FIREFIGHTER EXPOSURE TO SMOKE PARTICULATES
November 9, 2010 | "firefighter safety", "health and safety", building construction, Christopher Naum, Codes, construction, dynamics, fire behavior, Fire Protection Engineering, firefighter-safety-health, fires, health, Recommendations, Reports, research, UL | Christopher Naum | No Comments
Firefighter Exposure to Smoke Particulates
Under a U.S. Department of Homeland Security (DHS) Assistance to Firefighter Grant, Underwriters Laboratories in collaboration with the Chicago Fire Department and the University of Cincinnati College of Medicine, recently completed a sixteen month study on the smoke and gas exposure firefighters confront during firefighting operations and subsequent contact exposure resulting from residual contamination of personal protective equipment.
The project included investigations on three fire scales: (1) fires in the Chicago metropolitan area, (2) residential room content and automobile fires, and (3) material-level fire tests. Detected effluent gases, airborne chemicals and smoke particulates were assessed by the University of Cincinnati College of Medicine for their potential adverse health effects to fire service personnel.
�The potential for firefighters to experience acute and/or chronic respiratory health effects related to exposures during firefighting activities has long been recognized. Specific exposures of concern for firefighters, because of their potential respiratory toxicity, include:
•Asphyxiants (such as carbon monoxide, carbon dioxide and hydrogen sulfide),
•irritants (such as ammonia, hydrogen chloride, particulates, nitrogen oxides, phenol and sulfur dioxide),
•carcinogens (such as asbestos, benzene, styrene, polycyclic aromatic hydrocarbons and certain heavy metals).
An additional cardiovascular risk factor that is receiving increasing attention is exposure to respirable particles in the ultrafine range (particles less than 0.1 micron in diameter), which have been detected in smoke. Exposure to these gaseous and particulate agents has been linked to acute and chronic effects resulting in increased fire fighter mortality and morbidity (higher risk of specific cancers and cardiovascular disease).
Currently gaps exist in the knowledge concerning the size distribution of smoke particles generated in fires and the nature of the chemicals absorbed on the particles� surfaces. Some gaseous effluents may also condense on protective equipment and exposed skin, leaving an oily residue or film. These chemicals can pose a significant threat to firefighter health directly (via the skin and eyes, or by inhalation) or following dermal absorption. This fire research study fills gaps identified in previous studies on fire fighters� exposure to combustion products. The study focuses on gaseous effluents and smoke particulates generated during residential structure and automobile fires and subsequent contact exposure resulting from residual contamination of personal protective equipment.
The information developed from this research will provide a valuable background for interpreting fire hazards and can be used by:
•the medical community for advancing their understanding of the epidemiological effects of smoke exposure;
•first responders for developing situational assessment guidelines for self-contained breathing apparatus (SCBA) usage, personal protection equipment cleaning regimen and identifying the importance of personal hygiene following fire effluent exposure;
•organizations such as NIOSH and NFPA for developing new test method standards and performance criteria for respirators used by first responders and the care and maintenance of personal protection equipment.
This study investigated and analyzed the combustion gases and particulates generated from three scales of fires: residential structure and automobile fires, simulated real-scale fire tests, and material based small-scale fire tests. Material-level tests were conducted to investigate the combustion of forty-three commonly used residential building construction materials, residential room contents and furnishings, and automobile components under consistent, well-controlled radiant heating conditions. In these tests, material based combustion properties including weight loss rate, heat and smoke release rates, smoke particle size and count distribution, and effluent gas and smoke composition were characterized for a variety of natural, synthetic, and multi-component materials under flaming. The results from these tests were used to assess the smoke contribution of individual materials.
Nine real-scale fire tests representing individual room fires, an attic fire, deck and automobile fires were conducted at UL�s large-scale fire test laboratory to collect and analyze the gas effluents, smoke particulates, and condensed residues produced during fire growth, suppression and overhaul under controlled, reproducible laboratory conditions. During overhaul, firefighter personal atmospheres were sampled and analyzed for gases and smoke particles. Smoke particle analysis included mass and size distributions, and inorganic elemental composition. These tests also served as a platform for developing and refining the condensed residue sampling techniques for field usage.
Over a period of four months Chicago Fire Department designated personnel conducted personal gas monitoring and collected personal aerosol smoke samples at residential fires (knock-down, ventilation and overhaul). Replaceable personal protective components (gloves and hoods) used by the firefighters during this time period were analyzed to identify the chemical composition of accumulated smoke residue.
Collected data was forwarded to University of Cincinnati College of Medicine to assess the potential adverse health effects of the observed gaseous effluents and smoke particles on fire service personnel.
The key findings of the research were as follows:
•Concentrations of combustion products were found to vary tremendously from fire to fire depending upon the size, the chemistry of materials involved, and the ventilation conditions of the fire.
•The type and quantity of combustion products (smoke particles and gases) generated depended on the chemistry and physical form of the materials being burned.
•Synthetic materials produced more smoke than natural materials.
•The most prolific smoke production was observed for styrene based materials commonly found in residential households and automobiles. These materials may be used in commodity form (e.g. disposable plastic glasses and dishes), expanded form for insulation, impact modified form such as HIPS (e.g. appliances and electronics housing), copolymerized with other plastics such as ABS (e.g. toys), or copolymerized with elastomers such as styrene-butadiene rubber (e.g. tires).
•Vinyl polymers also produced considerable amounts of smoke. Again these materials are used in commodity form (e.g. PVC pipe) or plasticized form (e.g. wiring, siding, resin Chairs and tables).
•As the fraction of synthetic compound was increased in a wood product (either in the form of adhesive or mixture such as for wood-plastic composites), smoke production increased.
•Average particle sizes ranged from 0.04 to 0.15 microns with wood and insulation generating the smallest particles.
•For a given particle size, synthetic materials will generate approximately 12.5X more particles per mass of consumed material than wood based materials.
•Combustion of the materials generated asphyxiants, irritants, and airborne carcinogenic species that could be potentially debilitating. The combination and concentrations of gases produced depended on the base chemistry of the material:
•All of the materials formed water, carbon dioxide and carbon monoxide.
•Styrene based materials formed benzene, phenols, and styrene.
•Vinyl compounds formed acid gases (HCl and HCN) and benzene.
•Wood based products formed formaldehyde, formic acid, HCN, and phenols.
•Roofing materials formed sulfur gas compounds such as sulfur dioxide and hydrogen sulfide.
•The same asphyxiants, irritants, and airborne carcinogenic species were observed as in material-level tests supporting the premise that gases generated in large-complex fires arise from individual component material contributions.
•Ventilation was found to have an inverse relationship with smoke and gas production such that considerably higher levels of smoke particulates and gases were observed in contained fires than uncontained fires, and the smoke and gas levels were greater inside of contained structures than outside.
•Recommended exposure levels (IDLH, STEL, TWA) were exceeded during fire growth and overhaul stages for various agents (carbon monoxide, benzene, formaldehyde, hydrogen cyanide) and arsenic.
•Smoke and gas levels were quickly reduced by suppression activity however they remained an order of magnitude greater than background levels during overhaul.
•99+ % of smoke particles collected during overhaul were less than 1 micron in diameter. Of these 97+ % were too small to be visible by the naked eye suggesting that �clean� air was not really that clean.
•While not the focus of this research, it should be noted that the ion alarm activated sooner than the photoelectric alarm in every room fire scenario (living rooms, bedroom, kitchen). This is consistent with results reported in the Smoke Characterization Report for model flaming fire tests conducted in the smoke alarm fire test room. Carbon monoxide alarm activation lagged behind both ion and photoelectric alarms, furthermore.
�Field Events & Controlled Field Tests
•Concentrations of certain toxic gases were monitored at field events during the course of normal firefighter duties. These results were analyzed to determine:
•Average gas concentrations and exposures calculated for the field events, which may be useful for estimating total exposure from repeated exposures during a firefighter�s career.
•Potential gas concentration and exposures calculated for the field events, which may be useful for planning firefighter preparedness.
•Gas exposures in excess of NIOSH IDLH, STEL, and OSHA TWA. These were repeatedly observed at the monitored field events. Carbon monoxide concentrations most often exceeded recommended exposure limits; however instances were observed where Firefighter Exposure to Smoke Particulates other gases other than carbon monoxide exceeded recommended exposure limits yet carbon monoxide did not.
•Collected smoke particulates contained multiple heavy metals including arsenic, cobalt, chromium, lead, and phosphorous.
•The NIOSH STEL concentration for arsenic was exceeded at one fire and possibly at a second. Gas monitors would not provide warning for arsenic exposure.
•Chemical composition of the smoke deposited and soot accumulated on firefighter gloves and hoods was virtually the same except concentrations on the gloves were 100X greater than the hoods.
•Deposits contained lead, mercury, phthalates and PAHs.
•Carbon monoxide monitoring may provide a first line of gas exposure defense strategy but does not provide warning for fires in which carbon monoxide does not exceed recommended limits but other gases and chemicals do.
•The OP-FTIR was difficult to successfully implement in the field and even for the controlled field events in passive mode.
•While the OP-FTIR could be set-up in less than 2 minutes, it typically took as long as 5 to 10 minutes to start data collection. This time frame is too long when compared to the aggressive time frames of fire suppression.
•Poor thermal contrast led to insufficient signal-to-noise ratios.
•Multiple asphyxiants (e.g. carbon monoxide, carbon dioxide and hydrogen sulfide), irritants (e.g. ammonia, hydrogen chloride, nitrogen oxides, phenol and sulfur dioxide), allergens (e.g. isocyanates), and chemicals carcinogenic for various tissues (e.g. benzene, chromium, formaldehyde and polycyclic aromatic hydrocarbons) were found in smoke during both suppression and overhaul phases. Carcinogenic chemicals may act topically, following inhalation, or following dermal absorption, including from contaminated gear.
•Concentrations of several of these toxicants exceeded OSHA regulatory exposure limits and/or recommended exposure limits from NIOSH or ACGIH.
•Exposures to specific toxicants can produce acute respiratory effects that may result in chronic respiratory disease.
•High levels of ultrafine particles (relative to background levels) were found during both suppression and overhaul phases.
•Exposure to particulate matter has been found to show a positive correlation with increased cardiovascular morbidity and mortality for general population studies.
•The high efficiency of ultrafine particle deposition deep into the lung tissue can result in release of inflammatory mediators into the circulation, causing toxic effects on internal tissues such as the heart. Airborne toxics, such as metals and polycyclic aromatic hydrocarbons, can also be carried by the particles to the pulmonary interstitium, vasculature, and potentially subsequently to other body tissues, including the cardiovascular and nervous systems and liver.
•Interactions between individual exposure agents could lead to additive or synergistic effects exacerbating adverse health effects.
•Long-term repeated exposure may accelerate cardiovascular mortality and the initiation/progression of atherosclerosis.
FUTURE CONSIDERATIONS Based upon the results of this investigation, the following areas were identified for further research:
1.Greater in depth analysis of the obtained results in relation to previous studies such as those of Jankowic et al on firefighter exposure, LeMasters et al on firefighter cancer epidemiologies, and the first responders at the World Trade Center collapse.
2.Characterization of potential fire scene exposures including: 1.asphyxiants,
5.Better definition of the potential long-term respiratory, cancer and cardiovascular health impacts of varied and complex mixes of exposures such as those identified in this report. Such information could help guide decisions on the selection and utilization of respiratory protection, especially during overhaul activities.
6.Determination of the relative contribution of respiratory and dermal absorption routes to exposure and adverse health risks of firefighters to combustion products.
7.Factors determining coronary heart disease risk among firefighters. Such studies could help elucidate the mechanistic link between ultrafine particle exposure and coronary heart disease morbidity and mortality and identify measures to decrease its impact on this population.
8.Characterization of contaminants accumulated on firefighter protective equipment and the subsequent potential for firefighter exposures to these contaminants and resulting health effects.
9.Usage and industrial hygiene practices related to firefighter protective equipment, including cleaning patterns, length of use and storage practices.
UL�Final Report Project Number: 08CA31673 April 1, 2010 Firefighter Exposure to Smoke Particulates Report, HERE
Underwriters Laboratories Inc., HERE
The Voice of Reason with special guest Shawn Longerich, Executive Director for the Cyanide Poisoning Treatment Coalition (CPTC) Podcast, HERE
The Cyanide Poisoning Treatment Coalition (CPTC) is a 501(c)(3) non-profit comprised of firefighters and medical personnel.�The mission of the CPTC is to increase awareness about the risk of fire smoke cyanide exposure as it relates to Awareness, Prevention, Protection, Detection, Diagnosis and Treatment. Web Site HERE
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