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Fire, Volume 7, Issue 12 (December 2024) – 54 articles

Cover Story (view full-size image): In the Western parts of the United States, and in many other locations, electricity-ignited wildfires have become a rapidly growing problem, producing major economic consequences for affected areas. A new article by Dr. Babrauskas outlines a novel solution to the socioeconomic problems of this situation: legislation to convert from a tort-litigation to a no-fault system, broadly resembling existing systems for Workers’ Compensation. View this paper
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28 pages, 7454 KiB  
Article
Equations to Predict Carbon Monoxide Emissions from Amazon Rainforest Fires
by Sarah M. Gallup, Bonne Ford, Stijn Naus, John L. Gallup and Jeffrey R. Pierce
Fire 2024, 7(12), 477; https://doi.org/10.3390/fire7120477 (registering DOI) - 15 Dec 2024
Viewed by 422
Abstract
Earth systems models (ESMs), which can simulate the complex feedbacks between climate and fires, struggle to predict fires well for tropical rainforests. This study provides equations that predict historic carbon monoxide emissions from Amazon rainforest fires for 2003–2018, which could be implemented within [...] Read more.
Earth systems models (ESMs), which can simulate the complex feedbacks between climate and fires, struggle to predict fires well for tropical rainforests. This study provides equations that predict historic carbon monoxide emissions from Amazon rainforest fires for 2003–2018, which could be implemented within ESMs’ current structures. We also include equations to convert the predicted emissions to burned area. Regressions of varying mathematical forms are fitted to one or both of two fire CO emission inventories. Equation accuracy is scored on r2, bias of the mean prediction, and ratio of explained variances. We find that one equation is best for studying smoke consequences that scale approximately linearly with emissions, or for a fully coupled ESM with online meteorology. Compared to the deforestation fire equation in the Community Land Model ver. 4.5, this equation’s linear-scale accuracies are higher for both emissions and burned area. A second equation, more accurate when evaluated on a log scale, may better support studies of certain health or cloud process consequences of fires. The most accurate recommended equation requires that meteorology be known before emissions are calculated. For all three equations, both deforestation rates and meteorological variables are key groups of predictors. Predictions nevertheless fail to reproduce most of the variation in emissions. The highest linear r2s for monthly and annual predictions are 0.30 and 0.41, respectively. The impossibility of simultaneously matching both emission inventories limits achievable fit. One key cause of the remaining unexplained variability appears to be noise inherent to pan-tropical data, especially meteorology. Full article
(This article belongs to the Section Fire Science Models, Remote Sensing, and Data)
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<p>Maps of (<b>a</b>) mean GFED CO, (<b>b</b>) mean Naus CO, and (<b>c</b>) their difference, and (<b>d</b>) concept diagram of the form permutations for candidate regression equations. The legend between panels a and b applies to both. The average difference in cell means is 7006 g C km<sup>−2</sup> land d<sup>−1</sup>.</p>
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<p>Histogram of CO emissions fluxes in log scale. Bins are 0.1 units wide on a log<sub>10</sub> scale. The 48% of Naus monthly means and 50% of GFED’s whose value is zero are not shown.</p>
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<p>Accuracy metrics for the recommended equations and FireMIP CO emissions. Each recommended equation has a different color and shape. FireMIP models included are CLM4.5, CTEM, JBSpitfire, Jules, LGSimfire, LGSpitfire, and Orchidee. All <span class="html-italic">x</span>-axes show r<sup>2</sup> explanatory power. In the left column (panels (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>)), ratio of the mean prediction to the mean benchmark is on the <span class="html-italic">y</span>-axis. In the graphs on the right (panels (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>)), ratio of explained variances is on the <span class="html-italic">y</span>-axis. Black arrows mark the optimal score of one for both ratio of the mean prediction and ratio of explained variances, with the arrow emphasizing that higher r<sup>2</sup> is better. Each row of panels shows the same sets of predictions, scaled as linear monthly means (panels (<b>a</b>,<b>b</b>)), as linear annual means (<b>c</b>,<b>d</b>), log monthly means (<b>e</b>,<b>f</b>), or log annual means (<b>g</b>,<b>h</b>). Ratios of means higher than 2 and ratios of explained variances higher than 5 are not plotted. FireMIP emissions accuracy is for only 2003–2013 and is addressed in <a href="#sec4dot2-fire-07-00477" class="html-sec">Section 4.2</a> below. Which recommended equation is most accurate varies markedly by the scale at which prediction accuracy is judged.</p>
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<p>Binned distribution of monthly emission predictions from each recommended equation, compared to the merger of both CO inventories. The panels display the same underlying data but at different scales. The legend applies to both panels. Black dots describe CO fluxes for test cells and are the benchmark. Dashed gray vertical lines mark test cell benchmark means. Panel A shows the distribution of the linear-scale values, binned as the nearest multiple of 125,000. Frequencies in panel a are graphed on a log scale. In panel (<b>a</b>), the truncated <span class="html-italic">x</span>-axis omits the 0.019% (n = 40) of input fluxes larger than 1,600,000 g C km<sup>−2</sup> land d<sup>−1</sup>. For panel (<b>b</b>), the <span class="html-italic">x</span>-axis shows predicted values that have been transformed to a log scale, then binned as the nearest whole number. The spikes at log (0.32 g C km<sup>−2</sup> land d<sup>−1</sup>) are the log-scale replacement for zero emission instances. Inventory fluxes with log value of less than about 2.5 are likely to have large errors of both detection and relative magnitude. The graphs display the large differences in distributions of predictions compared to benchmark data for log versus linear forms of predictions.</p>
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<p>Each predictor’s relative contribution to total r<sup>2</sup> in selected equations. Contributions can be calculated only for training data, and at an equation’s native outcome transformation and time scale. Because the native scales differ across equations, the stacks describe, respectively: contributions when evaluated in monthly linear space for the Linear equation, contributions in monthly log space for the Log equation, and contributions in annual linear space for the LinearPMet equation. Predictors related to dryness and deforestation are the heart of each recommended equation.</p>
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18 pages, 8713 KiB  
Article
Smoke Precipitation by Exposure to Dual-Frequency Ultrasonic Oscillations
by Vladimir Khmelev, Andrey Shalunov, Sergey Tsyganok and Pavel Danilov
Fire 2024, 7(12), 476; https://doi.org/10.3390/fire7120476 (registering DOI) - 15 Dec 2024
Viewed by 210
Abstract
The analysis conducted herein has shown that the efficiency of smoke precipitation can be improved by additionally making smoke particles interact with ultrasonic (US) oscillations. Because the efficiency of US coagulation lowers when small particles assemble into agglomerates, the authors of this work [...] Read more.
The analysis conducted herein has shown that the efficiency of smoke precipitation can be improved by additionally making smoke particles interact with ultrasonic (US) oscillations. Because the efficiency of US coagulation lowers when small particles assemble into agglomerates, the authors of this work have suggested studying how smoke particles interact with complex sound fields. The fields are formed by at least two US transducers which work at a similar frequency or on frequencies with small deviations. To form these fields, high-efficiency bending wave ultrasonic transducers have been developed and suggested. It has been shown that a complex ultrasonic field significantly enhances smoke precipitation. The field in question was constructed by simultaneously emitting 22 kHz US oscillations with a sound pressure level no lower than 140 dB at a distance of 1 m. The difference in US oscillations’ frequencies was no more than 300 Hz. Due to the effect of multi-frequency ultrasonic oscillations induced in the experimental smoke chamber, it was possible to provide a transmissivity value of 0.8 at a distance of 1 m from the transducers and 0.9 at a distance of 2 m. Thus, the uniform visibility improvement and complete suppression of incoming smoke was achieved. At the same time, the dual-frequency effect does not require an increase in ultrasonic energy for smoke due to the agglomeration of small particles under the influence of high-frequency ultrasonic vibrations and the further aggregation of the formed agglomerates by creating conditions for the additional rotational movement of the agglomerates due to low-frequency vibrations. Full article
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<p>Design and simulation results fora disk emitter. (<b>a</b>) Distribution of amplitude; (<b>b</b>) distribution of stress. 1—emitter; 2—emitting pad of the piezoelectric transducer; 3—piezoceramic rings; 4—reflecting pad; 5—tightening bolt; 6—copper electrode; 7—tightening screw.</p>
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<p>The manufactured emitter with an electronic generator for supplying its power.</p>
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<p>Dual emitter for equal frequency action on smoke.</p>
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<p>Emitters for multi-frequency action on smoke.</p>
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<p>Stand for measuring the directional pattern of ultrasonic emitters. 1—Ultrasonic disk emitter, 2—electronic generator; 3—emitter stand, 4—microphone; 5—noise meter measuring unit; 6—microphone stand; 7—microphone direction point.</p>
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<p>Experimental setup; (<b>a</b>) with one emitter; (<b>b</b>) with two emitters. 1—Ultrasonic disk emitter; 2—electronic generator; 3—smoke chamber; 4—smoke generator; 5—infrared radiation source; 6—photodetector.</p>
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<p>Directivity pattern for a single emitter.</p>
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<p>Attenuation in relation to distance from the source in a smoke chamber (one emitter).</p>
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<p>Directivity pattern of dual disk emitters.Red color—two simultaneously operating disks at the same frequency; blue color—two simultaneously operating disks of different frequencies.</p>
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<p>Attenuation over distance in a smoke chamber (two emitters). Blue color—two simultaneously operating disks of different frequencies; red color—two simultaneously operating disks of equal frequencies.</p>
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<p>Difference frequency directivity pattern.</p>
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<p>Beat frequency attenuation over distance in smoke chamber.</p>
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<p>Results of visual observation of ultrasonic smoke agglomeration.</p>
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<p>Measurement of relative visibility from the time of ultrasonic exposure for different distances (in m) from the emitter.</p>
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<p>Measurement of relative visibility from the time of ultrasonic exposure for different distances (in m) from the emitters.</p>
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<p>Histogram of agglomerate size distribution.</p>
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<p>Images of smoke particle agglomerates (100×). (<b>a</b>) Single-frequency action; (<b>b</b>) dual-frequency action.</p>
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11 pages, 3414 KiB  
Article
Study on the Explosion Mechanism of Low-Concentration Gas and Coal Dust
by Li Liu, Xinyi Mao, Yongheng Jing, Yao Tang and Le Sun
Fire 2024, 7(12), 475; https://doi.org/10.3390/fire7120475 (registering DOI) - 13 Dec 2024
Viewed by 232
Abstract
In coal mines, the mixture of coal dust and gas is more ignitable than gas alone, posing a high explosion risk to workers. Using the explosion tube, this study examines the explosion propagation characteristics and flame temperature of low-concentration gas and coal dust [...] Read more.
In coal mines, the mixture of coal dust and gas is more ignitable than gas alone, posing a high explosion risk to workers. Using the explosion tube, this study examines the explosion propagation characteristics and flame temperature of low-concentration gas and coal dust mixtures with various particle sizes. The CPD model and Chemkin-Pro 19.2 simulate the reaction kinetics of these explosions. Findings show that when the gas concentration is below its explosive limit, coal dust addition lowers the gas’s explosive threshold, potentially causing an explosion. Coal particle size significantly affects explosion propagation dynamics, with smaller particles producing faster flame velocities and higher temperatures. Due to their larger surface area, smaller particles absorb heat faster and undergo thermal decomposition, releasing combustible gases that intensify the explosion flame. The predicted yield of light gases from both coal types exceeds 40 wt% daf, raising combustible gas concentrations in the system. When accumulated reaction heat elevates the gas concentration to its explosive limit, an explosion occurs. These results are crucial for preventing gas and coal dust explosion accidents in coal mines. Full article
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<p>Changes in flame propagation velocity and flame temperature in coal-dust mixture explosions at 2 vol% Gas (200 μm, 560 g/m<sup>3</sup> Dongtan coal).</p>
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<p>(<b>a</b>,<b>c</b>) Flame propagation distance and (<b>b</b>,<b>d</b>) velocity for gas-coal dust combustion (2 vol% Gas and 560 g/m<sup>3</sup> coal dust).</p>
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<p>Variation of mean flame propagation velocity for mixed combustion of 2 vol% (<b>a</b>) Dafosi coal (<b>b</b>) Dongtan coal.</p>
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<p>Variation of flame temperature with coal particle size in gas and coal dust explosions (2 vol% gas and 560 g/m<sup>3</sup> coal dust).</p>
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<p>Predicted yield of light gases in coal volatiles by CPD model calculated.</p>
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<p>Evolution of key species and flame temperature with flame propagation distance in gas and coal dust combustion.</p>
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<p>Laminar combustion velocity for coal combustion at the coal dust concentration of 560 g/m<sup>3</sup> and the gas concentration of 2 vol%.</p>
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<p>Mechanism of coal dust explosion under low concentration gas conditions.</p>
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17 pages, 2657 KiB  
Article
Short-Term Impacts of Fire and Post-Fire Restoration Methods on Soil Properties and Microbial Characteristics in Southern China
by Hongen Zhou, Mengmeng Yang, Xuan Luo, Zefang Yang, Lanqing Wang, Shizhong Liu, Qianmei Zhang, Mingdao Luo, Jinwei Ou, Shiyang Xiong, Yujie Qin and Yuelin Li
Fire 2024, 7(12), 474; https://doi.org/10.3390/fire7120474 - 12 Dec 2024
Viewed by 362
Abstract
Wildfires and post-fire restoration methods significantly impact soil physicochemical properties and microbial characteristics in forest ecosystems. Understanding post-fire soil recovery and the impacts of various post-fire restoration methods is essential for developing effective restoration strategies. This study aimed to investigate how fire and [...] Read more.
Wildfires and post-fire restoration methods significantly impact soil physicochemical properties and microbial characteristics in forest ecosystems. Understanding post-fire soil recovery and the impacts of various post-fire restoration methods is essential for developing effective restoration strategies. This study aimed to investigate how fire and soil depth influence soil physicochemical properties, enzymatic activities, and the structure of microbial communities, as well as how these factors change under different post-fire management practices. We sampled 0–10 cm (topsoil) and 10–20 cm (subsoil) in unburned plots, naturally restored plots, and two afforestation plots in southern China. The results showed that fire reduced topsoil soil moisture, nutrient levels, and microbial biomass. The variations in soil physicochemical properties significantly influenced microbial processes. Soil bulk density, nitrate, ammonium, carbon-to-nitrogen ratio, and availability of nitrogen, phosphorus, and potassium availability influenced soil enzyme activities. Soil pH, ammonium nitrogen, and the availability of nitrogen, phosphorus, and potassium were key factors shaping microbial composition. Fire altered the soil microbial communities by reducing the availability of nitrogen. Soil depth alleviated the impact of fire on the soil to some degree. Although artificial interventions reduced soil organic carbon, total nitrogen, and phosphorus, planting nitrogen-fixing species, such as Acacia mangium, promoted microbial recovery. Full article
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<p>Map showing the study area and the location of the sample site on Ling Yun.</p>
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<p>The content of microbial biomass carbon (MBC) (<b>a</b>) and nitrogen (MBN) (<b>b</b>) for unburned forest (UF), burned but naturally regenerating forest (NRF), and burned but afforestation restored with <span class="html-italic">Acacia mangium</span> (ARF1) and <span class="html-italic">Michelia macclurei</span> (ARF2) in different soil depths (M ± SE, <span class="html-italic">n</span> = 3). Varied lowercase letters reflect significant variations in sites (<span class="html-italic">p</span> &lt; 0.05); there was no significant difference with the same letter. Significant differences between soil depth (<span class="html-italic">p</span> &lt; 0.05) have been marked in the figure.</p>
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<p>Microbial enzyme activity of acid phosphate (AP), β-glucosidase (BG), N-acetyl-glucosidase (NAG), and peroxidase (POD) (panels <b>a</b>–<b>d</b>, respectively) (M ± SE, <span class="html-italic">n</span> = 3). Varied lowercase letters reflect significant variations in sites (<span class="html-italic">p</span> &lt; 0.05); there was no significant difference with the same letter. Unburned forest (UF); burned but naturally regenerating forest (NRF); burned but afforestation restored with <span class="html-italic">Acacia mangium</span> (ARF1) and <span class="html-italic">Michelia macclurei</span> (ARF2). Significant differences between soil depth (<span class="html-italic">p</span> &lt; 0.05) have been marked in the figure.</p>
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<p>Relative content of soil microbial phospholipid fatty acids (PLFAs). G+: Gram-positive bacteria; G−: Gram-negative bacteria; A: Actinobacteria; AMF: arbuscular mycorrhizal fungi; P: protozoa; GF: general fungi, which are fungi other than AMF; GB: general bacteria, which are bacteria except for G+, G−, and A; others: other microbes. Unburned forest (UF); burned but naturally regenerating forest (NRF); burned but afforestation restored with <span class="html-italic">Acacia mangium</span> (ARF1) and <span class="html-italic">Michelia macclurei</span> (ARF2).</p>
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<p>Total PLFAs (<b>a</b>), Shannon–Wiener diversity index (H, <b>b</b>), the ratio of Gram-positive bacteria to Gram-negative bacteria (G+/G−, <b>c</b>), and fungi to bacteria (F/B, <b>d</b>) (M ± SE, <span class="html-italic">n</span> = 3). Varied lowercase letters reflect significant variations in sites (<span class="html-italic">p</span> &lt; 0.05); there was no significant difference with the same letter. Unburned forest (UF); burned but naturally regenerating forest (NRF); burned but afforestation restored with <span class="html-italic">Acacia mangium</span> (ARF1) and <span class="html-italic">Michelia macclurei</span> (ARF2). Significant differences between soil depth (<span class="html-italic">p</span> &lt; 0.05) have been marked in the figure.</p>
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<p>Principal coordinate analysis (PCoA) plots demonstrating microbial community composition. Sites are depicted using various colors, and soil depths are represented by shapes. Confidence ellipses at the 95% level were outlined for each site. Unburned forest (UF); burned but naturally regenerating forest (NRF); burned but afforestation restored with <span class="html-italic">Acacia mangium</span> (ARF1) and <span class="html-italic">Michelia macclurei</span> (ARF2).</p>
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<p>The association between microbial activity (<b>a</b>) community composition (<b>b</b>) and soil physicochemical properties based on redundancy analysis (RDA). Blue arrows indicate soil characteristics and red arrows indicate microbial activity/microbial community. AK: available potassium; AN: available nitrogen; AVP: available phosphorus; BD: bulk density; NO: NO<sub>3</sub><sup>−</sup>-N; NH: NH<sub>4</sub><sup>+</sup>-N; CN: C N ratio; SWC: soil water content; T: total PLFAs; MBC: microbial biomass carbon; MBN: microbial biomass nitrogen; AP: acid phosphate; BG: β-glucosidase; NAG: N-acetyl-glucosidase; POD: peroxidase; G+: Gram-positive bacteria; G−: Gram-negative bacteria; A: Actinobacteria; AMF: arbuscular mycorrhizal fungi; P: protozoa; GF: general fungi, which are fungi other than AMF; GB: general bacteria, which are bacteria except for G+, G−, and A; others: other microbes. Unburned forest (UF); burned but naturally regenerating forest (NRF); burned but afforestation restored with <span class="html-italic">Acacia mangium</span> (ARF1) and <span class="html-italic">Michelia macclurei</span> (ARF2).</p>
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<p>Structural equation models examining the relationships between fire, soil physicochemical properties, and the microbial community (<span class="html-italic">X</span><sup>2</sup> = 11.53, <span class="html-italic">p</span> = 0.173, <span class="html-italic">df</span> = 8). The numbers associated with the arrows signify standardized path coefficients. Black and red arrows represent positive and negative effects, respectively. <span class="html-italic">R</span><sup>2</sup> values indicate the percentage of variance accounted for by each endogenous variable. ** <span class="html-italic">p</span> &lt; 0.01 and *** <span class="html-italic">p</span> &lt; 0.001. AN: available nitrogen; BD: bulk density; H: Shannon–Wiener diversity index.</p>
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34 pages, 23866 KiB  
Article
Experimental and Numerical Investigations of Crest-Fixed Corrugated Steel Claddings Under Wind Uplift Loading at Elevated Temperatures
by Lisa Pieper and Mahen Mahendran
Fire 2024, 7(12), 473; https://doi.org/10.3390/fire7120473 (registering DOI) - 12 Dec 2024
Viewed by 298
Abstract
The 2019–2020 Black Summer bushfire in Australia is a good example of the frequent and severe bushfires (wildfires) observed around the world in recent years. Fire-enhanced winds and fire–wind interactions during those bushfire events have caused increased wind velocities in the vicinity of [...] Read more.
The 2019–2020 Black Summer bushfire in Australia is a good example of the frequent and severe bushfires (wildfires) observed around the world in recent years. Fire-enhanced winds and fire–wind interactions during those bushfire events have caused increased wind velocities in the vicinity of a bushfire front. This can lead to a premature failure of the building envelope, making it vulnerable to ember attack and direct flame contact. In Australia, crest-fixed cold-formed steel (CFS) claddings are commonly used for buildings in bushfire-prone areas because of their non-combustibility. Therefore, this study investigated the pull-through failure behaviour of corrugated CFS claddings under wind uplift/suction loading at elevated temperatures, simulating fire-enhanced winds during a bushfire by means of experimental and numerical studies. Experimental results showed a negligible influence of the thermal expansion of the cladding system on the pull-through failure behaviour, while a significant decrease in pull-through capacity was observed with increasing temperatures. Suitable finite element models were developed, validated and used in a detailed numerical parametric study. Based on the findings from these studies, a design equation was proposed for the pull-through capacity of the crest-fixed corrugated claddings at elevated temperatures. Full article
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<p>Damage to the building envelope caused by fire–wind interaction during the 2009 Black Saturday bushfire [<a href="#B4-fire-07-00473" class="html-bibr">4</a>].</p>
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<p>Pull-through failures of crest-fixed CFS claddings: (<b>a</b>) local plastic dimpling of corrugated cladding and (<b>b</b>) splitting failure of trapezoidal cladding.</p>
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<p>(<b>a</b>) Overall test set-up and (<b>b</b>) loading system.</p>
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<p>(<b>a</b>) Screw arrangement and (<b>b</b>) 15 kN load cells attached to the critical screws underneath the cladding.</p>
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<p>Locations of laser sensors and load cells on the corrugated cladding specimen.</p>
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<p>(<b>a</b>) Movable frame and insulation layers between cladding and heating blanket and (<b>b</b>) test set-up for elevated temperature tests.</p>
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<p>Locations of thermocouples on the surface of the corrugated cladding.</p>
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<p>Validation of the load–deflection curve at ambient temperature.</p>
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<p>Load–deflection curves at ambient temperature.</p>
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<p>Local dimpling failure at the central support at (<b>a</b>) ambient temperature, (<b>b</b>) 200 °C, (<b>c</b>) 400 °C and (<b>d</b>) localised failure at the critical screw fastener.</p>
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<p>Displacement versus temperature curves at 400 °C.</p>
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<p>Load versus temperature curves at 200 °C and 400 °C.</p>
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<p>Overall applied load-deflection curves.</p>
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<p>Midspan line-loading FE model of corrugated cladding. Note: Different screw labelling compared with the test set-up in <a href="#fire-07-00473-f005" class="html-fig">Figure 5</a>.</p>
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<p>Boundary conditions and load application of (<b>a</b>) the corrugated FE model, (<b>b</b>) the screw head and washer and (<b>c</b>) at the screw fastener hole.</p>
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<p>Mesh of the midspan line-load FE model of corrugated cladding.</p>
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<p>FE model of corrugated cladding subject to uniform pressure loading.</p>
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<p>Load–deflection curves based on (<b>a</b>) the overall applied load from the line-load FE models and (<b>b</b>) the critical screw fastener load in the line-load FE model.</p>
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<p>Comparison of the localised dimpling failure around the critical screw fastener at (<b>a</b>) ambient temperature, (<b>b</b>) 200 °C and (<b>c</b>) 400 °C.</p>
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<p>Load–deflection curves of the critical screw in the large-scale FE model.</p>
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<p>Stress distribution at the pull-through failure of corrugated cladding at 600 °C.</p>
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<p>Influence of Young’s modulus on the pull-through capacity.</p>
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<p>Influence of pitch on the pull-through capacity.</p>
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<p>Influence of crest height on the pull-through capacity.</p>
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<p>Influence of radius on the pull-through capacity.</p>
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<p>Influence of span on the pull-through capacity.</p>
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<p>Load reduction factors from uniform pressure loading and line-loading FE models and line-load and small-scale tests.</p>
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18 pages, 25764 KiB  
Article
Evaluating Landsat- and Sentinel-2-Derived Burn Indices to Map Burn Scars in Chyulu Hills, Kenya
by Mary C. Henry and John K. Maingi
Fire 2024, 7(12), 472; https://doi.org/10.3390/fire7120472 - 11 Dec 2024
Viewed by 475
Abstract
Chyulu Hills, Kenya, serves as one of the region’s water towers by supplying groundwater to surrounding streams and springs in southern Kenya. In a semiarid region, this water is crucial to the survival of local people, farms, and wildlife. The Chyulu Hills is [...] Read more.
Chyulu Hills, Kenya, serves as one of the region’s water towers by supplying groundwater to surrounding streams and springs in southern Kenya. In a semiarid region, this water is crucial to the survival of local people, farms, and wildlife. The Chyulu Hills is also very prone to fires, and large areas of the range burn each year during the dry season. Currently, there are no detailed fire records or burn scar maps to track the burn history. Mapping burn scars using remote sensing is a cost-effective approach to monitor fire activity over time. However, it is not clear whether spectral burn indices developed elsewhere can be directly applied here when Chyulu Hills contains mostly grassland and bushland vegetation. Additionally, burn scars are usually no longer detectable after an intervening rainy season. In this study, we calculated the Differenced Normalized Burn Ratio (dNBR) and two versions of the Relative Differenced Normalized Burn Ratio (RdNBR) using Landsat Operational Land Imager (OLI) and Sentinel-2 MultiSpectral Instrument (MSI) data to determine which index, threshold values, instrument, and Sentinel near-infrared (NIR) band work best to map burn scars in Chyulu Hills, Kenya. The results indicate that the Relative Differenced Normalized Burn Ratio from Landsat OLI had the highest accuracy for mapping burn scars while also minimizing false positives (commission error). While mapping burn scars, it became clear that adjusting the threshold value for an index resulted in tradeoffs between false positives and false negatives. While none were perfect, this is an important consideration going forward. Given the length of the Landsat archive, there is potential to expand this work to additional years. Full article
(This article belongs to the Special Issue Fire in Savanna Landscapes, Volume II)
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<p>Location of Chyulu Hills, Kenya, in East Africa. Protected areas are shown in hatch-filled areas with labels in legend. Study area falls within three counties, Kajiado, Makueni, and Taita Taveta, as shown in map. Elevation is also shown in map, with higher elevations in white. Major roads include Mombasa Road to east of study area.</p>
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<p>Flow chart showing methods used in this study. OLI = Operational Land Imager, OLI2 = Operational Land Imager 2; MSI = MultiSpectral Instrument; BOA = Bottom of Atmosphere Reflectance; NBR = Normalized Burn Ratio; dNBR = Differenced Normalized Burn Ratio; RdNBR = Relative Differenced Normalized Burn Ratio; RdNBR2 = Relative Differenced Normalized Burn Ratio alternate calculation. Boxes with bold outline indicate inputs to final analysis.</p>
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<p>Mapped burn scars for the 2021 fire season in Chyulu Hills, Kenya. Yellow shows areas mapped as burned using Landsat RdNBR with a threshold of 0.23. Clouds and cloud shadows are masked out and shown in black. Purple boundaries indicate protected areas in the Chyulu Hills.</p>
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<p>Mapped burn scars for the 2021 fire season in Chyulu Hills, Kenya. Yellow shows areas mapped as burned using Sentinel-2 RdNBR with a threshold of 0.22. Clouds and cloud shadows are masked out and shown in black. Purple boundaries indicate protected areas in the Chyulu Hills.</p>
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12 pages, 2331 KiB  
Article
Electrical Home Fire Injuries Analysis
by Mark John Taylor, John Fielding and John O’Boyle
Fire 2024, 7(12), 471; https://doi.org/10.3390/fire7120471 - 10 Dec 2024
Viewed by 421
Abstract
Domestic electrical fires can occur for a variety of reasons, including faulty wiring and plugs, overloaded circuits, and malfunctioning electrical appliances. In this article, the circumstances of domestic electrical fire injuries between 2011 and 2022 in the county of Merseyside in Northwestern England [...] Read more.
Domestic electrical fires can occur for a variety of reasons, including faulty wiring and plugs, overloaded circuits, and malfunctioning electrical appliances. In this article, the circumstances of domestic electrical fire injuries between 2011 and 2022 in the county of Merseyside in Northwestern England were examined in order to inform fire prevention activities. Householder carelessness appeared to be less of a factor in electrical fire injury compared to other types of fire injury such as cooking or smoking fire injury. Faulty electricity supplies were the main cause of electrical fire injuries. Male residents were slightly more likely to sustain injury in an electrical fire in comparison to females (1.25 to 1). Those aged 75+ appeared to be more at risk of electrical fire injuries compared to other age groups. Full article
(This article belongs to the Special Issue Fire Detection and Public Safety, 2nd Edition)
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<p>Overall domestic and electrical domestic fire injuries in Merseyside 2011 to 2022.</p>
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<p>Domestic electrical fire injury by ignition source in Merseyside between 2011 and 2022.</p>
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<p>Domestic electrical fire injuries by room of origin of fire in Merseyside between 2011 and 2022.</p>
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<p>Domestic electrical fire injuries by property type in Merseyside between 2011 and 2022.</p>
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<p>Domestic electrical fire injuries by time of day in Merseyside between 2011 and 2022.</p>
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<p>Domestic electrical fire injuries per 100,000 of population between 2011 and 2022 in Merseyside.</p>
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<p>Domestic electrical fire injury types in Merseyside between 2011 and 2022.</p>
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22 pages, 2067 KiB  
Review
Synthesis and Perspectives on Disturbance Interactions, and Forest Fire Risk and Fire Severity in Central Europe
by Leonardos Leonardos, Anne Gnilke, Tanja G. M. Sanders, Christopher Shatto, Catrin Stadelmann, Carl Beierkuhnlein and Anke Jentsch
Fire 2024, 7(12), 470; https://doi.org/10.3390/fire7120470 - 9 Dec 2024
Viewed by 592
Abstract
Wildfire risk increases following non-fire disturbance events, but this relationship is not always linear or cumulative, and previous studies are not consistent in differentiating between disturbance loops versus cascades. Previous research on disturbance interactions and their influence on forest fires has primarily focused [...] Read more.
Wildfire risk increases following non-fire disturbance events, but this relationship is not always linear or cumulative, and previous studies are not consistent in differentiating between disturbance loops versus cascades. Previous research on disturbance interactions and their influence on forest fires has primarily focused on fire-prone regions, such as North America, Australia, and Southern Europe. In contrast, less is known about these dynamics in Central Europe, where wildfire risk and hazard are increasing. In recent years, forest disturbances, particularly windthrow, insect outbreaks, and drought, have become more frequent in Central Europe. At the same time, climate change is influencing fire weather conditions that further intensify forest fire dynamics. Here, we synthesize findings from the recent literature on disturbance interactions in Central Europe with the aim to identify disturbance-driven processes that influence the regional fire regime. We propose a conceptual framework of interacting disturbances that can be used in wildfire risk assessments and beyond. In addition, we identify knowledge gaps and make suggestions for future research regarding disturbance interactions and their implications for wildfire activity. Our findings indicate that fire risk in the temperate forests of Central Europe is increasing and that non-fire disturbances and their interactions modify fuel properties that subsequently influence wildfire dynamics in multiple ways. Full article
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<p>Geographic extent of the ‘Central European Mixed Forests’ and ‘Western European Broadleaf Forests’ ecoregions, and the respective burned forest area of each country for the period between 2000 and 2023. Figure was created using the ‘leafletR’ package (v. 0.4-0) [<a href="#B110-fire-07-00470" class="html-bibr">110</a>] in R (v. 4.4.1) [<a href="#B111-fire-07-00470" class="html-bibr">111</a>]. Data on the burned area were retrieved from the European Forest Fire Information System (EFFIS) (Available at: <a href="https://forest-fire.emergency.copernicus.eu/applications/data-and-services" target="_blank">https://forest-fire.emergency.copernicus.eu/applications/data-and-services</a>, accessed on 13 October 2024).</p>
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<p>(<b>a</b>) Summary and conceptual framework of disturbance interactions and their influence on fuel and fire properties in Central Europe. Lines with arrows indicate a generally positive interaction from one disturbance to the other. Dotted lines with arrows indicate a weak positive interaction between disturbances. Lines with no arrows indicate a mixed (both positive and negative) interaction. Disturbance interactions fall under the influence of fire weather, which in turn is affected by climate change. The black line and arrow indicate the positive interaction of both biotic disturbances on fuel load. Since no quantitative analysis was performed, circle size does not correspond to the influence of one disturbance agent on another; text and circle sizes, colours, lines, and arrows have been optimized purely for visualization purposes. (<b>b</b>) Mixed or unclear disturbance interactions in Central Europe that form research gaps. Circle size does not correspond to the potential influence of one disturbance agent on another; text and circle sizes, colours, lines, and arrows have been optimized purely for visualization purposes. Figures were generated using ‘Miro’ (Available at: <a href="http://www.miro.com/app" target="_blank">www.miro.com/app</a>, accessed on 4 December 2024).</p>
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<p>(<b>a</b>) Summary and conceptual framework of disturbance interactions and their influence on fuel and fire properties in Central Europe. Lines with arrows indicate a generally positive interaction from one disturbance to the other. Dotted lines with arrows indicate a weak positive interaction between disturbances. Lines with no arrows indicate a mixed (both positive and negative) interaction. Disturbance interactions fall under the influence of fire weather, which in turn is affected by climate change. The black line and arrow indicate the positive interaction of both biotic disturbances on fuel load. Since no quantitative analysis was performed, circle size does not correspond to the influence of one disturbance agent on another; text and circle sizes, colours, lines, and arrows have been optimized purely for visualization purposes. (<b>b</b>) Mixed or unclear disturbance interactions in Central Europe that form research gaps. Circle size does not correspond to the potential influence of one disturbance agent on another; text and circle sizes, colours, lines, and arrows have been optimized purely for visualization purposes. Figures were generated using ‘Miro’ (Available at: <a href="http://www.miro.com/app" target="_blank">www.miro.com/app</a>, accessed on 4 December 2024).</p>
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14 pages, 517 KiB  
Review
Effects of Wildfire Exposure on the Human Immune System
by Davide Frumento and Ștefan Țãlu
Fire 2024, 7(12), 469; https://doi.org/10.3390/fire7120469 - 9 Dec 2024
Viewed by 428
Abstract
Wildfires have become a significant environmental and public health concern worldwide, particularly due to their increased frequency and intensity driven by climate change. Wildfire smoke, composed of a complex mixture of particulate matter, gases and chemicals, has been linked to numerous health issues, [...] Read more.
Wildfires have become a significant environmental and public health concern worldwide, particularly due to their increased frequency and intensity driven by climate change. Wildfire smoke, composed of a complex mixture of particulate matter, gases and chemicals, has been linked to numerous health issues, primarily affecting the respiratory and cardiovascular systems. However, emerging evidence suggests that wildfire smoke exposure also has profound effects on the immune system. This review aims to synthesize current knowledge on how wildfire smoke exposure affects the human immune system, including acute and chronic impacts, underlying mechanisms and potential long-term consequences. The review discusses the role of inflammation, oxidative stress and immune cell modulation in response to wildfire smoke, highlighting the need for further research to fully understand these effects. Full article
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<p>Immune regulation methods.</p>
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19 pages, 10640 KiB  
Article
Fire Risk Assessment and Driving Factor Analysis for the Building Complex of the Palace Museum in China
by Xinwei Yang, Zhanfeng Shen, Yating Lei, Bo Wang and Jinzhou Liu
Fire 2024, 7(12), 468; https://doi.org/10.3390/fire7120468 - 7 Dec 2024
Viewed by 489
Abstract
The unique structure of ancient buildings poses a significant risk of fire hazards, so the assessment of potential fire risk is of great significance to fire safety management. This paper examines the fire risk associated with the building complex of the Palace Museum. [...] Read more.
The unique structure of ancient buildings poses a significant risk of fire hazards, so the assessment of potential fire risk is of great significance to fire safety management. This paper examines the fire risk associated with the building complex of the Palace Museum. Firstly, a fire risk assessment indicator system was constructed based on three dimensions: hazard factors, sensitivity of hazard-bearing bodies, and loss control factors. Secondly, the weight values for each index were calculated based on the entropy weight method. Finally, the monthly fire risk assessment levels in the year 2019 were visualized by using a geographic information system. Based on the fire risk assessment results, this study quantitatively reveals the fire risk driving mechanism of ancient buildings in the Palace Museum from the perspective of spatial stratified heterogeneity by using the geodetector model. The results show that there are differences between the main factors that affect the weight of fire risk assessment and the main factors that cause the spatial heterogeneity of fire risk. Factors such as the safety protective grade and staff number contribute to a stronger explanation of the spatial stratified heterogeneity for fire risk within the museum. The results can help us to understand the driving factors affecting the distribution patterns of fire risk for the Palace Museum and could provide support for the formulation of fire prevention and safety management measures. Full article
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<p>The Three Great Halls of the Palace Museum.</p>
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<p>The Three Great Halls of the Palace Museum.</p>
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<p>(<b>a</b>,<b>b</b>) Remote sensing image of the Palace Museum and the extracted building vector data.</p>
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<p>(<b>a</b>–<b>d</b>) The monthly temporal indicator data of the Palace Museum in 2019.</p>
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<p>The index weight obtained from the entropy weight method.</p>
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<p>Month-to-month fire risk assessment of the Palace Museum in 2019.</p>
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<p>Month-to-month fire risk assessment of the Palace Museum in 2019.</p>
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<p>The monthly <span class="html-italic">q</span> value for each of the fire risk indices based on the factor detector.</p>
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<p>The monthly interaction relation of fire risk indices based on interaction detector.</p>
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<p>The monthly interaction relation of fire risk indices based on interaction detector.</p>
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<p>The monthly statistical result of the number of buildings with different fire risk levels.</p>
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19 pages, 5918 KiB  
Article
Attica: A Hot Spot for Forest Fires in Greece
by Margarita Arianoutsou, George Athanasakis, Dimitrios Kazanis and Anastasia Christopoulou
Fire 2024, 7(12), 467; https://doi.org/10.3390/fire7120467 - 6 Dec 2024
Viewed by 582
Abstract
(1) Background: Forest fires are widespread in Mediterranean-climate regions and are becoming very common in urban and peri-urban areas. (2) Methods: Wildfires in Attica since 1977 are mapped and types of vegetation burned are reported. (3) Results: Fires are becoming larger. During the [...] Read more.
(1) Background: Forest fires are widespread in Mediterranean-climate regions and are becoming very common in urban and peri-urban areas. (2) Methods: Wildfires in Attica since 1977 are mapped and types of vegetation burned are reported. (3) Results: Fires are becoming larger. During the period of study (1977–2024), 45% of the burned area was covered with Pinus halepensis forests, 1.4% with Abies cephalonica forests, and 18.5% with shrublands. A relatively high percentage of the burned area (BA) affected more than once consisted of pine forests (65%). Ten percent of the total BA lies within the boundaries of the Natura 2000 network, Europe’s most important network of protected areas, of which 38.9% was burned. At the interannual scale, the BA in Attica is negatively correlated with relative humidity, while reduced precipitation may contribute to the expansion of wildfires. (4) Conclusions: Fires are becoming larger over time, with low humidity increasing the higher fire risk. Since the changing climate is expected to create more severe and uncontrollable conditions, mitigation and adaptation measures should be planned and be introduced immediately. Full article
(This article belongs to the Special Issue Effects of Fires on Forest Ecosystems)
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<p>Comparison of observed versus predicted total burned area in relation to the number of fires, using the generalized linear model (GLM) with the gamma family.</p>
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<p>Area burned in Attica during the study period (1977–2024). Only fire events larger than 150 hectares are included.</p>
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<p>Delineation of the burned areas in Attica Prefecture over the entire study period, along with the areas burned multiple times. Only fires larger than 150 hectares are included. Data Sources: Landsat 8 / USGS, RGB: Gray Scale. Resolution: 30 m. <a href="https://earthexplorer.usgs.gov/" target="_blank">https://earthexplorer.usgs.gov/</a>.</p>
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<p>Mean fire interval per mountain range for the period 1977–2024.</p>
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<p>Total vegetation burned across the study period (1977–2024). Data Sources: Landsat 8/USGS, RGB: Gray Scale, Resolution: 30 m. <a href="https://earthexplorer.usgs.gov/" target="_blank">https://earthexplorer.usgs.gov/</a>.</p>
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<p>Areas burned at least twice during the fire interval of 15 years and vegetation types burned. Data sources: Landsat-2, 8/USGS, RGB: Gray Scale, Resolution: 30 m. <a href="https://earthexplorer.usgs.gov/" target="_blank">https://earthexplorer.usgs.gov/</a>.</p>
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<p>Areas designated as Natura 2000 sites in Attica Prefecture, depicted over the total BA during the study period. Landsat-2, 9/USGS, RGB: Gray Scale, Resolution: 30 m. <a href="https://earthexplorer.usgs.gov/" target="_blank">https://earthexplorer.usgs.gov/</a>.</p>
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<p>BAs within the Natura 2000 Network during the period 1997–2024. Landsat-2, 9/USGS, RGB: Gray Scale, Resolution: 30 m. <a href="https://earthexplorer.usgs.gov/" target="_blank">https://earthexplorer.usgs.gov/</a>.</p>
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21 pages, 29630 KiB  
Article
Climatic Indicators and Their Variation Trends as Conditions for Forest Flammability Hazard in the South of Tyumen Oblast
by Elza Kuznetsova, Olesia Marchukova, Vera Kuznetsova, Alyona Pigaryova, Natalia Zherebyateva and Natalia Moskvina
Fire 2024, 7(12), 466; https://doi.org/10.3390/fire7120466 - 6 Dec 2024
Viewed by 456
Abstract
This study analyzes the forest flammability hazard in the south of Tyumen Oblast (Western Siberia, Russia) and identifies variation patterns in fire areas depending on weather and climate characteristics in 2008–2023. Using correlation analysis, we proved that the area of forest fires is [...] Read more.
This study analyzes the forest flammability hazard in the south of Tyumen Oblast (Western Siberia, Russia) and identifies variation patterns in fire areas depending on weather and climate characteristics in 2008–2023. Using correlation analysis, we proved that the area of forest fires is primarily affected by maximum temperature, relative air humidity, and the amount of precipitation, as well as by global climate change associated with an increase in carbon dioxide in the atmosphere and the maximum height of snow cover. As a rule, a year before the period of severe forest fires in the south of Tyumen Oblast, the height of snow cover is insignificant, which leads to insufficient soil moisture in the following spring, less or no time for the vegetation to enter the vegetative phase, and the forest leaf floor remaining dry and easily flammable, which contributes to an increase in the fire area. According to the estimates of the CMIP6 project climate models under the SSP2-4.5 scenario, by the end of the 21st century, a gradual increase in the number of summer temperatures above 35 °C is expected, whereas the extreme SSP5-8.5 scenario forecasts the tripling in the number of such hot days. The forecast shows an increase of fire hazardous conditions in the south of Tyumen Oblast by the late 21st century, which should be taken into account in the territory’s economic development. Full article
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<p>Stages of analyzing climatic indicators and determining their variation trends as conditions for forest flammability hazard in the south of Tyumen Oblast.</p>
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<p>Taylor diagrams comparing the CMIP6 models and their ensembles with observed data of the air temperature at Tyumen (<b>a</b>) and Ishim (<b>b</b>) weather stations during 1988–2023.</p>
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<p>Visualized Landsat images of the territory of Tyumen District: fires in 1998 (Landsat-5/TM in the synthesis of SWIR-NIR-GREEN channels) (<b>a</b>), fires in 2008 (Landsat-5/TM in the synthesis of SWIR-NIR-GREEN channels) (<b>b</b>), fires in 2017 (Landsat-8/OLI in the synthesis of SWIR-NIR-GREEN channels) (<b>c</b>), and fires in 2023 (Landsat-8/OLI in the synthesis of SWIR-NIR-GREEN channels) (<b>d</b>).</p>
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<p>Number and area of forest fires in the south of Tyumen Oblast in 2008–2023.</p>
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<p>Average annual air temperature (°C) for the period of 1988–2023, according to meteorological stations in Tyumen (blue line) and Ishim (red line), and linear trends.</p>
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<p>Total annual precipitation (mm) in 1988–2023 according to meteorological stations in Tyumen (blue columns) and Ishim (light green columns), and linear trends.</p>
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<p>Average annual relative air humidity (%) in 1988–2023, according to meteorological stations in Tyumen (blue columns) and Ishim (light green columns), and linear trends.</p>
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<p>Maximum snow depth per year (cm) in 1988–2023, according to meteorological stations in Tyumen (blue columns) and Ishim (light green columns), and linear trends.</p>
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<p>Spatial distribution of trend values in average monthly air temperature for the set of 34 CMIP6 project models for SSP2-4.5 (<b>a</b>) and SSP5-8.5 (<b>b</b>) scenarios for the period from 2024 to 2100.</p>
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<p>Spatial distribution of trend values in monthly temperatures for the set of 32 CMIP6 project models for SSP2-4.5 (<b>a</b>) and SSP5-8.5 (<b>b</b>) scenarios for the period from 2024 to 2100.</p>
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<p>Spatial distribution of trend values of the average monthly values of the average daily precipitation accumulation in the form of snow (mm) for the set of 29 CMIP6 project models for SSP2-4.5 (<b>a</b>) and SSP5-8.5 (<b>b</b>) scenarios for the period from 2024 to 2100.</p>
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<p>Total number of days with temperatures above 35 °C averaged for the south of Tyumen Oblast for the set of 27 CMIP6 project models for SSP2-4.5 (<b>a</b>) and SSP5-8.5 (<b>b</b>) scenarios for 2026–2050, 2051–2075, and 2076–2100.</p>
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<p>Total annual number of consecutive dry days for the south of Tyumen Oblast for the set of 31 CMIP6 project models for SSP2-4.5 and SSP5-8.5 scenarios for 2026–2050, 2051–2075, and 2076–2100.</p>
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<p>Empirical distribution functions (blue columns) and their normal distributions (red line) of four annual meteorological characteristics in Tyumen and Ishim from 1988 to 2023.</p>
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<p>Taylor diagrams comparing the CMIP6 models and their ensembles with observed data of the air temperature at the Tyumen weather stations during 1988–2023.</p>
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<p>Taylor diagrams comparing the CMIP6 models and their ensembles with observed data of the air temperature at the Ishim weather stations during 1988–2023.</p>
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12 pages, 1695 KiB  
Technical Note
Personality Fuels the Fire: Predicting Firefighter Physical Readiness
by Annmarie Chizewski and Steven J. Petruzzello
Fire 2024, 7(12), 465; https://doi.org/10.3390/fire7120465 - 6 Dec 2024
Viewed by 369
Abstract
Many firefighters have inadequate levels of physical fitness which can impair firefighting performance. Understanding the factors that influence exercise and fitness behaviors could help identify those less likely to stay physically fit. Methods: A sample (N = 45) of male recruit firefighters [...] Read more.
Many firefighters have inadequate levels of physical fitness which can impair firefighting performance. Understanding the factors that influence exercise and fitness behaviors could help identify those less likely to stay physically fit. Methods: A sample (N = 45) of male recruit firefighters were assessed during weeks 1 and 7 of a state firefighter academy. Measures included cardiovascular fitness, muscular fitness, performance on firefighter ability tasks, exercise intensity preference/tolerance, and extraversion. Results: Exercise intensity preference was directly related to physical fitness, which in turn was directly related to firefighter ability. Regression analyses showed that exercise intensity preference predicted variance in firefighter ability, and this relationship was statistically mediated by physical fitness levels. Firefighters with higher exercise intensity preference tended to have better physical fitness, which was associated with superior performance on firefighter tasks. Conclusions: These findings suggest that firefighters’ exercise intensity preferences play a key role in their physical fitness and, ultimately, their firefighting abilities. Assessing recruits’ exercise intensity preferences could help identify those who may struggle to maintain fitness, allowing for targeted interventions. Improving firefighters’ exercise intensity preference may be an effective strategy for enhancing their physical capabilities and job performance. Full article
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<p>Assessment components of the firefighter combat challenge (AFC) conducted at Week 1 and Week 7: This figure illustrates three critical tasks used to evaluate firefighter physical ability and job-specific performance. (<b>a</b>) Keiser<sup>®</sup> Force Machine Sled Test (Forcible Entry Simulation); (<b>b</b>) Charged Hose Advance; (<b>c</b>) Equipment Carry. Each task was timed and scored according to standardized protocols, with assessments conducted at both Week 1 and Week 7 to measure training adaptations and performance improvements.</p>
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<p>Week 1 mediation model: Path analysis demonstrating the relationships between personality traits (preference for exercise intensity), physical fitness components (cardiovascular and muscular endurance), and firefighter ability during Week 1 of training. Standardized regression coefficients (β) are shown on each path. The model reveals that preference had significant indirect effects on firefighter ability through both cardiovascular endurance (β = 0.344, <span class="html-italic">p</span> &lt; 0.05) and muscular endurance (β = 0.327, <span class="html-italic">p</span> &lt; 0.05). Direct paths from physical fitness components to firefighter ability indicate significant associations, suggesting a complex relationship between fitness metrics and overall firefighter performance in the initial training phase. In the figure, a single asterisk (*) indicates <span class="html-italic">p</span> &lt; 0.05, while double asterisks (**) represent <span class="html-italic">p</span> &lt; 0.001.</p>
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<p>Week 7 mediation model: Path analysis illustrating the relationships between personality traits (preference), physical fitness components (cardiovascular and muscular endurance), and firefighter ability after 7 weeks of training. The model demonstrates persistent significant associations between preference and both fitness components (cardiovascular: β = 0.316, <span class="html-italic">p</span> &lt; 0.05; muscular: β = 0.304, <span class="html-italic">p</span> &lt; 0.05). In the figure, a single asterisk (*) indicates <span class="html-italic">p</span> &lt; 0.05, while double asterisks (**) represent <span class="html-italic">p</span> &lt; 0.001.</p>
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13 pages, 3709 KiB  
Article
Simulations on Evacuation Strategy and Evacuation Process of the Subway Train Under the Fire
by Xingji Wang, Bin Liu, Weilian Ma, Yuehai Feng, Qiang Li and Ting Sun
Fire 2024, 7(12), 464; https://doi.org/10.3390/fire7120464 - 6 Dec 2024
Viewed by 497
Abstract
This study focuses on the safe evacuation strategy and evacuation process in the subway train under the fires. The subway station evacuation mode should be adopted if the power system of a subway train is normal on fire. While, the tunnel evacuation mode [...] Read more.
This study focuses on the safe evacuation strategy and evacuation process in the subway train under the fires. The subway station evacuation mode should be adopted if the power system of a subway train is normal on fire. While, the tunnel evacuation mode should be adopted if the power system of the train fails because of the effects of fire. Under the tunnel evacuation mode, the direction of tunnel smoke should be opposite to that of most passengers, and passengers should be evacuated toward the fresh wind. By using the numerical simulation software Pathfinder and PyroSim, the passenger evacuation time under different conditions is calculated, and the safety of the evacuation process is evaluated. The results show that the evacuation time of the station evacuation mode is obviously shorter than that of the tunnel evacuation mode. With the same conditions, the evacuation time of the tunnel evacuation mode is 2193 s, which is about four times as much as the evacuation time of the station evacuation mode (526 s). The total evacuation time increases with the total number of passengers and the proportion of older people and children. Under an oil pool fire, which is an extreme fire condition, the fire environment inside the train may reach a level threatening the passengers’ safety before the evacuation is complete, even before the door opens; therefore, special attention should be paid to the safety issues in stage from the fire begins to the evacuation complete. Full article
(This article belongs to the Special Issue Fire Numerical Simulation, Second Volume)
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<p>Nine typical evacuation modes under the tunnel evacuation conditions (<span class="html-italic">s</span>: evacuate distance that passengers need to walk to the safety exit; <span class="html-italic">l</span>: length of the tunnel between the two contact channels).</p>
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<p>Simulation models of the subway train, the tunnel, and the platform of the subway station.</p>
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<p>Evacuation process in the subway train and the platform in Case 1 (Unit: person/m<sup>2</sup>).</p>
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<p>Curve of the evacuation passengers versus time in Cases 1 to 3.</p>
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<p>Temperature profiles inside the subway train in the baggage and oil pool fire conditions before the door opened (Range: the fire carriage and its adjacent carriages; Unit: °C).</p>
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<p>Distribution of the passengers inside the carriages under different personnel densities.</p>
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<p>Evacuation process for passengers in a subway train and the tunnel in Case 4 (Unit: People/m<sup>2</sup>).</p>
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<p>Curve of the evacuation passengers versus time in Case 4.</p>
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<p>Smoke movement and temperature distribution in a tunnel for luggage fire and oil pool fire with different smoke exhaust conditions.</p>
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<p>The curve of evacuees versus time in Cases 5 to 9.</p>
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21 pages, 5876 KiB  
Article
Effect of Combining Fungal and Flame-Retardant Coatings on the Thermal Degradation of Spruce and Beech Wood Under Flame Loading
by Bohuš Leitner, Stanislava Gašpercová, Iveta Marková and Ivana Tureková
Fire 2024, 7(12), 463; https://doi.org/10.3390/fire7120463 - 6 Dec 2024
Viewed by 554
Abstract
Compliance with fire safety standards for wood is crucial for its application in the internal applications of buildings. This article focuses on monitoring the quality of protective coatings for wood under thermal loading conditions. The examined samples of spruce (Picea abies L. [...] Read more.
Compliance with fire safety standards for wood is crucial for its application in the internal applications of buildings. This article focuses on monitoring the quality of protective coatings for wood under thermal loading conditions. The examined samples of spruce (Picea abies L. Karst.) and beech wood (Fagus sylvatica L.) were treated with selected fungicidal coatings based on dimethylbenzyl ammonium chloride. Following this, they were soaked in a ferric phosphate-based flame-retardant solution. Additionally, a portion of the samples was treated solely with the flame retardant. The effectiveness of the protective coatings was assessed through experimental thermal loading of the prepared samples. The testing method adhered to according to selected standards, which evaluate the ignitability of building materials when subjected to a small flame source. The experimental results, including the mass loss, mass loss rate, and time–temperature curves of the thermally loaded samples, demonstrated a significant influence of the selected coatings on thermal degradation. Notably, the fungicidal coating exhibited protective properties. Samples treated only with the flame retardant showed higher mass losses compared to those treated first with the fungicidal coating followed by the retardant. Additionally, differences were observed between the wood types, with beech samples exhibiting greater mass losses and higher mass loss rates than spruce. Full article
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<p>(<b>a</b>) Schematic diagram of the test equipment (description: 1—gas cylinder, 2—shut-off valve, 3—flow regulator, 4—gas intake tube, 5—burner holder, 6—burner, 7—gas flow regulator on the burner, 8—scales, 9—sample holder, 10—sample, 11—connection between scales and computer, 12—computer) [<a href="#B56-fire-07-00463" class="html-bibr">56</a>]; (<b>b</b>) demonstration of measuring spruce modified with the retardant SPFREx at the 25th minute of the experiment.</p>
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<p>Spruce samples after the experiment in all combinations: (<b>a</b>) untreated spruce stored in the SPIn interior; (<b>b</b>) spruce treated with HR retardant, stored in the SPFRIn interior; (<b>c</b>) spruce treated with Bio fungicide coating and FR retarder, stored in the SPBioFRIn interior; (<b>d</b>) spruce treated with Fun fungicide coating and FR retardant, stored in the SPFunFRIn interior; (<b>e</b>) untreated spruce stored outdoors (SPEx); (<b>f</b>) spruce treated with FR retardant, stored outdoors (SPHREx); (<b>g</b>) spruce treated with Bio fungicide coating and FR retardant, stored outdoors (SPBioFREx); (<b>h</b>) spruce treated with Fun fungicide coating and FR retardant, stored outdoors (SPFunFREx).</p>
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<p>Actual mass loss of spruce samples during the experiment. Legend: black square with a red frame: SP—untreated spruce sample; dark-blue triangle: spruce treated with retardant and stored indoors (SPFRIn); light-blue triangle: spruce treated with retardant and stored outdoors (SPFREx); yellow rhombus: spruce treated with Bio fungicide coating and FR retardant, stored indoors (SPBioFRIn); green rhombus: spruce treated with Bio fungicide coating and FR retardant, stored outdoors (SPBioFREx); red rhombus: spruce treated with Fun fungicide coating and FR retardant, stored indoors (BCHFunFRIn); red circle: spruce treated with Fun fungicide coating and FR retardant, stored outdoors (SPFunFREx).</p>
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<p>Mass losses on spruce samples. Legend: black square with red frame: SP—untreated spruce sample; dark-blue triangle: spruce treated with retardant and stored indoors (SPFRIn); light-blue triangle: spruce treated with retardant and stored outdoors (SPFREx); yellow rhombus: spruce treated with Bio fungicide coating and FR retardant, stored indoors (SPBioFRIn); green rhombus: spruce treated with Bio fungicide coating and FR retardant, stored outdoors (SPBioFREx); red rhombus: spruce treated with Fun fungicide coating and FR retardant, stored indoors (BCHFunFRIn); red circle: spruce treated with Fun fungicide coating and FR retardant, stored outdoors (SPFunFREx).</p>
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<p>Comparison of mass loss rates of spruce samples. Legend: black cube with red frame (BCH): untreated spruce sample; dark-blue triangle: spruce treated with retardant and stored indoors (BCHFRIn); light-blue triangle: spruce treated with retardant and stored outdoors (BCHFREx); yellow diamond: spruce treated with fungicide coating (Bio) and retardant FR, and stored indoors (BCHBioFRIn); green diamond: spruce treated with fungicide coating (Bio) and retardant FR, and stored outdoors (BCHBioFREx); red diamond: spruce treated with fungicide coating (Fun) and retardant FR, and stored indoors (BCHFunFRIn); red circle: spruce treated with fungicide coating (Fun) and retardant FR, and stored outdoors (BCHFunFREx).</p>
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<p>Actual mass loss of beech samples during the experiment. Legend: black cube with a red frame (BCH): untreated beech sample, dark-blue triangle: beech treated with a fire retardant and stored indoors (BCHFRIn); light-blue triangle: beech treated with a fire retardant and stored outdoors (BCHFREx); yellow diamond: beech treated with a Bio fungicide coating and a fire retardant FR, stored indoors (BCHBioFRIn); green diamond: beech treated with a Bio fungicide coating and a fire retardant FR, stored outdoors (BCHBioFREx); red diamond: beech treated with a Fun fungicide coating and a fire retardant FR, stored indoors (BCHFunFRIn); red circle: beech treated with a Fun fungicide coating and a fire retardant FR, stored outdoors (BCHFunFREx).</p>
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<p>Mass loss in beech samples. Legend: black cube with a red frame (BCH): untreated beech sample; dark-blue triangle: beech treated with a fire retardant and stored indoors (BCHFRIn); light-blue triangle: beech treated with a fire retardant and stored outdoors (BCHFREx); yellow diamond: beech treated with Bio fungicide coating and a fire retardant FR, stored indoors (BCHBioFRIn); green diamond: beech treated with Bio fungicide coating and a fire retardant FR, stored outdoors (BCHBioFREx); red diamond: beech treated with Fun fungicide coating and a fire retardant FR, stored indoors (BCHFunFRIn); red circle: beech treated with Fun fungicide coating and a fire retardant FR, stored outdoors (BCHFunFREx).</p>
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<p>Beech samples after the experiment in all combinations: (<b>a</b>) untreated beech, stored indoors (BCHIn); (<b>b</b>) spruce treated with fire retardant (FR), stored indoors (BCHFRIn); (<b>c</b>) spruce treated with Bio fungicide coating and fire retardant (FR), stored indoors (BCHBioFRIn); (<b>d</b>) spruce treated with Fun fungicide coating and fire retardant (FR), stored indoors (BCHFunFRIn); (<b>e</b>) untreated spruce, stored outdoors (BCHEx); (<b>f</b>) spruce treated with fire retardant (FR), stored outdoors (BCHFREx); (<b>g</b>) spruce treated with Bio fungicide coating and fire retardant (FR), stored outdoors (BCHBioFREx); (<b>h</b>) spruce treated with Fun fungicide coating and fire retardant (FR), stored outdoors (BCHFunFREx).</p>
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<p>Comparison of mass loss rates in beech samples. Legend: black cube with a red frame (BCH): untreated beech sample; dark-blue triangle: beech treated with a fire retardant and stored indoors (BCHFRIn); light-blue triangle: beech treated with a fire retardant and stored outdoors (BCHFREx); yellow diamond: beech treated with Bio fungicide coating and a fire retardant FR, stored indoors (BCHBioFRIn); green diamond: beech treated with Bio fungicide coating and a fire retardant FR, stored outdoors (BCHBioFREx); red diamond: beech treated with Fun fungicide coating and a fire retardant FR, stored indoors (BCHFunFRIn); red circle: beech treated with Fun fungicide coating and a fire retardant FR, stored outdoors (BCHFunFREx).</p>
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<p>Examples of creating the thickness of the charred layer of selected spruce’s samples. (<b>a</b>) sample SPFunFRIn at 22 min ex-perimental time; (<b>b</b>) sample SPFunFRIn at 20 min experimental time. Legend: red arrows show the thickness of the char layer created durring experiment.</p>
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<p>Mutual comparison of the observed parameters “ν”, “Δm”, and “R” between spruce and beech samples.</p>
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<p>Mutual comparison of the observed parameters “ν”, “Δm”, and “R” between the Bio and Fun fungicidal coatings. (<b>a</b>) Δm(τ)—mass loss (g); (<b>b</b>) R—charring layer (mm); (<b>c</b>) ν(τ)—mass loss rate (%.s<sup>−1</sup>).</p>
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<p>Mutual comparison of the observed parameters “ν”, “Δm”, and “R” between storage locations (indoor and outdoor). (<b>a</b>) ν(τ)—mass loss rate (%.s<sup>−1</sup>); (<b>b</b>) Δm(τ)—mass loss (g); (<b>c</b>) R—charring layer (mm).</p>
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<p>Mutual comparison of the observed parameters “ν”, “Δm”, and “R” between storage locations (indoor and outdoor). (<b>a</b>) ν(τ)—mass loss rate (%.s<sup>−1</sup>); (<b>b</b>) Δm(τ)—mass loss (g); (<b>c</b>) R—charring layer (mm).</p>
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19 pages, 4373 KiB  
Article
Study on Public Perceptions and Disaster Prevention Framework of Tunnel Fires Based on Social Media and Artificial Intelligence
by Chuyao Lai, Yuxin Zhang, Xiaofan Tang and Chao Guo
Fire 2024, 7(12), 462; https://doi.org/10.3390/fire7120462 - 6 Dec 2024
Viewed by 471
Abstract
To investigate public perceptions regarding tunnel fire disasters and optimize the tunnel fire disaster prevention framework, this study takes the emerging social media platform Douyin as a case study, conducting an in-depth analysis of 2133 short videos related to tunnel fires on the [...] Read more.
To investigate public perceptions regarding tunnel fire disasters and optimize the tunnel fire disaster prevention framework, this study takes the emerging social media platform Douyin as a case study, conducting an in-depth analysis of 2133 short videos related to tunnel fires on the platform. A computational communication method was used for analysis, Latent Dirichlet Allocation was used to cluster the discussion topics of these tunnel fire short videos, and a spatiotemporal evolution analysis of the number of videos posted, user comments, and emotional inclinations across different topics was performed. The findings reveal that there is a noticeable divergence in public opinion regarding emergency decision making in tunnel fires, related to the complexity of tunnel fire incidents, ethical dilemmas in tunnel fire escape scenarios, and insufficient knowledge popularization of fire safety practices. The study elucidates the public’s actual needs during tunnel fire incidents, and a dynamic disaster prevention framework for tunnel fires based on social media and artificial intelligence is proposed on this basis to enhance emergency response capabilities. Utilizing short videos on social media, the study constructs a critical target dataset under real tunnel fire scenarios. It proposes a computer vision-based model for identifying critical targets in tunnel fires. This model can accurately and in real-time identify key targets such as fires, smoke, vehicles, emergency exits, and people in real tunnel fire environments, achieving an average detection precision of 77.3%. This research bridges the cognitive differences between the general public and professionally knowledgeable tunnel engineers regarding tunnel fire evacuation, guiding tunnel fire emergency responses and personnel evacuation. Full article
(This article belongs to the Section Fire Social Science)
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<p>Tunnel fire safety research strategy based on social media and artificial intelligence.</p>
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<p>The number of short video posts and discussions related to tunnel fires from 2017 to 2023.</p>
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<p>The number of tunnel fire-related short videos published on the Douyin platform.</p>
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<p>Number of short video discussions related to tunnel fire in the Douyin platform.</p>
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<p>Topic modeling of tunnel fire short video on the Douyin platform.</p>
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<p>Changes in the proportion of emotional tendency of different themes in tunnel fires from 2017 to 2023. (<b>a</b>) the theme of tunnel fire alarm systems; (<b>b</b>) the theme of tunnel fire accidents; (<b>c</b>) the theme of tunnel fire emergency drills.</p>
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<p>Typical tunnel fire emergency treatment and evacuation plan.</p>
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<p>Dynamic disaster prevention framework for tunnel fire based on social media and artificial intelligence.</p>
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<p>The standard normalized confusion matrix of the tunnel fire critical target recognition model.</p>
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<p>Loss, precision, and recall during model training. (<b>a</b>) loss variation with the training epoch; (<b>b</b>) precision and recall variation with the training epoch.</p>
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<p>Real-time recognition results of tunnel CCTV surveillance video.</p>
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13 pages, 9433 KiB  
Article
Study on Fire Characteristics of Flame-Retardant Polycarbonate Under Low Pressure
by Zhuoer Sun, Xuehui Wang and Jian Wang
Fire 2024, 7(12), 461; https://doi.org/10.3390/fire7120461 - 6 Dec 2024
Viewed by 378
Abstract
This work presents experimental and numerical research on the pyrolysis and combustion characteristics of flame-retardant polycarbonate under low ambient pressure. A novel experimental low-pressure combustion platform was constructed to determine the heat release rate, a key combustion parameter of polycarbonate. The ignition process [...] Read more.
This work presents experimental and numerical research on the pyrolysis and combustion characteristics of flame-retardant polycarbonate under low ambient pressure. A novel experimental low-pressure combustion platform was constructed to determine the heat release rate, a key combustion parameter of polycarbonate. The ignition process of polycarbonate under external radiation was analyzed, and an ignition time prediction model was developed. In addition, theoretical calculations of the main gas components and concentrations during the pyrolysis stage of polycarbonate and estimations of the calorific values of the combustible gas components produced during pyrolysis were carried out, providing a new explanation for the phenomenon of advancing ignition time in low-pressure environments. Full article
(This article belongs to the Special Issue Sustainable Flame-Retardant Polymeric Materials)
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<p>Schematic diagram of experimental low-pressure combustion platform.</p>
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<p>Typical combustion stages of the PC samples.</p>
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<p>Heat release rates of three kinds of PC: (<b>a</b>) additive flame-retardant polycarbonate, (<b>b</b>) intrinsically flame-retardant polycarbonate, and (<b>c</b>) pure polycarbonate.</p>
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<p>Ignition times of the PC samples under different experimental conditions.</p>
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<p>Linear relationship of Ln(P) and ignition times.</p>
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<p>Parameter <span class="html-italic">x</span> of the three samples under different ambient pressures.</p>
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<p>Concentrations of H<sub>2</sub> and CO in pyrolysis gas at different pressures. (<b>a</b>) Volume fraction of H<sub>2</sub> at 700 °C, (<b>b</b>) volume fraction of H<sub>2</sub> at 900 °C, (<b>c</b>) volume fraction of CO at 700 °C, and (<b>d</b>) volume fraction of CO at 900 °C.</p>
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<p>Concentrations of CO<sub>2</sub> and CH<sub>4</sub> in pyrolysis gas. (<b>a</b>) Volume fraction of CO<sub>2</sub> at 700 °C, (<b>b</b>) volume fraction of CO<sub>2</sub> at 900 °C, (<b>c</b>) volume fraction of CH<sub>4</sub> at 700 °C, and (<b>d</b>) volume fraction of CH<sub>4</sub> at 900 °C.</p>
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<p>Concentrations of C<sub>2</sub>H<sub>4</sub> and C<sub>6</sub>H<sub>6</sub> in pyrolysis gas. (<b>a</b>) Volume fraction of C<sub>2</sub>H<sub>4</sub> at 700 °C, (<b>b</b>) volume fraction of C<sub>2</sub>H<sub>4</sub> at 900 °C, (<b>c</b>) volume fraction of C<sub>6</sub>H<sub>6</sub> at 700 °C, and (<b>d</b>) volume fraction of C<sub>6</sub>H<sub>6</sub> at 900 °C.</p>
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<p>The LHV results with variations in pressure. (<b>a</b>) LHV at 700 °C, and (<b>b</b>) LHV at 900 °C.</p>
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14 pages, 8183 KiB  
Article
Improving Fire Suppression Efficiency in Electric Vehicles: A Study on Optimized Upward Spray Devices
by Jin-Dong Oh, Chan-Hoo Kim and Sung-Young Park
Fire 2024, 7(12), 460; https://doi.org/10.3390/fire7120460 - 6 Dec 2024
Viewed by 395
Abstract
Fire accidents in electric vehicles are mainly caused by battery fires, and one of the most effective fire suppression methods is to spray water from the bottom of a vehicle in an upward direction. In this study, analyses and experiments were conducted to [...] Read more.
Fire accidents in electric vehicles are mainly caused by battery fires, and one of the most effective fire suppression methods is to spray water from the bottom of a vehicle in an upward direction. In this study, analyses and experiments were conducted to improve the spray angle of a fluidic oscillator used for attaching an upward spray device. Through these analyses, the factors resulting in the maximum spray angle were derived from the four design variables of the fluidic oscillator, which were reconstructed for further analysis. The model that combined the radius of the mixing chamber curvature, inlet wedge width, and outlet wedge width exhibited the largest spray angle (84°) among the combination models that included the outlet wedge width variable. To evaluate the fire suppression performance of the fluidic oscillator nozzle, a cooling-rate comparison experiment was conducted with a recently used orifice nozzle. The results showed that the fluidic oscillator nozzle leads to a faster overall cooling rate than the orifice nozzle, rendering it more suitable for suppressing battery fires. After the production of the upward spray device, practical tests showed that it could spray a large area under a vehicle, thereby suggesting its applicability in actual fire scenes. Full article
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<p>Concept design for fire suppression using an upward spray device.</p>
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<p>Operation principles of the fluidic oscillator.</p>
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<p>(<b>a</b>) Schematic representation of the design variables. (<b>b</b>) Definitions of the various design variables.</p>
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<p>Three-dimensional model of the fluidic oscillator for simulation purposes.</p>
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<p>Results of the fluid spray angle and frequency experiments for the (<b>a</b>) MR model, (<b>b</b>) IW model, (<b>c</b>) OR model, and (<b>d</b>) OW model.</p>
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<p>Results of the fluid spray angle and frequency experiments for the (<b>a</b>) MR model, (<b>b</b>) IW model, (<b>c</b>) OR model, and (<b>d</b>) OW model.</p>
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<p>Results of the maximum spray angle for the (<b>a</b>) MR-0.97, (<b>b</b>) IW-1.18, (<b>c</b>) OR-1.08, and (<b>d</b>) OW-1.16 models.</p>
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<p>(<b>a</b>,<b>b</b>) Simulation results according to the different variable combinations, and the spray angle results.</p>
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<p>Spray angle results according to the different variable combinations: (<b>a</b>) MR + OW, (<b>b</b>) IW + OW, and (<b>c</b>) MR + IW + OW.</p>
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<p>The fluidic oscillator nozzle experiment rig: (<b>a</b>) schematic representation, and (<b>b</b>) photographic image.</p>
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<p>Experiment results for the fluid spray angle. (<b>a</b>) The base model, (<b>b</b>) the MR + OW model, (<b>c</b>) the IW + OW model, and the (<b>d</b>) MR + IW + OW model.</p>
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<p>Comparison of the experimental and simulated spray angle results.</p>
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<p>The nozzle cooling performance test device: (<b>a</b>) heating plate, (<b>b</b>) FON cooling model, and (<b>c</b>) ON cooling model.</p>
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<p>Average temperature changes on the heating plate.</p>
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<p>Upward spray device to suppress electric vehicle battery fires: (<b>a</b>) 3D model and (<b>b</b>) manufactured device.</p>
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<p>Performance evaluation of the upward spray device. (<b>a</b>) Rear view of the spray from outside the vehicle, (<b>b</b>) side view of the spray from outside the vehicle, and (<b>c</b>) rear view of the spray from under the vehicle.</p>
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18 pages, 5936 KiB  
Article
A Self-Adaptive Escape Route Planning Model Based on Dynamic Wildfire Information
by Hesun Wang, Junhao Sheng, Xindong Li, Hongyang Zhao and Dandan Li
Fire 2024, 7(12), 459; https://doi.org/10.3390/fire7120459 - 5 Dec 2024
Viewed by 630
Abstract
Background: Escape routes are important measures for firefighters to ensure their own safety, providing predetermined paths to safe areas. Their establishment needs to consider numerous factors, such as the timeliness and safety of the routes. Aims: Optimize the path planning method previously studied [...] Read more.
Background: Escape routes are important measures for firefighters to ensure their own safety, providing predetermined paths to safe areas. Their establishment needs to consider numerous factors, such as the timeliness and safety of the routes. Aims: Optimize the path planning method previously studied by our team to ensure the dynamic nature, timeliness, and safety of the routes. Methods: (1) Propose a comprehensive safety index that encompasses both spatial and temporal safety indices, providing a more holistic approach to route safety. (2) Introduce spatial adaptive factors and spatial safety windows corresponding to the spatial safety index within the comprehensive safety index. (3) Present a new concept, the “observation cycle”, as a standard for the frequency of updating wildfire spread information, thereby addressing the issue of a lack of real-time input information. Based on this, we propose a reliable dynamic update rule for its updating. Results: Compared to the unoptimized model, the final optimized model’s planned escape routes offer impressive dynamic performance, effectively guarding against sudden changes in wildfire conditions, enhancing route safety, and ensuring timeliness. Conclusions: This research ensures that firefighters can effectively guard against the threats posed by sudden changes in wildfire conditions when escaping in wildfire environments, while also guaranteeing timeliness and safety. Full article
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<p>Research Area 1.1 and Research Area 1.2.</p>
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<p>The 15 sets of meteorological data input within the one-hour framework.</p>
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<p>Possible directions for the firefighter to move forward from position n. The black arrow line indicates the horizontal or vertical direction, namely, n + 1, while the white arrow line indicates the diagonal direction, namely, the translation of n + 1.</p>
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<p>Evacuation route results with different spatial safety window values set in Research Areas 1.1 and 1.2.</p>
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<p>Legend information.</p>
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<p>Line graph of data for Research Area 1.1.</p>
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<p>The path over six observation cycles.</p>
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<p>The path over four observation cycles.</p>
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<p>From left to right, these are AT-Dijkstra, CP-ATS-Dijkstra, and DP-ATS-Dijkstra.</p>
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<p>On the left is the intermediate fire situation, and on the right is the final fire situation.</p>
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17 pages, 759 KiB  
Article
Better Be Ready! Evacuation Experiences During a Bushfire Emergency
by Carina C. Anderson, Susan F. Rockloff, Lucinda P. Burton, Victoria R. Terry, Sally K. Jensen, Anne T. Nolan and Peter C. Terry
Fire 2024, 7(12), 458; https://doi.org/10.3390/fire7120458 - 5 Dec 2024
Viewed by 492
Abstract
This paper reports on research undertaken for the Building Resilience for Bushfire-Affected Communities in Noosa Shire project, funded by the Australian Government. Being evacuated from a home in the path of a bushfire can be traumatic. Therefore, it is important for evacuees to [...] Read more.
This paper reports on research undertaken for the Building Resilience for Bushfire-Affected Communities in Noosa Shire project, funded by the Australian Government. Being evacuated from a home in the path of a bushfire can be traumatic. Therefore, it is important for evacuees to have safe places to stay, both physically and psychologically. Using a qualitative approach, we aimed to (a) understand the experiences of people who were displaced from their homes and sheltered at evacuation centres during the Noosa Shire bushfires and (b) understand what support is needed during disasters, such as bushfires, to help create positive experiences for future evacuees. Twelve participants displaced by bushfires in Noosa, Australia, in 2019 recalled their experiences in semi-structured interviews (conducted in 2022–2023). Inductive thematic analysis using NVivo 13 identified three themes that can inform government and public disaster preparation and response: planning, support, and communication. Findings from this study centred around building community resilience and offer valuable insights for organising disaster evacuation processes and evacuation centres on a broader scale. For individuals, it involves planning optimal evacuation routes, gathering necessary personal items, feeling safe and calm in evacuation centres, and receiving regular and accurate communication from authorities during disaster events. Full article
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<p>Bureau of Meteorology rainfall map showing unprecedented dry conditions and widespread decline in rainfall across Australia in 2019. (Image available under Creative Commons Attribution CC-BY 3.0 AU Deed 3.0).</p>
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<p>Diagrammatic representation of the core theme Building Community Resilience informed by Planning, Support, and Communication.</p>
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21 pages, 12422 KiB  
Article
Assessment and Validation of a Computer Vision Algorithm for Wildfire Rate of Spread Estimation
by Ehsan Ameri, Kyle Awayan and Jeanette Cobian-Iñiguez
Fire 2024, 7(12), 457; https://doi.org/10.3390/fire7120457 - 5 Dec 2024
Viewed by 507
Abstract
As wildfire activity increases worldwide, developing effective methods for estimating how fast it can spread is critical. This study aimed to develop and validate a computer vision algorithm for fire spread estimation. Using visual flame data from laboratory experiments on excelsior and pine [...] Read more.
As wildfire activity increases worldwide, developing effective methods for estimating how fast it can spread is critical. This study aimed to develop and validate a computer vision algorithm for fire spread estimation. Using visual flame data from laboratory experiments on excelsior and pine needle fuel beds, we explored fire spread predictions for two types of experiments. In the first, the experiments were conducted in an environment where the flame was maintained visually undisturbed while in the second, real-world scenarios were simulated with visual obstructions. Algorithm performance evaluation was conducted by computing the index of agreement and normalized root mean square deviation (NRMSD) error. Results show that the algorithm estimates fire spread well in pristine visual environments with varying accuracy depending on the fuel type. For instance, the index of agreement between the rate of spread values estimated by the algorithm and the measured values is 0.56 for excelsior fuel beds and 0.51 for pine needle fuel beds. For visual obstructions, varying impacts on the rate of spread predictions were observed. Adding an orange background behind the flame had the least effect on algorithm performance (IAmedian = 0.45), followed by placing a Y-shape element resembling a branch (IAmedian = 0.31) and adding an LED light near the flame (IAmedian = 0.30). Full article
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<p>Experimental setup for the rate of spread experiments. (<b>a</b>) Diagram depicting experimental configuration in model A and model B. (<b>b</b>) Photographs of top view and front view of the experimental fuel bed tray. (<b>c</b>) Visual obstruction scenarios for false alarm parametric tests.</p>
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<p>The plots of temperature vs. time with the red dashed vertical lines as indicators of the time criteria (t<sub>i</sub>) when a rapid change in the temperature gradient occurs at the start of the preheating zone.</p>
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<p>The schematic flowchart of the algorithm.</p>
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<p>(<b>a</b>) A closeup of the software environment and (<b>b</b>) the adjustment section of the software.</p>
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<p>The box that is generated around the flame root for the determination of flame area before image thresholding, or in other words the cropping area.</p>
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<p>Different steps in the computer vision algorithm. (<b>a</b>) Raw image. (<b>b</b>) Cropping region. Processing only takes place inside this box. (<b>c</b>) The filtered hue ranges. (<b>d</b>) The mask generated from the HSV filter. (<b>e</b>) The calculated leading edge is shown as the red line.</p>
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<p>(<b>a</b>) The location vs. time plots and (<b>b</b>) rate of spread vs. location plots for model A excelsior. (<b>c</b>) The frame in which flames passed each thermocouple (at x<sub>i</sub>) is also depicted.</p>
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<p>(<b>a</b>) The location vs. time plots and (<b>b</b>) rate of spread vs. location plots for model A pine needles. (<b>c</b>) The frame in which flames passed each thermocouple (at x<sub>i</sub>) is also depicted.</p>
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<p>(<b>a</b>) Box plots for model A with excelsior comparing false alarms IA for the rate of spread in different orange background colors based on orange color saturation. (<b>b</b>) The real pictures of flames spreading with this background are depicted.</p>
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<p>(<b>a</b>) Box plots for model A with excelsior comparing the index of agreement (IA) for the rate of spread in Y shape obstruction in different positions of false alarms. (<b>b</b>) The real pictures of flame spreading with this obstruction are depicted.</p>
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<p>(<b>a</b>) Box plots for model A with excelsior comparing the index of agreement (IA) for the rate of spread in different LED light luminance false alarms. (<b>b</b>) The real pictures of flame spreading with this LED obstruction are depicted.</p>
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24 pages, 42885 KiB  
Article
Experimental Study and Application of Unmanned Aerial Vehicle Releasing Fire-Extinguishing Bomb on Transmission Line Wildfires
by Tejun Zhou, Yu Liu, Wei Wu and Tiannian Zhou
Fire 2024, 7(12), 456; https://doi.org/10.3390/fire7120456 - 4 Dec 2024
Viewed by 524
Abstract
Experimental studies on the application of unmanned aerial vehicles (UAVs) to extinguish high-repeatability transmission line wildfires are not available. In this study, a scheme involving a UAV releasing a fire-extinguishing bomb at a high altitude for firefighting was proposed, and a simulated fire-extinguishing [...] Read more.
Experimental studies on the application of unmanned aerial vehicles (UAVs) to extinguish high-repeatability transmission line wildfires are not available. In this study, a scheme involving a UAV releasing a fire-extinguishing bomb at a high altitude for firefighting was proposed, and a simulated fire-extinguishing experimental platform was constructed to simulate a UAV releasing a fire-extinguishing bomb. In addition, the characteristics of water-based fire-extinguishing bombs of 5, 10, 20, and 50 kg as well as dry powder bombs of 25, 30, and 50 kg were investigated by changing parameters such as the type and mass of the fire-extinguishing agent carried by the bombs. It was noted that a 30 kg or more dry powder fire-extinguishing bomb could extinguish a fire in four 1A cribs at one time. The diffusion area of the fire-extinguishing medium was obtained from the perspective of the UAV. The diffusion area was 45–90 m2 for the water-based fire-extinguishing bomb and 130–700 m2 for the dry powder bomb. As calculated from the area of the fire scene extinguished by each fire-extinguishing bomb per unit mass, the utilization rate of a fire-extinguishing medium was highest with the 30 kg fire-extinguishing bomb, followed by the 50 kg bomb. In the high wildfire incidence period during the Qingming Festival in 2024, a UAV was used to release fire-extinguishing bombs to extinguish an incipient wildfire near a transmission line at a Hunan Power Grid site. Full article
(This article belongs to the Special Issue Firefighting Approaches and Extreme Wildfires)
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<p>Layout of UAV fire-extinguishing test system.</p>
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<p>Height of thermocouples relative to the ground.</p>
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<p>UAV fire-extinguishing measurement system.</p>
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<p>Structure of a fire-extinguishing bomb loaded with a water-based extinguishing agent (<b>a</b>) and of one loaded with a dry powder extinguishing agent (<b>b</b>).</p>
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<p>Combustion condition of fire scenes in the model when using 5 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 5 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 5 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 5 kg fire-extinguishing bomb with a water-based extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a 10 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 10 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 10 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 10 kg fire-extinguishing bomb with a water-based extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a 10 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 10 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 10 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 10 kg fire-extinguishing bomb with a water-based extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a 20 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 20 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 20 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 20 kg fire-extinguishing bomb with a water-based extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a 20 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 20 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 20 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 20 kg fire-extinguishing bomb with a water-based extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a 30 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the 30 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>) Subgraph shows the fire-extinguishing temperature curve of a 30 kg fire-extinguishing bomb with a superfine dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a 50 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the 50 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>) Subgraph shows the fire-extinguishing temperature curve of a 50 kg fire-extinguishing bomb with a superfine dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using TENYU 25 kg dry powder fire-extinguishing bombs to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 25 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 25 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>,<b>f</b>) Subgraph shows the top view and front view of the third 25 kg fire-extinguishing bomb explosion, respectively. (<b>g</b>) Subgraph shows the fire-extinguishing temperature curve of a 25 kg fire-extinguishing bomb with a dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using TENYU 25 kg dry powder fire-extinguishing bombs to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 25 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 25 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>,<b>f</b>) Subgraph shows the top view and front view of the third 25 kg fire-extinguishing bomb explosion, respectively. (<b>g</b>) Subgraph shows the fire-extinguishing temperature curve of a 25 kg fire-extinguishing bomb with a dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a SINOBANG 50 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 50 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 50 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 50 kg fire-extinguishing bomb with a dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a SINOBANG 50 kg fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 50 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 50 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 50 kg fire-extinguishing bomb with a dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using TENYU 50 kg dry powder fire-extinguishing bombs to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the 50 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>) Subgraph shows the fire-extinguishing temperature curve of a 50 kg fire-extinguishing bomb with a superfine dry powder extinguishing agent.</p>
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<p>Combustion condition of fire scenes in the model when using a KGT 50 kg water-based fire-extinguishing bomb to extinguish wood crib fires. (<b>a</b>,<b>b</b>) Subgraph shows the top view and front view of the first 50 kg fire-extinguishing bomb explosion, respectively. (<b>c</b>,<b>d</b>) Subgraph shows the top view and front view of the second 50 kg fire-extinguishing bomb explosion, respectively. (<b>e</b>) Subgraph shows the fire-extinguishing temperature curve of a 50 kg fire-extinguishing bomb with a water-based extinguishing agent.</p>
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<p>Curve of diffusion area versus time after explosion of fire-extinguishing bomb loaded with water-based extinguishing agent.</p>
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<p>Curve of diffusion area versus time after explosion of fire-extinguishing bomb loaded with dry powder extinguishing agent.</p>
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<p>500 kV Jinhong line #31 before fire extinguishing.</p>
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<p>500 kV Jinhong line #31 during fire extinguishing.</p>
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<p>500 kV Jinhong line #31 after fire extinguishing.</p>
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24 pages, 2795 KiB  
Article
Importance Sampling for Cost-Optimized Estimation of Burn Probability Maps in Wildfire Monte Carlo Simulations
by Valentin Waeselynck and David Saah
Fire 2024, 7(12), 455; https://doi.org/10.3390/fire7120455 - 3 Dec 2024
Viewed by 422
Abstract
Background: Wildfire modelers rely on Monte Carlo simulations of wildland fire to produce burn probability maps. These simulations are computationally expensive. Methods: We study the application of importance sampling to accelerate the estimation of burn probability maps, using L2 distance as the metric [...] Read more.
Background: Wildfire modelers rely on Monte Carlo simulations of wildland fire to produce burn probability maps. These simulations are computationally expensive. Methods: We study the application of importance sampling to accelerate the estimation of burn probability maps, using L2 distance as the metric of deviation. Results: Assuming a large area of interest, we prove that the optimal proposal distribution reweights the probability of ignitions by the square root of the expected burned area divided by the expected computational cost and then generalize these results to the assets-weighted L2 distance. We also propose a practical approach to searching for a good proposal distribution. Conclusions: These findings contribute quantitative methods for optimizing the precision/computation ratio of wildfire Monte Carlo simulations without biasing the results, offer a principled conceptual framework for justifying and reasoning about other computational shortcuts, and can be readily generalized to a broader spectrum of simulation-based risk modeling. Full article
(This article belongs to the Special Issue Patterns, Drivers, and Multiscale Impacts of Wildland Fires)
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<p>Contour plot of the maximum potential efficiency gain from importance sampling for an imaginary model in which the cost <span class="html-italic">c</span> is proportional to a constant term plus the fire size <span class="html-italic">A</span> raised to the exponent <math display="inline"><semantics> <mi>ϵ</mi> </semantics></math> (<math display="inline"><semantics> <mrow> <mi>c</mi> <mo>=</mo> <msub> <mi>c</mi> <mn>0</mn> </msub> <mrow> <mo>(</mo> <mn>1</mn> <mo>+</mo> <msup> <mrow> <mo>(</mo> <mi>a</mi> <mrow> <mo>(</mo> <mi>F</mi> <mo>)</mo> </mrow> <mo>/</mo> <msub> <mi>A</mi> <mn>0</mn> </msub> <mo>)</mo> </mrow> <mi>ϵ</mi> </msup> <mo>)</mo> </mrow> </mrow> </semantics></math>). The underlying distribution of fire sizes is the one recorded in the FPA-FOD [<a href="#B14-fire-07-00455" class="html-bibr">14</a>] in the Conterminous United States from 1992 to 2020. <math display="inline"><semantics> <msub> <mi>A</mi> <mn>0</mn> </msub> </semantics></math> is the natural size constant determined by the constant term. Note that the value of <math display="inline"><semantics> <msub> <mi>c</mi> <mn>0</mn> </msub> </semantics></math> is immaterial.</p>
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<p>Same-cost frequency multipliers for the optimal importance sampling scheme that reweights each pyrome uniformly. Each pyrome is colored by its frequency multiplier (note in particular that the color does not represent the prevalence of fire in each pyrome). The color bar is logarithmic and saturates to blue at 0.4 and to red at 2.5. More details in <a href="#fire-07-00455-t0A1" class="html-table">Table A1</a>.</p>
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<p>Same-cost frequency multipliers for the reweighting function fitted to Pyrome 33 (solid curve), along with the best possible reweighting function (point cloud) of the calibration sample. <math display="inline"><semantics> <mrow> <mo>(</mo> <mi>x</mi> <mo>,</mo> <mi>y</mi> <mo>)</mo> </mrow> </semantics></math> means the following: for the same compute time, importance sampling multiplies by <span class="html-italic">y</span> the sampling frequency of a fire of duration <span class="html-italic">x</span>.</p>
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<p>Same-cost frequency multipliers for the <math display="inline"><semantics> <msub> <mi>w</mi> <mn>2</mn> </msub> </semantics></math> reweighting function fitted to Pyrome 33 (solid curve), along with the best possible reweighting function (point cloud) of the calibration sample.</p>
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13 pages, 2119 KiB  
Article
Mapping Variable Wildfire Source Areas Through Inverse Modeling
by Stephen W. Taylor, Nicholas Walsworth and Kerry Anderson
Fire 2024, 7(12), 454; https://doi.org/10.3390/fire7120454 - 3 Dec 2024
Viewed by 465
Abstract
Global climate change is leading to increased wildfire activity in many parts of the world, and with increasing development, a heightened threat to communities in the wildland urban interface. Evaluating the potential for fire to affect communities and critical infrastructure is essential for [...] Read more.
Global climate change is leading to increased wildfire activity in many parts of the world, and with increasing development, a heightened threat to communities in the wildland urban interface. Evaluating the potential for fire to affect communities and critical infrastructure is essential for effective response decision-making and resource prioritization, including evacuation planning, with changing weather conditions during the fire season. Using a receptor–pathway–source assessment framework, we estimate the potential source area from which a wildfire could spread to a community in British Columbia by projecting fire growth outward from the community’s perimeter. The outer perimeter of the source area is effectively an evacuation trigger line for the forecast period. The novel aspects of our method are inverting fire growth in both space and time by reversing the wind direction, the time course of hourly weather, and slope and aspect inputs to a time-evolving fire growth simulation model Prometheus. We also ran a forward simulation from the perimeter of a large fire that was threatening the community to the community edge and back. In addition, we conducted a series of experiments to examine the influence of varying environmental conditions and ignition patterns on the invertibility of fire growth simulations. These cases demonstrate that time-evolving fire growth simulations can be inverted for practical purposes, although caution is needed when interpreting results in areas with extensive non-fuel cover or complex community perimeters. The advantages of this method over conventional simulation from a fire source are that it can be used for pre-attack planning before fire arrival, and following fire arrival, it does not require having an up-to-the-minute map of the fire location. The advantage over the use of minimum travel time methods for inverse modeling is that it allows for changing weather during the forecast period. This procedure provides a practical tool to inform real-time wildfire response decisions around communities, including resource allocation and evacuation planning, that could be implemented with several time-evolving fire growth models. Full article
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<p>Hourly values of ISI, FFMC, and wind speed and direction used in the variable source area mapping example for 96 h (9–12 August 2018) in reverse order of time.</p>
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<p>Inverse fire growth simulation scenarios (see <a href="#fire-07-00454-t001" class="html-table">Table 1</a> for details). (<b>A</b>) Uniform wind, fuels, and topography (level). Polygon ignition. (<b>B</b>) Changing wind direction (uniform speed). Uniform fuels, and no topography. Polygon ignition. (<b>C</b>) Variable topography. Uniform wind direction and fuels. Polygon ignition. (<b>D</b>) Varying fuels. Uniform wind and topography. Polygon ignition. (<b>E</b>) Varying fuels (see legend) and topography. Uniform wind. Polygon ignition. (<b>F</b>) Fuel-free barriers in uniform fuels; uniform wind direction and topography. Single forward polygon ignition, and two polygon ignitions on return that merge. (<b>G</b>) Staggered polygon ignitions merge, changing wind, and uniform fuels and topography. (<b>H</b>) Complex ignition from multiple ignition polygons merging, and concave on return. Shifting wind direction, and uniform fuels and topography.</p>
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<p>The estimated potential wildfire source area surrounding Ft. St. James, British Columbia (red line) for 4 days (9–12 August 2018). Inset: location within BC. The final extent of the Shovel Lake fire is in dark grey.</p>
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<p>(<b>a</b>) Projected forward spread of the Shovel Lake Fire (grey polygon) from the pink perimeter easterly to the edge of the community (yellow line) and (<b>b</b>) backwards for the same time period from the community edge (magenta line) to reach the fire (orange line). Fires were ignited in sections along the (<b>a</b>) pink and (<b>b</b>) magenta lines. The white lines demarcate the contribution of the different sectors to overall fire growth as well as unburned areas.</p>
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13 pages, 5044 KiB  
Article
Study on Smoke Characteristics in Cavern Complexes of Pumped-Storage Power Stations
by Peifeng Hu, Tong Xu, Chang Liu, Kai Wang, Fazheng Chong, Fengju Shang and Jiansong Wu
Fire 2024, 7(12), 453; https://doi.org/10.3390/fire7120453 - 2 Dec 2024
Viewed by 374
Abstract
The underground power houses of pumped-storage power stations (PSPSs) are highly complex, with interconnected and multidimensional structures, including various tunnels, such as the main and auxiliary power houses (MAPH), main transformer tunnel (MTT), tailrace gate tunnel (TGT), access tunnels (ATs), cable tunnels (CTs) [...] Read more.
The underground power houses of pumped-storage power stations (PSPSs) are highly complex, with interconnected and multidimensional structures, including various tunnels, such as the main and auxiliary power houses (MAPH), main transformer tunnel (MTT), tailrace gate tunnel (TGT), access tunnels (ATs), cable tunnels (CTs) etc. During intensive civil construction and electromechanical installation, fire risk becomes particularly prominent. Current research mainly examines fire incidents within individual tunnels, lacking comprehensive analyses of smoke spread across the entire cavern network. Therefore, in this study, a numerical model of a cavern complex in a PSPS was established to analyze smoke behavior and temperature distribution under various fire scenarios. The results indicated that when a fire occurred in the MAPH, the fire risk was relatively higher compared to fires in other places. Using the example of smoke spread from the MAPH to the MTT, the smoke spread process through key connecting caverns was analyzed. Initially, the temperature and velocity were stable, and the CTs and traffic cable tunnel in the auxiliary powerhouse (TCTAP) were the main smoke paths. After 7 min, the heat release rate (HRR) became stable, and CTs and ATs became the main paths for smoke spread, which could provide a reference for improving fire design in underground cavern systems. Full article
(This article belongs to the Special Issue Modeling, Experiment and Simulation of Tunnel Fire)
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<p>Geometry model of underground cavern group for PSPS.</p>
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<p>Schematic diagram of fire scenarios in MAPH: (<b>a</b>) front view; (<b>b</b>) side view.</p>
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<p>Smoke spread paths for different fire development stages at different fire source positions: (<b>a</b>) MAPH; (<b>b</b>) MTT; (<b>c</b>) TGT.</p>
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<p>Temperature characteristics of cavern groups at different fire development stages: fire in (<b>a</b>) MAPH; (<b>b</b>) MTT; (<b>c</b>) TGT.</p>
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<p>Smoke flow characteristics of cavern groups at different fire development stages: fire in (<b>a</b>) MAPH; (<b>b</b>) MTT; (<b>c</b>) TGT.</p>
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<p>Temperature distribution under ceiling in key caverns: (<b>a</b>) MAPH; (<b>b</b>) MTT.</p>
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<p>Temperature variations of ceiling in key connecting caverns: (<b>a</b>) CT; (<b>b</b>) TCTAPH; (<b>c</b>) AT.</p>
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<p>Variations in smoke flow velocity at the ceiling of key caverns: (<b>a</b>) MAPH; (<b>b</b>) MTT.</p>
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<p>Variations in Smoke Flow Velocity at the Ceiling of Key Connecting Caverns: (<b>a</b>) CT; (<b>b</b>) TCTAPH; (<b>c</b>) AT.</p>
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17 pages, 2722 KiB  
Article
The Effects of Fire Intensity on the Biochemical Properties of a Soil Under Scrub in the Pyrenean Subalpine Stage
by Andoni Alfaro-Leranoz, David Badía-Villas, Clara Martí-Dalmau, Marta Escuer-Arregui and Silvia Quintana-Esteras
Fire 2024, 7(12), 452; https://doi.org/10.3390/fire7120452 - 1 Dec 2024
Viewed by 441
Abstract
Fire causes changes in many soil attributes, depending on multiple factors which are difficult to control in the field, such as maximum temperature, heat residence time, charred material incorporation, etc. The objective of this study is to evaluate the effect of a gradient [...] Read more.
Fire causes changes in many soil attributes, depending on multiple factors which are difficult to control in the field, such as maximum temperature, heat residence time, charred material incorporation, etc. The objective of this study is to evaluate the effect of a gradient of fire intensities on soils at the cm scale. Undisturbed topsoil monoliths were sampled under scrubs in the subalpine stage in the Southern Pyrenees (NE Spain). They were burned, under controlled conditions in a combustion tunnel, to obtain four charring intensities (CIs), combining two temperatures (50 and 80 °C) and two residence times (12 and 24 min) reached at 1 cm depth from the soil. Unburned soil samples were used as a control. All soils were sampled, cm by cm, up to 3 cm deep. The following soil properties were measured: soil respiration (basal, bSR and normalized, nSR), β-D-glucosidase (GLU), microbial biomass carbon (MBC), glomalin-related soil proteins (GRSPs), soil organic carbon (SOC), labile carbon (DOC), recalcitrant organic carbon (ROC), total nitrogen (TN), soil pH, electrical conductivity (EC) and soil water repellency (SWR). Even at low intensities, GLU, SOC and total GRSP were significantly reduced and, conversely, SWR was enhanced. At the higher CIs, additional soil properties were significantly reduced (MBC and C/N) or increased (DOC, ROC, nSR, easily extractable GRSP). This study demonstrates that there is a differential degree of thermal sensitivity in the measured biochemical soil properties. Furthermore, these properties are more affected at 0–1 cm than at 1–2 and 2–3 cm soil thicknesses. Full article
(This article belongs to the Special Issue Post-fire Effects on Environment)
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<p>(<b>a</b>) Experimental burning setup; (<b>b</b>) thermocouples’ arrangement at the different soil depths: 1, 2 and 3 cm.</p>
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<p>Fire’s effects on (<b>a</b>) soil organic matter: soil organic carbon, (<b>b</b>) labile carbon, (<b>c</b>) recalcitrant organic carbon and (<b>d</b>) C/N ratio. Lowercase letters on top of the bars indicate significant differences between treatments and those between brackets between depths (<span class="html-italic">p</span> &lt; 0.05). Uppercase letters on top of the bars indicate significant differences within all samples when the interaction between treatment and depth was significant. In each bar, the mean (<span class="html-italic">n</span> = 3) and the standard deviation are represented.</p>
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<p>Fire’s effects on (<b>a</b>) soil organic matter: soil organic carbon, (<b>b</b>) labile carbon, (<b>c</b>) recalcitrant organic carbon and (<b>d</b>) C/N ratio. Lowercase letters on top of the bars indicate significant differences between treatments and those between brackets between depths (<span class="html-italic">p</span> &lt; 0.05). Uppercase letters on top of the bars indicate significant differences within all samples when the interaction between treatment and depth was significant. In each bar, the mean (<span class="html-italic">n</span> = 3) and the standard deviation are represented.</p>
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<p>Fire’s effects on soil biological properties: (<b>a</b>) microbial biomass carbon (MBC), (<b>b</b>) β-D-glucosidase activity (GLU), (<b>c</b>) basal soil respiration (bSR) and (<b>d</b>) normalized soil respiration (nSR). Lowercase letters on top of the bars indicate significant differences between treatments and those between brackets between depths (<span class="html-italic">p</span> &lt; 0.05). Uppercase letters on top of the bars indicate significant differences within all samples when the interaction between treatment and depth was significant. In each bar, the mean (<span class="html-italic">n</span> = 3) and the standard deviation are represented.</p>
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<p>Fire’s effects on soil biological properties: (<b>a</b>) microbial biomass carbon (MBC), (<b>b</b>) β-D-glucosidase activity (GLU), (<b>c</b>) basal soil respiration (bSR) and (<b>d</b>) normalized soil respiration (nSR). Lowercase letters on top of the bars indicate significant differences between treatments and those between brackets between depths (<span class="html-italic">p</span> &lt; 0.05). Uppercase letters on top of the bars indicate significant differences within all samples when the interaction between treatment and depth was significant. In each bar, the mean (<span class="html-italic">n</span> = 3) and the standard deviation are represented.</p>
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<p>Fire’s effects on glomalin-related soil proteins fractions (GRSP): (<b>a</b>) total fraction (T) and (<b>b</b>) relative labile fraction (EE). Lowercase letters on top of the bars indicate significant differences between treatments and those between brackets between depths (<span class="html-italic">p</span> &lt; 0.05). In each bar, the mean (<span class="html-italic">n</span> = 3) and the standard deviation are represented.</p>
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<p>Fire’s effects on (<b>a</b>) soil pH and (<b>b</b>) soil electric conductivity (EC). Lowercase letters on top of the bars indicate significant differences between treatments and those between brackets between depths (<span class="html-italic">p</span> &lt; 0.05). Uppercase letters on top of the bars indicate significant differences within all samples when the interaction between treatment and depth was significant. In each bar, the mean (<span class="html-italic">n</span> = 3) and the standard deviation are represented.</p>
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<p>Occurrence (%) of soil water repellency (SWR) according to the Water Drop Penetration Time (WDPT) test for the unburned (UB) and burned (LS, LL, HS, HL) samples, within the different soil depths (0–1, 1–2 and 2–3 cm). SWR classes defined by [<a href="#B33-fire-07-00452" class="html-bibr">33</a>].</p>
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<p>Score and loading plots of the ANOVA simultaneous component analysis (ASCA). (<b>a</b>) Scores and (<b>b</b>) loadings for treatment: charred intensity (CI); (<b>c</b>) scores and (<b>d</b>) loadings for soil depth: circles (0–1 cm), triangles (1–2 cm) and squares (2–3 cm); and (<b>e</b>) scores and (<b>f</b>) loadings for the interaction between treatment and depth. Blue dots from score plots refer to unburned (UB), light brown to low temperature and short time (LS), dark brown to low temperature and long time (LL), gray to high temperature and short time (HS) and black to high temperature and long time (HL). Abbreviations from loading plots refer to soil organic carbon (SOC), labile or dissolved organic carbon (DOC), recalcitrant organic carbon (ROC), total glomalin-related soil proteins (T-GRSPs), labile GRSP (EE-GRSPs), microbial biomass carbon (MBC), β-D-glucosidase activity (GLU), basal soil respiration (bSR), normalized soil respiration (nSR), electrical conductivity (EC) and soil water repellency (SWR).</p>
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25 pages, 4267 KiB  
Article
Deep Learning-Based Multistage Fire Detection System and Emerging Direction
by Tofayet Sultan, Mohammad Sayem Chowdhury, Mejdl Safran, M. F. Mridha and Nilanjan Dey
Fire 2024, 7(12), 451; https://doi.org/10.3390/fire7120451 - 30 Nov 2024
Viewed by 450
Abstract
Fires constitute a significant risk to public safety and property, making early and accurate detection essential for an effective response and damage mitigation. Traditional fire detection methods have limitations in terms of accuracy and adaptability, particularly in complex environments in which various fire [...] Read more.
Fires constitute a significant risk to public safety and property, making early and accurate detection essential for an effective response and damage mitigation. Traditional fire detection methods have limitations in terms of accuracy and adaptability, particularly in complex environments in which various fire stages (such as smoke and active flames) need to be distinguished. This study addresses the critical need for a comprehensive fire detection system capable of multistage classification, differentiating between non-fire, smoke, apartment fires, and forest fires. We propose a deep learning-based model using a customized DenseNet201 architecture that integrates various preprocessing steps and explainable AI techniques, such as Grad-CAM++ and SmoothGrad, to enhance transparency and interpretability. Our model was trained and tested on a diverse, multisource dataset, achieving an accuracy of 97%, along with high precision and recall. The comparative results demonstrate the superiority of the proposed model over other baseline models for handling multistage fire detection. This research provides a significant advancement toward more reliable, interpretable, and effective fire detection systems capable of adapting to different environments and fire types, opening new possibilities for environmentally friendly fire type detection, ultimately enhancing public safety and enabling faster, targeted emergency responses. Full article
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<p>Total civilian fire deaths and home fire deaths, United States, 1977–2021 [<a href="#B13-fire-07-00451" class="html-bibr">13</a>].</p>
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<p>Sample images of each class from the merged dataset.</p>
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<p>The figure illustrates the proposed approach for detecting fires in different stages including preprocessing, pretrained DenseNet201 and multiple custom layers.</p>
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<p>The performance of each model is simply summarized in this bar chart.</p>
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<p>Confusion matrix of different models.</p>
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<p>The graphic displays the training and validation accuracies on the left side, and the training and validation losses on the right side.</p>
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<p>The left side of the figure shows the graph for training and validation precision, whereas the right side shows the graph for training and validation recall.</p>
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<p>This graphic illustrates the efficacy of the AUC in training and validation.</p>
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<p>Explainable AI for all classes.</p>
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<p>Explainable AI for all classes.</p>
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<p>Explainable AI for misclassified data.</p>
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15 pages, 2639 KiB  
Article
Effects of Prescribed Burns on Soil Respiration in Semi-Arid Grasslands
by Juan Carlos De la Cruz Domínguez, Teresa Alfaro Reyna, Carlos Alberto Aguirre Gutierrez, Víctor Manuel Rodríguez Moreno and Josué Delgado Balbuena
Fire 2024, 7(12), 450; https://doi.org/10.3390/fire7120450 - 30 Nov 2024
Viewed by 448
Abstract
Carbon fluxes are valuable indicators of soil and ecosystem health, particularly in the context of climate change, where reducing carbon emissions from anthropogenic activities, such as forest fires, is a global priority. This study aimed to evaluate the impact of prescribed burns on [...] Read more.
Carbon fluxes are valuable indicators of soil and ecosystem health, particularly in the context of climate change, where reducing carbon emissions from anthropogenic activities, such as forest fires, is a global priority. This study aimed to evaluate the impact of prescribed burns on soil respiration in semi-arid grasslands. Two treatments were applied: a prescribed burn on a 12.29 ha paddock of an introduced grass (Eragostis curvula) with 11.6 t ha−1 of available fuel, and a simulation of three fire intensities, over 28 circular plots (80 cm in diameter) of natural grasslands (Bouteloua gracilis). Fire intensities were simulated by burning with butane gas inside an iron barrel, which represented three amounts of fuel biomass and an unburned treatment. Soil respiration was measured with a soil respiration chamber over two months, with readings collected in the morning and afternoon. Moreover, CO2 emissions by combustion and productivity after fire treatment were quantified. The prescribed burns significantly reduced soil respiration: all fire intensities resulted in a decrease in soil respiration when compared with the unburned area. Changes in albedo increased the soil temperature; however, there was no relationship between changes in temperature and soil respiration; in contrast, precipitation highly stimulated it. These findings suggest that fire, under certain conditions, may not lead to more CO2 being emitted into the atmosphere by stimulating soil respiration, whereas aboveground biomass was reduced by 60%. However, considering the effects of fire in the long-term on changes in nutrient deposition, aboveground and belowground biomass, and soil properties is crucial to effectively quantify its impact on the global carbon cycle. Full article
(This article belongs to the Special Issue Fire in Savanna Landscapes, Volume II)
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<p>Location map of the study area and experimental plot design.</p>
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<p>Availability of initial biomass, residual biomass, and emitted carbon after prescribed burn application.</p>
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<p>Time series of shortwave (285–3000 nm) and longwave radiation (4500–42,000 nm) at the study site one day before the burn (arrow indicates the day of the burn) and days after it. The upper panel shows downwelling radiation, while the lower panel presents upwelling radiation. Day of year (DOY).</p>
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<p>Soil respiration rates, soil temperature, and precipitation before and after burn prescription. Day of year (DOY).</p>
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<p>Diurnal carbon fluxes recorded with the eddy covariance system. The arrow indicates the occurrence of precipitation on day 130. Day of year (DOY).</p>
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<p>Temporal variation of soil respiration in the three intensity treatments and the control, during the period from 21 June to 17 August 2021.</p>
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25 pages, 7946 KiB  
Article
Effectiveness of Sorbents in the Equipment of Firefighting Units in Practice
by Miroslav Betuš, Martin Konček, Marian Šofranko, Andrea Rosová, Marek Szücs and Martin Cvoliga
Fire 2024, 7(12), 449; https://doi.org/10.3390/fire7120449 - 29 Nov 2024
Viewed by 632
Abstract
The presented study deals with the effectiveness of sorbents in the equipment of firefighting units in Slovakia. Currently, there are many manufacturers of sorbents on the market and also a number of types of these products. As a result of an emergency on [...] Read more.
The presented study deals with the effectiveness of sorbents in the equipment of firefighting units in Slovakia. Currently, there are many manufacturers of sorbents on the market and also a number of types of these products. As a result of an emergency on the road, especially in the case of traffic accidents, there can be a leakage of dangerous substances. From this point of view, it is necessary to prevent the dangerous substance escaping into the environment as quickly as possible and to choose a suitable sorption material to prevent the leakage. For the stated reasons, the aim of the submitted paper was to research the effectiveness of sorbents used by fire brigades in the Slovak Republic in traffic accidents. Part of the publication is on the specification of sorbents, and as part of the research there is an evaluation of their composition and a description, and according to the method and the successive laboratory tests, the operating fluid that is applied to the selected sorbents. After the test and the resulting values, the initial and absorbed weight of the sorbents were determined. The sorption capacity and absorbency were determined from the resulting values. The time factor and the ability to remove adsorbed sorbents from solid surfaces was evaluated after visualizing the process and the final result. The resulting values were unified and compared with other sorbents, where their suitability for the purposes of firefighting units in practice was determined. Full article
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<p>Vapex (source: elaborated by authors).</p>
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<p>LITE DRY (source: elaborated by authors).</p>
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<p>REOSORB (source: elaborated by authors).</p>
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<p>ECO-DRY (source: elaborated by authors).</p>
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<p>Absodan plus (source: elaborated by authors).</p>
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<p>Spinkleen (source: elaborated by authors).</p>
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<p>Diesel, gasoline, coolant, engine oil, oil + gasoline (source: elaborated by authors).</p>
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<p>Beakers used in research (source: elaborated by authors).</p>
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<p>REOSORB immersed in diesel and after adsorption and dripping (source: elaborated by authors).</p>
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<p>Measuring diesel fuel and determining the initial weight of the sorbent (source: elaborated by authors).</p>
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<p>Sorption process on engine oil (source: elaborated by authors).</p>
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<p>Vapex sorption process with motor gasoline (source: elaborated by authors).</p>
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<p>LITE-DRY immersed in gasoline and after draining (source: elaborated by authors).</p>
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<p>Vapex immersed in engine oil and after draining (source: elaborated by authors).</p>
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<p>REOSORB with coolant and after draining (source: elaborated by authors).</p>
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<p>Absodan, Spilkleen, and ECO-DRY immersed in gasoline and ECO-DRY after dripping (source: elaborated by authors).</p>
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<p>Distribution of sorbents from the point of view of removal (source: elaborated by authors).</p>
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<p>Leaked operating fluids on the road and their backfilling using sorbents (source: elaborated by authors).</p>
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<p>Absorbency of sorbents on operating fluids in % (source: elaborated by authors).</p>
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21 pages, 4705 KiB  
Article
Thermal Reaction Process and Thermokinetic Characteristics of Coking Coal Oxidation
by Ruoyu Bao, Changkui Lei, Chengbo Wang and Fubao Zhou
Fire 2024, 7(12), 448; https://doi.org/10.3390/fire7120448 - 29 Nov 2024
Viewed by 496
Abstract
The coal–oxygen composite reaction is a complex physicochemical reaction process, and different heating rates have a great influence on this reaction. In order to reveal the influence of different heating rates on the coal–oxygen composite reaction of coking coal, the TG-DSC experimental method [...] Read more.
The coal–oxygen composite reaction is a complex physicochemical reaction process, and different heating rates have a great influence on this reaction. In order to reveal the influence of different heating rates on the coal–oxygen composite reaction of coking coal, the TG-DSC experimental method was adopted to analyze the hysteresis effect of the characteristic temperature, inflection point temperature, and peak temperature under different heating rates. Furthermore, the KAS method was employed to calculate the apparent activation energy, and the Málek method was utilized to infer the most probable mechanism functions and determine the compensation effects at different stages of the coal oxidation process. The results show that with an increase in heating rate, the temperature values corresponding to each characteristic temperature point increase, the characteristic temperature exhibits a hysteresis phenomenon, and the heat flow rate and heat flux rate also show an increasing trend. The apparent activation energy gradually increases in Stages II and III, with a maximum value of 198.7 kJ/mol near the ignition point T3, which first increases and then gradually decreases in Stage IV, where the maximum value is around the temperature point T4 of the maximum mass loss rate, which is 170.02 kJ/mol. The variation trend in the pre-exponential factor is consistent with the apparent activation energy, and the dynamic compensation effect is greater in Stage IV. The three different oxidation stages have different mechanism functions: a three-dimensional diffusion mode is present in Stages II and III, which is ultimately transformed into an accelerated form α-t curve with E1 and n = 1 in Stage IV. Full article
(This article belongs to the Special Issue Simulation, Experiment and Modeling of Coal Fires)
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<p>Characteristic temperature points and stage division.</p>
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<p>TG-DTG curves at different heating rates.</p>
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<p>DSC curves at different heating rates.</p>
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<p>Characteristic temperature variation of DSC curve at different heating rates.</p>
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<p>Relationship curves in Stage II: (<b>a</b>) conversion rate and temperature; (<b>b</b>) linear correlation between <math display="inline"><semantics> <mrow> <mi>ln</mi> <mo stretchy="false">(</mo> <mstyle scriptlevel="0" displaystyle="true"> <mfrac> <mi>β</mi> <mrow> <msup> <mi>T</mi> <mn>2</mn> </msup> </mrow> </mfrac> </mstyle> <mo stretchy="false">)</mo> </mrow> </semantics></math> and 1/T.</p>
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<p>Relationship curves in Stage III: (<b>a</b>) conversion rate and temperature; (<b>b</b>) linear correlation curve <math display="inline"><semantics> <mrow> <mi>ln</mi> <mo stretchy="false">(</mo> <mstyle scriptlevel="0" displaystyle="true"> <mfrac> <mi>β</mi> <mrow> <msup> <mi>T</mi> <mn>2</mn> </msup> </mrow> </mfrac> </mstyle> <mo stretchy="false">)</mo> </mrow> </semantics></math> with 1/T.</p>
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<p>Relationship curves in Stage IV: (<b>a</b>) conversion rate and temperature; (<b>b</b>) linear correlation curve <math display="inline"><semantics> <mrow> <mi>ln</mi> <mo stretchy="false">(</mo> <mstyle scriptlevel="0" displaystyle="true"> <mfrac> <mi>β</mi> <mrow> <msup> <mi>T</mi> <mn>2</mn> </msup> </mrow> </mfrac> </mstyle> <mo stretchy="false">)</mo> </mrow> </semantics></math> with 1/T.</p>
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<p>Relationship between apparent activation energy and conversion rate at Stages II, III and IV.</p>
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<p>Relationship between apparent activation energy and temperature at Stages II, III and IV.</p>
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<p>Málek theoretical values of different mechanism functions.</p>
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<p>Málek method for determining mechanism functions at different stages.</p>
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<p>Málek method for determining mechanism functions at different stages.</p>
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<p>Linear relationship of ln <span class="html-italic">A</span> − <span class="html-italic">E<sub>a</sub></span> compensation effect.</p>
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