This presentation by Emma Burgess investigates the broadly accepted paradigm that increased pyrodiversity will beget increased biodiversity. Recent research however, has questioned the relevance of a heterogeneous fire regime to a range of taxa. Controlled burning for biodiversity conservation thus remains a controversial topic. Landscape-scale bird functional diversity in this study appears to be maintained by the extent of long unburnt habitat.
Presentation from Nature Conservation Council of NSW 2015 Bushfire Conference - Fire and Restoration: working with fire for healthy lands.
2. • Private nature reserve managed by Bush Heritage Australia
• Located in Brigalow Belt Bioregion, central QLD
• BBB extensively cleared: 61% native veg cleared since
European settlement in 1840’s
• Overarching goal: restore the condition, functioning &
dynamics of the assemblages of species that would have
been present prior to European settlement
3. • Fire important management tool:
1. Mitigate wildfires
2. Maintain veg. structures that benefit faunal assemblages
• Mosaic burning approach
• Pyrodiversity begets
biodiversity
4. • At what scale does pyrodiversity influence biodiversity?
Alpha (α) diversity
Gamma (γ) diversity
Beta (β) diversity
• Components of
biodiversity:
6. Alpha, beta & gamma diversity (birds):
•Environmental heterogeneity (range in elevation)
» However, explanatory power varied depending on spatial
scale& component of diversity under investigation
•Limited support for pyrodiversity begets biodiversity paradigm
7. Foraging guilds:
•Different correlates of richness within particular
guilds & depending on spatial scale e.g.
Extent longer unburnt vegetation:
•Frugivores, insectivores, nectarivores, carnivores &
canopy feeders
8. 1. Things we can’t control important-
landscape context
2. Not pyrodiversity, but extent of
longer UB (> 10 yrs since last fire)
3. BUT management approaches
considered appropriate are dependent
on the scale at which a biodiversity
conservation goal is conceptualised
9. Advisory team: Dr Martine Maron
(UQ); Dr Patrick Moss (UQ); &
Murray Haseler (Bush Heritage
Australia)
Funding: AndyInc. Foundation; GPEM
Volunteers: Peta Mather; Donna
Oliver
10. Advisory team: Dr Martine Maron
(UQ); Dr Patrick Moss (UQ); &
Murray Haseler (Bush Heritage
Australia)
Funding: AndyInc. Foundation; GPEM
Volunteers: Peta Mather; Donna
Oliver
Editor's Notes
This project part of my PhD
Component that will present focus on bird responses to mosaic burning
this study is being conducted in a private nature reserve known as CSR which is located in the sub-tropical woodlands of Brigalow Belt Bioregion, in central QLD
BBB has been extensively cleared: with 61% native veg cleared since European settlement in 1840’s
The reserve was previously a grazing property for about 150yrs; currently managed by Bush Heritage Australia with the overarching goal: restore the condition, functioning and dynamics of the assemblages of species that would have been present on Carnarvon Station prior to European settlement in this region (Bush Heritage Australia 2011).
Various activities towards this goal including removal of feral grazing by horses& cows; weed control (buffel and johnston grass); and fire is an important management tool being used to achieve this goal.
BHA manages the property as a conservation reserve. Fire represents an important management tool towards restoring the reserve with the key aims of:
1) reducing the frequency& extent of large, intense wildfires particularly in fire-sensitive communities such as brigalow, vine scrub etc.
2) create and maintain viability of vegetation communities & their dependant fauna, especially in a fragmented landscape.
- Common assumption in fire ecology is that ‘pyrodiversity will beget biodiversity’ in which it is assumed that by increasing the range of burn conditions (burning in different seasons, different intensities) & no. of ignitions (increase frequency, smaller in extent), the resultant diversity in the fire history and representation of different successional stages of vegetation, will accommodate a wider range of species.
This method of prescribed burning is also known as mosaic burning and it is this approach that has been applied since 2001.
So whilst we assume pyrodiversity will increase habitat diversity and therefore support greater animal diversity, there is uncertainty regarding the scale at which pyrodiversity influences biodiversity with majority of research to date focused at the site or regional level!
As probably aware three main components or levels of biodiversity – illustrated in diagram in which each symbol represents a different species
Site scale: Alpha diversity – number of different species within a particular site or habitat
Among sites within landscape: Beta diversity – is a measure of the difference in species identities among sites – also known as species turnover
Landscape scale: Gamma diversity - total number of different species across all sites in a region
So we are interested in how different properties of the fire mosaic would influence different components of bird species richness; and what we expect was that the range in sucessional stages of vegetation produced by mosaic burning, would drive beta diversity between the different sites in a landscape, which give greater gamma diversity
Through active control burning we also aim to reduce the extent and frequency of wildfires. Areas of long unburnt habitat can be a limiting factor in fire-prone ecosystems. In our system, these areas of long unburnt would be expected to support higher alpha diversity –contributes positively to gamma diversity.
Conversely, if we have no active control of fire we might expect large scale wildfires to occur more frequently, that can remove key resources and create a homogeneous vegetation mosaic. Negatively impact gamma diversity.
So what did we find when we looked at bird response to mosaic burning across spatial scales:
When we looked at aggregated measured of bird species richness we found environmental heterogeneity, as measured by range in elevation, was consistently important, however, its explanatory power varied depending on the spatial scale and the component of diversity under investigation.
Despite heterogeneity being important, there was limited support for pyrodiversity begets biodiversity paradigm
We also investigated the response of different foraging guilds top mosaic burning; and we found different correlates of richness within particular foraging guilds, and depending on the scale at which richness was measured.
Importantly, we found the extent of longer unburnt vegetation was a strong driver of important foraging guilds: frugivores, insectivores and nectarivores; canopy feeders, carnivores
So what might this mean for ecological fire management?
Things we can’t control important- in this case range in elevation
Not pyrodiversity, but extent of longer UB (> 10 yrs since last fire): support increased richness across the landscape of important bird functional guilds
BUT management approaches considered appropriate are dependent on the scale at which a biodiversity conservation goal is conceptualised: so broad brush approach may not be appropriate