VANCOUVER LANDFILL DEMOLITION FIRE
Monitoring Program
On
October 20th the City of Vancouver retained Sperling
Hansen Associates Inc. to monitor the progress of the fire fight
and to provide recommendations on future actions. Through a simple
monitoring program focusing on the installation of subsurface
probes in the demolition area, Sperling Hansen was able to show
conclusively that the fire had been completely extinguished and
that the conditions that had created the potential for a fire
had been resolved.
The
monitoring program involved collecting temperature and gas composition
data throughout the demolition cell. Readings were taken at all
observed steamer vents as well as over a grid of regularly spaced
“barhole punch” probes installed through the intermediate cover
into the shallow sub-surface.
Barhole
punch monitoring points were created by driving a solid steel
bar approximately 1.5 m below grade with an excavator, then pushing
a hollow steel 2.5 cm diameter sampling pipe into the cavity.
An oversize bolt was used to prevent the pipe annulus from clogging
during insertion. On achieving full depth, the sampling
pipe was pulled back approximately 15 cm, dislodging the bolt
and allowing sub-surface samples of gas composition to be collected.
Maximum
temperatures noted at surface using a hand held infra-red sensor
were 54.1 °C.
On this project, as well as on several other landfill fire projects
investigated by Sperling Hansen, temperature readings taken at
surface did not prove to be particularly useful in indicating
the extent of the fire zone. Subsurface temperature readings
from thermister strings installed in boreholes within the waste
typically provide a much more effective indication of fire conditions
in the subsurface. On this project,
thermisters were not installed because of the relatively shallow
fill and also on the basis that the gas composition data from
the barhole punch monitoring program indicated that the extent
of the fire was limited. Gas samples were analyzed using
portable sensors for oxygen, methane, carbon monoxide and hydrogen
sulphide.
At
the start of the monitoring program, sub-surface oxygen levels
within the burn area were typically in the range of 15 to 21%
oxygen. As fire fighting and capping efforts progressed,
oxygen levels dropped consistently. By the time the monitoring
program was completed on November 3rd, oxygen levels
in most wells dropped below 1%.
Similarly,
subsurface methane concentrations were below 1% methane in many
of the sampling ports at the onset of monitoring. Low methane
concentrations indicated that decomposition was occurring in an
aerobic regime. As mentioned previously, aerobic decomposition
is associated with greater generation of heat, and can lead to
spontaneous combustion. By November 3rd, methane
concentrations had climbed above 40% in most of the wells.
On
this project carbon monoxide (CO) proved to be the most effective
indicator of landfill fire. Initially, CO concentrations
up to 315 ppm were noted in the vicinity of the active burn zone.
These concentrations gradually declined as fire was brought under
control. Because elevated CO concentrations were not noted
in steam vents and barhole punch sites outside the active burn
zone and because there was a direct relationship between CO concentrations
and fire activity, we believe that CO provides an excellent indication
of subsurface fire activity. Contours showing the gradual
reductions in CO concentrations are shown in Figure 2.
Based
on observations on this project as well as on experience at landfill
fires at Campbell Mountain Landfill, the Delta Shake and Shingle
Landfill and the recent landfill fire in Minnesota, Sperling Hansen
Associates have developed the following empirical scale that we
now use routinely to assess fire conditions in construction demolition
landfills.
Carbon Monoxide Concentration
(ppm)
No Fire Indication
0
-
25
Possible Fire in Area
25
- 100
Potential Smoldering Nearby
100
- 500
Fire or Exothermic Reaction Likely
500
- 1000
Fire in Area
>1000
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Conclusions and Lessons Learned
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