<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about Goorooyarroo Nature Reserve Site 2, ACT, Australia </br><br> Pre-European benchmark-analogue vegetation: The site was originally woodlands on the deeper soils of the lower slopes and flats (<em>Eucalyptus blakelyi</em> and <em>Eucalyptus melliodora</em>) (McIntrye et al 2010). </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1819: Area managed by indigenous Ngunnawal people</li> <li>1826: Sheep grazing with shepherds commenced</li> <li>1860: Fences constructed - continuous stocking with sheep commenced</li> <li>1905: Area used for sheep grazing - continuous /set stocking</li> <li>1920: Fallen timber collected for firewood started</li> <li>1961: Mature trees on the site were ring barked to promote pasture grasses</li> <li>1973: Dead and fallen trees felled for fire wood</li> <li>1979: Bushfire burns through the area</li> <li>1994: Mulligans Flat Nature Reserve established</li> <li>1995: Continuous stocking with sheep grazing ceased</li> <li>1995: Collection of firewood ceased</li> <li>1995: Pasture improvement ceased</li> <li>1996: Kangaroo population begins to rapidly increase</li> <li>2006: Roo proof fence completed</li> <li>2006: Commenced annual removal of pest species of plants and animals</li> <li>2010: Commenced annual Kangaroo cull.</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about the Taroom Shire Potters Flat. </br><br> Pre-European benchmark-analogue vegetation: The site was originally brigalow <em>Acacia harpophylla</em>, mixed community associated with overstorey several species, including <em>Eucalyptus coolabah</em>, <em>E. cambageana</em>, <em>Casuarina cristata</em>, and a range of understorey species, grassy woodlands and open forests. </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1860: Area used for sheep grazing by shepherds</li> <li>1870: Permanent fences established</li> <li>1875: Start of continuous or set stocking with sheep</li> <li>1880: Incursion of prickly pear started</li> <li>1904-1929: Continuous grazing with sheep</li> <li>1929-1932: Gradual increase in cattle numbers, decline in sheep</li> <li>1930-1935: Land clearance via ringbarking</li> <li>1932-1970: Almost continuous grazing with cattle - relatively low stock numbers</li> <li>1935: Prickly pear had been destroyed</li> <li>1940-1955: Re-clearing brigalow regrowth with axes and fallen timber burnt</li> <li>1956-1960: Brigalow regrowth left unchecked</li> <li>1960-1962: Brigalow regrowth pulled mechanically and burnt</li> <li>1962-1970: Regrowth commenced restabilising without treatment or control</li> <li>1970: Area/s designated as blocks to be left as shelter belts for cattle</li> <li>1970: Commenced managing areas surrounding the site regrowth (i.e. shelter belt) mechanically</li> <li>1971-2010: Areas surrounding the site regularly and intensively managed with ploughing, fertilising the pasture and cropping</li> <li>1971-2010: Site almost continually used as shelter belt for cattle - high use.</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about Organ Pipes National Park, Volcanic Plains Bioregion, Victoria. </br><br> Pre-European reference-analogue vegetation: Treeless basalt plain predominantly grassland dominated by Kangaroo Grass <em>Themeda triandra</em> with an array of inter-tussock species. </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1830: Indigenous people manage the area</li> <li>1835: Sheep grazing commenced (shepherds)</li> <li>1851: Alienated from the Crown as freehold and fenced</li> <li>1851-1965: Area managed for dairying, an orchard and cropping and grazing modified pastures</li> <li>1965: Agricultural production abandoned</li> <li>1965-1986: Area minimally managed</li> <li>1972: Organ Pipes National Park declared</li> <li>1986-1992: Commenced species re-introduced site with supplemental plantings. Area managed to control weed and further incursions</li> <li>1989-2003: Repeated monitoring. Area lightly grazed by rabbits and macropods</li> <li>1993: Site burnt [prescribed fire]; supplemental re-vegetation with indigenous local species </li> <li>1995: Site was burnt [prescribed fire]</li> <li>1997: Site was burnt [prescribed fire] followed by drought</li> <li>2003: Ceased monitoring and enhancement to the site</li> <li>2004-10: Minimal intervention.</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details for the Wooroonooran Nature Refuge. </br><br> Pre-European benchmark-analogue vegetation: the original vegetation for the site was a complex mesophyll vine forest on basaltic red loams on wet uplands, altitude 720&nbsp;m with 4.421&nbsp;mm rainfall (av annual records for the period 1993-2011, source: Peter Stanton). </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1800: Indigenous management of mesophyll rainforest by Ngadyan people</li> <li>1924: Start of selective logging of high value timber species</li> <li>1930: Finish of selective logging of high value timber species - intent to convert rainforest to pasture</li> <li>1931: Start of land clearing of the previously logged forest - intent to convert rainforest to pasture</li> <li>1938: End of land clearing of the previously logged forest - forest trash burnt</li> <li>1939: Start of intensive soil and pasture management - soil not ploughed - aggressive pasture grasses sown into ash bed</li> <li>1940: Start of grazing - pasture for dairying</li> <li>1958: End of grazing, planted pasture for dairying. Pastures infertile. All livestock removed</li> <li>1959: Start of land abandonment and minimal use</li> <li>1983: Commenced large scale spraying and poisoning and physical removal of lantana</li> <li>1993: Regrowth rainforest (complex mesophyll vine forest) in gullies and on lower slopes - 50% of lot 2</li> <li>1994: Continued large scale spraying and poisoning of lantana and carpet grass</li> <li>2003: Site formally gazetted as Wooroonooran Nature Refuge by WTMA</li> <li>2011: Site continues to be manage for multiple values: timber reserve, biodiversity and habitat values.</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about Belconnen Naval Transmitter Station in ACT, Australia. </br><br> Pre-European benchmark-analogue vegetation: the original vegetation for the site Belconnen Naval Transmitter Station was a temperate grassland in an ecological community dominated by native species of perennial tussock grasses. </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>Up to late 1820s the area was managed by indigenous Ngunnawal people</li> <li>1830s: Area first grazed by sheep and cattle with the aid of shepherds</li> <li>1860: Fences were established and continuous stocking commenced</li> <li>1900: Patches of woodland areas on higher ground were partly cleared</li> <li>1900-39: High likelihood of moderate to heavy grazing pressure due to sheep and cattle</li> <li>1940-1993: Area managed as a naval transmission station</li> <li>1940-92: Area managed for sheep grazing under continuous grazing</li> <li>1970: Secure people and kangaroo proof fence established</li> <li>1993: Sheep removed from the site</li> <li>1995: mowers used to manage the grass</li> <li>1997-2008: Kangaroo population increased to unacceptable levels</li> <li>2006: Naval transmission towers demolished, area continued to have a secure people proof fence</li> <li>2008: Kangaroo population culled to reduce grazing pressure</li> <li>2011: Site managed for nature conservation values.</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details for the Big Scrub Rocky Creek Dam, NSW. </br><br> Pre-European benchmark - analogue vegetation: The site was originally Lowland Subtropical Rainforest on basalt-derived and alluvial soils. The forest is distinguished by its dense, uneven canopy comprised of typically two to three tall tree layers. Eucalypts and brushbox (<em>Lophostemon confertus</em>) may be present as sparse emergent. Characteristic life-forms include buttressed trees, strangler figs, stands of bangalow palms (<em>Archontophoenix cunninghamiana</em>), woody vines and large epiphytes. </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1840: Intact rainforest</li> <li>1862: Area opened-up for selection</li> <li>1900: Cedar getters select large trees</li> <li>1910: Rainforest cleared and converted to pasture for dairying</li> <li>1911-1948: Area used for grazing dairy cattle</li> <li>1948: Area acquired for public use (water storage)</li> <li>1950-1989: Minimal management - land in transition (open public space)</li> <li>1950-1952: Rocky Creek Dam constructed</li> <li>1983-1990: Commenced experiments using assisted regeneration on small test plots</li> <li>1991-2000: Large scale assisted regeneration (25&nbsp;ha) by converting lantana thickets to rainforest</li> <li>2001-2011: Minimal management.</li></ul></br>

The dataset comprises of a biological and a spatial component. Biological data: This was collated from several sources, collected over the period 2000-2009. Data are lists of presence-absence of 215 native plant species (i.e., exotic species removed) from 76 seasonal wetlands (size range 0.5 - 35 ha) located on the Fleurieu Peninsula, South Australia (centred on latitude 35.5 °S). After data were collated into a single dataset, sampling bias was removed to create a dataset of near-complete census wetlands. Spatial data: For each of the 76 wetlands a small amount of spatial data is also provided, i.e., area, centroids, catchment etc. The dataset could be of interest for any typical community data analysis (e.g. beta diversity, similarity, assembly)- provided only native wetland plant species are of interest. Data presented here were used to model extinction risk, species-area relationships, occupancy distributions and so on.

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about Goorooyarroo Nature Reserve Site 3. </br><br> Pre-European benchmark-analogue vegetation: The site was originally woodlands on the deeper soils of the lower slopes and flats (<em>Eucalyptus blakelyi</em> and <em>Eucalyptus melliodora</em>) (McIntyre et al., 2010). </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1819: Area managed by indigenous Ngunnawal people</li> <li>1826: Sheep grazing with shepherds commenced</li> <li>1860: Fences constructed - continuous stocking with sheep commenced in large paddocks</li> <li>1920-1925: Large old and dead trees felled for firewood for Canberra market</li> <li>1961: 50 acre paddock fenced as a future lambing paddock</li> <li>1962-1965: Remaining trees ringbarked, left to stand to dry out and sold as firewood</li> <li>1966-1978: Paddock converted to improved pasture. Repeated resown and fertilized</li> <li>1979-2004: Holding paddock for lambing ewes</li> <li>1994: Mulligans Flat Nature Reserve established</li> <li>2004: Continuous stocking with sheep grazing ceased</li> <li>2005: Kangaroo proof fence erected</li> <li>2008: Kangaroo population begins to rapidly increase</li> <li>2008: Commenced annual removal of pest species of plants and animals</li> <li>2009: Introduced large logs to the site from off the Reserve</li> <li>2010: Commenced annual kangaroo cull.</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about the Cumberland State Forest, Old Abandoned Arboretum site, NSW, Australia. </br><br> Pre-European reference-analogue vegetation: The Cumberland State Forest is part of the Blue Gum High Forest (Daniel Connolly pers comm). It is a tall wet sclerophyll forest found on Wianamatta group Ashfield Shale. Blue Gum High Forest is dominated by Sydney blue gum (<em>Eucalyptus saligna</em>), blackbutt (<em>E. pilularis</em>), and turpentine (<em>Syncarpia glomulifera</em>) with a number of other eucalypts occurring patchily. A sparse open cover of small trees includes a variety of sclerophyllous and mesophyllous species. The ground layer is variable in composition and cover; including ferny, grassy or herbaceous and/or vines and climbers. The characteristics of the ground cover are related to the topgraphic position. </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1788- Area managed by indigenous Darug people</li> <li>1788-1824: Region explored, un-modified native forest blue gum/ironbark on shale</li> <li>1825: Parcel selected by Mr Shepherd</li> <li>1860: Tree cover likely to have been thinned - selective logging for fences and housing</li> <li>1826-1907: Grazing stock on native pastures</li> <li>1908: Land parcel cleared and sown to improved pasture, and evidence of chicken farm and fruit orchards</li> <li>1909-1937: Managed as improved pasture and grazing</li> <li>1937-38: Purchased by NSW Forestry Commission</li> <li>1941-42: Remaining native forest trees cleared to establish an arboretum</li> <li>1943-45: Arboretum planted as a future urban working forest</li> <li>1946-73: Arboretum managed for education and demonstration - infilling regrowth native forest observed</li> <li>1974-84: Arboretum increasing managed for recreation - infilling regrowth native forest observed</li> <li>1985-2012: Area managed for recreation (ex-arboretum and regrowth native forest).</li></ul></br>

<br>The aim of this project is to compile land use and management practices and their observed and measured impacts and effects on vegetation condition. The results provide land managers and researchers with a tool for reporting and monitoring spatial and temporal transformations of Australia’s native vegetated landscapes due to changes in land use and management practices. Following are the details about Talaheni Horse Paddock, Murrambatman, NSW. </br><br> Pre-European benchmark-analogue vegetation: The site was originally a <em>Themeda sp.</em> grassy woodland. </br><br> Brief chronology of changes in land use and management:<ul style="list-style-type: disc;"> <li>1830: Grazing of native vegetation - shepherds</li> <li>1900-1961: Fencing and continuous grazing with sheep</li> <li>1905: Overstorey thinned by ringbarking</li> <li>1906-1920: Continuous removal of suckers and regrowth</li> <li>1962: Remaining larger trees pushed over with a bull dozer</li> <li>1962-1974: Continuous grazing with cattle</li> <li>1968-1978: Four applications of superphosphate and exotic pasture species</li> <li>1975-1982: Continuous grazing with horses</li> <li>1983-1984: Continuous grazing with sheep</li> <li>1985: Continuous grazing ceased</li> <li>1986: Commenced rehabilitation</li> <li>1987-2008: Area lightly grazed using rotational grazing with sheep</li> <li>2008-2010: All stock removed - increasing high numbers of kangaroos.</li></ul></br>