN KHẢ NĂNG CỐ ĐỊNH BORON TRONG GỖ BỒ ĐỀ 
 Nguyễn Thị Thanh Hiền1, Li Shujun2 
 1Trường Đại học Lâm nghiệp 
 2Trường Đại học Lâm nghiệp Đông Bắc, Trung Quốc 
 TÓM TẮT 
 Mục đích của nghiên cứu này là đánh giá ảnh hưởng của keo nhựa thông đến khả năng rửa trôi của boron từ gỗ 
 Bồ đề được xử lý bởi hỗn hợp của 3% axit boric và 1% keo nhựa thông. Các mẫu gỗ sau khi xử lý được quan 
 sát và phân tích bằng một phổ kế tán sắc năng lượng tia X kết hợp với kính hiển vi điện tử (SEM-EDX). Kết 
 quả cho thấy rằng tất cả các công thức boron - nhựa thông được ngâm tẩm vào gỗ Bồ đề đều thẩm thấu tốt vào 
 các mẫu gỗ thí nghiệm. Gỗ được xử lý bởi công thức kết hợp boron-nhựa thông đã giảm 16% lượng boron bị 
 rửa trôi so với khi chỉ sử dụng axit boric để xử lý. Kết quả phân tích SEM-EDX cũng đã chứng minh nguyên tố 
 B vẫn tồn tại trong khoang tế bào của gỗ được xử lý bởi boron-nhựa thông sau khi rửa trôi. Kết quả đã cho thấy 
 rằng dung dịch keo nhựa thông có một ảnh hưởng nhất định đến khả năng cố định boron trong gỗ. Điều này gợi 
 ý rằng sử dụng nhựa thông để làm chất cố định có thể góp phần nâng cao khả năng sử dụng của gỗ được xử lý 
 bởi các hợp chất chứa boron. 
 Từ khóa: Boron, boron-nhựa thông, kháng rửa trôi, nhựa thông. 
 Received : 22/3/2017 
 Revised : 27/4/2017 
 Accepted : 10/5/2017 
 JOURNAL OF FORESTRY SCIENCE AND TECHNOLOGY NO. 5 - 2017 139

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