Reg egio ional Veg egetatio ion Map appin ing Work
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Reg egio ional Veg egetatio ion Map appin ing Work orkshop - - PowerPoint PPT Presentation
Reg egio ional Veg egetatio ion Map appin ing Work orkshop Introduction Workflow Segmentation of imagery Interpretation of vegetation photo patterns Use of existing vegetation mapping Vegetation structures are interpreted using a range
Reg egio ional Veg egetatio ion Map appin ing Work
Introduction
Segmentation of imagery Interpretation of vegetation photo patterns Use of existing vegetation mapping Vegetation structures are interpreted using a range of data in addition to digital imagery including landscape position, survey records, environmental data, existing mapping and local knowledge. Approximate scale of mapping 1:8,000 for coastal areas up to 1:25,000 for western regions Some structural units include a large number of PCTs (ie Dry Sclerophyll) Vegetation modelling will be specific to structural groupings and utilise particular environmental predictors for each PCT
Code Structural Class Code Structural Class Non-native 21 Wet heath 1 Candidate native grasslands 22 Dry heath 2 Dry sclerophyll 23 Grassy headlands 3 Wet sclerophyll 24 Swamp forest (treed wetlands) 5 Floodplain Forests 26 Foredune 7 Non-woody wetlands 29 Woodland (shrubby) 8 Grassy woodlands & open forest 30 Callitris woodland & forest 9 Dry Rainforest and Vine Thicket 31 Shrubby regrowth 10 Rainforests 32 Riparian River Oak Forest 11 Riparian forests (generic) 33 Riparian Moist Eucalypt Forest 13 Scrub / Tall Heath 34 Riparian rainforests 14 Hanging Swamps 35 Swamp Oak Forest 15 DSF gully/riparian 36 Mallee eucalypt heathy forest/woodlands 16 Rock 37 Riparian shrublands 18 Saltwater wetlands (mangroves/saltmarsh) 38 Camphor laurel dominated forests 20 Littoral rainforest
Relationships between vegetation structure, environmental variables and survey records will be established for each PCT and applied across the landscape Each structural grouping will have a separate model of relevant PCTs Some PCTs will extend across several vegetation structures Envelopes will be used to constrain modelling to the known distributional and environmental ranges of PCTs Some PCTs will not be modelled due to insufficient data or restricted distributions and mapped manually where there is sufficient site data Evaluation of accuracy will be invited as part of a user testing program and new information will be incorporated into the mapping
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PROGRESS OF CANDIDATE PCT REVISIONS Stage 1
Completed Remaining