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Help save the grey-crowned babbler (eastern subspecies) (Pomatostomus temporalis temporalis) Conservation status in NSW: Vulnerable Commonwealth status: N/A Saving our Species management stream: Landscape species Species profile: http://www.environment.nsw.gov.au/threatenedspeciesapp/profile.aspx?id=10660 Saving our Species aims to conserve as many threatened species as possible. Experts have identified the distribution of the grey-crowned babbler (eastern subspecies) and the critical management actions required to conserve the species in the long-term. All conservation work being undertaken to conserve the grey-crowned babbler (eastern subspecies) around the state is vital to its recovery. If you are carrying out critical management actions within the species’ habitat, please contact us at www.environment.nsw.gov.au/savingourspecies/contactus.htm Map of grey-crowned babbler (eastern subspecies) distribution Legend Species distribution Threats to this species are outlined at http://www.environment.nsw.gov.au/threatenedspeciesapp/profile.aspx?id=10660#threats . The actions listed in the action toolbox are supplementary to NSW legislation, policy and programs and can be used by stakeholders, where applicable, to guide management at a site, regional or state scale. 1 Action toolbox Action description Scale Negotiate conservation agreements to protect patches of good condition core habitat across all tenures. Prioritise areas currently being used by grey-crowned babblers with relative high numbers of large mature rough barked eucalypt trees (box, stringybark, mahogany, peppermint, ironbark) greater than 0.6m diameter in the overstorey, scattered shrubs/small trees, native grassy understorey containing areas of leaf litter, stick debris in inter-tussock areas and large woody debris scattered throughout. Priority should be given to habitat around nesting sites as it is especially important for foraging during breeding periods and patches of greater than 5ha area within 300m of other habitat. Site, Area Target habitat restoration/revegetation projects to increase area of grey-crowned babbler habitat using a diverse mix of locally appropriate species. Restoration should ensure a native grassy understorey is present with inter-tussock space for leaf and stick litter to accumulate, large woody debris, some shrubs and appropriate local rough barked eucalypt species. Priority for expansion of habitat is to increase patch size up to 5ha. Restoration for improved connectivity in relative order of priority should focus on ensuring connectivity between groups within a local population separated by more than 2km, between local populations, improving connectivity between areas of core habitat, expanding areas of existing core habit, and restoration of vegetated corridors or stepping stones connecting large patches that are greater than 100m away from habitat and are not used because of isolation. Site, Area Identify and map all grey-crowned babbler groups over a defined area and ascertain the number of birds in each group to inform strategic management planning, on-ground actions and development of an extension program with local land managers. Site, Area Negotiate agreements with land managers to change management practices in areas where total grazing pressure and removal of coarse woody debris has degraded known habitat resulting in absence of natural regeneration and coarse woody debris. Habitat restoration can be achieved through a range of methods including managing over-abundant native herbivores, total stock grazing exclusion or reducing stock pressure through a range of strategic grazing systems and importation of coarse woody debris. Sites should not be grazed until tree regeneration is tall enough to withstand grazing (minimum of 3 to 10 years). However, periodic grazing can be important in managing the dense grass sward so that babblers can access the ground layer for food. Prioritise areas of fertile soil types as these provide the richer foraging habitat. Site, Area Deliver a community education program with a focus on threatened woodland birds in important areas of the grey-crowned babbler habitat including: promotion of the Office of Environment and Heritage Threatened Species website, development of landholder guidelines for habitat management, running of bird identification courses, threatened woodland bird field days and promotion of habitat enhancement for woodland birds at Landcare events, schools and agricultural shows. Site, Area Identify, map and prioritise for negotiation of conservation agreements areas of habitat that may function as drought or climate change refuge sites for source populations in a defined area. Examples of areas likely to provide refuge sites are large areas of habitat on high fertility soil types such as on floodplains and riparian areas. These areas provide the highest productivity foraging habitat in the landscape. Area Monitor noisy miner population trends, levels of harassment to babblers and impact on babblers in areas of conservation agreements. Implement management actions to decrease impacts from over-abundant noisy miners in areas where it is demonstrated that they are significantly impacting on the long term viability of babbler groups. This could include habitat manipulation techniques such as planting of compound-leaved shrubs in the understorey (e.g. acacias), smoothing or rounding of remnant edges when revegetating to enlarge patches, making vegetation corridors as wide as possible by adding to existing roadside corridors (ideally more than 600m) and fence remnants to establish all vegetation layers. Where impacts on a babbler group long-term viability is significant, removal of noisy miners may have to be considered as an option. Site Liaise with Roads and Maritime Services, as well as local councils to negotiate appropriate management of roadsides where they represent core habitat for the species (e.g. installing 'important habitat' signage, implementing procedures to minimise disturbance to roadside vegetation). Site, Area Conduct strategic hazard reduction burning in known habitat areas to provide a mosaic of different post fire ages so that a large proportion of the habitat area remains unburnt in any one year. Conduct low intensity burns (to retain large woody debris) and ensure that the period between hazard reduction burns is long enough to enable the recruitment of young trees and shrubs as these are important for shelter and nesting. Use crash grazing as a fuel reduction tool during years that a fire may cause high mortality in a recruitment event. Site Control invasive exotic perennial pasture grasses including, but not limited to phalaris ( Phalaris aquatica), Chilean needle grass (Nassella neesiana), serrated tussock (Nassella trichotoma), coolatai grass (Hyparrhenia hirta), kikuyu (Penisetum clandestinum)and invasive forms of African love grass (Eragrostis curvula) in known habitat. These species are very aggressive and form dense grass swards covering inter-tussock spaces preventing access to leaf and stick litter where babblers commonly forage for invertebrates. Site 2 Are you helping to save threatened species? Tell us about the work you’re doing, and find out more about our program - visit http://www.environment.nsw.gov.au/savingourspecies. Published on 31-Jul-2015 3