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Bushfire Hazard Assessment & Management Plan v2 - 30 Pottery St Pomona 2021
Bushfire Hazard Assessment & Management Plan v2 NCES REF: J000864 Lot 496 on MCH591 – 30 Pottery St, Pomona 3 HAZARD ASSESSMENT 3.1 Hazard Assessment Methodology The Noosa Planning Scheme requires that a site-specific bushfire hazard assessment be prepared to assess the degree of bushfire hazard on a site captured within a mapped Designated Bushfire Hazard Area. The SPP Bushfire Prone Area mapping prevails over the Noosa Bushfire Hazard Area mapping with respect to the currency of the methodology adopted to prepare the mapping. Accordingly, the site-specific hazard mapping required is to be prepared consistent with the methodology adopted to prepare the SPP mapping. The methodology used to prepare the SPP mapping is described in: • Department of Infrastructure, Local Government and Planning’s Natural Hazards, Risk and Resilience –– Bushfire (December 2019) State Planning Policy – state interest guidance material; and • Queensland Fire and Emergency Services - (2019) Planning for Bushfire Resilient Communities. Site-specific hazard maps are referred to as Local Hazard Area Maps in the SPP documents. The preparation of Local Hazard Area Maps has been undertaken for the site in accordance with the methodology described in the above referenced documents. 3.2 Local Hazard Area Map A Local Hazard Area Map was prepared by adopting the following methodology: • Categorizing the vegetation within the site in accordance with the vegetation hazard classes derived from QFES (2019); • Using the patch and corridor filtering process to remove narrow corridors and small patches of VHC’s1; • Subdividing the identified vegetation hazard classes into bushfire hazard sub-units based on slope differences and vegetation hazard classes. All upslope and across slope vegetation units are allocated an underlying slope of 1 degree as per methodology prescribed within Queensland Fire and Emergency Services - (2019) Planning for Bushfire Resilient Communities. The maximal slope recorded within a 3 x 3 grid comprised of 25m x 25m individual grids within the VHC’s is adopted as the effective slope underlying the VHC. A conservative approach is adopted where multiple slopes persist within VHC’s; • Assigning SPP Potential Bushfire Intensity classes to the sub-units; • Application of 150m Potential Impact Buffers to the amended sub-units to derive an overall Local Hazard Area Map. 1 The patch and corridor filtering process to remove or downgrade hazard levels of small patches and narrow corridors involves the following three stages: • Merging small patches of a single Vegetation Hazard Class less than 0.5 ha; • Merging small Vegetation Hazard Class patches between 0.5 and 1 ha with higher or moderate fuel loads (greater than 8 tonnes/ha); and • Removing narrow corridors of vegetation less than 50m wide through a process of patch erosion and dilation. These small patches are merged with surrounding vegetation by allocating a patch to the Vegetation Hazard Class that is most common to the patch boundary (Leonard et al., 2017). © 2021 11
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