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.

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.

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.

This Terrestrial Vertebrate Monitoring data package comprises data for a sub-sample of the 41 plots situated in Litchfield National Park. Terrestrial mammals, birds, reptiles and amphibians are sampled in a 50 x 50 m plot adjacent to each fire plot monitoring site (below). Each vertebrate plot is sampled every five years. Within each five yearly-interval plots are sampled in different months over a three-year period. Each individual plot is always sampled in the same month. The plots are assessed for fire occurrence at least annually by means of on-ground visits by ranger staff. This record is used, in conjunction with aerial surveys, to assess the reliability of the fire history which has been developed from satellite imagery. A photo record assembled for field visits to Kakadu National Park (and Nitmiluk National Park) visits spanning 1995-2004 has also been used to develop a practical field-based index of fire severity. The Three Parks Savanna Plot Network’s full program uses a total of 220 permanent monitoring plots established in the Kakadu, Litchfield and Nitmiluk National Parks which commenced in 1994-1995. The research is aimed at improving our understanding of impacts associated with imposed fire on vegetation structure, plant species and vertebrate fauna, in order to improve our knowledge and management of fire in tropical savanna landscapes. A synopsis of related data packages which have been collected as part of the Three Park Savanna's full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/three-parks-savanna.

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

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.

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

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.

The Three Parks Savanna Fire-Effects Network was established in 1994 with the primary aim of training management staff and assisting with the development of adaptive approaches to conservation-based fire management in regional savanna systems. This dataset comprises the vegetation sampling data from the 220 plots located across the Three Parks Savanna Fire-effects Plot Network, of which 133 are in Kakadu National Park, 41 in Litchfield National Park and 46 in Nitmiluk National Park. The vegetation data consists of the quantitative assessment of all species in three major strata within 800 square meter plots. Plots are positioned to investigate environmental changes in areas of interest by land managers and may reveal environmental dynamics. Plots are located in a variety of landform and vegetation type / habitats and conditions, and may be in vicinity of intensively managed sites such as camp grounds and other tourist attractions. Areas also include ecotones and patches of fire-sensitive vegetation such as stands of Callitris and sandstone heaths. The full program assesses fire regimes and their impacts on plant and vertebrate biodiversity components. The program consists of two complementary elements – mapping of fire histories based upon interpretation of satellite imagery, and assessment of vegetation and faunal components at a large series of permanent monitoring plots located across respective parks. *Note: Plots are located within a National Park and physical access to the plots is restricted.

This dataset contains bird occurrence data collected at the Litchfield Savanna site in 2015.