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 |
|
| 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). |
| 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: |
Fire Behavior in the Intermix of Vegetative and Structural Fuels |
| Simulation of a grass
fire spreading into structures with different fuel treatments |
![]() |
|
| Fuel/atmosphere
specifications: -
grass fue loading is 0.3 kg/m^2 (between NFFL1 [short
grass, 0.166 kg/m^2] and NFFL 3 [long grass, 0.674 kg/m^2])
-
tree crowns have a bulk density of 4.72 kg/m^3
-
underbrusg bulk density 4.72 kg/m^3
- wind is 1 m/s from
right to left
Computational
specifications:-
domain is 80 m x 80 m x 100 m (80x80x36 grid cells)
- horizontal grid
resolution of 1 m; vertical grid is 1 m
at ground and stretches to 3 m at top
Animations from Smokeview: A grassland line fire spreads into structures which have varying amounts of surrounding vegetative fuel loads. The structure on the upper right-hand side has the highest vegetative fuel loading. As seen in the animations the ignition of the underbrush surrounding this structure leads to a crown fire. |
Firebrand
Experiments
|
| The brands below were
ignited and dropped on target fuels of different moistures and wind
enviornments. |
||
![]() |
Disk shaped. This
shape has good lofting capabilites and is an approximation of
firebrands generated from burning bark and roof shingles. Disk dimensions: diameter = 25 mm; thickness = 8 mm Disk dimensions: diameter = 50 mm; thickness = 6 mm A paper covering disk shaped brands is here.. |
|
![]() |
Cylindrical shaped:
This shape approximates branches and twigs based on brands collected
from burning Douglas firs tree in NIST Large Fire Laboratory (see image
at right). Size of Douglas fire dowels at left are: length = 76 mm; diameter = 10 mm length = 51 mm; diameter = 5mm |
![]() |
![]() |
![]() |
![]() |
| shredded paper |
pine needles |
shredded hardwood
mulch |
![]() |
![]() |
![]() |
| no igntion from
glowing firebrand |
flaming ignition from
single flaming firebrand |
flaming ignition from
multiple glowing firebrands |
![]() |
![]() |
| In order to study the
ignition properties of target fuels under more realistic setting a
brand generator (pictured above), capable of producing a mass flux of
firebrands, is being constructed. This project is still in a
preliminary stage of characterizing the size, mass, and burning state
of the firebrands generated from different "feeder" materials. For
example, among the materials tested to date are mulched Douglas Fir
trees and 50 mm long Douglas dowels. See below. |
|
![]() |
Mulched Douglas Fire
tree. movie of brand generator (12.4 MB, avi - might not work with quicktime) |
![]() |
50 mm long, 5 mm
diameter Douglas Fir dowels movie of brand generator (14 MB, avi - might not work with quicktime) |
Realistic
Inputs for WUI Fire Simulations
|
![]() |
|
Southern Study Area.
Derived from a combination of LiDAR and color imagery. Structures
are colored according to NFPA rating of the roofs, siding, decks, and
eaves.![]() |
|
WFDS represetation of
the above 500 m by 500 m area using input data created by the Coeur
d'Alene Tribe GIS program. Trees are shown in blue. The roofs and sides
of structures are colored according to their ratings from field
observation using the NFPA 1144 standard (a simplified scheme of red,
blue, green for most to least combustible was used at this point).![]() |
Presentations
(in reverse chronological order)
|
| # |
Title |
Venue |
| 17 | The NIST Wildland-Urban Interface Program pdf | Presentation to CALFIRE and City of San Diego Fire Department; February 2008 |
| 15 | Measurement of firebrand production and heat release rate (HRR) from burning Korean pine trees | Asia-Oceania Symposium (IAFSS), Sept. 20-23, 2007, Hong Kong |
| 14 | On the use of a firebrand generator to investigate the ignition of structures in wildland-urban interface fires | 11 International Conference on Fire Science and Engineering (INTERFLAM), September 3-5, London, UK (2007) |
| 13 |
Firebrand production from burning vegetation | 5th Intnl. Conference Forest Fire Research, Combria, Portugal, November, 2006 |
| 12 |
Numercial modeling of fires spread through trees and shrubs | " " |
| 11 |
Quantifying and ranking the flammability of ornamental shrubs in the southern United States | 3rd Intn'l Fire Ecology and Management Congress, San Diego, Nov. 13-17, 2006 |
| 10 |
Fire spread and structural ignitions from horticultural plantings in the wildland-urban interface | " " |
| 9 |
Flammability rankings of commonly used horticultrual plant in the southern U.S. | " " |
| 3 |
Numerical
simulations of grassland fire behavior from the LANL-FIRETEC and
NIST-WFDS models (paper)
(presentation)
(avi) |
EastFIRE Proceedings, May
11-13, 2005 George
Mason University, Fairfax, VA presentation |
| 2 |
Physics-Based Modeling of Community Fires | International Interflam Conference, 10th Proceedings. Volume 2. July 5-7, 2004Edinburgh, Scotland, Interscience Communications Ltd., London, England, 11 p., 2004 |
| 1 |
Neighborhood-Scale Fire Spread | Fire and Forest Meteorology, 5th Symposium. Joint With 2nd International Wildland Fire Ecology and Fire Management Congress. Proceedings. November 16-20, 2003, Orlando, FL, 8 p., 2003 |
Archival
Publications (in reverse chronological order)
|
| # | Title |
Journal |
| 8 | Mass and size distribution of firebrands generated from burning Korean Pine (Pinus Koraiensis) Trees | Fire and Materials, to appear |
| 7 | On the development and characterization of a firebrand generator | Fire Safety Journal, to appear |
| 6 | Experimental investigation of firebrands: Generation and ignition of fuel beds | Fire Safety Journal, 43, 226-233, 2008 |
| 5 | Firebrand generation from burning vegetation | Int'l J. Wildland Fire, 16, 458-462, 2007 |
| 4 |
A
physics-based approach to modeling grassland fires (preprint) accessory publication with model details is here or here |
Int'l J. Wildland Fire, 16, 1-22, 2007 (note the accesory pub. is here too) |
| 3 |
Ignition
of mulch and grasses by firebrands in WUI fires |
Int'l J. Wildland Fire, 15: 427-431, 2006 |
| 2 | An evaluation of the fire plume properties simulated with the FDS and Clark coupled wildfire model | Canadian J. Forest Research, 36, 1-15, 2006 |
| 1 |
On
the ignition of fuel beds by firebrands |
Fire & Materials, 30:77-87, 2006 |
Other
publications (in reverse chronological order)
|
| # |
Title |
Venue |