
Stew Walkinshaw, Montane Forest
Management Ltd., Canmore, AB
Ray Ault, FPInnovations Feric Division,
Wildland Fire Operations Research Group, Hinton, AB
Video 1. Sprinkler Water Application
Video 2. Aqueous Gel Application
Video 4. Sprinkler Cabin Front Right
Video 5. Sprinkler Cabin Back Left.
Video 6. Aqueous Gel Cabin Front Left
Video 7. Aqueous Gel Cabin Back Right
Structure protection, Fire suppression, Sprinklers, Aqueous
gel, ,Wildfires, Wildland - urban interface.
With the help of the Northwest Territories
government, FPInnovations–Feric Division
conducted test burns near Fort Providence
in June 2005 and documented the setup and
application, resources required to operate,
and success of structure protection for both
sprinkler and aqueous gel systems on test
cabins. This report presents results from the
first of the test burns; the other burns will be
documented in future reports.
This study had the following objectives:
·
Determine the effectiveness of structure protection
equipment that is readily available to homeowners.
·
Evaluate the effectiveness of sprinklers and aqueous
gel in structure protection under extreme fire behaviour conditions and determine
the conditions that influence success.
·
Evaluate the time and resources required to treat
structures with sprinklers or aqueous gel.
·
Evaluate the temperatures at critical points on each
structure during and after wildfire passage.
·
Evaluate the effect of exterior structural materials to
structure survival.
Cabin dimensions were 2.4 m × 3 m with
a 1.2 m × 2.4 m deck on the back (Figures
1 and 2). The cabins were pre-assembled in
sections in Alberta and transported to the
Northwest Territories site by trailer. Each
cabin was then re-assembled onsite.


Cabins were wood-frame construction with the following
exterior materials:
Cabin locations were chosen based on the
need for extreme fire behaviour to approach
and surround the cabin with ease. The only
trees removed were those necessary to site
the cabin. No modifications were made to
the stand or the fuels surrounding the cabins
other than erecting the cabins. Cabins were
placed within approximately 20 m of each
other to ensure each experienced similar fire
behaviour, while not influencing each other
(Figures 3 and 4).
Each cabin was pre-wired with 20 temperature sensors to
record temperatures before, during, and after the fire. The sensors were placed
at the following locations:
·
under cedar siding (4 locations) – right
rear and side, left front and side
·
outside window (2 locations) – right and
left sides
·
inside window (2 locations) – right and
left sides
·
under vinyl siding (4 locations) – right
front and side, left rear and side
· in soffit (4 locations) –1 m from right
and left front and 1 m from right and
left rear
·
in peak (2 locations) – 1 m from rear and
1 m from front
· interior of cabin (2 locations) – centre
1 m and 2 m above ground
Each cabin site had four radiant cubes to record radiant
heat flux (kW/m2) in the wildfire environment and in-fire video
cameras to record the sequence of events before, during, and after the fire.

corners, and two were elevated 1.2 m off the
ground on wooden poles at the northeast
and southwest corners. The sprinkler arc was
set for 90o to wet only the cabin area. Two
people installed the sprinklers.
Water supply was provided from an 11,000 L relay tank and pumped with a Honda pump through 38 mm lined fire hoses. Water supply volume and pressure was 68 L/min at 364 kPa. The main supply line was buried 15 cm below ground to avoid burning the hose and losing water supply. Water was supplied to the sprinklers with a 16 mm Wildfire Econoflo® hose, in a closed-loop circuit, from a wye off the northwest corner of the cabin (Figure 5). Following installation, the system was tested and pressures and volumes were recorded. Sprinklers were operated for 22 minutes prior to wildfire impingement (Figure 4).


A homeowner application package
consisting of a one-gallon plastic jug of gel
and a brass eductor nozzle was used to apply
aqueous gel. The same relay tank, Honda
pump, and hose as used in the sprinkler
system were used for water supply.
One 15 m length of 16 mm Econoflo hose
supplied water to the eductor nozzle for gel
application (Figure 6).

The vegetation consisted of C3 (jack pine) fuel type with a
moderate black spruce understory and Cladonia
ground cover (Figure 8). Ladder fuels
and ground fuels were light to moderate.
direction.
The fire was ignited under the Canadian
Forest Fire Danger Rating System (CFFDRS)
fire weather indices shown in Table 1 (Turner
and Lawson 1978). Intense wildfire was
anticipated as a result of igniting under these
weather conditions and indices.
Table 1. CFFDRS weather and fire indices at time of ignition
|
Plot |
Date |
Temp (C) |
RH (%) |
Wind (kmh) |
FFMC |
DMC |
DC |
ISI |
BUI |
FWI |
|
1 |
June 28/05 |
25.4 |
24 |
E @ 6 |
93 |
46 |
385 |
10 |
71 |
27 |
Results and discussion
Two people each spent 45 minutes to install the sprinkler
for a total installation time of 1.5 person-hours (Table 2).
Sprinklers operated for 22 minutes prior to wildfire
impingement for a total of 2000 L of water applied.
Video 1. Sprinkler Water Application. (Click on it to start)
Two people each spent 12 minutes on the gel system setup and
application for a total setup and application time of 0.4 person-hours (Table
2). Gel application time was approximately 6.5 minutes.
A total of 5.7 L of aqueous gel was applied at the
recommended application rate of 2% resulting in a total of 335 L of water
usage. Application was complete approximately 53 minutes prior to wildfire
encroachment.
Video 2. Aqueous Gel Application. (Click on it to start)
Table 2. Installation and application
details sprinkler and aqueous gel systems
|
|
Sprinkler |
Aqueous
Gel |
|
Installation/Application Manpower |
2 |
2 |
|
Installation/Application Time |
1.5 person hours |
0.4 person hours |
|
Application Water Volume |
2000 litres |
335 litres |
Less time and water were
required to set up and apply the aqueous gel than to install and operate the
sprinkler system. This may be a benefit where manpower, time, or water supplies
are limited for structure protection.
The wildfire approached both cabins as an active crown fire with significant airborne firebrand transport landing on the structures ahead of the fire. The sprinkler cabin survived wildfire passage with significant damage and the aqueous gel cabin was destroyed (Figure 9).
Video 3. Plot 1 Fire Behaiour. (Click to start)
In-fire video of the event indicates that
water application from sprinklers reduced
the combustibility of the structural fuels and
reduced the fire intensity in the wildland
fuels immediately adjacent to the cabin. As
a result, the structure survived and surface
fuels were unburned for 2 m surrounding
the cabin within the sprinkler arc. The
cabin exterior was ignited by the initial
passage of the flame front but did not sustain
combustion once the flame front had passed.
Damage to the sprinkler cabin included the
following:
The sprinkler arc was set at 90o because water
was limited and it was determined more important to wet the structural fuels
than to wet forest fuels.
Above-ground sprinkler equipment was damaged and ceased
operation upon flame-front passage (Figures 14 and 15). The 16 mm Econoline
hose melted or cracked in several locations and water flow to the sprinkler
loop ceased. The sprinkler heads were undamaged because the areas surrounding
them were moist. The buried 38 mm mainline was not damaged.

The sprinkler system was operational up to the point of
wildfire passage, which appeared to be an extremely important factor in
structure survival. Past Feric case studies have shown that if water supply is
lost prior to the arrival of the flame front, the probability of structure
survival is significantly reduced. Therefore, structure protection personnel should
install the water supply, pump, and supply hose in non-combustible areas to
ensure that water supply is maintained during flame front passage.
Video 4. Sprinkler Cabin Front Right. (Click to start)
Video 5. Sprinkler Cabin Back Left. (Click to start)

Figure 12. Post-fire soffit material.
Figure 13. Post-fire window.

Figure 14. Post-fire elevated sprinkler.
Figure 15. Post-fire ground sprinkler
Figure 16. Post-fire gel cabin.
In-fire video indicates that the flame front completely
enveloped the gel cabin and resulted in severe burning of all surface and
aerial wildland fuels surrounding the cabin (Figure 16). The cabin was
destroyed as a result of both wildland and structural fuels igniting under the
untreated underside of the back deck. As with the sprinkler cabin, the gel
cabin exterior was ignited by initial passage of the flame front but did not
sustain combustion once the flame front had passed, except for the rear deck, under
the eaves, and on the joint between the vinyl and cedar siding on the front
side of the cabin. The main ignition point for the gel cabin was the underside
of the back deck which then supported the combustion on the back wall and under
the back eaves. Fire burned on the back wall for approximately 6 minutes before
entering the cabin interior through the rear soffit, fracturing the windows,
and resulting in cabin collapse approximately 13 minutes after flame-front
passage.
The asphalt-shingle roofing material was ignited by the
flame front but did not sustain combustion once the flame front had passed. Airborne
firebrands ahead of the main flame front did not ignite the roofing material or
the deck surface; however, they did ignite the surrounding surface vegetation.
The double-glazed windows remained intact during flame-front
passage; however, they were eventually fractured when fire entered the interior
of the structure. It is unknown if one or both panes were cracked with
flame-front passage.
The cabin temperature sensors provided
valuable information. Table 3 presents the
maximum and average temperatures at
various locations for both cabins. Table 4
presents temperatures that were taken at
or about the same time at various locations
for both cabins. Data from the gel cabin
sensors should be used with caution and may
be inaccurate due to exposure and sensor
damage from the structure fire.


FireSmart Protecting
Your Community from Wildfire (Partners in Protection 2003) recommends that
a minimum of double-glazed windows are used for interface structures. The maximum
temperature on the outside pane of the sprinkler cabin was 354oC compared
to 73oC on the inside pane recorded at the same time. The maximum
temperature on the outside pane of the gel cabin was 969oC compared
to 188oC on the inside pane at the same time (Figure 18). The data
for both cabins indicate that double-glazed windows significantly reduce
radiant heat transfer to the interior of the structure.

The maximum temperature in the
sprinkler cabin at 1 m above ground level
(AGL) was 47oC compared to 80oC at 2 m
AGL and 154oC at 3 m AGL (Figure 18).
The maximum temperature in the gel cabin
at 1 m AGL was 162oC compared to 170oC at
2 m AGL and 358oC at 3 m AGL. The results
confirm that interior structure temperatures
are significantly lower than exterior temperatures
during flame front passage but they
increase with distance from the ground.
Comparison of interior temperatures
between the sprinkler and gel cabins
indicates significantly lower temperatures in
the sprinkler cabin, which may be attributed
to the flame front being much closer to the
gel cabin and the cooling effect of the water
on the sprinkler cabin.
The average temperature under the cedar
siding of the gel cabin was 288oC compared
to 838oC under the vinyl siding. The temperatures
under the vinyl siding were significantly
higher due to the early melting of the
vinyl siding from the sheathing, resulting
in exposure of the temperature sensors.
The under-siding temperatures for the gel
cabin should be used with caution as the
temperature sensors lose accuracy once they
are exposed to flame from the burning
structure.
The average under-siding temperatures were significantly
higher for the gel cabin than the sprinkler cabin. This is attributed to the
flame front being much closer to the gel cabin and the continued cooling
provided by the sprinklers.
The structure protection materials (i.e.,
water storage, pumps, hose, and sprinklers)
that are readily available to the homeowner
from local hardware stores and retail outlets
can be successful in providing structure
protection.
Sprinkler systems work well for structure protection under extreme fire behaviour conditions providing the water supply continues up to and during the time of fire front passage. Therefore, the water supply lines should be protected from radiant heat and direct flame impingement, and sprinkler arc patterns should be set to wet as large an area surrounding the structure as possible.
This study examined the effectiveness
of certain structural materials to withstand
extreme fire behaviour. The results of this
study support the information presented
in FireSmart – Protecting Your Community
from Wildfire (Partners in Protection 2003)
regarding the recommended use of asphaltshingle
roofing materials and double-glazed
windows, and the recommended practice of
skirting decks and open spaces.
McCulloch, W. 2006. Evaluating the effectiveness of a fire torch system for community protection prescribed f ire operations. Feric, Vancouver, B.C. http://f ire.feric.ca/36112001/ TerraTorchReport.pdf
Partners in Protection 2003. FireSmart– protecting your community from wildfire (2nd ed.). Partners in Protection, Edmonton, Alta.
Turner, J.A.; Lawson, B.D. 1978. Weather
in the Canadian forest fire danger rating
system: A user guide to national standards
and practices. Canadian Forestry Service,
Pacific Forest Research Centre, Victoria,
B.C. BC-X-177.
Acknowledgements
The author would like to thank the Northwest Territories and Alberta governments for their support of this project, and Mark Ackerman from the University of Albertas Faculty of Engineering for his time and effort spent working on the project and for producing the heat flux and temperature data in this report.