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Bushfire Hazard Assessment
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Bushfire Hazard Assessment 14 Serenity Close, Noosa Heads however occurred at scales too small to map and were otherwise surrounded by other discontinuous or grassfire-prone fuel types. These areas were mapped as VHC 39.2 Low to moderate tree cover in built-up areas (8 tonnes per hectare) (Refer to Map 6). However, there was continuous remnant vegetation consistent with RE 12.3.4 which was located on the southern side of the waterway (Refer to Appendix 2, VHC Assessment Site 5). The latter was mapped as VHC 22.1 Melaleuca open forests on seasonally inundated lowland coastal swamps (28 tonnes per hectare) (Refer to Map 6). There was no evidence of VHC 29.3 Heathlands and associated scrubs and shrublands with the waterway area (c.f. Maps 4 and 6). ● Site assessment also indicated that parts of the Weyba Creek Bushland Reserve North to the west of the proposed development (Lot 600 on SP188270) which were mapped as VHC 29.3 Heathlands and associated scrubs and shrublands on the SPP Input Map (Refer to Map 4) were comprised predominantly of 22.1 Melaleuca open forests on seasonally inundated lowland coastal swamps (28 tonnes per hectare) (Refer to Appendix 2, VHC Assessment Site 3). Whereas any areas of VHC 29.3 Heathlands and associated scrubs and shrublands (20.1 tonnes per hectare) were located outside of the 150m site assessment area (c.f. Maps 4 and 6). ● The SPP Input Map also indicated an area of VHC 4.1 Notophyll and notophyll palm or vine forest (4 tonnes per hectare) located on a steep bank adjacent to the river on the northern side of the existing Serenity Close buildings. Site assessment indicated that the vegetation contained a mix of maintained gardens and lawns consistent with VHC 39.2 Low to moderate tree cover in built-up areas (8 tonnes per hectare) and also VHC 9.1 Moist to dry eucalypt open forests on coastal lowlands and ranges (24.2 tonnes per hectare) (Refer to Appendix 2, VHC Assessment Site 4). The latter was consistent with the current regional ecosystem mapping for the land which indicates the vegetation is comprised of RE 12.2.5 6. As per Leonard et al. (2014), the Potential Fuel Load assigned to each Vegetation Hazard Class is generally representative of the higher fuel load expected for the typical vegetation types, landscape and site conditions within each Vegetation Hazard Class. This Potential Fuel Load of each Vegetation Hazard Class would approximate the 80th percentile fuel load of the “long unburnt condition” for the class (generally greater than 10 years without burning). Modelled fuel loads for each of the amended VHCs were unchanged from the loads recommended by Bushfire Resilient Communities (Queensland Fire and Emergency Services 2019). Fuel loads for modelled VHCs were as per the Bushfire Resilient Communities (Queensland Fire and Emergency Services 2019); with hybrid or complex communities receiving the sum of the proportional fuel load of each constituent VHC (e.g. remnant vegetation containing a mix of regional ecosystems). Areas containing unmanaged regrowth or revegetation were mapped according to “long unburnt condition” for the class i.e. the potential fuel load of the vegetation type at maturity. Map 7 indicates the modelled fuel loads. 6 State of Queensland (Department of Resources) (2021). Vegetation management regional ecosystem map - version 12.0. Q. Herbarium. http://qldspatial.information.qld.gov.au/catalogue/ 16 | 38
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