Introduction
There is some concern that metal-containing wood preservatives cause environmental degradation or affect human health. A few review articles have been published about usage of natural oils and extracts in wood protection (Evans 2003, Yang 2009, Singh and Singh 2012, González-Laredo et al. 2015). From this perspective, some natural compounds that have bioactive properties can be an attractive alternative for wood protection (Singh and Singh 2012) On the other hand, González-Laredo et al. (2015) noted that “it continues to be imperative developing sustainable technologies for protecting wood and wood products from biodegradation with a minimum environmental impact. It is expected that at some point the totally organic systems will be required for wood products in residential uses”. However, the performance difference between laboratory and field tests of natural preservatives has limited the commercial use of these substances (González-Laredo et al. 2015). In another aspect, it is stated that there are few limiting factors for the use of natural products in the preservation of wood, on the contrary, that there is a great potential for the evaluation of natural compounds such as wood preservatives (Singh and Singh 2012). In another review article, it is stated that natural compounds exhibit promising results, but they cannot compete with industrial wood preservatives in terms of current requirements in the wood preservation industry, low cost and long-term durability (Yang 2009).
In a preliminary study, heartwood extracts of very durable tropical hardwood species were found effective in preventing fungal attack (Onuorah 2000). In another preliminary study, Nakayama et al. (2001) noted that “the resin material extracted from the guayule plant has both insect and microbial resistance properties”. The common sources of the natural compounds are extracts from bark, extracts from heartwood of durable wood species, and extracts from seed, fruit and herbaceous plants (Yang 2009). Some natural oils and food additives have been reported to be effective in preventing decay mechanism, and termite attack (Kartal et al. 2006). Poisonous extracts from oleanders were found effective against some decay fungi (Goktas et al. 2007). Alkaloids from Sophora flavescens (Leguminosae) have proved highly effective against Formosan subterranean termites (Mao and Henderson 2007). Sen et al. (2009) conducted laboratory tests of effectiveness of some commercial extracts from fruit of valonia oak, sumac leaves, and pine bark as antifungal agents on beech and scotch pine woods. On the other hand, Abdul-Khalil et al. (2009) suggested that antioxidants in the bark of mangrove plant Rhizophora apiculata played an important role in preventing of termite attack. In a recent study, natural compounds extracted from the bark of mimosa and quebracho woods provided anti-termite potential as environmental wood protection agents for indoor applications (Tascioglu et al. 2012). In another recent study, it was also reported that the same natural extracts could protect wood against decay fungi (Tascioglu et al. 2013). Recently, some articles have been published regarding the evaluation of various natural resources as wood preservatives. It was investigated the effect of essential oils obtained from Atlas cedar wood sawdust against four decay fungi and determined that these extractive agents could prevent fungal decay (Fidah et al. 2016). In other recent study, the toxic effects of some Malaysian timbers heartwood extracts have been studied against some termite species and showed that high termite mortality was only achieved with Madhuca utilis extracts and methanol solvents (Kadir 2017). Bajraktari et al. (2018) determined the extractive content of Turkey oak (Quercus cerris) and showed that comparatively low amount of phenolics and tannins in comparison with other oaks (Bajraktari et al. 2018). The effectiveness of heartwood extracts of two Morus species against termites has been investigated and these substances have been found to be effective in preventing termite activity (Hassan et al. 2019).
It is known that lichens and mistletoe have bioactive properties. Bioactive natural products from lichens have been utilized for medicinal and cosmetic applications throughout history. The anti-microbial properties of usnic acid, one of the secondary metabolites of lichens, have been proven (Cocchietto et al. 2002). Six lichen species containing usnic acid in various quantities were found to be effective against different bacteria (Cansaran et al. 2006). On the other hand, biologically active compounds of mistletoe have been reviewed (Ochocka and Piotrowski 2002). Ertürk et al. (2004) evaluated anti-microbial effectiveness of mistletoe (Viscum album L.) against six bacteria and a fungus, and found that different concentration of n-hexane extracts of mistletoe was effective against micro-organisms tested. The objective of this research was to evaluate the possibilities of using lichen (Usnea filipendula) and mistletoe (Viscum album L.) extracts as natural wood preservative.
Material and methods
Wood materials
Wood specimens measuring 1,5 (T) x 0,5 (R) x 2,5 (L) cm were prepared from sound sapwood of Scotch pine (Pinus sylvestris L.) which met requirements of ASTM D-1413 (1988). The wood specimens were conditioned at (20 ± 2) °C and (65 ± 3) % relative humidity for 2 weeks.
Plant material
Lichen (Usnea filipendula) was collected from wild areas in Trabzon province Tonya district (Figure 1). Mistletoe (Viscum album L.) was collected from Trabzon province Sürmene district located in the north-eastern of Turkey (Figure 2). The plants were brought to laboratory for extraction.
Preparation of treatment solutions
Lichen and leaves of mistletoe were dried in an oven at 60°C at 24 hours before grinding. A laboratory scale Wiley mill was utilized to grind the coarse particles further until they pass through a 60-mesh screen for the subsequent (1) hot water, and (2) methanol extraction process (Figure 3 and Figure 4). For hot water extraction, solutions were prepared with distilled water at 3%, 5%, 10%, 15% (by weight) concentration levels from all fine powders. The prepared solutions were subjected to hot water extraction on a hot plate at 80 °C for a period of 2 hours under continuous stirring with a magnetic stirrer. For methanol extraction, in order to obtain methanol solutions at 3,75%; 6,25%; 12,5%; 18,75% concentration levels, 2, 6, 10 and 14g of plant powders were placed into a falcon tube. Then, methanol (99%) was added to the tube and the mixture was stirred continuously with a shaker (Heidolph Promax 2020, Schwabach, Germany) at room temperature for a total of 2 hours. The difference in concentration between hot water solutions and methanol solutions is due to the specific gravity difference between water and methanol. However, the amount of active chemical substance (plant powder) used in each solution is the same. As the basic value that should be taken into consideration here is the amount of active chemical, it can be stated that the small differences between the solution concentrations can be neglected. All extracted solutions were filtrated by Whatman No:4 after cooling for subsequent treatments. Since the concentration values expressed herein are not the concentration of impregnation solution but the concentration of the extraction solution, the retentions thus obtained are also retentions of the extraction solution.
Treatment method
The treatment procedure was applied according to the ASTM D-1413 (1988) standard test method. The whole experiment was performed with ten repetitions. The samples were impregnated in a medium scale impregnation container using a vacuum of 635 mm of Hg for 40 min followed by 15 min atmospheric pressure. Treated samples were then removed from the treatment solution, wiped lightly to remove solution from the wood surface, and weighed to the nearest 0,01 g to determine the retention of each solution.
Untreated blocks were used as controls. The retention for each concentration was calculated using the following Equation 1 and Equation 2:
Where:
R1: is the retention in kg per cubic meter
R2: is the retention in percentage
G = (T2 - T1): grams of treatment solution absorbed by the wood specimen (initial weight of specimen subtracted from initial weight plus the treatment solutions absorbed),
C: grams of extracted solution in 100 g of the treatment solution
V: volume of specimen in cubic centimeters
T2: sample of weight after treatment
T1: sample of weight before treatment
The treated wood blocks were stored in a conditioning room at (20 ± 2) °C and (65 ± 3) °C relative humidity until they reach stable weight before the decay resistance tests.
Decay resistance test
The fungal decay test was done according to the EN 113 (1996) standard test method using a brown rot fungus, Coniophora puteana for both treated test and untreated control samples. Four replicates for each treatment were used. The incubation time was approximately 7 weeks at 22 °C and 70 % relative humidity. After incubation, the samples were dried at temperature of (103 ± 2) °C, weighed and the mass loss caused due to fungal attack calculated as follows (Equation 3):
Where:
Results and discussion
Retention
R1 (kg/m3) retention levels of treated Scotch pine are shown Figure 6 and Figure 7. R1 (kg/m3) and R2 (%) retention levels are also presented in Table 1. As can be seen from Figure 6 and Figure 7, the mistletoe retentions were found higher than lichen retentions at all concentrations. Also, the retention of solutions prepared with hot water extraction were found higher than the retention of solutions prepared with methanol in both lichen and mistletoe. The retention rate of natural extract solutions was the highest in 15% mistletoe prepared with hot water, and the lowest in 3,75% mistletoe preapered with methanol. Similiar to mistletoe, the highest retention in lichen was obtained in 15% hot water extraction solution, and the lowest in 3,75% methanol extraction solution. As seen in Table 1, the increase in concentration had a possitive effect on retention. In contrast, this effect is much less in the percentage retention (Table 1). All the solutions gave different retention increases of between 81 and 150%. In a similiar study using natural extracts, it was observed that as the solution concentration increased, the amount of retention increased (Sen et al. 2009). In addition, it has been stated that in the solutions obtained from mimosa and quebracho bark extracts, as the concentration increases from 3% to 12%, the retention values are also increased (Tascioglu et al. 2013). In the present study, the retention values are the values obtained by using the entire plant body, not the active chemical substances within plant. Therefore, the higher retention values can be regarded as a normal result.
In the Figure 6 and Figure 7 marked values show water solution concentrations (%), the others show methanol solution concentrations.
Decay resistant
Data of laboratory decay test using treated wood specimens and non-treated controls are shown in Figure 8 and Figure 9. The figures show that the weight losses of untreated control samples are higher than those in treated wood specimens in both lichen and mistletoe. Untreated control samples of lichen and mistletoe extracts gave mean weigt losses of 29,1% and 28,1%, respectively, indicating vigorous fungal activity of C. puteana under the test conditions. Weight losses were less in specimens treated with high concentration solutions. The highest weight loss (19,8%) was obtained in the hot water extracted 3% lichen solution, while the lowest weight loss (6,8%) was found in the methanol extracted 18,75% lichen solution (Figure 9). In the same solution variations, the highest weight loss was 19,3% and the lowest 8% in the samples treated with mistletoe. The weight loss values were statiscially analysed with a one way ANOVA followed by Tukey test for both lichen and mistletoe, and the results were summarized in Table 2 and Table 3. According to both tables, the weight losses of the control samples were statistically higher than those of the solution treated samples. This suggests that extraction solutions are effective in preventing decay. On the other hand, the fact that the standard deviation values for weight loss are not high allow robust analysis of our set of data and reliable interpretation. In a similiar study, Kartal et al. (2006) determined that natural plant extracts such as cinnamaldehyde, cinnamic acid, cassia oil, wood tar oil and dodecanal compounds were effective against decay fungi (Kartal et al. 2006). In another study, solutions prepared from valonia oak, sumac leaves, and pine bark were reported to be significantly effective against wood decay (Sen et al. 2009). According to the Figure 4 and Figure 5, it can be considered that methanol-extracted solutions give a higher decay resistance than the water extracted ones. However, differences in weight losses were not significant between the extraction methods in lichen and mistletoe solutions (Table 2 and Table 3). On the other hand, all one way interactions were significant at the 95% confidence level for concentrations in the decay test. Accordingly, as the concentration increases both in the lichen and in the mistletoe solutions, the weigt loss is reduced (Table 2 and Table 3). The lowest weight losses were recorded on lichen methanol extract treated wood samples at 18,75% concentration level as 6,8%. Likewise, the lowest weight loss was determined to be 8% in the methanol-extracted 18,75% mistletoe solution. Similar results have been obtained in some other studies carried out with natural extracts. Taşçıoğlu et al. stated that “increases in solution concentrations resulted in significant reductions in mass losses for mimosa and quebracho treated wood species tested” (Tascioglu et al. 2013).
In the Figure 6 and Figure 7 marked values show water solution concentrations (%), the others show methanol solution concentrations.
a: Methanol-extracted lichen solutions b: Water extracted lichen solutions
In the Table 2 and Table 3, the standard deviation values are given in paranthesis.
Nakayama et al. (2001) found that pine wood samples impregnated with guayule resin were higly effective against brown-rot fungi, G. trabeum, if the resin content was 52% or higher (Nakayama et al. 2001). In contrast, Göktaş et al. reported that low-concentrate solutions were more effective against white-rot fungus, T. versicolor than that of high concentrate in wood specimens treated with oleander extract. In our study, however, it can be stated that the extracts used had no effect such as accelerating decay in the case of increase in concentration.
The usnic acid is a natural extract produced only by lichen plant. A review summarising studies on biological activities of usnic acid in different areas has been published. In this review, it has been stated that usnic acid played many biological roles such as antibiotic, antimycotic, antifeedant, phytotoxic, photobiont regulator, UV filter, and its most important characteristic was its antibiotic activity (Cocchietto et al. 2002). Cansaran et al. (2006) found that extractive substances obtained from six different lichen species in varying proportions were higly effective against Bacillus subtilis and Bacillus megaterium. In the same study, it was also found that protective effect increased as the amount of usnic acid increased (Cansaran et al. 2006). Our results show similar findings for the antimicrobial activity of lichen extraction solutions.
In a review article on the biologically active chemical substances of European mistletoe (Viscum album), it is stated that lectins and viscotoxins extracts are main causative agents in this sense. Continuation of this compilation, Ochocka and Piotrowski (2002) noted that “the European mistletoe is used in an adjuvant cancer therapy because of their immunostimulatory and simultaneously cytotoxic properties. These types of effects are generally more apparent for the whole extracts than for purified mistletoe lectins and viscotoxins alone” (Ochocka and Piotrowski 2002). In the current study, the mistletoe extracts were also used as a whole, and effective results were obtained. Unlike this, Ertürk et al. (2004) vaporized the mistletoe n-hexan extract and investigated its biological activity at various concentrations. Accordingly, they determined that fractions 6 and 7 of n-hexan extract of Viscum album subps. abietis had antimicrobial activity. The effective results obtained in our study can be attributed to similar active chemical agents in mistletoe extracts.
One of the most important problems in natural compounds is that they do not dissolve in water; therefore, they require organic solvent. However, the plants in our study yielded approximately similar performance in both water and methanol solutions. This should be seen as an advantage for the future.
Conclusions
In the present study, lichen and mistletoe extracts which were tested potential environmentally friendly wood preservatives. Sufficient retention values were reached in both natural extract solutions. Methanol extracts have given a somewhat higher retention value than hot water extracts. In addition, mistletoe retentions were found higher than lichen retentions at all concentrations.
Both lichen and mistletoe extraction solutions have showed good protection performance compared to the control samples. In both the lichen and the mistletoe, the lowest weight loss value has been obtained in extract solutions of 15% and 18,75% concentrations. However, the weight losses in the treated test specimen have not met the standard requirements. Nevertheless, it can be assumed that both natural extracts provide promising protection performance.