|
Wildland-Urban Interface and Wildland FiresAFTER APRIL 9th,
2011, THIS SITE WILL NO LONGER BE UPDATED
FOR FURTHER INFORMATION PLEASE REFER TO WUI RESEARCH AT THE NIST ENGINEERING LABORATORY WEBSITE AND THIS US FOREST WEBSITE (this USFS website may take a few weeks to become fully functional) This webpage contains an overview of ongoing work at the National Institute of Standards and Technology in the areas of wildland-urban interface (WUI) and wildland fires. Post-doctoral opportunities within NIST WUI fire research and other fire research areas exist. See one page description. For descriptions of the projects within NIST's WUI program go here. last updated November, 2010 |
Disclaimer: Any links to non-Federal Government Web sites do not imply endorsement of any particular product, service, organization, company, information provider, or content. |
Recent Activity ( within ~ the last year) | |
Articles in the pubic media | |
Defining exposure at the wildland urban interface | Fire Protection Engineering, September 2009 |
'07 Wildfire Study Focuses on Devastated Community | San Diego Union Tribune, June 21, 2009 |
Economics / Statiscal based research | |
Economic optimization of wildfire intervention activities | Int'l J. Wildland Fire 19(5):659-672 |
Enticing arsonists with broken windows and social disaster | to appear in Fire Technology |
Fighting fire with fire: estimating the efficacy of wildfire mitigation programs using propensity scores | Environ Ecol Stat 16:291-319 (2009) |
Field Studies and Building Codes | |
A Case Study of a Community Affected by the Witch and Guejito Fires | to appear in Fire Technolgoy and NIST TN 1635, April 2009 |
Development
of rapidly deployable instrumentation packages for data aquisition in
wildland-urban interface fires |
Fire
Safety J. 45:327-336 (2010) |
Fire behavior at the wildland-urban interface: Modifying building codes to reduce losses | Presentation
to San Diego Chapter of the ICC August 2009 |
Laboratory
Studies
|
|
Comparison testing protocol for firebrand penetration through building vents: Summary of BRI/NIST fuel scale and NIST reduced scale results | NIST TN 1659, January 2010 |
Quantifying the vulnerabilites of ceramic tile roofing assemblies to ignition during a firebrand attack | Fire Safety J., 45, 35-43 (2010) |
Investigation
on the ability of glowing firebrands deposited within crevices to ignite common building materials |
Fire
Safety J., 44, 894-900 (2009) |
Fire Behavior Modeling | |
Fire-front propagation using the level set method | NIST TN 1611, March 2009 |
Numerical Simulation and Experiments of Burning Douglas Fir Trees | Combustion & Flame 156 2023-2041 (2009) |
A Simple
Model for Wind Effects of Burning Structures and Topography on WUI Surface-Fire Propagation |
Int'l J. Wildland Fire, 18, 290-301 (2009) |
Other | |
Summary of Workshop on Research Needs for Full Scale Testing to Determine Vulnerabilities of Siding Treatments and Glazing Assemblies to Ignition by Firebrand Showers | NIST Special Pub 1111 (2010) |
The Wildland-Urban Interface Fire Problem Current Approaches and Research Needs | Int'l J. Wildland Fire, 19, 238-251 (2010) |
Contents |
Contacts |
|
1 page overview pdf 218 kB |
Introduction |
vegetation-to-vegetation fire spread | vegetation-to-structure |
|
|
Fire spreading within
vegetative fuels approaches a community. |
Fire spreading
through vegetation in the upper part of the photo ignited a single
structure. |
structure-to-structure |
|
(John Gibbons) Fire spread occured without significant particpation from burning vegetation or significant flame contact from adjacent structures. |
Fire spread between structures due to direct flame contact. |
Fire Behavior in Structural Fuels |
Structural fuels:
Experiment on structure-to-structure fire spread |
|
The
separation distance between structures and the materials used in their
construction are both important factors in structure-to-structure fire
spread. For exampe, as
seen in the
above photograph from a 2003 WUI fire in San Diego, CA (USA
Today), Experiments
have been conducted to investigate the
likelihood that fire can spread from one structure to another. The
materials and design used in the structures were either typical of
current building practices or included a fire barrier. In these
experiments a fire was started and allowed to burn in a typically
furnished room. Eventually the fire exited a window and an adjacent
structure
either ignited (in the case of typical construction, shown below) or
did not ignite (when a fire barrier was included in the wall
construction). In these experiments the structures were separated by 6
feet (1.8 m) which is currently allowed in some local building codes. |
|
Downloads:
|
|
In the above
photographs a structural fire exits an enclosure through a window and
ignites an adjacent wall. |
Structural fuels:
Simulations of structure-to-structure fire spread |
|
---|---|
Downloads:
|
|
The snapshots
above are from preliminary simulations of the structure seperation experiments discussed above.
These
simulations were conducted on 4 processors using measured heat release
information from the room fire in the experiments. Further work is
required in the
modeling of the target wall which has been assumed to be spruce in the
simulation. |
Fire Behavior in Vegetative Fuels |
Vegetative fuels:
Single, isolated, tree burns (experiments and simulations) |
|
|
The sequence of
snapshots are of a 2.4 m tall Douglas fir; top row are the experimental
burn, bottom row are Smokeview rendered WFDS predictions. |
|
Movies of
experimental
burns:
-
mpeg movie (12
MB) of a 1.5 m, 3 m, and 3.8 m tall Douglas fir trees burning
Comparison of
experimental and computer simulated tree burn: - quicktime movie (5 MB) of 5 m Douglas fire - mpeg movie
(17
MB) or avi
movie (60MB) of a 2.9 m (10 ft) tall Douglas tree burning, mass loss
rate, net radiation flux
|
|
Additional
information is available in the NIST technical report: "Physics-Based
Modeling for WUI Fire Spread - Simplified Model Algorithm for Ignition
of Structures by Burning Vegetation" |
|
Vegetative fuels:
Grassland
fire simulation results |
|
The homogeneous fuel
and lack of terrain variation in the grassland fires of Australia and
Brazil make these fires good candidates for use in model
validation. The figures below are some examples of simulation
results of Australian grassland fires from a
current validation study. Australian grassland experiment 200 m x 200 m plot; 5 m/s wind left to right Ignition: over 56 s two field workers walked in opposite directions starting from the center of the left-hand-side fire break. WFDS computer simulation of the experiment Ignition procedure was simulated. Grass fuel is modeled as a subgrid fuel along the base of the gas phase. Convective and radiative heat transfer is accounted for. See here for preprint of paper in the Intnl. J. Wildland Fire. Animation of WFDS simulation: mpeg (17MB) or avi (38MB) Note: simulation domain extends ~ 700 m in all directions. Only the 200 m x 200 m grassland plot in the WFDS simulation is shown here. |
|
The figure at left shows the steady state spread rate from the grassland simulations (symbols), BEHAVE (solid line), and from Eq. 4 in Cheney et al. (Prediction of Fire Spread in Grasslands, Int. J. Wildland Fire, 8: 1-13, 1998). BEHAVE is the most commonly used fire spread prediction model in the U.S. |
Vegetative
fuels: Intermix of vegetative fuels leading transition to crown fire. |
Many of today's
forests have historically dense accumulations of dead
fallen material which pose a fire threat to the overall ecology of the
forest and nearby communities. An important question in forest
management is, therefore, how much of this material should be removed
to reduce the fire threat to acceptable levels. In the example below
WFDS is used to simulate a surface fire spreading through a forested
region part of which has underbrush. |
|
Plan View |
|
Side View of Vegetative Fuel |
|
In the above
figures grass and pine needle fuel are colored green and black,
respectively; the underbrush, tree trunks and tree crowns are colored
blue. In the movies (see links below) this blue color changes according
to the temperature of the fuel (red is hottest). Fuel/Wind Specifications: -
grass fuel loading is NFFL 3 (tall grass, 0.674
kg/m^2)
- pine needles: 5 cm depth, 20 kg/m^3 bulk density - underbrush: 0.5 m - 2.0 m height, 1 kg/m^3 bulk density - tree crown: 7 m - 14 m height, 0.24 kg/m^3 bulk density (160 trees in 80 m x 80 m area) - wind is 6 m/s from left to right Computational Specification: -
domain is 320 m x 320 m x 80 m (160x160x20 grid cells)
- horizontal grid resolution is 2 m, vertical is 2 m near ground and stretches to 8 m at top. Animations from Smokeview: -
plan view quicktime
movie
(1.3 MB) showing fire spread
- tour view avi movie (15 MB) showing fire spread and smoke) The animations clearly show the loss of tree crowns in areas where the underbrush was present and provided a ladder fuel for fire spread from the pine needles to the crowns. Additional information is in a talk given at the March 2004 Core Fire Science Caucas meeting in Reno, NV. |
|
WFDS Simulation of a Stand Burn Similar to the International Crown Fire Experiment |
Two wall assemblies are placed 10 m and 20 m down spread of the stand. This mimics similar experiments performed during the International Crown Fire Experiments conducted in the Northwest Territories of Canada. The simulated stand is approximately 1/4 the size of the experimental stand. A movie of the simulation is here. Time histories of the radiant fluxes on the walls are shown in the movie. The magnitudes and duration of the rise to maximum value of the fluxes are similar to the experiment. |
|
wfds_one_tree_movie.avi
(8.5 MB) Example of a fire spreading through an excelsior surface fuel under a 6 m tall conifer. |
Vegetative fuels: Simulation of enclosure
effects:
excelsior fuel bed burning in a wind tunnel |
|
|
Two different
simulations were conducted. The two lower images in the figure above
show a side view (on the left) of the wind tunnel and an end view
looking downwind (on the right). The wind tunnel on the bottom row of
the figure has
the same cross-section (3 m x 3 m) dimensions as the experimental
facility used by the USDA
Foreset Service in their Missoula, Montana laboratory. The wind tunnel
in the upper row has crossection dimensions which have been doubled (6
m x 6 m). Both wind tunnels are 16 m long. A
fuel bed of excelsior 1 m wide, 8 m long and 20 cm tall is placed in
the center of the wind tunnel floor. A 1.8 m/s wind blow from left to
right. The fuel properties of the excelsior are from an experiment
conducted by Catchepole et al. (Rate of Spread of Free-Burning
Fires of Woody Fuels in a Wind Tunnel, Comb. Sci. Tech., 131, 1-37, 1998).
The As can be seen in the figure above and the movies (links are below) the walls and ceiling of the wind tunnel sufficiently confine the buoyant plume that the plume itself it acts as a barrier to the incoming flow. Links to movies: - fuel_bed_wind_tunnel.mpg
(4.6 MB)
- fuel_bed_wind_tunnel.avi (12 MB) |
Fire Behavior in the Intermix of Vegetative and Structural Fuels |