ArticlePDF Available

The Effects of Outdoor Conditions on the Combustion Properties of Scotch Pine (Pinus Sylvestris L.) Wood

Authors:

Abstract and Figures

The wooden material, which is a light and durable material, has also undesirable properties such as contagion from outdoor conditions and combustion properties. This research is conducted with the intent of determining the combustion properties of wood material left in outdoor conditions for one year. For this purpose, samples prepared from scotch pine (Pinus sylvestris L.) according to ASTM-E 160-50 are first impregnated with tanalith-E (T) and wolmanit-CB (W-CB) in compliance with ASTM-D 1413-76, and then are varnished with synthetic (St) and water based (wb) varnish according to ASTM-D 3023. The weight loss, the collapse time in combustion, the total combustion duration, the temperature values in the combustion levels are identified by subjecting pieces, which are left in outdoor air conditions, to combustion tests according to the principles specified in ASTM G7-05 standard by the end of the year. According to the results, the impregnation materials have decreased the collapse time by %7-26 in the combustion, increased the total combustion duration by %14-34, and the varnishes have raised the collapse times and reduced the total combustion durations.
Content may be subject to copyright.
92
E. J. Engineering Sciences and Technology, Vol. 1:(2017),92-99.
http://www.cessciencegroup.com All rights reserved.
The Effects of Outdoor Conditions on the Combustion Properties of Scotch
Pine (Pinus Sylvestris L.) Wood
Ş. Şadiye YAŞAR1,*, Musa ATAR2, Mehmet YAŞAR1 and M. Said FIDAN3
1 The University of Gumushane, Gumushane Vocational High School, Department of Design, Gümüşhane/TURKEY
2 The University of Gazi, Faculty of Technology, Department of Wood Products Industry Engineering,
Ankara/TURKEY
3 The University of Bursa Technical University, Faculty of Forestry, Department of Forest Industry Engineering,
Bursa/TURKEY
*E-mail: ssyasar@gumushane.edu.tr
Received 03 April 2017; Accepted 26 May 2017
ABSTRACT
The wooden material, which is a light and durable material, has also undesirable
properties such as contagion from outdoor conditions and combustion properties. This research is
conducted with the intent of determining the combustion properties of wood material left in
outdoor conditions for one year. For this purpose, samples prepared from scotch pine (Pinus
sylvestris L.) according to ASTM-E 160-50 are first impregnated with tanalith-E (T) and
wolmanit-CB (W-CB) in compliance with ASTM-D 1413-76, and then are varnished with
synthetic (St) and water based (wb) varnish according to ASTM-D 3023. The weight loss, the
collapse time in combustion, the total combustion duration, the temperature values in the
combustion levels are identified by subjecting pieces, which are left in outdoor air conditions, to
combustion tests according to the principles specified in ASTM G7-05 standard by the end of the
year. According to the results, the impregnation materials have decreased the collapse time by
%7-26 in the combustion, increased the total combustion duration by %14-34, and the varnishes
have raised the collapse times and reduced the total combustion durations.
Keywords: Combustion, wood, impregnation, varnish, gases analysis, outdoor
conditions.
1.Introduction
The wooden material is a highly-preferred material because of its durability and
naturalness. The wooden material can be preserved for centuries when appropriate conditions are
provided. It is observed that various furniture made of wood, such as a bed, a cabinet, has
93
S.S.. Yasar et al. / E. J. Engineering Sciences and Technology, 1 (2017) 92-99
survived until today as undisturbed in the grave of the Egyptian Pharaoh Tutankhamen
(Desroches, 1963).
Increasing the usage life of this precious material can only be achieved through protecting
it against fire, chemical degradation, mechanical weathering, outdoor weather conditions and
conservation from biological pests (Archer & Lebow, 2006) .
The wooden material is disfigured by outdoor weather conditions like humidity, sunlight, acid
degradation, temperature and the wind. Sapwood samples of southern pine have an average life
span of 1.8-3.6 years in open air conditions without projection, 45 years with copper oxide, 25
years with CCA, 55 years with coal tar creosote, and 29,6 years with copper naphthenate
(Crawford et al., 2002)
Nowadays, commercial protectors have been developed for the protection of wooden
materials. The permanence of the protective materials has a high importance. In our day, greased
preservative substances like creosote and pentachlorophenol, and waterborne salt preservative
substances like chlorinated copper arsenate (CCA), amine-copper quaternary (ACQ), copper-
chrome-boron (CCB), copper-potassium bichromate-boric acid (Wolmanit-CB) are applied as
water solutions. There are many factors such as the amount of concentration, temperature and
amount of pressure which affect the activity of these impregnation materials (Baysal et al., 2007;
Toker et al., 2009; Percin, 2015)
Nowadays, chemicals such as borax, boric acid, ammonium, phosphorus and nitrogen are
used to prevent the combustion of wooden material and to delay it. However, the biggest
diffculties in these formulations are water erosion and leaking inconveniences (Rowell &
Dietenberger, 2005).
Baysal et al. state that he has applied the Turkish pine and Poinciana wood, which are treated
with a mixture of boric acid and borax mixture before varnishing procedure, with phrases of the
combustion with flame, combustion without flame source and ember combustion phase according
to ASTM 160-50 standard. The best results are obtained only in test samples impregnated with
boric acid and borax mixture (BA + BX) with regard to combustion properties. (Baysal et al.,
2003). The retention amount of Abies Nordmanniana fir impregnated with water-based
preservatives and copper-based preservatives such as tanalith-E, wolmanit-CB and ACQ has
shown an increase in comparison with concentration amounts (Cavdar, 2014).
Atar et al. (2015) have stated that after the impregnation of Scotch pine (Pinus sylvestris
Lipsky) wood with boric acid and borax, it is coated with cellulosic, synthetic, polyurathane,
waterborne, acrylic and acid hardening varnishes. Combustion temperature is highest in the
Borax and waterborne in combustion with flame according to material and process type (Atar et
al., 2015)
The highest measured weight loss during combustion of Sapele tree impregnated with Tanalith-E,
immersol aqua borax and boric acid is obtained in control samples impregnated with Tanalith-E.
Tanalirh-E + water-based varnish has shown the highest values in the average combustion
temperature. It is concluded that water-based varnishes accelerate combustion (Uysal et al.,
2011).
94
S.S.. Yasar et al. / E. J. Engineering Sciences and Technology, 1 (2017) 92-99
2. Material and Methods
Scotch pine (Pinus sylvestris L.) samples are selected from Trabzon region with the
coincident method. Impregnation material, Tanalith-E is supplied from Hemel and Wolmanit-CB
is provided from Ramtaş-Emsan Korusan. Tanalith-E is a material which is used as water-based
with copper triazole solution (Hemel, 2017). The combination of Wolmanit-CB contains 28 %
copper sulphate, 48 % potassium bichromate, 24 % boric acid (Bozkurt et al., 1993). Aqua
Compact Lasur brand water-based varnish and Wood Art brand synthetic varnish are applied
during the varnishing stage. Wolmanit-CB and Tanalith-E impregnation materials have been
impregnated to the wood material according to ASTM-D 1413-76 principles (vacuum-pressure).
The impregnated materials are left in an air recirculating room for 20 days for evaporation of the
dissolvent agents. It is held at the relative humidity of 65 ± 3% at 20 ± 2 ° C to reach the constant
moisture. Retention amounts (R) of impregnation materials are as follows.
3
10
G.C
= R
V
(kg/m3), (1)
G= T1 T2
Here, G is the amount of impregnation solution absorbed by the sample, T1 is the
specimen weight after the impregnation, T2 is the specimen weight before the impregnation. C is
the concentration (%) of the impregnation solution and V is the volume of the samples.
The retention amounts and solution concentrations of impregnation materials are shown in Table
1. The principals specified in ASTM-D 3023 are followed in the varnishing of the
acclimatised samples after impregnation. The instructions of the producing companies are
complied with in the application of varnishes. After the implementation, samples are kept at
room temperature.
The varnished samples are left in open air conditions for one year with respect to the
principles stated in ASTM G7-05 standard. The samples are placed on the test stand with an
angle of 45 ° with their surfaces facing south. The combustion characteristics of the samples
received from the outside air are measured in the combustion testing device, which is shown in
Figure 1, by following the ASTM E 160-50 principles. Before the combustion test, each sample
group is weighed and a total of 24 pieces overlapping in 12 layers with 2 rows are stacked on top
of the wire table in the machine. The fire source is placed in the center of the stack at the bottom.
After combustion has occurred for 3 minutes while the fire source is open, it is switched off and
combustion without flame source and combustion during ember combustion phase are carried
out. Temperature changes (° C) are measured regularly from a thermometer for 15 seconds on the
combustion with flame, and for 30 seconds on the Combustion without flame source and ember
combustion phase.
95
S.S.. Yasar et al. / E. J. Engineering Sciences and Technology, 1 (2017) 92-99
Figure 1. Fire test apparatus (Temiz et al., 2008)
For all parameters, multiple variance analysis (ANOVA) and least significant difference
test (LSD) performed with SPSS 20 are used.
3. Results and Discussion
The retention amounts and solution concentrations are given in Table 1.
Table 1. Mean retention of the test samples used in the experiments.
Impregnation Material
Retention (kg/m3)
Concentration (%)
Tanalith-E
2,47
2,4
Wolmanit-CB
2,90
4
Studies showing that solution amount of impregnation materials increases the retention
amount are available. The high concentration of Wolmanit-CB may have led to increase in the
retention amount (Temiz et al., 2008).
Results of variance analysis are given in Tab. 2. According to variance analysis, the
impact of impregnation material and the type of varnish has been found to be significant except
for TC’ s double interaction (P<0.05).
The mean result values of the of the LSD test are given in Table 3. The graph of the change in
combustion temperatures is given in Figure 2.
96
S.S.. Yasar et al. / E. J. Engineering Sciences and Technology, 1 (2017) 92-99
Table 2. Results of the analysis of variance for the temperature of combustion, illuminance, the
duration of combustion and weight loss ratios
Combustion With Flame(CWF)
Combustion Without Flame Source(CWOF)
F.D.
S.S.
S.M.
F.V
P.V*
F.D.
S.S.
S.M.
F.V
P.V*
im
2
766,500
383,250
34,359
0,000
2
256,500
128,250
8,679
0,002
vt
2
326,625
163,312
14,641
0,000
2
1771,875
885,938
59,951
0,000
im*vt
4
1617,375
404,344
36,250
0,000
4
1562,625
390,656
26,435
0,000
Error
18
200,778
11,154
18
266,000
14,778
Total
26
2911,278
26
3857,000
Ember Combustion Phase(ECP)
Weight Loss (WL) (%)
F.D.
S.S.
S.M.
F.V
P.V*
F.D.
S.S.
S.M.
F.V
P.V*
im
2
26497,125
13248,563
66,409
0,000
2
1,165
0,582
9,526
0,002
vt
2
11127,375
5563,687
27,888
0,000
2
1,418
0,709
11,595
0,001
im*vt
4
10854,000
2713,500
13,602
0,000
4
12,273
3,068
50,190
0,000
Error
18
3591,000
199,500
18
1,100
0,061
Total
26
52069,500
26
15,956
Total Time of Combustion (TC)
Demolition Time (DT)
F.D.
S.S.
S.M.
F.V
P.V*
F.D.
S.S.
S.M.
F.V
P.V*
im
2
142340,625
71170,312
72,582
0,000
2
1822753,125
911376563
37,299
0,000
vt
2
89184,375
44592,188
45,476
0,000
2
2103721,875
1051860,937
43,048
0,000
im*vt
4
6750,000
1687,500
1,721
*0,189
4
2011078,125
500769,531
20,576
0,000
Error
18
17650,000
980,556
18
439818,750
24434,375
Total
26
255925,000
26
6377371,875
im: impregnating material, vt: types of varnish, F.D: Degrees of Freedom, S.S: Sum of Squares, S.M: Mean of Squares, F.V: F Value
(<0.005)
Table 3. Mean values of the weight loss, combustion temperatures, combustion durations, and
the groups resulting from the least significant difference (LSD) analysis
Factor
WL
(%)
Temperature Values (Co)
Combustion Time (sec.)
CWF
CWOF
ECP
TC
DT
Impregnation Materials
(IM)
Wolmanit-CB (W-CB)
92,6
458,9
549,3
298,8
621,7
2146
Tanalith-E (T)
92
466,4
541,8
363,3*
497,9
2514
Nimp
92,5
453,4
544,8
295
670,4
1880
Varnish Types
(VT)
Synthetic (Syn)
92,5
459,9
534,1
290,5
677,9*
2353
Water-Based (Wb)
92,1
455,1
552,8*
336,3
557,9
1786
Nvar
92,6
463,6
549,1
330,3
554,2
2401
IM+VT
W-CB+Syn
91,4
460,6
538,3
274,8
700,4
1940
W-CB+Wb
92,6
446,4
546,6
304
587,9
1805
T+Syn
92,8*
467,4
536,1
313,8
587,9
3099*
T+Wb
91,2
474,9*
557,1
419,5
430,4
1794
Nimp: None impregnated Nvar: None varnished, WL: Weight Loss, CWF: Combustion With Flame, CWOF: Combustion Withou Flame
Sourcet, ECP: Flame, Ember Combustion Phase, TC: Total Time of Combustion, DT: Demolition Time, * : maximum values
97
S.S.. Yasar et al. / E. J. Engineering Sciences and Technology, 1 (2017) 92-99
The lowest weight loss has shown up in T+Wb, the highest has shown up in T+Syn. The
highest combustion with flame temperature (CWF) has been observed in T+Wb, the lowest has
observed in W-CB+Wb. In the combustion without flame source (CWOF), Wb has resulted in the
highest temperature, Syn has shown the lowest results. In the Ember Combustion Phase (ECP),
the highest results are obtained in T+Wb, the lowest ones are obtained W-CB+Syn. The total
combustion duration values (TC) are determined as highest in W-CB+Syn, as lowest in T+Wb.
The demolition time (DT) values are found highest in T+Syn, lowest in Wb.
200
300
400
500
600
W-CB
T
Nimp
Syn
Wb
Nvar
W-CB + Syn
W-CB + Wb
T + Syn
T + Wb
Combustion Temperatures (Co)
CWF
CWOF
ECP
Figure 2. Combustion with flame, combustion without flame source and ember combustion
phase temperature changes
4.Conclusions
The impregnation materials have increased temperature values when used alone in
proportion to the control samples. Wolmanit-CB has shown lower temperatures at combustion
temperatures when compared with Tanalit-E. The varnish type has been more effective in the
combustion without flame stage. Better results have been obtained from synthetic varnishes, one
of varnish types. The combustion temperatures have increased in the water-based varnishes
compared with control samples. Even though it has demolished early, Tanalith-E + synthetic
varnish has continued to burn ember combustion phase. The Tanalit-E + water-based varnish duo
has been extracted early while showing high temperatures.
The impregnation material and varnish choice affects the combustion properties of wooden
material. Wolmanit-CB can be recommended as impregnation material, synthetic varnish can be
recommended as a type of varnish for especially places which are exposed to outdoor weather
conditions with the risk of burning.
98
S.S.. Yasar et al. / E. J. Engineering Sciences and Technology, 1 (2017) 92-99
Acknowledgments
This research has been constituted from some sections of doctoral thesis of Şadiye
YAŞAR prepared under the supervision of Prof. Dr. Musa ATAR in Gazi University Institute of
science and technology in April 2015. This study was presented as an oral presentation at the
International Conference on Agriculture Forest Food Sciences and Technologies (ICAFOF 2017),
15-17 May 2017, Cappadocia, Turkey.
References
ASTM-E 160-50. 1975. Standart test method for combustible properties of terated wood by the
crib test. ASTM Standards, USA.
ASTM-D 1413-07. 2007. Standard test method of testing wood preservatives by laboratory
soilblock cultures. ASTM Standards. USA, 1-9.
ASTM-D 3023. 1988. Practica for determination of resistance of factory applied coatings of
wood products of stain and reagents. ASTM Standards, USA.
ASTM G7-05. 2005. Standard practice for atmospheric environmental exposure testing of
nonmetallic materials. ASTM Standards, USA, 2-10.
Archer K. & Lebow S. 2006. Wood preservation. Primary Wood Processing Principles and
Practice, Chapter 9, 2nd edition, pp 297-338, https://doi.org/10.1007/1-4020-4393-7_9
Atar M., Döngel N. & Cinar H. 2015. An analysis of varnish and ımpregnation processes for
combustion temperature of Scotch Pine. Materials Sciences and Applications, 6,78-85.
Baysal E., Peker H., Colak M., Goktas O. & Tarimer I. 2003. Varnished wood material
combustion characteristics and combustion Retardant Effect of Boron Operations with Pre-
Impregnated Compounds. Firat University Journal of Science and Engineering, 15(4), 645-
653.
Baysal E., Yalinkilic M.K., Altinok M., Sönmez A., Peker H. & Colak M. 2007. Some physical,
biological, mechanical, and fire properties of wood polymer composite (WPC) pretreated
with boric acid and borax mixture. Construction and Building Materials, 21 18791885,
Bozkurt Y., Goker Y. & Erdin N., 1993. Impregnation technique. Faculty of Forestry.
Publications, Istanbul, 3779 -425 :125, 135.
Cavdar A.F. 2014. Effect of various wood preservatives on limiting oxygen index levels of fir
wood. Measurement, 50, 279-284.
Crawford D.M., Woodward B.M. & Hatfield C.A. 2002. Comparison of Wood Preservatives in
Stake Tests. 2000 Progress Report. Res. Note FPL-RN-02. U.S. Department of Agriculture,
Forest Service, Forest Products Laboratory: Madison, WI.
Desroches N.C. 1963. Tutankhamen. New York Graphic Society, New York.
Hemel Product Catalog. 2017 website. [Online]. Available from URL: http://hemel.com.tr
Percin O. 2015. Impact of various chemicals on combustion properties of heat-treated and
impregnated laminated veneer lumber (lvl)”, Wood Research, 60(5): 801-814.
Rowell R.M. & Dietenberger M.A. 2005. Handbook of wood chemistry and wood composites,
CRC press, USA, p. 128-147, (Chapter 6).
Temiz A., Gezer E.D., Yildiz U.C., & Yildiz S. 2008. Combustion properties of alder (Alnus
glutinosa L.) Gaertn. subsp. barbata (C.A. Mey) Yalt.) and southern pine (Pinus sylvestris L.)
99
wood treated with boron compounds. Construction and Building Materials, 22(11),
November, p. 21652169. DOI: 10.1016 / j.conbuildmat.2007.08.011
Toker H., Baysal E., Sımsek H., Senel A., Sonmez A., Altinok M., Ozcıfcı A. & Yapıcı F. 2009.
Effects of some environmentally-friendly fire-retardant boron compounds on modulus of
rupture and modulus of elasticity of wood. Wood Research, 54, pp.77-88 ref.26.
Uysal B., Kurt S., Esen R., Ozcan C., Yildirim M.N. & Kilinc I. 2011. Some chemicals
impregnated with Sapele wood is applied on top of the combustion process to the Effects of
Surface Resistance. 6th International Advanced Technologies Symposium (IATS’11), Elazıg.
... This may be due to the removal of some volatile organic materials in the wood during the heat treatment. Müllerová [11] reported that wood material contains organic and inorganic matters and total volatile [34] also reported that impregnation chemicals effects the combustion characteristics of wood material. In a similar study, Čekovsá et al. [35] studied that higher heat treatment temperatures caused higher combustion rate on spruce specimens and burning stopped suddenly with the removal of the flame source during combustion. ...
Article
Full-text available
The use of heat-treated wood material and eco-friendly impregnation chemicals are steadily increasing in the woodworking industry over the last decades. In this study, the effects of applications of impregnation and heat treatment on combustion properties of Hornbeam (Carpinus betulus L.) wood were investigated. The test specimens were impregnated with Imersol-aqua (Ia) and Timbercare-aqua (Ta) impregnation material according to ASTM D 1413-76 standards. Impregnated specimens were subjected to heat treatment at 150, 170 and 190 °C for 2 h. The temperature of flame source combustion, the temperature of without flame source combustion and varying light intensities (Lux) depending on the smoke production in these combustion stages were determined according to ASTM E 160-50. According to the test results, the highest combustion temperature of flame source combustion was determined in unimpregnated and heat-treated samples at 190 °C, while the highest combustion temperature of without flame source combustion was determined in impregnated with Ta and heat-treated samples at 170 °C. The highest light density in flame source combustion phase was determined in unimpregnated and heat-treated samples at 190°C, while in without flame source combustion was in unimpregnated and heat-treated samples at 170°C. As a result, as the heat treatment temperature increase, the combustion temperature increased and the smoke density decreased. In addition to impregnation materials increased the smoke density while reduced the combustion temperatures of test specimens.
Article
Full-text available
This study was performed to determine the effects of varnishing after impregnation with boron compounds on the combustion properties of Scotch pine. For this purpose, test samples prepared from Scotch pine (Pinus sylvestris Lipsky) wood were impregnated according to ASTM-D 1413-99 standard with boric acid (Ba) and borax (Bx) by vacuum technique. After impregnation, surfaces were coated by cellulosic (Cv), synthetic (Sn), polyurathane (Pu), waterborne (Wb), acrylic (Ac) and acid hardening (Ah) varnishes in accordance with ASTM D-3023 standard and then, combustion temperature was determined. According to material and process type, combustion temperature was the highest in Bx and Wb in flame source combustion (FSC), the lowest in Ba and Ac without flame source combustion (WFSC). According to combustion type, impregnation material and varnish type, combustion temperature was the highest in FSC, borax and cellulosic varnish combination and the lowest in WFSC, boric acid and acid hardening varnish combination. In conclusion , impregnation materials decrease while varnishes increase the combustion temperature of Scotch pine wood.
Book
Full-text available
The degradable nature of high-performance, wood-based materials is an attractive advantage when considering environmental factors such as sustainability, recycling, and energy/resource conservation. The Handbook of Wood Chemistry and Wood Composites provides an excellent guide to the latest concepts and technologies in wood chemistry and bio-based composites. The book analyzes the chemical composition and physical properties of wood cellulose and its response to natural processes of degradation. It describes safe and effective chemical modifications to strengthen wood against biological, chemical, and mechanical degradation without using toxic, leachable, or corrosive chemicals. Expert researchers provide insightful analyses of the types of chemical modifications applied to polymer cell walls in wood, emphasizing the mechanisms of reaction involved and resulting changes in performance properties. These include modifications that increase water repellency, fire retardancy, and resistance to ultraviolet
Article
This study was designed to determine some mechanical properties such as modulus of rupture (MOR) and modulus of elasticity (MOE) of wood treated with some environmentally-friendly fire-retardant boron compounds. Sodium perborate (SP) boric acid, (BA), and borax (BX) were used as boron compounds. Wood specimens were prepared from Calabrian pine (Pinus brutiaTen.) and beech (Fagus orientalis Lipski) wood. Before MOR and MOE tests, wood specimens were impregnated with aqueous solutions (1,2, 3,4, 5, and 6 %) of borates according to ASTM D 1413-76. Our results showed that MOR values of wood specimens treated with borates were lower compared to untreated control specimens. The MOR and MOE values of wood specimens were the lowest for treatments with SP followed by BX and BA, respectively. In general, the higher concentration levels of borates, the lower MOR of wood resulted.
Article
Wood preservatives have been widely used to extend the service life of wood. The aim of this study is to evaluate the effects of various wood preservatives with different chemical loadings on fire performance of treated fir wood using by oxygen index test technique (ASTM D 2863-6). The limiting oxygen index (LOI) is the minimum percentage oxygen that is required to continue flaming combustion of a sample under laboratory conditions. For this purpose; wood preservatives commonly used in wood protection industry including amine–copper-quaternary, tanalith-E, wolmanit-CB, imersol aqua, vacsol aqua, timbercare aqua and protim-418 were studied as wood preservative chemicals. Mixture of boric acid + borax was also used as reference sample. The results indicated that LOI levels of all treated fir wood samples were higher than that of control samples except for timbercare aqua and protim-418 treated samples. The highest LOI level was obtained within 5% of wolmanit-CB and 2% of boric acid + borax treated wood samples. It appears that more than 3% concentration of wolmanit-CB treatment may have a potential fire retardant.
Article
Wood polymer composite (WPC) was obtained by vinyl monomers such as styrene (ST), methylmethacrylate (MMA), and their mixture (50:50; volume:volume) of treated sapwood of Scots pine (Pinus sylvestris L.). Boric acid (BA) and borax (BX) mixture was impregnated into wood at 1% concentration prior to monomer treatment. Wood polymer composite with and without BA and BX mixture pretreatment was evaluated in terms of some physical, biological, mechanical, and fire properties.Vinyl monomers considerably improved physical properties of wood such as increased antiswelling efficiency (ASE), specific gravity (SG), and reduced water absorption (WA) levels of wood. Modulus of elasticity (MOE) and modulus of rupture (MOR) were also higher than that of untreated control specimens. The treated wood proved to be resistant against decay fungi, Tyromycetes palustris and Coriolus versicolor. Boric acid and borax mixture pretreatment imparted WPC total resistance against both decay fungi. Although, ASE, MOE, and MOR levels of WPC pretreated with BA and BX mixture were reduced in some extent, it improved fire resistance of wood.
Article
Samples from alder (Alnus glutinosa L.) Gaertn. subsp. barbata (C.A. Mey) Yalt.) and southern pine (Pinus sylvestris L.) wood were impregnated with boric acid, borax and their mixed solutions according to ASTM D 1413-88 in order to determine their combustion properties.In this study, the fire resistance properties of wood treated with boron compounds were investigated. In addition, the models for each wood species and fire retardant solution were also determined. The results demonstrated that the lowest mass losses for both alder and southern pine specimens treated with a mixture of 5% boric acid and borax aqueous solutions were found to be 68.72% and 72.37%, respectively. It was found that 5% of borax was the most effective treatment in terms of lengthening the time of glowing.
Chapter
Wood preservation can be interpreted to mean protection from fire, chemical degradation, mechanical wear, weathering, as well as biological attack. In this chapter, the term preservation is applied more restrictively to protection from biological hazards and the reader is directed to one of several references (Feist and Hon 1984; Hon and Shiraishi, 2000; USDA, 1999) for a more extensive discussion of non-biological aspects of wood protection. Most people accept that because wood is of biological origin it must be a perishable material. In contrast, man made materials such as concrete and steel are generally considered to be more durable and permanent. The non-durability of wood is often cited as being one of its greatest disadvantages when compared to other building materials. The premature degradation of solid timber and wood-based composite products costs the consumer substantial amounts of money. Indeed in the United States alone the annual financial losses attributed to fungal decay of timber have been estimated to be well in excess of five billion dollars (Lee et al., 2004). Estimates of the damage just caused by termites in the United States range from 750-3,400 million dollars, and these estimates can be doubled if the damage caused by other wood-destroying insects and fungi are included (Williams, 1990). Much of this loss is avoidable. The first line of defense is the use of construction techniques that minimize the exposure of wood to conditions that favour biodeterioration. Usually this means keeping it dry. Where such construction is not practical, wood preservation techniques can greatly extend the service life of wood. The use of preservative chemicals and treated wood has been and still is sometimes criticized on the basis of health or environmental concerns. Ignorance on the part of the treating industry, poor work practices and lax environmental regulation all share part of the blame for that negative perception. Innovation in the first half of the 20th century led to the development of more effective wood protecting chemicals and processing techniques that turned a specialty industry into a commodity business (Preston, 2000). As can happen in all commodity businesses, research and development was not sustained when profit margins began to fall and the door was opened for competitive products such as plastics, concrete and steel. Some countries, such as New Zealand, have a well established and regulated timber preservation industry and the benefits of construction with treated timber are well appreciated by the public at large. This is not so true of the United States or Europe where treated wood for residential decking and other consumer applications is losing market share to man made materials such as plastics (Clemons, 2002). The old adage familiarity breeds contempt might certainly be applied to wood preservation in recent years. The construction industry, building code enforcement and the public at large have come to expect extended lifetimes for wood-based building components while forgetting how that longevity is achieved. In New Zealand in 1998 an ill-advised decision to allow untreated house frames coincided with a trend toward monolithic cladding systems which aided by inadequate design/ detailing and coupled with poor construction practices resulted in a leaky building crisis. The failure was in the weather tightness of the external envelope arising from the rigidity of the panels and the movement of the underlying timber, from poor detailing or even the absence of flashings around openings, and in poor performance of jointing materials. This allowed egress of water with no means of drying out any wet elements within the enclosed wall cavity. The problem was systemic, with the way the components were put together rather than poor performance of an identified product. While blame was diffuse the reputation of timber framing suffered. The inference is that timber treatment is not a solitary activity and needs to be seen in the context of building design and construction practices. Preservative treatment should not be used to compensate for loss of eaves, omission of flashings, abuse of sealants, moisture entry into concealed spaces with nowhere to drain etc. Sadly the problem has been evident elsewhere, in Canada, the U.S. and Europe. Moving into the 21st century the wood preservation industry is of necessity facing a major overhaul. Health and safety concerns are being alleviated through a transition to less toxic chemicals. Environmental concerns with preservative treatments are counter-balanced by their ability to extend the durability of wood products, allowing conservation of forest resources. New preservative chemistries have been developed to target specific wood biodeteriogens. While other construction materials could substitute for wood in many applications, such materials are generally more expensive and require more energy to produce (Cassens et al., 1995). In that regard, life cycle analysis concepts are being used to promote the virtues of wood preservation (Hillier and Murphy, 2000). Best management practice concepts are also being adopted by the wood preservation industry (Anon., 1996). Wood is no longer being over treated, efforts are being taken to minimize dripping after treatment and surface residues are no longer an issue. Innovative processes and preservative chemistries are being developed to protect wood-based composites such as oriented strand board and medium density fibre board further expanding the universe of wood protection. In short the future for preservative treated wood is a positive one.
Standard test method of testing wood preservatives by laboratory soilblock cultures
  • Astm-D
ASTM-D 1413-07. 2007. Standard test method of testing wood preservatives by laboratory soilblock cultures. ASTM Standards. USA, 1-9.
Varnished wood material combustion characteristics and combustion Retardant Effect of Boron Operations with Pre-Impregnated Compounds
  • E Baysal
  • H Peker
  • M Colak
  • O Goktas
  • I Tarimer
Baysal E., Peker H., Colak M., Goktas O. & Tarimer I. 2003. Varnished wood material combustion characteristics and combustion Retardant Effect of Boron Operations with Pre-Impregnated Compounds. Firat University Journal of Science and Engineering, 15(4), 645-653.
Comparison of Wood Preservatives in Stake Tests
  • D M Crawford
  • B M Woodward
  • C A Hatfield
Crawford D.M., Woodward B.M. & Hatfield C.A. 2002. Comparison of Wood Preservatives in Stake Tests. 2000 Progress Report. Res. Note FPL-RN-02. U.S. Department of Agriculture, Forest Service, Forest Products Laboratory: Madison, WI.