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    This data package comprises fire severity scores from Kakadu in 2014. A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 132 plots are located in Kakadu. These sample a variety of landform and vegetation type/habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

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    This data package comprises fire severity scores from Kakadu in 2012–2013. A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 132 plots are located in Kakadu. These sample a variety of landform and vegetation type/habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

  • Categories  

    This data package comprises fire severity scores from Kakadu, Litchfield and Nitmiluk from 1994 onwards. A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk National Parks) in 1994-1995 to monitor biotic change. Of these, 133 plots are located in Kakadu, 41 plots are located in Litchfield and 46 plots are located in Nitmuluk. These sample a variety of landform and vegetation type/habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation (for example, stands of Callitris and sandstone heaths). In addition, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network's full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

  • Categories  

    A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 41 plots are located in Litchfield. These sample a variety of landform and vegetation type /habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

  • Categories  

    A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 46 plots are located in Nitmuluk. These sample a variety of landform and vegetation type/habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

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    This data package is a derivative product consisting of a subset of already published data fire severity data packages (from Dr Jeremy Russell-Smith), combined with data indicating time since last fire (from Brett Murphy). These data are used to produce the graphs and conclusions found on pages 355 & 356 of Lindenmayer et. al 2014, Biodiversity and Environmental Change: Monitoring Challenges and Directions. A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 132 plots are located in Kakadu, 41 plots are located in Litchfield, and 47 are located in Nitmiluk. These sample a variety of landform and vegetation type /habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna

  • Categories  

    A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 41 plots are located in Litchfield. These sample a variety of landform and vegetation type /habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

  • Categories  

    A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 41 plots are located in Litchfield. These sample a variety of landform and vegetation type /habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

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    This data package is a derivative comprising of a subset of data from four existing data packages: • Weather Data (daily and monthly), Simpson Desert, Western Queensland, 1995–2011 (http://www.ltern.org.au/knb/metacat/ltern.48/html) • Vegetation Plot-data, Simpson Desert, Western Queensland, 1990–2011 (http://www.ltern.org.au/knb/metacat/ltern.44/html) • Mammal Abundance Plot-data, Simpson Desert, Western Queensland, 1990–2011 (http://www.ltern.org.au/knb/metacat/ltern.37/html) • Reptile Abundance Plot-data, Simpson Desert, Western Queensland, 1990–2011 (http://www.ltern.org.au/knb/metacat/ltern.42/html) These data are used to produce the graphs found in figure 10.25 on pages 411–412 in Lindenmayer et. al 2014, Biodiversity and Environmental Change: Monitoring Challenges and Direction. They have been combined to illustrate the vegetation and vertebrate response to weather patterns, and the interaction between predator and prey during these cycles. The data includes: • monthly rainfall data for automatic weather stations situated at 13 sites separated by distances of between 5 and 80 km. • percentage ground cover of spinifex (Triodia basedowii) • mammal abundance data for two species of rodent (Spinifex Hopping-mouse & Sandy Inland Mouse) who feed on spinifex seed • mammal abundance data for the Lesser Hairy-footed Dunnart (an insectivore) • mammal abundance data for the Brush-tailed Mulgara, a predator who feeds on the Spinifex Hopping-mouse & Sandy Inland Mouse • reptile abundance data for the Military Dragon • reptile abundance data for the Central Netted Dragon Vegetation attributes were recorded in an area occupying 2.5 m radius around six traps on each trapping grid and have been aggregated to grid level data. Weather data is collected from automatic weather stations situated at 13 sites separated by distances of between 5 and 80 km. Capture data for a specified duration of trapping nights (usually 3 night session) in the Simpson Desert, Western Queensland. Captured mammal and reptile fauna were identified and recaptures during the same session were removed (i.e. individuals were only counted once). Date, site and grid number were recorded for all captures, and captured animals were also marked by a unique ear notch prior to their release to identify recaptures. The network program uses a core of 12 sites which are sampled every April-May. The trapping survey aims to quantitatively track long-term shifts in biodiversity and ecological processes in relation to key drivers, including unpredictable rainfall and droughts, fire, feral predators and grazing. A synopsis of related data packages which have been collected as part of the Desert Ecology's full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/desert-ecology.

  • Categories  

    A total of 220 permanent monitoring plots (40 m x 20 m) were established across three parks (Kakadu, Litchfield and Nitmiluk) in 1994-1995 to monitor biotic change. Of these, 41 plots are located in Litchfield. These sample a variety of landform and vegetation type /habitat conditions. A substantial proportion of plots were positioned deliberately at sites likely to reveal environmental dynamics, especially at ecotones and in patches of fire-sensitive vegetation. For example stands of Callitris, sandstone heaths. As well, many plots are located at, or in the near vicinity of, intensively managed sites such as camp-grounds and other tourist destinations. A synopsis of related data packages which have been collected as part of the Three Park Savanna Fire-effects Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.