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Fire as a tool for
maintaining diversity and influencing
vegetation structure
The management
of GGRP sites
1. Protection of life
2. Protection of assets
Biomass reduction
Weed control
Biodiversity attributes
Cultural connections
Why do we
burn?
Roadside burns in western Victoria maintain
strategic fire breaks for human and asset
protection
Burns also play an important role in preserving
remnant roadside communities
Ground layer Fire response in remnant vegetation
Why do we burn GGRP sites?
• Reduce biomass and inhibit grassy dominants
• Restrict undesired tree regrowth
• Rejuvenate vegetation (grasses and forbs)
• Allow for persistence of sub-dominants (forbs)
• Maintain canopy gaps for recruitment
• Cost (?)
• Ease (?)
• Effectiveness (?)
• Competing objectives (?)
Restricting biomass and opening
grassy canopy
Grass dropping seed into gaps
after fire
Restricting tree regrowth
Rejuvenating vegetation
Allowing sub-dominants to persist
Opening niches for species to move to
in adjoining vegetation
Issues with fire in current-day Australia
Can these goals be achieved by
other means?
• Cut and bale
• Slashing
• Grazing
– Deferred
– Rotational
• Herbicides
• Combinations of the above
Grazing
• Grazing can be effective in maintaining or increasing
native cover in semi-natural grasslands, but as a
management tool requires good stock management
skills
• Deferred (short or long term) or rotational grazing aims
to graze pasture intensively (crash or cell grazing) at the
point where annual grasses have raised (but not
ripened) seed heads (early spring), and then remove
stock over summer when natives are setting and
dropping seed
• Conversely, set-stocking has been shown to have
negative effects including selective grazing of native
herbs, trampling, soil compaction, importation of weed
seed, localised deposition and return to the soil of dung
and urine
Mowing/baling
• Slashing/mowing of grass biomass (native and exotic) on
public roads is a common practice due to the ready access of
machinery and relatively low cost
• In native grasslands mowing is ideally followed by raking and
baling to remove fallen biomass as herbage can return
unwanted nutrients to soils, smother vegetation or restrict
seedling recruitment
• Mowing and baling of built up grass canopy (autumn through
winter) can reduce competition on wildflower species and
provide recruitment gaps for seedlings
• Drawbacks of mowing include the possible introduction of
weed seeds on equipment, soil compaction, and physical
damage to plant structure by the tires of mowing equipment
Cut & Baling
Seed Hay
GGRP burns
Burn cues –
> 70% vegetative cover
Burn cues –
Dry material above 150 mm
Chepstowe
Patch burns
Hamilton
Is burning always best?
Probably not always but it is a very effective tool for grassland management in many situations

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BushfireConf2015 - 7. Fire as a tool for maintaining diversity and influencing vegetation structure

  • 1. Fire as a tool for maintaining diversity and influencing vegetation structure The management of GGRP sites
  • 2. 1. Protection of life 2. Protection of assets Biomass reduction Weed control Biodiversity attributes Cultural connections Why do we burn?
  • 3. Roadside burns in western Victoria maintain strategic fire breaks for human and asset protection
  • 4. Burns also play an important role in preserving remnant roadside communities
  • 5. Ground layer Fire response in remnant vegetation
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  • 9. Why do we burn GGRP sites? • Reduce biomass and inhibit grassy dominants • Restrict undesired tree regrowth • Rejuvenate vegetation (grasses and forbs) • Allow for persistence of sub-dominants (forbs) • Maintain canopy gaps for recruitment • Cost (?) • Ease (?) • Effectiveness (?) • Competing objectives (?)
  • 10. Restricting biomass and opening grassy canopy
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  • 14. Grass dropping seed into gaps after fire
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  • 20. Opening niches for species to move to in adjoining vegetation
  • 21. Issues with fire in current-day Australia
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  • 27. Can these goals be achieved by other means? • Cut and bale • Slashing • Grazing – Deferred – Rotational • Herbicides • Combinations of the above
  • 28. Grazing • Grazing can be effective in maintaining or increasing native cover in semi-natural grasslands, but as a management tool requires good stock management skills • Deferred (short or long term) or rotational grazing aims to graze pasture intensively (crash or cell grazing) at the point where annual grasses have raised (but not ripened) seed heads (early spring), and then remove stock over summer when natives are setting and dropping seed • Conversely, set-stocking has been shown to have negative effects including selective grazing of native herbs, trampling, soil compaction, importation of weed seed, localised deposition and return to the soil of dung and urine
  • 29. Mowing/baling • Slashing/mowing of grass biomass (native and exotic) on public roads is a common practice due to the ready access of machinery and relatively low cost • In native grasslands mowing is ideally followed by raking and baling to remove fallen biomass as herbage can return unwanted nutrients to soils, smother vegetation or restrict seedling recruitment • Mowing and baling of built up grass canopy (autumn through winter) can reduce competition on wildflower species and provide recruitment gaps for seedlings • Drawbacks of mowing include the possible introduction of weed seeds on equipment, soil compaction, and physical damage to plant structure by the tires of mowing equipment
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  • 37. Burn cues – > 70% vegetative cover
  • 38. Burn cues – Dry material above 150 mm
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  • 55. Is burning always best? Probably not always but it is a very effective tool for grassland management in many situations