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Accelerant

An accelerant, or accelerator, is a substance that increases the rate of a chemical process.^[1] In various fields, accelerants are used to speed up reactions, such as in rubber vulcanization and cement curing. In fire science, an accelerant is specifically a fuel or oxidizer, often an ignitable liquid, intentionally used to initiate a fire or increase the rate of growth or spread of fire.^[2] Common fire accelerants are primarily hydrocarbon-based ignitable liquids, including gasoline, kerosene, diesel fuel, lighter fluid, and turpentine, which are readily available and highly volatile.^[3] Gaseous accelerants such as propane and butane are also used, particularly in confined spaces. In fire science, accelerants are classified by organizations like ASTM International into categories based on boiling point ranges and chemical composition, such as light petroleum distillates (e.g., gasoline) and medium petroleum distillates (e.g., kerosene).^[4] Accelerants are most notably associated with arson investigations, where their deliberate application indicates intentional fire-setting to maximize property damage, often for motives like insurance fraud or revenge.^[4]

Overview

Definition

An accelerant is a substance that increases the rate of a chemical reaction or process, often by altering reaction conditions, bonds, or pathways, and may be partially or fully consumed during the process.^[5]^[6] While applicable broadly in chemistry, the term "accelerant" is most commonly used in modern contexts to refer to substances that accelerate the spread or intensity of fire, such as ignitable liquids in arson cases.^[7]^[8] In chemical contexts, accelerants function by facilitating the progression of reactions that would otherwise occur more slowly, distinguishing them from true catalysts, which remain unchanged. This role is critical in various industrial and practical applications, where controlled acceleration enhances efficiency without fundamentally altering the reaction's outcome. Historically, "accelerant" served as a term for substances like catalysts, but its usage has shifted toward fire-related applications in the 20th century.^[1] Unlike retardants, which reduce the speed of reactions by impeding molecular interactions, or inhibitors, which prevent or substantially halt reactions through binding or deactivation mechanisms, accelerants actively promote reaction advancement.^[9]^[10] Retardants typically moderate rates to avoid premature progression, as seen in polymer processing, while inhibitors serve protective functions, such as corrosion prevention or enzyme regulation.^[11] This distinction underscores accelerants' promotional effect, enabling faster completion of processes like curing or combustion. Examples of accelerants span broad categories, including organic compounds such as amines employed in polymerization reactions to enhance radical initiation and chain growth. Inorganic salts, like calcium chloride, accelerate hydration in cement by promoting the dissolution of key ions and rapid formation of hydration products.^[12] Flammable liquids, such as gasoline, serve as accelerants in combustion by providing volatile hydrocarbons that intensify oxidation rates.^[13] The term "accelerant" derives from the Latin accelerāre, meaning "to hasten" or "to quicken," combining ad- (toward) and celerāre (to go fast).^[14] Its earliest documented uses in English date to the 1860s, initially appearing in chemical literature tied to 19th-century industrial advancements, such as process optimization in manufacturing.^[15]

Historical Development

The formal concept of accelerants as deliberate rate-increasing additives emerged in 19th-century industrial chemistry, coinciding with the rise of systematic material processing in Europe and the United States.^[16] A pivotal milestone occurred in 1839 when Charles Goodyear discovered the vulcanization of rubber using sulfur, patented in 1844, which transformed natural rubber from a perishable material into a durable one; initially, the process was slow, requiring hours of heating, and relied on inorganic accelerators like white lead or zinc oxide to modestly speed it up.^[17] Vulcanization remained inefficient for mass production until the early 20th century, when organic accelerators revolutionized the industry; in 1906, chemist George Oenslager identified aniline as a highly effective organic accelerator, dramatically reducing curing times from hours to minutes and enabling commercial scalability, though its toxicity limited widespread adoption.^[18] This breakthrough was followed by less hazardous alternatives, such as thiocarbanilide in the 1910s and 2-mercaptobenzothiazole (MBT) in 1925, the latter patented as the first major commercial rubber accelerator and becoming dominant for both natural and emerging synthetic rubbers due to its versatility and efficiency.^[17] In parallel, accelerants found applications in construction during the 20th century; calcium chloride emerged as a key cement accelerator by the late 19th century, with documented use since 1873 to hasten hydration and setting, particularly in cold weather, but its widespread incorporation into concrete admixtures occurred in the 1920s and 1930s amid booming infrastructure projects.^[19] World War II accelerated innovation in synthetic rubbers like GR-S (styrene-butadiene), where accelerators such as MBT derivatives and thiurams were essential for rapid vulcanization in wartime production, scaling output from negligible amounts in 1941 to over 800,000 tons annually by 1944 to meet military demands.^[20] Post-1950s developments emphasized safer, non-toxic alternatives driven by growing environmental and health concerns over carcinogens like nitrosamines formed from traditional accelerators such as thiurams; this led to the formulation of low-nitrosamine systems and substitutes like sulfenamides by the 1970s, reducing toxicity while maintaining performance.^[21] Notable patents underscore these advances: Oenslager's 1906 work on aniline laid the groundwork for organic acceleration (U.S. Patent 873,619, 1907), while MBT's commercialization followed Vulcanization's U.S. Patent 1,127,903 (1915) and full adoption via Monsanto's 1925 formulations; in concrete, 1930s patents like U.S. Patent 1,877,298 (1932) expanded admixture use, including calcium chloride blends for accelerated curing.

Chemical Principles

Mechanisms of Acceleration

Fire accelerants enhance the combustion process by providing additional fuel or oxidizer that rapidly vaporizes and mixes with air, increasing the rate of heat release and fire spread. Combustion is an exothermic oxidation reaction involving free-radical chain mechanisms: initiation (where heat breaks bonds to form radicals), propagation (radicals react with fuel and oxygen to produce more radicals and heat), and termination (radicals combine to stop the chain). Accelerants like gasoline supply hydrocarbons that readily form flammable vapors, lowering the energy needed for ignition and sustaining propagation through increased reactant concentration and temperature rise, as described by the Arrhenius equation where higher effective temperature T exponentially increases the reaction rate constant k = A e^{-E_a / RT}.^[13]^[8] Unlike catalysts, accelerants are consumed in the reaction, fully oxidizing to carbon dioxide and water while releasing significant heat (e.g., gasoline's heat of combustion is approximately 47 MJ/kg). This exothermic energy elevates local temperatures, accelerating pyrolysis of surrounding materials and extending the fire beyond natural fuel sources. Gaseous accelerants such as propane further enhance this by diffusing quickly in air, promoting uniform combustion in enclosed spaces.^[4]

Key Properties

The effectiveness of fire accelerants depends on physical and chemical properties that facilitate easy ignition and rapid burning. Volatility, measured by vapor pressure and boiling point, allows quick formation of ignitable vapors; for example, gasoline (boiling range 30–200°C) has a high vapor pressure at room temperature, enabling flash points as low as -43°C. Flammability limits define the concentration range for sustained burning, with gasoline's lower flammable limit (LFL) at 1.4% and upper (UFL) at 7.6% by volume in air.^[3]^[4] Chemically, most accelerants are hydrocarbons classified by ASTM International standards (E1618) into categories based on carbon chain length and composition: light petroleum distillates (e.g., gasoline, C4–C12), medium (e.g., kerosene, C9–C20), heavy (e.g., diesel), and aromatics (e.g., toluene). These classes reflect boiling point ranges and volatility, aiding forensic identification. Oxygenated accelerants like alcohols (e.g., ethanol, flash point 13°C) add polarity for faster evaporation but are less common.^[4]^[22] Accelerants are typically liquids or gases due to their ease of application and dispersion. Liquids like lighter fluid penetrate porous surfaces, while gases like butane provide instant ignition without residue. Solids are rarely used as primary accelerants but may include magnesium in incendiary devices. Toxicity varies; gasoline has an LD50 >5000 mg/kg (oral, rat), indicating low acute hazard, though inhalation risks are higher due to volatile organic compounds (VOCs). Efficacy is dosage-dependent, with small volumes (e.g., 1–5 liters) sufficient to intensify fires, but compatibility with the environment (e.g., avoiding water dilution) is crucial.^[3]^[4]

Industrial Applications

In Rubber Vulcanization

In rubber vulcanization, accelerants play a crucial role in enhancing the efficiency of the sulfur crosslinking process, transforming raw rubber into a durable, elastic material suitable for industrial use. Without accelerants, vulcanization typically requires prolonged heating at high temperatures, such as approximately 6 hours at 140°C or higher durations at elevated temperatures around 200°C, to achieve adequate crosslinking. The addition of accelerants dramatically shortens this timeframe to mere minutes while allowing the process to occur at lower temperatures, typically 140-160°C, thereby reducing energy consumption and improving production scalability.^[23]^[24] Common types of accelerants used in rubber vulcanization include sulfenamides, thiurams, and guanidines, each selected based on the desired curing speed and processing safety. Sulfenamides, such as CBS (N-cyclohexyl-2-benzothiazole sulfenamide), provide delayed action, enabling safe handling and extrusion of uncured rubber before vulcanization begins, making them ideal for thick molded articles. Thiurams, exemplified by TMTD (tetramethylthiuram disulfide), offer fast-acting acceleration suitable for thin rubber products like cables and belts, where rapid curing is beneficial. Guanidines, such as DOTG (di-o-tolylguanidine), are often employed in natural rubber formulations to promote steady vulcanization, particularly in blends requiring balanced reactivity.^[24]^[23] The mechanism of these accelerants involves the formation of accelerator-sulfur complexes that facilitate efficient polysulfide generation for crosslinking. Initially, the accelerator reacts with activators like zinc oxide to form an active complex, which then interacts with elemental sulfur to produce polysulfidic species (e.g., BtS-S_x-SBt, where x represents sulfur atoms). These polysulfides react with allylic sites on rubber polymer chains, creating polysulfidic intermediates that link adjacent chains, ultimately yielding 1-5 sulfur bridges per polymer chain for optimal elasticity and strength. This process minimizes wasteful sulfur incorporation compared to unaccelerated vulcanization, where longer, less stable polysulfides predominate.^[25] Accelerants are typically dosed at 0.5-2 parts per hundred rubber (phr) to balance curing speed and compound stability. At these levels, they enhance crosslink density and mechanical properties like tensile strength, but excessive dosage can lead to scorching—premature curing during processing, which causes surface defects and processing difficulties. Careful formulation, often combining primary accelerants like sulfenamides with secondary ones such as thiurams, mitigates this risk while optimizing cure characteristics.^[23]^[24] In industrial applications, accelerants have been integral to tire manufacturing since the 1920s, where they improved rubber's elasticity, durability, and resistance to wear, enabling mass production of high-performance tires. Modern developments include eco-friendly alternatives like xanthates (e.g., zinc isopropyl xanthate, ZIX), which provide ultra-fast curing with reduced environmental impact compared to traditional sulfur-based systems, supporting sustainable rubber processing.^[23]

In Cement and Concrete Curing

Accelerants in cement and concrete curing primarily function by promoting the early formation of calcium silicate hydrate (C-S-H) gel, the primary binding phase in hydrated cement, which significantly reduces the initial set time from the typical 2-4 hours for ordinary Portland cement to as little as 30-60 minutes depending on dosage and conditions.^[26] This acceleration occurs through mechanisms such as nucleation seeding, where accelerants provide sites for rapid C-S-H precipitation, enhancing the overall hydration kinetics without substantially altering the long-term composition.^[27] Common types of accelerants include chloride-based compounds, such as calcium chloride (CaCl₂), typically dosed at 1-2% by weight of cement, which increase ion mobility in the pore solution to facilitate faster dissolution of cement clinker phases like tricalcium silicate (C₃S).^[28] Non-chloride alternatives, such as triethanolamine, are preferred in reinforced concrete to avoid corrosion risks to embedded steel, as they accelerate hydration via adsorption on cement particles without introducing aggressive chloride ions.^[29] The use of accelerants leads to early strength gains, with compressive strength development up to 50% faster in the first few days compared to non-accelerated mixes, allowing concrete to reach significant load-bearing capacity sooner; however, overdosing can result in reduced long-term durability due to increased porosity or efflorescence.^[29] At 28 days, accelerated concretes often achieve comparable ultimate strengths to standard mixes when properly dosed, though excessive accelerant may compromise resistance to environmental factors like freeze-thaw cycles.^[30] These accelerants find key applications in cold-weather concreting, where temperatures below 5°C slow natural hydration, enabling placement and curing in adverse conditions, as well as in rapid repair works for infrastructure like bridges or runways requiring quick return to service.^[31] Dosage is regulated by standards such as ASTM C494 for Type C accelerants, which limit chloride content to a maximum of 2% by weight of cement to balance acceleration benefits with corrosion prevention.^[32] Historically, accelerants like calcium chloride were introduced in the early 20th century, gaining prominence during wartime infrastructure projects in the 1940s for expedited construction of military facilities, though their use dates back to the late 19th century.^[33] Modern formulations increasingly incorporate aluminates, such as aluminum sulfate-based accelerators, to enhance sulfate resistance in environments prone to chemical attack, providing alkali-free options that maintain performance while improving durability.^[34]

As Combustion Enhancers

In the context of fire initiation and intensification, accelerants are defined as fuels or oxidizers, often ignitable liquids, intentionally used to start a fire or accelerate its growth and spread.^[35] These substances are typically volatile materials with low flash points, enabling rapid vaporization and mixing with ambient oxygen to facilitate quick flame propagation. For instance, gasoline has a flash point of approximately -40°C, while diesel fuel exhibits a higher flash point around 52°C, influencing their ease of ignition in arson or controlled burn scenarios.^[36] Common types of accelerants include petroleum distillates such as gasoline and kerosene, which are frequently employed due to their availability and effectiveness in promoting rapid fire development.^[37] Alcohols like ethanol are also used. Solid accelerants, such as magnesium, find application in incendiary devices, where their high reactivity generates intense, sustained heat upon ignition.^[38] The combustion process involving accelerants begins with the substance vaporizing at ambient temperatures, forming a flammable mixture with air that ignites through autoignition, a spark, or an open flame. This vapor-air interaction enhances oxygen access to the fuel, dramatically elevating the heat release rate and enabling fire spread rates that can be substantially faster than unassisted combustion.^[13] In practice, accelerants are often poured in deliberate patterns to direct fire progression, leaving potential evidentiary trails in investigations, while historically, mixtures like napalm—developed in the early 1940s—were deployed in warfare to create large-scale incendiary effects.^[39] Quantities sufficient to overwhelm standard fire loads and achieve rapid involvement vary by scenario per established fire investigation guidelines.^[40]

Detection in Forensic Investigations

In forensic investigations of suspected arson cases, the detection of accelerant residues is essential for distinguishing intentional fires from accidental ones, focusing on the identification of ignitable liquid residues (ILR) in fire debris. Sampling techniques begin with non-invasive methods such as canine detection, where trained dogs alert to vapors from common accelerants like gasoline or kerosene; studies have reported accuracies around 92% in controlled scenarios.^[41] For physical sampling, adsorbent traps are employed to collect debris according to ASTM E1412 standards, which outline passive headspace concentration using materials like activated charcoal strips to separate volatile ILR from substrates without altering the scene. These methods prioritize preserving trace evidence, as even small quantities—down to microliter levels—can indicate accelerant use.^[42] Once collected, analytical methods rely on gas chromatography-mass spectrometry (GC-MS) as the gold standard for identifying volatile organic compounds (VOCs) in residues, producing characteristic patterns such as clustered alkane peaks for petroleum-based accelerants like gasoline, which exhibit C4 to C20 hydrocarbon distributions.^[43] GC-MS distinguishes ILR from background pyrolysis products by comparing total ion chromatograms against reference libraries, confirming classes like light, medium, or heavy petroleum distillates per ASTM E1618 guidelines. This technique achieves detection limits as low as 0.1 μL for evaporated samples, providing confirmatory evidence in court.^[44] Detection faces significant challenges, including rapid evaporation of accelerants, where volatile components like those in gasoline can be substantially lost shortly post-ignition due to heat and airflow, complicating recovery from open scenes.^[45] Substrate interference further hinders analysis, as burned plastics or synthetic materials, such as polystyrene-butadiene rubber, produce pyrolysis products mimicking accelerant hydrocarbons, like benzene or toluene, which can overlay ILR peaks in chromatograms.^[46] Investigators mitigate this by using selective extraction and pattern subtraction in GC-MS data.^[47] Key indicators of accelerant use include pour patterns revealed through charring analysis, where irregular, deepened char lines or "alligatoring" (large blistering) on floors suggest liquid application and rapid burning, often corroborated by multiple samples showing consistent ILR.^[48] Residue thresholds for confirmation typically require ILR concentrations exceeding background levels, such as greater than 1% total extractables matching a specific ignitable liquid class, to rule out natural substrates.^[49] Advances since the 2000s include portable GC units, like the FLIR Griffin G510, enabling on-scene analysis of vapors and residues in under 10 minutes, reducing contamination risks and speeding investigations. AI-driven pattern recognition has emerged, using machine learning algorithms on GC-MS data to classify gasoline residues with over 95% accuracy, even in weathered samples, by analyzing peak ratios and weathering profiles.^[50] The ASTM E1618 standard, first published in 1994, established hierarchical categories for ILR (e.g., gasoline as a light petroleum distillate) based on chromatographic profiling, improving inter-laboratory consistency.

Safety and Regulations

Health and Environmental Risks

Accelerants pose significant health risks through various exposure routes, primarily due to their chemical composition and physical properties. Inhalation of vapors from petroleum-based accelerants, such as gasoline, can lead to central nervous system depression, manifesting as dizziness, headache, and confusion, with benzene—a common component—exacerbating these effects at occupational exposure limits set by OSHA at 1 ppm as an 8-hour time-weighted average.^[51]^[52] Skin contact with amine-based accelerants used in rubber vulcanization often results in irritant or allergic contact dermatitis, characterized by redness, itching, and fissuring, particularly in occupational settings where percutaneous absorption occurs.^[53] Chronic exposure to many petroleum accelerants carries carcinogenic risks, with automotive gasoline classified as Group 1 (carcinogenic to humans) by the International Agency for Research on Cancer, linked to leukemia and bladder cancer from components like benzene.^[54] In fire scenarios, accelerants amplify hazards beyond initial ignition. Combustion byproducts such as carbon monoxide (CO) and hydrogen cyanide (HCN) from burning materials can cause asphyxiation by binding to hemoglobin and inhibiting cellular respiration, contributing to 60-80% of fire-related fatalities through smoke inhalation. The rapid spread facilitated by accelerants' low flash points intensifies burn injuries, leading to increased incidence of severe thermal trauma as flames propagate quickly across surfaces.^[55]^[56]^[57] Environmentally, accelerants contribute to persistent contamination. Spills of gasoline-based accelerants introduce methyl tert-butyl ether (MTBE), which migrates rapidly through soil due to its high solubility and low biodegradability, contaminating groundwater supplies and detected in monitoring studies across multiple U.S. states.^[58]^[59] Exposure data underscores acute and chronic toxicities. For calcium chloride (CaCl₂), a common accelerant in concrete curing, the oral LD50 in rats is approximately 1000 mg/kg, indicating moderate acute toxicity with risks of gastrointestinal irritation and hypercalcemia upon ingestion. Chronic studies on rubber accelerator exposure, including occupational cohorts and animal models, reveal reproductive toxicity, such as reduced fertility and developmental effects in offspring, observed in workers handling sulfenamide compounds like N,N-dicyclohexyl-2-benzothiazolesulfenamide.^[60] Mitigation efforts have driven shifts toward less harmful alternatives. Since the 1990s, EPA regulations under the Clean Air Act Amendments prompted the phase-out of MTBE in gasoline formulations due to groundwater risks, accelerating adoption of biodegradable oxygenates like ethanol to reduce environmental persistence. In rubber processing, regulatory pressures have favored non-toxic, biodegradable accelerators to minimize chronic health impacts on workers.^[61]^[62]

Handling Protocols and Legal Frameworks

Safe storage and handling of accelerants, particularly flammable liquid types used in industrial and fire-related applications, follow guidelines outlined in NFPA 30, which mandates the use of approved, grounded metal containers to prevent static electricity buildup and storage in well-ventilated areas away from ignition sources such as open flames or electrical equipment. Personal protective equipment (PPE) requirements, enforced by OSHA, include respirators for handling accelerants emitting volatile organic compounds (VOCs) to protect against inhalation hazards when exposure exceeds permissible limits. In industrial settings like rubber vulcanization and cement curing facilities, OSHA's Process Safety Management standard (29 CFR 1910.119) requires comprehensive programs to manage highly hazardous chemicals, including accelerants, through hazard analyses, operating procedures, and mechanical integrity checks to prevent releases.^[63] Spill response protocols under this standard emphasize immediate containment using absorbents for liquid accelerants, followed by neutralization and proper disposal to minimize environmental impact, with trained personnel equipped with appropriate PPE.^[64] Legal frameworks governing accelerants include ATF regulations under 18 U.S.C. § 844, which classify the malicious use of fire accelerants in arson as a federal felony punishable by up to 20 years imprisonment, with jurisdiction extending to investigations involving interstate commerce.^[65] For toxic variants like certain thiurams used as rubber accelerators, the EU's REACH regulation imposes restrictions on their use in cosmetics due to skin sensitization risks, prohibiting them since their inclusion in Annex II of the Cosmetics Regulation in the 2010s, while EPA enforces emission controls under NESHAP for rubber production to limit airborne toxins.^[66] In forensic contexts involving fire accelerants as evidence, chain-of-custody protocols per ISO/IEC 17025 ensure integrity through documented handling, secure storage, and traceability from collection to analysis, preventing contamination or tampering in laboratory accreditation standards.^[67] Training standards for workers handling accelerants include HAZWOPER certification under OSHA 29 CFR 1910.120, requiring 40-hour initial training for those at hazardous waste sites or involved in emergency responses, covering recognition, containment, and decontamination.^[68] Internationally, the UN Globally Harmonized System (GHS) standardizes labeling for accelerants, requiring pictograms, signal words, and hazard statements on containers to communicate risks uniformly across borders.

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Flash Points - Liquids - The Engineering ToolBox
The flash points for some common liquids and fuels. ; Diesel Fuel (1-D), 100 ; Diesel Fuel (2-D), 126 ; Diesel Fuel (4-D), 130 ; Diethanolamine, 342.
[51]
[PDF] 240686.pdf - Office of Justice Programs
This project applied target compound analysis from high resolution Gas Chromatography/Mass. Spectrometry (GCMS) utilized for gasoline individualization to ...
[52]
[PDF] Just the Basics: Ethanol
Ethanol helps keep engines clean, too. It burns more ... Oxygen atoms inside ethanol join forces with oxygen molecules in the air to help ethanol burn more.
[53]
When Was Napalm First Used in World War II? - HistoryNet
Jun 17, 2021 · A: Invented in 1942, napalm saw combat for the first time in Sicily in August 1943, when American troops incinerated a wheat field believed to ...
[54]
[PDF] Fire investigation handbook - NIST Technical Series Publications
The Handbook is a reference tool designed to be used by the beginning or by the experienced fire investigator. How each person.
[55]
Evaluation of canines for accelerant detection at fire scenes - PubMed
Both dogs were generally able to alert on spots containing 0.01 microL or more of all three accelerants, at or beyond the purge and trap recovery and gas ...
[56]
ANSI/ASTM E1412-19 Standard Practice for Separation of Ignitable ...
Dec 1, 2020 · ANSI/ASTM E1412-19 Standard Practice for Separation of Ignitable Liquid Residues from Fire Debris Samples by Passive Headspace Concentration ...Missing: accelerant | Show results with:accelerant
[57]
Who Set the Fire? Determination of Arson Accelerants by GC-MS in ...
Students interpret the standards and the charred samples using chromatographic retention times and MS data. From this information, they determine which ...
[58]
Rapid GC-MS as a Screening Tool for Forensic Fire Debris Analysis
This work focuses on the development of a method for ignitable liquid analysis using rapid GC-MS. A sampling protocol and temperature program were developed.
[59]
Mathematically modeling chromatograms of evaporated ignitable ...
In this work, a mathematical model was used to predict the chemical composition of several ignitable liquids at various evaporation levels.
[60]
Interference from combustion residues of polystyrene-butadiene ...
The current study aims to determine potential interference on gasoline identification from the combustion/pyrolysis products of polystyrene-butadiene rubber ( ...
[61]
The effect of volatile residues in burnt household items on the ...
The influence of the type of accelerant, type of burned material, time of burning and availability of air on the possibility of detection of accelerants traces.
[62]
Was Flammable Liquid Used as an Accelerant?
Evidence of the use of a flammable liquid in a fire can be established by an examination of burn patterns, charring, melted metals, heat colors, glass.
[63]
[PDF] Interpretation of Ignitable Liquid Residues in Fire Debris Analysis
ABSTRACT. The funded research had three major goals: 1. To investigate the effect of competitive adsorption of substrates typically found in fire debris.
[64]
Recognition of gasoline in fire debris using machine learning
In the present study, machine learning algorithms capable of recognizing gasoline residues in fire debris based on GC-MS data have been developed.
[65]
[PDF] Forensic Analysis of Ignitable Liquid Fuel Fires
IGNITABLE LIQUID RESIDUE IN FIRE DEBRIS ... Nowicki, J.F. (1990), “An accelerant classification scheme based on analysis by gas.
[66]
https://www.epa.gov/stationary-sources-air-pollution/rubber-tire-manufacturing-national-emission-standards-hazardous
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Medical Management Guidelines for Gasoline - CDC
Acute gasoline exposure can cause transient CNS excitation followed by CNS depression. Confusion, giddiness, nausea, headache, blurred vision, dizziness, and ...
[68]
Percutaneous absorption of aromatic amines in rubber industry ...
The skin lesions can be classified as early stages of irritant contact dermatitis. Table 3 Overview of skin lesions, depending on localisation and intensity.
[69]
IARC Monographs evaluation of the carcinogenicity of automotive ...
Mar 21, 2025 · The Working Group evaluated automotive gasoline as carcinogenic to humans (Group 1) on the basis of sufficient evidence for cancer in humans ...Missing: accelerants | Show results with:accelerants
[70]
Hydrogen Cyanide: New Concerns for Firefighting and Medical Tactics
Jun 29, 2009 · Research is pointing to hydrogen cyanide as a substance that is as much as a threat to responders and victims encountering fire smoke as carbon monoxide.
[71]
Smoke inhalation injury during enclosed-space fires: an update - NIH
Between 60% and 80% of all sudden deaths occurring at the scene of a fire are attributed to smoke inhalation.( ) The classic scenario is an enclosed-space fire, ...Missing: spread | Show results with:spread<|separator|>
[72]
Upstate Burn Center issues warning on accelerants use to start ...
Oct 15, 2021 · Experts from the Upstate Medical University's Clark Burn Center are issuing a warning about the increase in fire-related injuries due to the use of accelerants.
[73]
Toxicological Profile for Methyl tert-Butyl Ether (MTBE) - NCBI
MTBE released from USTs has been shown to move rapidly in the soil column and contaminate groundwater; this has been verified in large monitoring studies (WQP ...
[74]
[PDF] Occurrence of the Gasoline Additive MTBE in Shallow Ground Water ...
Alternatively, gasoline spills may directly contribute to. MTBE contamination of ground water and surface water. Where, how frequently, and at what con ...
[75]
Bioaccumulation and Biotransformation of Chlorinated Paraffins - NIH
Dec 12, 2022 · Chlorinated paraffins (CPs) are persistent, toxic, bioaccumulated compounds. This study summarizes their bioaccumulation and biotransformation, ...Missing: accelerants | Show results with:accelerants
[76]
Two-generation reproductive toxicity study of the rubber accelerator ...
Exposure of workers handling sulfenamide accelerator materials is likely to be highest in the area of materials packaging. During material packout at the ...
[77]
1990 Clean Air Act Amendment Summary | US EPA
In 1989, President George W. Bush proposed revisions to the Clean Air Act designed to curb acid rain, urban air pollution, and toxic air emissions.Other Titles · Title I · Title II · Title IV
[78]
MTBE in Gasoline: Clean Air and Drinking Water Issues
This report provides background information concerning the gasoline additive methyl tertiary butyl ether (MTBE), discusses air and water quality issues ...
[79]
https://www.osha.gov/laws-regs/regulations/standardnumber/1910/1910.119
[80]
https://www.osha.gov/laws-regs/regulations/standardnumber/1910/1910.120AppC
[81]
18 U.S. Code § 844 - Penalties - Law.Cornell.Edu
Any person who violates any other provision of section 842 of this chapter shall be fined under this title or imprisoned not more than one year, or both.
[82]
National Emission Standards for Hazardous Air Pollutants (NESHAP)
On November 13, 2024, EPA finalized amendments to the national emission standards for hazardous air pollutants (NESHAP) for Rubber Tire Manufacturing.
[83]
https://anab.ansi.org/resource/iso-iec-17025-forensic-documents-resources/
[84]
https://www.osha.gov/emergency-preparedness/hazardous-waste-operations/faq