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Bushfire ConsultantsAbel Ecology ecological consultants has a team of trained bushfire consultants, with years of experience in providing advice regarding construction in bushfire prone areas.
We now have a web-based, interactive radiant heat calculator to assist bushfire planners and consultants, which enables performance-based solutions based on site-specific conditions. Performance-based solutions are to be used specifically for infill developments that have to be built in flame zone conditions.
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| Fuel Management |
We offer an hourly consultation as a cost effective means to prepare a submission to council.
Development consent for a single dwelling on bushfire prone land may be granted by your local council if it is satisfied that the development conforms to the specifications and requirements of Planning for Bushfire Protection. If your development does not comply, then Council must consult with RFS before a decision is taken on your application.
Warning: A bushfire hazard assessment may affect the design of your house, so it is unwise to make commitments either to a design or to a builder before finding the constraints imposed by bushfire hazards.
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| House Under Threat |
(Addition, Alteration, new home on an existing Lot)
Section 79BA of the Environmental Planning and Assessment Act 1979 No 203 states:
"79BA Consultation and development consent - certain bush fire prone land
(1) Development consent cannot be granted for the carrying out of development for any purpose (other than a subdivision of land that could lawfully be used for residential or rural residential purposes or development for a special fire protection purpose) on bush fire prone land unless the consent authority:
(a) is satisfied that the development conforms to the specifications and requirements of the document entitled Planning for Bushfire Protection, ISBN 0 9751033 2 6, prepared by the NSW Rural Fire Service in co-operation with the Department of Planning (or, if another document is prescribed by the regulations for the purposes of this paragraph, that document), that are relevant to the development ("the relevant specifications and requirements"), or
(b) has been provided with a certificate by a person who is recognised by the NSW Rural Fire Service as a qualified consultant in bush fire risk assessment stating that the development conforms to the relevant specifications and requirements.
(1A) If the consent authority is satisfied that the development does not conform to the relevant specifications and requirements, the consent authority may, despite subsection (1), grant consent to the carrying out of the development but only if it has consulted with the Commissioner of the NSW Rural Fire Service concerning measures to be taken with respect to the development to protect persons, property and the environment from danger that may arise from a bush fire.
(2) In this section:
"special fire protection purpose" has the same meaning as it has in section 100B of the Rural Fires Act 1997."
(Integrated Development, Schools, SEPP 5, etc.)
Section 100B of the Rural Fires Act 1997 No 65 states:
"100B Bush fire safety authorities
(1) The Commissioner may issue a bush fire safety authority for:
(a) a subdivision of bush fire prone land that could lawfully be used for residential or rural residential purposes, or
(b) development of bush fire prone land for a special fire protection purpose.
(2) A bush fire safety authority authorises development for a purpose referred to in subsection (1) to the extent that it complies with standards regarding setbacks, provision of water supply and other matters considered by the Commissioner to be necessary to protect persons, property or the environment from danger that may arise from a bush fire.
(3) A person must obtain such a bush fire safety authority before developing bush fire prone land for a purpose referred to in subsection (1).
(4) Application for a bush fire safety authority is to be made to the Commissioner in accordance with the regulations.
(5) Development to which subsection (1) applies:
(a) does not include the carrying out of internal alterations to any building, and
(b) is not complying development for the purposes of the Environmental Planning and Assessment Act 1979, despite any environmental planning instrument.
(6) In this section:
special fire protection purpose means the purpose of the following:
(a) a school,
(b) a child care centre,
(c) a hospital (including a hospital for the mentally ill or mentally disordered),
(d) a hotel, motel or other tourist accommodation,
(e) a building wholly or principally used as a home or other establishment for mentally incapacitated persons,
(f) housing for older people or people with disabilities within the meaning of State Environmental Planning Policy No 5 - Housing for Older People or People with a Disability,
(g) a group home within the meaning of State Environmental
Planning Policy
No 9 - Group Homes,
(h) a retirement village,
(i) any other purpose prescribed by the regulations."
We recommend that prior to purchase of land for a development, a constraints plan be prepared to identify opportunities and constraints that a bushfire assessment may provide on land. The factors that we take into account include intended use of a site, site characteristics, statutory requirements and design opportunities.
A common misconception regarding Australia and fire is that Australian plants and animals are adapted to fire, leading to the idea that the bush can be burnt frequently, and at any time. This is now known to be incorrect.
A better way to think of our natural flora and fauna is that they can survive an appropriate fire regime. This means that there are times when it is all right for the bush to burn, and times when it isn't.
What is the best way to understand the impact of fire on ecological communities?
A long term perspective is the best way to look at the impact of fire. Also, an understanding of how local species either respond to, or cope with, a fire event, or a long term fire history, will drive our management choices. Since our main aim is to maintain biodiversity, we need to avoid burning species to extinction. This requires us to ask what fire regime each native species can best live with.
Another common misconception is that some frogs (for example Red-crowned Toadlets) are adapted to fire. This is not correct. A hazard reduction burn at the wrong time can kill an entire population of breeding individuals. Breeding often coincides with ideal hazard reduction burn season. They also respond badly to drip torch fluid being poured into a breeding site. In conditions that are conducive to a wildfire in summer, Red-crowned Toadlets are likely to be safely underground and thus safe from burning. A simple change to a burn strategy can achieve both maintenance of fauna habitat and reduction of the fuel hazard.
Waratahs are known to flower vigorously after fire. Of course, flowers can produce fruit with lots of seed, so in the past Waratahs were burnt frequently, in the belief that this was good for them. The trouble is, frequent fire kills juvenile plants, which are not old enough to survive any fire. They may take up to ten years to become fire tolerant adults. Thus, frequent fire will drive a local population to extinction. This is the case for many plant species: time to reproductive maturity is the minimum time span before a local population can cope with a second fire.
The structure of vegetation is also affected by fire. Frequent fire, typically less than ten years between burns, will simplify the vegetation structure. This happens in two ways. Firstly, logs, branches and other shelter sites are removed from the ground level. These provide shelter for many species of both plants and animals. Some animals which use this shelter are important pollinators of flowering plants. If there is no pollination, plant species eventually die out. Secondly, extinction of herbs and shrubs removes the lower layers of vegetation, which are vital shelter for smaller birds, sugar gliders and other animals which control many insects which attack the trees.
New changes in the legislation (the Rural Fires Act 1997) now recognise the need for some new ways of thinking when preparing Bushfire Risk Management Plans. One of the key achievements of the Act is that it recognises that we need to respect the needs of the natural environment (ecological sustainability and threatened species conservation).
Prevention, mitigation and suppression of bush and other fires in rural fire districts;
Co-ordination of bush fire fighting and bush fire prevention throughout the State;
Protection of persons from injury or death;
Protection of property from damage, arising from fires;
Protection of the environment by requiring certain activities, referred to in the items above, to be carried out having regard to the principles of ecologically sustainable development, described in section 6(2) of the Protection of the Environment Administration Act 1991.
Adoption of ecological sustainability as an underlying principle in the exercise of any function that affects the environment - binding on members of the Rural Fire Service, the Bush Fire Coordinating Committee and Bush Fire Management Committees. [s. 9(3), 48(3) and 51(2)]
Prohibition of the destruction of trees necessary for the protection of threatened species, populations, communities or critical habitats within the meaning of the Threatened Species Conservation Act 1995 in respect of bush fire hazard reduction requirements [s. 66(6)]
Extension of the life of bush fire risk management plans from two to five years, providing for such plans to be more strategic in nature and scope. (s. 52)
Provision for bush fire risk management plans to prohibit or restrict the use of fire as a method of fuel reduction in environmentally sensitive areas. (s. 54)
Provision for land owners and occupiers to object to obligatory bush fire hazard reduction work and to appeal the resolution of such objections to the Commissioner of the Rural Fire Service.
A private landowner can apply to Council for a fire permit to burn off during the bush fire season. Even if the landowner does not need to apply for a permit outside the bushfire season, the landowner must in both cases comply with the requirements of Part Six of the Threatened Species Conservation Act. These matters are covered in sections 85 - 98 (especially s.96) of the Rural Fires Act 1997.
As well, local government has the role of local service delivery manager, having significant fire prevention responsibilities at district level [section 37(2) and variously at Part 4].
The challenge in this is to find a balance: protection of persons and property versus protection of the natural environment. The resolution mechanism is community shaped Bush Fire Risk Management Plans (local collective knowledge and input in the form of bush fire management committees).
So, what is the way to do this?
1. The local bush fire management committee is responsible for preparing a risk management plan;
2. The proponent for operations on land is responsible to prepare a Review of Environmental Factors (REF), which includes the EP&A Act Part 5A "Seven Part Test". Where the land is managed by NSW NPWS (DECCW) or State Forests, those organisations are required to provide the REF. Where a local Council issues a notice to a private landowner for hazard reduction works, the REF is the responsibility of Council, who may delegate the task to the Fire Control Officer, or Council's Environmental Officer, or an outside agency.
3. The proponent is to bring the REF to the local bush fire management committee to endorse and confirm the REF.
4. If the REF shows no significant impact, then the operation can be approved. If a significant impact is likely, the plan is to be amended.
In preparing a plan in the greater Sydney area for example, suitable consideration could thus be given to the following habitat needs:
1. Dry ridgetop depressions are important for Red Crowned Toadlets as breeding sites, where they have nests of eggs in leaf litter, and they shelter under logs and bush rock. Avoid any burn within 5 metres of any watercourse, no matter how ephemeral, especially on ridge tops.
2. Mature live trees with hollows, and dead trees with hollows (stags), are significant roosts for many kinds of animals such as micro bats, parrots, yellow-bellied gliders, squirrel gliders and owls. Avoid burning within 5 metres of the trunk of such a tree.
3. Fallen logs and branches with hollows also provide habitat, and erosion control after a burn removes leaf litter protecting the soil. Avoid burning within one metre of these logs.
4. Koalas and Powerful Owls may be affected by a burn below the tree in which they roost. Neither are easy to find, so care needs to be taken that burns are of low flame intensity where these animals are known to range.
5. Many plant species are slow to mature to the age where they produce seed. Eight years is generally accepted as the minimum time viable between burns in any area. More frequent burns will kill out species slow to mature, and cause local extinctions. On the other hand, some plant species and communities need a hot burn once every 20 years or so to maximise seed utilisation.
6. Maintaining the natural vegetation structure in an area. Recent claims have been made in popular literature that the natural state of vegetation in Australia is grassland and open woodland with little in the form of shrub layer. Such claims have been rejected by scientists (JS Benson at the Royal Botanic Gardens, PA Redpath at DLWC, in the Journal Cunninghamia 1997). Each vegetation type will be able to cope with a different fire regime to maintain that structure over the long term.
These considerations require accurate control of burns, both in flame intensity and height, and also fire path. For example, downhill burns will usually be appropriate, but be met by a burn moving uphill from watercourses.
As well, the concept of burn zones around residential areas may need to be reconsidered, especially in light of the needs of threatened species such as Red-crowned Toadlet and Glossy Black-cockatoo.
In summary, fauna depends on vegetation. If the fire regime for an area changes, the vegetation will change, and thus the fauna able to live there will change.
J.S. Benson & P.A. Redpath (1997) Cunninghamia 5(2):285-329 The nature of pre-European native vegetation in south-eastern Australia: a critique of Ryan, D.G., Ryan, J.R. and Starr B.J. (1995) The Australian landscape- Observations of Explorers and Early Settlers
NSW Rural Fire Service internet home page www.bushfire.nsw.gov.au
This is a short introductory course for anyone wishing to learn a range of skills required to assist a professional bushfire consultant.
The two-day course consists of one day in the field and one day in our computer laboratory. Maximum course size is four people, run any time that you are available.
Applicants do not need to be a fire fighter to do this course or to be employable in this field. Desirable background is familiarity with native vegetation, e.g. bachelor degree or TAFE course.
Course cost $1,100 including GST. Apply by email to Abel Ecology.
Course content:
1. How to read Planning for Bushfire Protection 2006.
2. How to read AS 3959-2009
3. Vegetation assessment using Keith 2004 Ocean Shores to Desert Dunes: the native vegetation of New South Wales and the ACT, the journal Cunninghamia, vegetation maps and AS3959-2009.
4. Fuel load measurement and assessment, vegetation structure and vegetation typing
5. Slope measurement and analysis.
6. Fire history analysis
7. Application of Bushfire Environmental Assessment Code 2006
8. Using bushfire attack radiant heat calculators (RFS and Abel Ecology calculators are both based on the algorithm in AS3959-2009) to calculate BAL ratings 9. Using PBP 2006 to calculate BAL ratings
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ACN 079 079 762 ABN 72 516 253 75 |
Abel Ecology Pty Ltd 2011. Trading as Abel Earthcare, Abel EarthScape
and Abel Archaeology