This dataset indicates lots across the state of Victoria that are eligible for Future Homes. Eligible lots, in accordance with Clause 53.24 of the Victorian Planning Scheme are within General Residential Zoned land, are not affected by a Heritage Overlay or a Neighbourhood Character Overlay, and are within an 800m buffer of a designated activity centre or passenger carrying train station. This dataset is provided by the Department of Transport (DTP) for informational purposes only and is solely intended to provide general information on the potential eligibility for 'Future Homes' lots. No information provided in this dataset constitutes legal or other professional advice. The information is provided on the basis that any person viewing the data will assume responsibility for assessing the relevance and accuracy of its contents and reliance on the information will be at one's own risk. DTP excludes, to the maximum extent permitted by law, any liability for loss of any kind arising directly or indirectly from any inaccuracy, incompleteness or other defect in any information provided by DTP, or any negligence or lack of care in relation to the preparation or provision of the information. For any queries regarding the data please contact the team at FutureHomes@delwp.vic.gov.au.

The Statewide Forest Resource Inventory (SFRI) is a program of information collection and analysis of Victoria's native forests that supports statewide planning and management. One SFRI product is SFRImap Database - a database of information on the eucalypt composition, structure and history of Victoria's forests. SFRImap Database covers most of Victoria's forests on public land at a scale of 1:25,000. Relative Age is a layer derived from SFRImap. It is SFRImap dissolved on the RELAGE attribute. Derived layers from SFRImap Database are complimented with the same metadata as the SFRImap layer.

The Victorian Alpine Fires 2003 were ignited on 8th January 2003 by a series of lightning strikes across north-eastern Victoria. This layer depicts the boundary of Landsat TM7 based fire severity mapping for this fire (FIRE_SEV03). This layer does not necessarily co-incide completely with the actual fire boundary which is held as fire number 39 in the fire100_2003 fire history dataset.

Last updated: November 2019 This dataset represents the spatial extent of prescribed burns planned for ignition and associated mechanical and vegetation works on Public Land in Victoria and some CFA burns. This data is prepared annually for prescribed burns planned for the immediate three-year period. This dataset is now the joint fuel management plan and now includes the CFA burns as well as VicForest coupe burns.

Model-based predictions of the distribution of deer on Victorian public land. Model predictions are based on camera-trap and deer sign surveys at 317 sites across Victoria conducted between 2021 and 2023. The raster data is divided into four layers/bands for the four species analysed in this study: Sambar deer (Cervus unicolor), Fallow deer (Dama dama), Red deer (Cervus elaphus) and Hog deer (Axis porcinus). Distribution estimates are presented as a categorical value of model confidence in deer occupancy per square kilometre of public land within each grid cell. The values represent (i) the Smallest estimated range (5th percentile), (ii) the Average/median estimated range (50th percentile), and (iii) the Largest estimated range (95th percentile). The technical report accompanying this data is available from the Arthur Rylah Institute (ARI) website: https://www.ari.vic.gov.au/__data/assets/pdf_file/0035/686591/ARI-Technical-Report-368-Deer-abundance-in-Victoria.pdf The raster data may be loaded into programs such as R or QGIS for analysis. When opening the data in QGIS, undertake the following steps: 1) Follow 'Layer > Add Later > Add Raster Layer' to select the tif file to be added 2) Right-click on the added layer in the 'Layers' panel and select 'Properties' 3) Visualise the distribution of one of the four species of deer by selecting 'Symbology > Band Rendering > Render Type = Paletted/Unique Values' 4) Choose the band (species) you wish to display 5) Click the 'Classify' button 6) The layer values can be renamed according to the associated XML datafile. The values are: 0 = Not present, 1 = Largest estimated range (95th percentile), 2 = the Average/median estimated range (50th percentile), and 3 = Smallest estimated range (5th percentile)

This map is derived from a screen based interpretation and mapping of aerial imagery into fire severity classes using Vexcel imagery. The classes represent levels of fire burn and scorch activity in the eucalypt and non-eucalypt forest, understorey and treeless areas. The classification was validated using field check sites. An accuracy assessment has not been carried out. Fire severity for Boulder Creek, Dergholm and central area of Little Desert (Brooks) mapped using this methodology.

This boundary has been created at 1:25,000 showing the Metropolitan Melbourne Investigation, for the Victorian Environmental Assessment Council. The Minister, under Section 15 of the Victorian Environmental Assessment Council Act 2001 required VEAC to carry out an investigation of the public land in Metropolitan Melbourne. The area investigated is the LGA's predominantly not covered by the Melbourne 1 and Melbourne 2 Studies.

Test version of Cosmetic Point for MapShare Editing testing. This is our Test data, and good for testing the load. Not many fields and just 2 domains Type and Status

This is a derived dataset that delineates the current Bioregional Conservation Status of EVCs within the modeled 1750 EVC dataset. The dataset is derived from a combination of both Victorian bioregions (VBIOREG100) and the modeled 1750 EVC dataset (NV1750_EVC), with an assigned conservation status on the basis of unique Bioregion EVC units. The dataset underpins the implementation of Victoria's Native Vegetation Management Framework, and the preparation of Regional Vegetation Plans in addition to other biodiversity planning. The dataset requires upgrading when either of the two input datasets change. Note erratum under Data Quality-Completeness-Classification

The Port Phillip Bay Coastal Hazard Assessment (the product) is a digital dataset consisting of multiple spatial layer outputs from modelled erosion, inundation and groundwater hazard scenarios. The product is recommended for use at the regional scale around Port Phillip Bay. Application of the data should be guided by the accompanying Port Phillip Bay hazard assessment technical reports (CSIRO 2022, Water Technology 2023, Kennedy 2022) and expert advice. The product is not suitable for individual property scale assessments. The datasets available are as follows. Further detail on technical assumptions for these scenarios are provided in the accompanying technical reports. Additional data sets referenced in the reports are also available on request. Storm tide inundation Storm tide inundation extents for the 1% Annual Exceedance Probability (AEP) for a range of Sea Level Rise (SLR) scenarios (0m, 0.5m, 0.8m, 1.1m): - PPBCHA_INUNDATION_EXTENT_1AEP_00SLR - PPBCHA_INUNDATION_EXTENT_1AEP_05SLR - PPBCHA_INUNDATION_EXTENT_1AEP_08SLR - PPBCHA_INUNDATION_EXTENT_1AEP_11SLR - PPBCHA_INUNDATION_EXTENT_1AEP_14SLR - PPBCHA_INUNDATION_EXTENT_1AEP_00SLR_WITHRAINFALL - PPBCHA_INUNDATION_EXTENT_1AEP_05SLR_WITHRAINFALL - PPBCHA_INUNDATION_EXTENT_1AEP_08SLR_WITHRAINFALL - PPBCHA_INUNDATION_EXTENT_1AEP_11SLR_WITHRAINFALL - PPBCHA_INUNDATION_EXTENT_1AEP_14SLR_WITHRAINFALL Storm tide inundation extents for each SLR scenario are presented as a combined vector layer that incorporates the modelled 95th, 50th, and 5th percentiles. Erosion Erosion extents for the 1%AEP for a range of Sea Level Rise (SLR) scenarios (0m, 0.2m, 0.5m, 0.8m, 1.1m). - PPBCHA_EROSION_EXTENT_1AEP_2010_00SLR - PPBCHA_EROSION_EXTENT_1AEP_2040_02SLR - PPBCHA_EROSION_EXTENT_1AEP_2070_05SLR - PPBCHA_EROSION_EXTENT_1AEP_2100_08SLR - PPBCHA_EROSION_EXTENT_1AEP_2100_11SLR - PPBCHA_EROSION_EXTENT_1AEP_2100_14SLR Erosion hazard extents are the modelled 95th percentile. Sea level of 0m as of 2010. Groundwater Groundwater extents indicating where the hazard is shallow (within 0 to 2m below land surface) for a range of Sea Level Rise (SLR) scenarios (0m, 0.2m, 0.5m, 0.8m): - PPBCHA_GROUNDWATER_EXTENT_SHALLOW_00SLR - PPBCHA_GROUNDWATER_EXTENT_SHALLOW_02SLR - PPBCHA_GROUNDWATER_EXTENT_SHALLOW_05SLR - PPBCHA_GROUNDWATER_EXTENT_SHALLOW_08SLR - PPBCHA_GROUNDWATER_EXTENT_SHALLOW_11SLR - PPBCHA_GROUNDWATER_EXTENT_SHALLOW_14SLR Shallow groundwater extent layer is derived from the groundwater depth raster. Report Citations: CSIRO - McInnes, K.L., O’Grady, J.O., Prakash, M., Dahlhaus, P., Rosengren, N.J., Hoeke, R.K., Lauchlan Arrowsmith, C., Hernaman, V., Cohen, R., Seers, B., Chen, Y., Walters, D., Couto, P., Trenham, C., Forbes-Smith, N. Gregory, R., Hemer, M. and Power, R. (2022) Port Phillip Bay Coastal Hazard Assessment: Final Report. Report to Department of Environment, Land, Water and Planning. 236 pages + 11 Appendices. Water Technology (2023) Erosion Hazard Summary Report, Port Phillip Bay Coastal Erosion Hazards, Report to Department of Energy, Environment and Climate Action Kennedy, D. M. (2022), Tertiary Coastal Compartments in Port Phillip Bay: Review, Definition and Methodology, Report to Department of Energy, Environment and Climate Action. School of Geography, Earth and Atmospheric Sciences, The University of Melbourne.