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The Chemistry of Fires at the Wildland-Urban Interface (2022)

Chapter: Appendix E: Engineering Calculations for Table 3-2

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Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
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Appendix E

Engineering Calculations for Table 3-2

Table 3-2 presents data describing two characteristics of structural materials—combustible mass and energy content—that relate to how the homes built from those materials would burn and their potential emissions if they were destroyed by a WUI fire. Although the committee searched for this type of data in the existing literature, no data of this type are currently available. The values in the table were therefore calculated by the committee to demonstrate how combustible mass and energy content can be derived from published information on the quantities of different typical materials found in residential construction. The table provides values for two example single-family homes for which construction material quantities were publicly available (EPA, 2016; Messerschmidt, 2021).

The committee wishes to emphasize that multiple assumptions are involved in completing the engineering calculations that resulted in Table 3-2. The data in that table are intended only as an illustrative example, and an uncertainty analysis was therefore not performed. For the reader who may be interested in replicating, improving upon, or extending these calculations to expand the scientific community’s understanding of fire loading in WUI fires, the committee’s assumptions and calculations are detailed in this appendix. The first section describes combustible mass calculations, and the second section describes energy content calculations.

CALCULATING COMBUSTIBLE MASS

Combustible mass must be obtained from the source or calculated before energy content can be determined. Messerschmidt provided material quantities directly on the basis of combustible mass (Messerschmidt, 2021), and no engineering calculations were needed to provide those values in Table 3-2.

The US Environmental Protection Agency (EPA) provided quantities of each material in terms of weight, area, or length, which can be found in Table 1-1 of the reference (EPA, 2016). The committee applied conversion factors to convert the quantities from source units into mass equivalents (Table E-1). To convert area and length values to a mass basis, the committee made informed assumptions about the specific material composition, when not specified, and sought out sources for the relevant density information.

CALCULATING ENERGY CONTENT

The committee identified the best available sources for net calorific value. When possible, energy content data were derived from the Society of Fire Protection Engineers (SFPE) Handbook of Fire Protection Engineering (SFPE, 2016) or from Xie et al. (2019) to conform with standard fire loading calculation methodology. In all

Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×

TABLE E-1 Conversion Factors Used in Calculating Mass-Basis Quantities for EPA Example Home

Materiala Source Amount Source Units Conversion Factor Conversion Factor Units Total Mass (kg) Combustible Mass (kg)
Lumber (assumed white pine)b 13,837 board ft 0.95 kg/board ft 13,159 13,159
Sheathing (assumed 1/2″ OSB)c 13,118 ftd 0.77 kg/ftb 10,115 10,115
Exterior wood sidinge 3,206 ftd 1.09 kg/ftb 3,485 3,485
Roofing material (assumed ½ inch OSB)c 3,103 ftd 0.77 kg/ftb 2,393 2,393
Roofing asphalt shinglese 3,103 ftd 1.23 kg/ftb 3,805 746
Glass fiber insulation 3,061 ftd -d -d 1,830 183d
Wall material (assumed 3/8 inch gypsum board)f 6,050 ftd 0.57 kg/ftb 3,429g -g
Ceiling material (assumed 3/8 inch gypsum board)f 2,335 ftd 0.57 kg/ftb 1,323g -g
Ducting (assumed galvanized steel) 266 linear ft 2.27 kg/ftb 603 -g
Windows (assumed vinyl)h 19 units 20.1 kg/ftb 382 192
Concrete 19 tons 907.185 kg/ton 17,237g -g
Total 62,168 34,680

NOTE: OSB = oriented strand board.

a If the source did not provide a specific material composition for a given construction material, the composition assumed is given in parentheses in the first column.

b The linear density of lumber was assumed to be 0.95 kg/board ft, based on the density of white pine (eastern and western averaged) adjusted to a moisture content of 12 percent. Source: https://www.fpl.fs.fed.us/documnts/fplgtr/fpl_gtr190.pdf.

c A ½ inch assumption was made for all OSB to match Messerschmidt (2021). Area density (kg/ft2) for ½ inch OSB was obtained from https://roofonline.com/weights-measures/weight-of-plywood-and-osb/.

d The conversion factor approach used for most materials was not appropriate for glass fiber insulation because this material is composed of only a fraction of combustible adhesives in addition to the noncombustible glass fibers. For this material, the equivalent combustible mass was obtained by multiplying the replacement mass provided in the source (EPA, 2016) by 10 percent, the combustible fraction according to Messerschmidt (2021) and https://pharosproject.net/common-products/2080060#contents-panel.

e EPA provided replacement mass values for wood shingle siding and roofing asphalt shingles (Appendix A1 in EPA, 2016), but the area densities (kg/ft2) that resulted were too high to be reasonable. Instead, the committee obtained area densities for each of these materials from https://www.engineeringtoolbox.com/roofing-materials-weight-d_1498.html. The percentage of combustible material of a shingle was obtained from https://greet.es.anl.gov/greet_building, Building Life-Cycle Analysis with the GREET Building Module: Methodology, Data, and Case Studies, as 20 percent asphalt by mass.

f Area density (kg/ft2) of gypsum board was obtained from https://www.certainteed.com/drywall/products/regular-drywall/.

g Not a combustible material.

h The window materials were obtained from Building Industry Reporting and Design for Sustainability (BIRDS) New Residential Database Technical Manual (NIST Technical Note 1878, https://nvlpubs.nist.gov/nistpubs/TechnicalNotes/NIST.TN.1878.pdf) for a 1 m2 vinyl casement window composed of 40 percent vinyl and 10 percent other materials.

SOURCE: EPA, 2016.

Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×

TABLE E-2 Net Calorific Values Used to Calculate Energy Content

Material Mean Net Calorific Value (MJ/kg) Net Calorific Source
Wood 18.50 Xie et al., 2019; Bain et al., 2003
OSB / particle board 18.54 Phyllis, n.d.
Polyvinyl chloride 10.07 SFPE, 2016, Table A.31
Polyurethane foam 25.60a SFPE, 2016, Table A.31
Fiberglass phenol formaldehyde resin 28.55a SFPE, 2016, Table A.31
Asphalt (from shingles) 40.20 UNSD, n.d.

a For these materials, the reference provided ranges, from which mean values were calculated (as the center of the range).

other cases, net calorific values were sourced from measurement data (Phyllis, n.d.) or from widely adopted reference data (United Nations standard net calorific values [UNSD, n.d.]). The applicability of standardized data for representing in-use construction materials requires validation.

The combustible mass values taken from Messerschmidt (2021) and calculated from EPA (2016) were then multiplied by the mean net calorific values in Table E-2 to obtain the energy content data shown in Table 3-2.

REFERENCES

Bain, R. L., W. A. Amos, M. Downing, and R. L. Perlack. 2003. Biopower Technical Assessment: State of the Industry and Technology. Golden, CO: National Renewable Energy Laboratory. https://www.nrel.gov/docs/fy03osti/33123.pdf.

EPA (US Environmental Protection Agency). 2016. Analysis of the Lifecycle Impacts and Potential for Avoided Impacts Associated with Single Family Homes. EPA Report 530-R13-004. Washington, DC: EPA. https://www.epa.gov/smm/analysis-lifecycle-impacts-and-potential-avoided-impacts-associated-single-family-homes (accessed February 16, 2022).

Messerschmidt, B. 2021. “The Fuel of Our Homes – From Building Materials to Content.” Presented at The Chemistry of Urban Wildfires: An Information-Gathering Workshop on June 8, 2021, National Academies of Sciences, Engineering, and Medicine, Washington, DC.

Phyllis. n.d. Phyllis2 Database for the Physico-chemical Composition of (Treated) Lignocellulosic Biomass, Micro- and Macroalgae, Various Feedstocks for Biogas Production and Biochar. TNO Biobased and Circular Technologies. https://phyllis.nl/.

SFPE (Society of Fire Protection Engineers). 2016. SPFE Handbook of Fire Protection Engineering 5th edition. Edited by M. Hurley. Gaithersburg, MD: SFPE.

UNSD (United Nations Statistics Division). n.d. Standard Net Calorific Values. New York, NY: United Nations Statistics Division. https://unstats.un.org/unsd/energy/balance/2014/05.pdf.

Xie, Q., et al. 2019. “Probabilistic Analysis of Building Fire Severity Based on Fire Load Density Models.” Fire Technology 55: 1349–1375. https://doi.org/10.1007/s10694-018-0716-0 (accessed April 1, 2022).

Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×

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Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×
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Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×
Page 198
Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×
Page 199
Suggested Citation:"Appendix E: Engineering Calculations for Table 3-2." National Academies of Sciences, Engineering, and Medicine. 2022. The Chemistry of Fires at the Wildland-Urban Interface. Washington, DC: The National Academies Press. doi: 10.17226/26460.
×
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The Chemistry of Fires at the Wildland-Urban Interface Get This Book
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 The Chemistry of Fires at the Wildland-Urban Interface
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Wildfires in America are becoming larger, more frequent, and more destructive, driven by climate change and existing land management practices. Many of these fires occur at the wildland-urban interface (WUI), areas where development and wildland areas overlap and which are increasingly at risk of devastating fires as communities continue to expand into previously undeveloped areas. Unlike conventional wildfires, WUI fires are driven in part by burning of homes, cars, and other human-made structures, and in part by burning vegetation. The interaction of these two types of fires can lead to public health effects that are unique to WUI fires.

This report evaluates existing and needed chemistry information that decision-makers can use to mitigate WUI fires and their potential health impacts. It describes key fuels of concern in WUI fires, especially household components like siding, insulation, and plastic, examines key pathways for exposure, including inhalation and ingestion, and identifies communities vulnerable to exposures. The report recommends a research agenda to inform response to and prevention of WUI fires, outlining needs in characterizing fuels, and predicting emissions and toxicants.

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