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Bushfire Report
Attached to the e-mail MCU16/0081 Bushfire report, Survey, Ecological Assessment Report Email 2 of 3.
Original PDF page 92, section 1. The text section number identifies this passage in the reader.
A steel fence after testing at the Mogo site.
RESEARCH OUTCOMES TOXIC CONTAMINANT RELEASE dispersion, and the degree to which site
SMALL-SCALE EXPERIMENTS The major issue related to the combustion occupants are exposed to the gases.
This investigation confirmed that Colorbond of Copper Chrome Arsenic (CCA)-treated
LARGE-SCALE EXPERIMENTS
steel fencing panels do not ignite and pine is the release of significant levels of
arsenic, as well as the high arsenic content Colorbond steel
contribute significant heat release during
in the timber ash (2.2% by weight). Arsenic This had the best performance as it is a
cone calorimeter exposure. Both pine and
can cause eye, throat and respiratory non-combustible material. It maintained
hardwood materials provide significant heat structural integrity as a heat barrier under
irritation, and is a confirmed human
release under these exposures. The ranking of all experimental exposure conditions, and it
carcinogen. It is worth noting that the
performance of these materials in descending did not spread flame laterally or contribute
National Environmental Protection Measure
order are: Colorbond steel (insignificant to fire intensity during exposure. The fencing
provides health impact criteria for arsenic
release), new hardwood, old hardwood, old reduced radiation levels within the fencing
in soils in the range of 0.01-0.05%, and so
pine and new pine. boundary to below 5 kW/m2 immediately
the dispersion of CCA-treated pine ash
Of particular interest was the effect moisture could lead to site contamination, especially behind the fencing system during all radiation
content had on the time to ignition for all where large quantities of the material has exposures, and reduced the radiant heat
these materials. In particular, the observation been burnt. Analysis also showed that it exposure on a structure nine metres from the
that a material exposed for six hours to 40 could be harmful for a person to come into fencing by at least a factor of two for the given
degreesC and 20% relative humidity had direct skin contact with the ash. fire size in the experiment.
similar fire properties to the same material As for Colorbond steel, two human Hardwood
when conditioned at same temperature and carcinogens (benzene and formaldehyde) Although combustible, closed paling
relative humidity until moisture equilibrium were detected in the air toxicity experiments hardwood fencing maintained a radiant heat
was achieved. This highlights a significant conducted on this material. While these barrier during radiation-only exposures,
point – that the fire behaviour of these gases were detected, the risks they present resulting in a reduction in heat received at the
specimens was influenced more by the surface would depend on the levels of exposure to structure. In exposures where flame contact
moisture content rather than the average nearby occupants, which is unknown. In of the fencing occurred, flame emission
moisture content of the specimens, and hence fact, evaluating the risks from these gases from the fencing provided additional radiant
the weather conditions on the day of fire will depend on combustion conditions, heat exposure on the structure. Open paling
impact will have a significant effect on the fire the quantity of material burnt, the volume hardwood fencing systems were partially
performance of timber elements. of combustion gases generated and its effective in attenuating incident radiation
3 Background briefings on emerging issues for fire managers from AFAC and Bushfire CRC. 3
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