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TERN: Data infrastructure that
enables fire management
Nikki Thurgate, S. Guru and T. Clancy
TERN:
• Infrastructure and networks to support a coordinated, collaborative
ecosystem science community
• Enabling sustained, long-term collection, storage, synthesis and
sharing of ecosystem data
• Connecting science with policy and management
TERN: Australia’s ecosystem observatory delivering data
streams to enable environmental research and
management
Instruments
+ Sensors
Policy +
Management
Analysis
+ Synthesis
Modelling
Data
Searching
Data
Sharing
Data Curation
+ Publishing
Data
Storage
Processing
+ Analysis
Collection
Methods
TERN FIRE DATA- TASMANIA 2016-
COMBINATION OF METHODS ALLOWS
IMPROVED BUSHFIRE PREDICTION MODELS
Connecting science
TERN Fire data- Repeated fuel reduction burns in
temperate forests, like this one in
southeast Australia, have little long-term
impact on soil greenhouse gas exchange
Fire Management
Pre-processed MODIS fire
burnt area satellite
imagery
Vegetation Map and
Expert elicitation
Thank you
Carl Gosper, Suzanne Prober and Colin Yates
t (08) 9333 6442
e carl.gosper@csiro.au
CSIRO ECOSYSTEM SCIENCES AND DEPARTMENT OF ENVIRONMENT & CONSERVATION
Further information:
Parsons & Gosper (2011) International Journal of Wildland Fire 20, 184-194
Prober et al. (2012) Climatic Change 110, 227-248
Gosper et al. (in press) Australian Journal of Botany doi: 10.1071/BT12212
Age-structure in GWW woodlands
Age class (years since fire)
Percentageofwoodlandarea
0
20
40
60
80
Satellite image analysis
0-60 61+
• Understanding the age structure of GWW woodlands could provide
clues as to whether recent levels of woodland fire are unprecedented
• To provide a crude assessment of the age structure of woodlands
across the GWW, we extrapolated the results from gimlet woodlands
and landsat fire mapping to the regional scale, by assuming that the
distribution in age classes older than 60 years is proportional to
random samples from E. salubris woodlands
Area mapped for
fire age
GWW boundary
Square-root (years since fire)
0 5 10 15 20 25
ShannonDiversity
1.0
1.5
2.0
2.5
3.0
3.5
4.0
y = 3.313 - 0.194x + 0.011x2
Adj. r2
= 0.304, F2,69 = 16.5, P < 0.0001
•globally rare ‘U’-shaped
relationship between diversity
and time since fire is likely to be
driven by dominant trees and
shrubs having maximum
competitive influence at
intermediate times since fire
Results (1):
Young Mature
Intermediate
•graph shows linear model for
stand age
Management implications
• As diversity was highest in mature woodlands,
there is no support for gimlet woodlands
requiring recurrent fire to maintain plant
diversity, at least within 400+ year timeframes
• Intense stand-replacing fires at intervals of <
200 yrs would have adverse implications for
biodiversity conservation. Species diversity
would not increase to the community
maximum
Multi-century changes in plant diversity
International Partners
TERN is supported by the Australian Government through
the National Collaborative Research Infrastructure Strategy
www.tern.org.au
More information?

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TERN: Data infrastructure that enables fire management

  • 1. TERN: Data infrastructure that enables fire management Nikki Thurgate, S. Guru and T. Clancy
  • 2. TERN: • Infrastructure and networks to support a coordinated, collaborative ecosystem science community • Enabling sustained, long-term collection, storage, synthesis and sharing of ecosystem data • Connecting science with policy and management TERN: Australia’s ecosystem observatory delivering data streams to enable environmental research and management
  • 3. Instruments + Sensors Policy + Management Analysis + Synthesis Modelling Data Searching Data Sharing Data Curation + Publishing Data Storage Processing + Analysis Collection Methods
  • 4. TERN FIRE DATA- TASMANIA 2016- COMBINATION OF METHODS ALLOWS IMPROVED BUSHFIRE PREDICTION MODELS Connecting science
  • 5. TERN Fire data- Repeated fuel reduction burns in temperate forests, like this one in southeast Australia, have little long-term impact on soil greenhouse gas exchange
  • 6. Fire Management Pre-processed MODIS fire burnt area satellite imagery Vegetation Map and Expert elicitation
  • 7. Thank you Carl Gosper, Suzanne Prober and Colin Yates t (08) 9333 6442 e carl.gosper@csiro.au CSIRO ECOSYSTEM SCIENCES AND DEPARTMENT OF ENVIRONMENT & CONSERVATION Further information: Parsons & Gosper (2011) International Journal of Wildland Fire 20, 184-194 Prober et al. (2012) Climatic Change 110, 227-248 Gosper et al. (in press) Australian Journal of Botany doi: 10.1071/BT12212
  • 8. Age-structure in GWW woodlands Age class (years since fire) Percentageofwoodlandarea 0 20 40 60 80 Satellite image analysis 0-60 61+ • Understanding the age structure of GWW woodlands could provide clues as to whether recent levels of woodland fire are unprecedented • To provide a crude assessment of the age structure of woodlands across the GWW, we extrapolated the results from gimlet woodlands and landsat fire mapping to the regional scale, by assuming that the distribution in age classes older than 60 years is proportional to random samples from E. salubris woodlands Area mapped for fire age GWW boundary
  • 9. Square-root (years since fire) 0 5 10 15 20 25 ShannonDiversity 1.0 1.5 2.0 2.5 3.0 3.5 4.0 y = 3.313 - 0.194x + 0.011x2 Adj. r2 = 0.304, F2,69 = 16.5, P < 0.0001 •globally rare ‘U’-shaped relationship between diversity and time since fire is likely to be driven by dominant trees and shrubs having maximum competitive influence at intermediate times since fire Results (1): Young Mature Intermediate •graph shows linear model for stand age
  • 10. Management implications • As diversity was highest in mature woodlands, there is no support for gimlet woodlands requiring recurrent fire to maintain plant diversity, at least within 400+ year timeframes • Intense stand-replacing fires at intervals of < 200 yrs would have adverse implications for biodiversity conservation. Species diversity would not increase to the community maximum Multi-century changes in plant diversity
  • 11. International Partners TERN is supported by the Australian Government through the National Collaborative Research Infrastructure Strategy

Hinweis der Redaktion

  1. Age-class predictions are based of the assumption that the distribution in age classes older than 38 years is proportional to our random samples of E. salubris woodlands whose time since fire was determined
  2. This contrasts some adjoining communities, such as mallee-heath, where recurrent fire does appear important for maintaining plant community vigour and diversity It has been speculated that fires initiate community change from Eucalyptus woodlands to mallee or Acacia shrublands, but we found no evidence for this