Improving estimates of savanna burning emissions for greenhouse accounting in northern Australia: limitations, challenges, applications

2009 ◽  
Vol 18 (1) ◽  
pp. 1 ◽  
Author(s):  
Jeremy Russell-Smith ◽  
Brett P. Murphy ◽  
C. P. (Mick) Meyer ◽  
Garry D. Cook ◽  
Stefan Maier ◽  
...  

Although biomass burning of savannas is recognised as a major global source of greenhouse gas emissions, quantification remains problematic with resulting regional emissions estimates often differing markedly. Here we undertake a critical assessment of Australia’s National Greenhouse Gas Inventory (NGGI) savanna burning emissions methodology. We describe the methodology developed for, and results and associated uncertainties derived from, a landscape-scale emissions abatement project in fire-prone western Arnhem Land, northern Australia. The methodology incorporates (i) detailed fire history and vegetation structure and fuels type mapping derived from satellite imagery; (ii) field-based assessments of fuel load accumulation, burning efficiencies (patchiness, combustion efficiency, ash retention) and N : C composition; and (iii) application of standard, regionally derived emission factors. Importantly, this refined methodology differs from the NGGI by incorporation of fire seasonality and severity components, and substantial improvements in baseline data. We consider how the application of a fire management program aimed at shifting the seasonality of burning (from one currently dominated by extensive late dry season wildfires to one where strategic fire management is undertaken earlier in the year) can provide significant project-based emissions abatement. The approach has wider application to fire-prone savanna systems dominated by anthropogenic sources of ignition.

2009 ◽  
Vol 18 (2) ◽  
pp. 127 ◽  
Author(s):  
Andrew C. Edwards ◽  
Jeremy Russell-Smith

The paper examines the application of the ecological thresholds concept to fire management issues concerning fire-sensitive vegetation types associated with the remote, biodiversity-rich, sandstone Arnhem Plateau, in western Arnhem Land, monsoonal northern Australia. In the absence of detailed assessments of fire regime impacts on component biota such as exist for adjoining Nitmiluk and World Heritage Kakadu National Parks, the paper builds on validated 16-year fire history and vegetation structural mapping products derived principally from Landsat-scale imagery, to apply critical ecological thresholds criteria as defined by fire regime parameters for assessing the status of fire-sensitive habitat and species elements. Assembled data indicate that the 24 000 km2 study region today experiences fire regimes characterised generally by high annual frequencies (mean = 36.6%) of large (>10 km2) fires that occur mostly in the late dry season under severe fire-weather conditions. Collectively, such conditions substantially exceed defined ecological thresholds for significant proportions of fire-sensitive indicator rain forest and heath vegetation types, and the long-lived obligate seeder conifer tree species, Callitris intratropica. Thresholds criteria are recognised as an effective tool for informing ecological fire management in a variety of geographic settings.


2010 ◽  
Vol 19 (1) ◽  
pp. iii ◽  
Author(s):  
Miguel G. Cruz ◽  
Martin E. Alexander ◽  
Ronald H. Wakimoto

Application of crown fire behavior models in fire management decision-making have been limited by the difficulty of quantitatively describing fuel complexes, specifically characteristics of the canopy fuel stratum. To estimate canopy fuel stratum characteristics of four broad fuel types found in the western United States and adjacent areas of Canada, namely Douglas-fir, ponderosa pine, mixed conifer, and lodgepole pine forest stands, data from the USDA Forest Service's Forest Inventory and Analysis (FIA) database were analysed and linked with tree-level foliage dry weight equations. Models to predict canopy base height (CBH), canopy fuel load (CFL) and canopy bulk density (CBD) were developed through linear regression analysis and using common stand descriptors (e.g. stand density, basal area, stand height) as explanatory variables. The models developed were fuel type specific and coefficients of determination ranged from 0.90 to 0.95 for CFL, between 0.84 and 0.92 for CBD and from 0.64 to 0.88 for CBH. Although not formally evaluated, the models seem to give a reasonable characterization of the canopy fuel stratum for use in fire management applications.


2003 ◽  
Vol 12 (1) ◽  
pp. 39 ◽  
Author(s):  
Miguel G. Cruz ◽  
Martin E. Alexander ◽  
Ronald H. Wakimoto

Application of crown fire behavior models in fire management decision-making have been limited by the difficulty of quantitatively describing fuel complexes, specifically characteristics of the canopy fuel stratum. To estimate canopy fuel stratum characteristics of four broad fuel types found in the western United States and adjacent areas of Canada, namely Douglas-fir, ponderosa pine, mixed conifer, and lodgepole pine forest stands, data from the USDA Forest Service's Forest Inventory and Analysis (FIA) database were analysed and linked with tree-level foliage dry weight equations. Models to predict canopy base height (CBH), canopy fuel load (CFL) and canopy bulk density (CBD) were developed through linear regression analysis and using common stand descriptors (e.g. stand density, basal area, stand height) as explanatory variables. The models developed were fuel type specific and coefficients of determination ranged from 0.90 to 0.95 for CFL, between 0.84 and 0.92 for CBD and from 0.64 to 0.88 for CBH. Although not formally evaluated, the models seem to give a reasonable characterization of the canopy fuel stratum for use in fire management applications.


2020 ◽  
Vol 29 (11) ◽  
pp. 974
Author(s):  
William Nikolakis ◽  
Emma Roberts ◽  
Ngaio Hotte ◽  
Russell Myers Ross

After generations of fire-suppression policy, Indigenous fire management (IFM) is being reactivated as one way to mitigate wildfire in fire-prone ecosystems. Research has documented that IFM also mitigates carbon emissions, improves livelihoods and enhances well-being among participants. This study documents the goals of the Yunesit’in and Xeni Gwet’in First Nations as they develop a fire management program in central British Columbia, Canada. Drawing on goal setting theory and interviews, a qualitative coding and cluster analysis identified three general goals from fire management: (1) strengthen cultural connection and well-being, (2) restore the health of the land and (3) respect traditional laws. Sub-goals included enhancing community member health and well-being, improving fire management practices to maintain ‘pyrodiversity’ and food security and re-empowering Indigenous laws and practices. This community-developed framework will guide program evaluation and brings insight to a theory of IFM.


2015 ◽  
Vol 24 (4) ◽  
pp. 534 ◽  
Author(s):  
Tim S. Doherty ◽  
Robert A. Davis ◽  
Eddie J. B. van Etten ◽  
Neil Collier ◽  
Josef Krawiec

Fire plays a strong role in structuring fauna communities and the habitat available to them in fire-prone regions. Human-mediated increases in fire frequency and intensity threaten many animal species and understanding how these species respond to fire history and its associated effect on vegetation is essential to effective biodiversity management. We used a shrubland mammal and reptile community in semiarid south-western Australia as a model to investigate interactions between fire history, habitat structure and fauna habitat use. Of the 15 species analysed, five were most abundant in recently burnt habitat (8–13 years since last fire), four were most abundant in long unburnt areas (25–50 years) and six showed no response to fire history. Fauna responses to fire history were divergent both within and across taxonomic groups. Fire management that homogenises large areas of habitat through either fire exclusion or frequent burning may threaten species due to these diverse requirements, so careful management of fire may be needed to maximise habitat suitability across the landscape. When establishing fire management plans, we recommend that land managers exercise caution in adopting species-specific information from different locations and broad vegetation types. Information on animal responses to fire is best gained through experimental and adaptive management approaches at the local level.


2006 ◽  
Vol 234 ◽  
pp. S152
Author(s):  
J. Russell-Smith ◽  
A.C. Edwards ◽  
G.D. Cook ◽  
J. Schatz ◽  
P. Brocklehurst

2021 ◽  
Author(s):  
Isabel Belloni Schmidt

<p>Fire-prone ecosystems evolved and have been managed by humans with fire for<br>millennia. Ignoring these socioecological realities, zero-fire policies have been<br>implemented in fire-prone ecosystems across the world. These inappropriate policies are<br>mainly originated from a forest-centered perception that fire is an essentially negative<br>and anthropogenic disturbance. The attempts to exclude fires have generated deleterious<br>ecological impacts, high fire-fighting costs, damage to properties and human lives in<br>grasslands, savannas and Mediterranean-type ecosystems. These zero-fire policies also<br>generate conflicts between governments and local communities who use fire to manage<br>the landscape, food production and livestock raising. Excluding fires from fire-prone<br>ecosystems may lead to changes ecosystem functioning and biodiversity due to woody<br>encroachment and/or fuel load accumulation. In regions where soil conditions allow<br>grasslands can be invaded by trees, changing vegetation structure and their ability to<br>provide ecosystem services, especially water production. In most fire-prone ecosystems,<br>fuel load accumulates, and the long-time unburned areas become time bombs waiting<br>for the next ignition source to cause disastrous wildfires. Fire bans disrupt traditional<br>fire management practices and commonly lead to more irresponsible uses of fire, since<br>local communities continue to depend on fire for their productive areas but use fire in<br>furtive ways to avoid criminalization. In combination with large areas with high and<br>homogeneous fuel loads, this leads to large, hard to control and highly impacting<br>wildfires, especially during late-dry season, when fires tend cause more severe impacts.<br>After decades under these scenarios, zero-fire policies have been substituted by active<br>fire management policies in fire-prone ecosystems in many countries in Africa, Latin<br>America, in the US and Australia, among other countries. Fire management policies<br>should be adapted for each regional socioecological context and allow for the active use<br>of fires for landscape management, biodiversity conservation and/or productive<br>activities. The Brazilian savanna (Cerrado) is the most biodiverse and threaten savanna<br>in the world and has been managed under zero-fire policy for decades. It is a tropical<br>humid savanna (1,500mm mean annual precipitation) where large (>10,000 hectares),<br>frequent (2-4 years fire interval) late-dry season wildfires are common, including in<br>Protect Areas (PA) dedicated to biodiversity conservation and traditional communities’<br>livelihoods. In 2014, a pilot Integrated Fire Management (IFM) program has been<br>implemented in three Cerrado PAs. The program considers local uses of fire,<br>implements prescribed burns and landscape management planning aiming to (i) change<br>the main season of burnings (from late- to early- and mid-dry season); (ii) protect fire-<br>sensitive vegetation, such as riparian forests, from fires; (iii) decrease firefighting costs;<br>(iv) reduce conflicts with local communities and (v) lower greenhouse gases emissions.<br>The IFM program has since been implemented in more than 30 federal PA, including<br>Indigenous Territories., where this approach has successfully achieved its main<br>objectives. The present challenge is to expand IFM actions to the state and especially<br>private -owned lands, which will allow for a significant change in wildfire patterns<br>across the whole 2 million km 2 of the Brazilian savanna.</p>


2010 ◽  
Vol 19 (1) ◽  
pp. 46 ◽  
Author(s):  
Brett P. Murphy ◽  
Jeremy Russell-Smith

Using a detailed fire history collected over a 10-year period throughout a savanna landscape in northern Australia, we have addressed the question of whether fire severity, inferred from a semiquantitative fire severity index, increases with time since previous fire. There was a clear trend of fires becoming much more severe with increasing time since previous fire. Between 1 and 5 years following a fire, the probability of a subsequent fire being classified as ‘severe’ increased from 3 to 8% for early dry-season fires, and from 21 to 43% for late dry-season fires. It was clear that the strong increase in fire severity was not confined to the first 2–3 years following the previous fire, as previously suspected. These findings highlight the difficulty of reducing both fire frequency and severity in northern Australian savanna landscapes, as they imply that a negative feedback process exists between the two; that is, reducing fire frequency is likely to increase the severity of fires that do occur.


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