Editorial on Special Issue on Wildland–Urban Interface (WUI) Fires

IF 2.4 4区 材料科学 Q3 MATERIALS SCIENCE, MULTIDISCIPLINARY
Samuel L. Manzello, Anja Hofmann
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The global coverage of contributed papers demonstrated the growing nature of the WUI fire problem.</p><p>The first paper in the special issue discusses the efforts in ISO TC 92 Fire Safety to standardize a global approach to large outdoor fires, including WUI fires [<span>1</span>]. The paper highlights that although ISO TC92 has been around for several decades, there has only recently been a shift from fires that occur inside buildings to large outdoor fires.</p><p>In recent times, several devastating WUI fires have been initiated by powerline issues. Babrauskas presents a discussion on powerline clearance regulations and the relation to WUI fires in the United States of America [<span>2</span>]. In the paper, it is argued to improve powerline regulations in the future to help lessen the initial ignition risk from this type of infrastructure. Xu and co-workers also discuss complications with powerlines in WUI fires [<span>3</span>].</p><p>WUI fire damage assessments were reported from 2016 to 2023 in Norway by Mikalsen et al. [<span>4</span>]. It was found that the spring season and direct flame contact are the primary contributors to vegetation fires that damage buildings in Norway.</p><p>WUI fires have a significant impact on the ecosystem. In the paper by Liu and Zhou [<span>5</span>], a discussion is presented on the impact of local water ecosystems due to an increasing WUI fire threat in China. The results of their investigation suggest the need to improve understanding of the impacts of wildland fires on water and soil resources in China in the aftermath of these fires.</p><p>Elevated temperatures in the soil and radiant heat flux from WUI fires can be a threat to infrastructure. Wang and Zhou [<span>6</span>] provide a modeling discussion on radiant heat flux that a simulated wildland fire front would expose fuel tanks located in a WUI community. In many countries, propane gas tanks are stored above ground and there have been cases where WUI fire exposure has resulted in ruptures and secondary fires from these tanks. The work of Janssen [<span>7</span>] presented a simplified model to understand potential damage from water pipes located underground during WUI fire exposures.</p><p>Smoke and particulates emitted during WUI fire disasters are an important research topic because the pollutants may vary depending on the type of fuel, and these can also enter homes and are often responsible for severe health issues. In work from Martinent et al. [<span>8</span>], different local shrub species were combusted to provide information on the emissions of pollutants that homeowners would experience in WUI areas in France. It was reported that the type of shrub species has quite different combustion characteristics, and this influences the measured emissions. Another study by Piechnik et al. [<span>9</span>], smaller-sized vegetative samples from tree species and ground cover samples being combusted in a tube furnace. Results indicate that significantly higher concentrations of CO can be expected in the case of a coniferous forest fire compared with a fire in a deciduous forest in Germany.</p><p>As the vegetation is the fuel in wildland fires, its characterization and assessment of burning behavior provided insight in the development of and growth of wildland fires. Guillaume et al. [<span>10</span>] investigated the ignition and propagation of live vegetation to build a semi-empirical model. Cobian et al. [<span>11</span>] reported insights from bench scale experiments on effects of fuel structure and species on ignition. Similar insights are provided given by Krim et al. [<span>12</span>], Dias et al. [<span>13</span>], and Heydick et al. [<span>14</span>] into vegetation in Algeria, Brazil and Germany, respectively.</p><p>A method to rank flammability of ornamental vegetation is provided by Muñoz et al. [<span>15</span>]. The capability of ignition of vegetation by hot particles is investigated by Wang et al. [<span>16</span>]. Such studies are also related to the arcing of powerlines discussed above.</p><p>In WUI fires, once a wildland fire reaches a community, it is well known that structure to structure fire spread processes become important. Following many previous studies on this topic, Gorham et al. [<span>17</span>] investigated the response to a thermal exposure generated by a compartment fire with a single opening oriented towards the target. In the work of Tihay-Felicelli et al. [<span>18</span>], the combustion of ornamental vegetation also provides exposure to influence structure ignition in WUI fires, that various hedge types were studied. 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引用次数: 0

Abstract

Particularly sought after were studies that aim to bridge the gap between current building codes, standards, and regulations, and the latest scientific advancements in wildland fire and WUI fire research. In addition to posting on the website, the help of experts in this topical area was enlisted to help spread the word via social media channels.

In total, 25 papers were accepted as part of this special issue. Contributed papers came from all across the globe and included Algeria, Australia, Brazil, China, France, Germany, Japan, Poland, Norway, New Zealand, Spain, Sweden, and the United States of America. The global coverage of contributed papers demonstrated the growing nature of the WUI fire problem.

The first paper in the special issue discusses the efforts in ISO TC 92 Fire Safety to standardize a global approach to large outdoor fires, including WUI fires [1]. The paper highlights that although ISO TC92 has been around for several decades, there has only recently been a shift from fires that occur inside buildings to large outdoor fires.

In recent times, several devastating WUI fires have been initiated by powerline issues. Babrauskas presents a discussion on powerline clearance regulations and the relation to WUI fires in the United States of America [2]. In the paper, it is argued to improve powerline regulations in the future to help lessen the initial ignition risk from this type of infrastructure. Xu and co-workers also discuss complications with powerlines in WUI fires [3].

WUI fire damage assessments were reported from 2016 to 2023 in Norway by Mikalsen et al. [4]. It was found that the spring season and direct flame contact are the primary contributors to vegetation fires that damage buildings in Norway.

WUI fires have a significant impact on the ecosystem. In the paper by Liu and Zhou [5], a discussion is presented on the impact of local water ecosystems due to an increasing WUI fire threat in China. The results of their investigation suggest the need to improve understanding of the impacts of wildland fires on water and soil resources in China in the aftermath of these fires.

Elevated temperatures in the soil and radiant heat flux from WUI fires can be a threat to infrastructure. Wang and Zhou [6] provide a modeling discussion on radiant heat flux that a simulated wildland fire front would expose fuel tanks located in a WUI community. In many countries, propane gas tanks are stored above ground and there have been cases where WUI fire exposure has resulted in ruptures and secondary fires from these tanks. The work of Janssen [7] presented a simplified model to understand potential damage from water pipes located underground during WUI fire exposures.

Smoke and particulates emitted during WUI fire disasters are an important research topic because the pollutants may vary depending on the type of fuel, and these can also enter homes and are often responsible for severe health issues. In work from Martinent et al. [8], different local shrub species were combusted to provide information on the emissions of pollutants that homeowners would experience in WUI areas in France. It was reported that the type of shrub species has quite different combustion characteristics, and this influences the measured emissions. Another study by Piechnik et al. [9], smaller-sized vegetative samples from tree species and ground cover samples being combusted in a tube furnace. Results indicate that significantly higher concentrations of CO can be expected in the case of a coniferous forest fire compared with a fire in a deciduous forest in Germany.

As the vegetation is the fuel in wildland fires, its characterization and assessment of burning behavior provided insight in the development of and growth of wildland fires. Guillaume et al. [10] investigated the ignition and propagation of live vegetation to build a semi-empirical model. Cobian et al. [11] reported insights from bench scale experiments on effects of fuel structure and species on ignition. Similar insights are provided given by Krim et al. [12], Dias et al. [13], and Heydick et al. [14] into vegetation in Algeria, Brazil and Germany, respectively.

A method to rank flammability of ornamental vegetation is provided by Muñoz et al. [15]. The capability of ignition of vegetation by hot particles is investigated by Wang et al. [16]. Such studies are also related to the arcing of powerlines discussed above.

In WUI fires, once a wildland fire reaches a community, it is well known that structure to structure fire spread processes become important. Following many previous studies on this topic, Gorham et al. [17] investigated the response to a thermal exposure generated by a compartment fire with a single opening oriented towards the target. In the work of Tihay-Felicelli et al. [18], the combustion of ornamental vegetation also provides exposure to influence structure ignition in WUI fires, that various hedge types were studied. Finally, it is also important to quantify structures that have been damaged during WUI fire disasters, and the work of Kang et al. [19] discussed a method using deep learning methods using imagery obtained from aerial measurements.

Mitigating the ignition risks in WUI fires are of course very important. In this special issue, three studies considered these aspects. For homeowners to consider various mitigation strategies, Barrett and Quarles [20] discuss the costs of such measures. You et al. [21] investigated the use of inorganic solidified foam for forest fires. Dossi et al. [22] considered the use of sand protection measures to try to guard against firebrand accumulation processes in WUI fires.

There is no globally accepted definition as to what specifically constitutes the WUI, in terms of structure density. In the work of Elio Medina et al. [23], it is argued that an approach to define the term WUI in Northern Europe is required.

It is also important to compare and understand current WUI fire standards and codes. Hirschler [24] provided insights into a comparison between the WUI codes and standard from the International Code Council and the State of California. To also better assist future standards and codes, in a brief literature review by Penney et al. [25], it was argued that WUI fires require more engineered based approaches.

The authors declare no conflicts of interest.

荒地-城市界面(WUI)火灾特刊社论
特别受欢迎的是旨在弥合当前建筑规范、标准和法规与野火和WUI火灾研究的最新科学进展之间差距的研究。除了在网站上发布外,该专题领域的专家也被邀请帮助通过社交媒体渠道传播这个消息。总共有25篇论文作为本期特刊的一部分被接受。投稿论文来自全球各地,包括阿尔及利亚、澳大利亚、巴西、中国、法国、德国、日本、波兰、挪威、新西兰、西班牙、瑞典和美国。贡献论文的全球覆盖表明了WUI火灾问题日益严重的本质。特刊的第一篇论文讨论了ISO TC 92消防安全为使大型室外火灾的全球方法标准化所做的努力,包括WUI火灾b[1]。该论文强调,尽管ISO TC92已经存在了几十年,但直到最近才从发生在建筑物内部的火灾转变为大型室外火灾。最近,几起毁灭性的WUI火灾都是由电力线问题引起的。Babrauskas讨论了美国的电力线清理规定及其与WUI火灾的关系。本文认为,未来应改进电力线法规,以帮助减少此类基础设施的初始点火风险。许和同事们还讨论了WUI火灾中电力线的并发症。Mikalsen等人报告了2016年至2023年挪威WUI火灾损失评估。研究发现,春季和直接火焰接触是挪威植被火灾破坏建筑物的主要原因。WUI火灾对生态系统有重大影响。在Liu和Zhou b[5]的论文中,讨论了由于中国WUI火灾威胁的增加对当地水生态系统的影响。他们的调查结果表明,有必要在这些火灾发生后提高对中国水土资源影响的认识。土壤温度升高和WUI火灾产生的辐射热通量可能对基础设施构成威胁。Wang和Zhou[6]提供了一个模拟野火前线将暴露位于WUI社区的燃油箱的辐射热流的建模讨论。在许多国家,丙烷气罐储存在地面上,并且已经发生过WUI火灾导致这些气罐破裂和二次火灾的情况。Janssen[7]的工作提供了一个简化的模型来理解地下水管在WUI火灾暴露时的潜在损害。在WUI火灾中排放的烟雾和颗粒是一个重要的研究课题,因为污染物可能因燃料类型而异,这些污染物也可以进入家庭并经常导致严重的健康问题。在Martinent等人的工作中,他们燃烧了不同的当地灌木物种,以提供有关法国WUI地区房主将经历的污染物排放的信息。据报道,灌木种类的燃烧特性有很大的不同,这影响了测量的排放量。另一项由Piechnik等人进行的研究是,在管式炉中燃烧来自树种和地被植物的较小尺寸的植物样本。结果表明,与德国的落叶林火灾相比,针叶林火灾的CO浓度明显更高。由于植被是野火的燃料,其燃烧行为的表征和评估为野火的发生和发展提供了新的思路。Guillaume et al.[10]研究了活植被的点火和繁殖,建立了半经验模型。Cobian et al.[11]报道了燃料结构和种类对点火影响的实验结果。Krim et al. b[12]、Dias et al.[13]和Heydick et al.[14]分别对阿尔及利亚、巴西和德国的植被进行了类似的研究。Muñoz等人提供了一种对观赏植物可燃性进行排序的方法。Wang等人研究了热颗粒点燃植被的能力。这些研究也与上面讨论的电力线的电弧有关。在WUI火灾中,一旦野火到达社区,众所周知,结构到结构的火灾蔓延过程变得重要。Gorham等人([17])在之前对这一主题进行了许多研究之后,研究了对单个开口面向目标的隔间火灾产生的热暴露的反应。在Tihay-Felicelli等人的研究中,观赏植被的燃烧也提供了暴露来影响WUI火灾中的结构点火,研究了各种树篱类型。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Fire and Materials
Fire and Materials 工程技术-材料科学:综合
CiteScore
4.60
自引率
5.30%
发文量
72
审稿时长
3 months
期刊介绍: Fire and Materials is an international journal for scientific and technological communications directed at the fire properties of materials and the products into which they are made. This covers all aspects of the polymer field and the end uses where polymers find application; the important developments in the fields of natural products - wood and cellulosics; non-polymeric materials - metals and ceramics; as well as the chemistry and industrial applications of fire retardant chemicals. Contributions will be particularly welcomed on heat release; properties of combustion products - smoke opacity, toxicity and corrosivity; modelling and testing.
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