Introduction
The impact of human activities on the Earth's climate has been widely recognized as a significant threat [
1]. In light of this, reduction of energy use and greenhouse gas emissions, particularly carbon dioxide, has become a major global concern [
2]. In particular, the construction sector faces significant challenges in preserving natural resources and reducing its carbon footprint [
3].
Globally, this industry is accountable for 40-50% of total CO
2 emissions [
4].
Wood has been used in the construction industry for thousands of years as a fundamental building material and primary furnishings source [
5,
6,
7]. Wood offers environmental benefits such as renewability, sustainability, and minimization of energy loss through production and disposal. Therefore, increasing the use of wood in construction could be one strategy to reduce the carbon footprint [
8,
9]. To align with carbon footprint reduction goals, the French government mandated that more than 50% of new public buildings be constructed using wood by 2022 [
10,
11]. This initiative reflects a commitment to promoting the use of renewable and environmentally friendly materials in construction [
10].
However, wood has some disadvantages compared to materials like steel and concrete. One of the challenges with wood is its hydrophilic nature, which readily absorbs and releases moisture [
12]. Changes in dimensional stability due to moisture levels in wood materials may cause wooden structures to warp, twist, or crack [
12].
Additionally, wood is more susceptible to microbiological decay. Fungi, insects, and other organisms can thrive in wood materials, potentially leading to wood rot and degradation over time if proper precautions are not taken [
13,
14]. This necessitates preservation treatment and maintenance to protect wood from decay-causing agents [
13,
14,
15]. However, the biggest disadvantage of wood as a building material is that it is flammable, a matter related to human safety and life. Therefore, various methods have been proposed to protect wood from fire [
16,
17].
There are two methods for applying flame retardant treatment to wood: coating the wood with flame-retardant material and impregnating the wood pores with vacuum pressure [
18,
19]. Compared to coating, impregnation is a more beneficial method for introducing a flame-retardant effect of wood [
20].
The vacuum pressure impregnation process can be optimized by adjusting the flow characteristics of the chemical, chamber temperature, and impregnation pressure and time. Jang and Kang [
21] reported that, among various variables in the vacuum pressure impregnation process, pressure was a significant variable in improving the impregnation of wood.
In addition, it has been reported by various researchers that impregnation ability can be improved by inducing pore structure changes through chemical pretreatment of wood or through physical pretreatments such as drilling, laser incising, and grooving [
22,
23,
24]. Flame retardant impregnation of wood is meaningful only when accompanied by improvement of flame-retardant properties. Therefore, it is essential to investigate the flame-retardant properties of wood after flame retardant treatment.
Park et al. [
25] investigated the effective heat of combustion of 12 species mainly used as domestic building materials using a cone calorimeter. From their results, Merbau showed the lowest value with 5.85 MJ/kg and Kempas showed the highest value with 13.31 MJ/kg.
Jin and Chung [
26] treated Hinoki wood with metal oxides and metal silicates and investigated the fire hazard characteristics using a cone calorimeter. The smoke performance index indicated an increase in smoke risk in the following sequence: SnO < mica < CO
3O
4 < ZrSiO
4 < Hinoki. Meanwhile, the smoke growth index showed a decrease of 93% to 98% compared to untreated wood. The smoke risk attributed to the smoke growth index increased in the order of SnO < mica < ZrSiO4≈ Co3O4 < Hinoki.
Li et al. [
27] investigated the flame-retardant properties of wood treated with chitosan-SiO
2. Chitosan promotes the deposition of silicon dioxide (SiO
2) in the cell walls and intercellular space of wood forming a chitosan-SiO
2 film. The highest peak in the cone calorimeter reflected a significant decrease in the heat release rate of mineralized wood, and similar results were obtained in microcalorimeter experiments.
According to the administrative rules announced by the Ministry of Land, Infrastructure, and Transport in Korea, "Flame Retardant Performance of Building Finishing Materials and Fire Spread Prevention Structure," the total heat emission of semi-noncombustible materials is stipulated to be less than 8 MJ/m
2 [
28,
29,
30]. Therefore, even if flame-retardant material is not entirely impregnated into the wood, it can be used as a building exterior if this standard is met. Insufficient flame-retardant impregnation leads to lower fire safety. On the other hand, excessive flame-retardant impregnation can lead to longer processing time and unnecessary flame-retardant abuse, which may cause an increase in the cost of flame-retardant wood.
Therefore, it is necessary to investigate the optimal flame-retardant impregnation amount for each species that meets Ministry of Land, Infrastructure, and Transport standards. However, research in this area is limited. Therefore, we selected Korean larch and Japanese cedar, the most widely used exterior building materials in Korea, and investigated whether they met the Ministry of Land, Infrastructure, and Transport standard in Korea according to the degree of impregnation of flame retardants.
Author Contributions
SUJ: First author, experiments, formal analysis, writing (review & edition), HBC: co-First author, experiments, formal analysis, HJP: Corresponding author, supervision, conceptualization, methodology, writing (review & editing), ESJ: Corresponding author, writing (original draft, review & editing)