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BUSHFIRE HAZARD ASSESSMENT AND MANAGEMENT PLAN v2 - Coveys Road TINBEERWAH (1)
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Log in to see the plans as drawnBushfire Hazard Assessment and Management Plan v2 NCES REF: J000545 Lot 2, 4 & 5 on RP172460 & Lot 7 on RP895754 66, 82 & 98 Coveys Rd & 39 Tinbeerwah Rd, Tinbeerwah Compliance with Assessment Benchmark 4 can be attained where all allotments are sufficiently separated from the nearby forest hazard so that a radiant heat flux level at any point on the building or envelope does not exceed 29 kW/m². Determination of the anticipated radiant heat flux exposure to the proposed building envelopes is identified in Section 4. 6.2.2 Radiant Heat Flux Setbacks Determination of the setbacks required to satisfy Assessment Benchmark 4 can be identified from the quantitative modelling output presented in Section 4 herein. The output results from Plates 8 and Plate 9 can be used to identify the setback requirements to achieve the <29 kW/m² radiant heat flux SPP requirement and are summarized in Table 5. Table 5 – Radiant Heat Flux Setbacks to secure <29kW/m² Lot No. VHC Direction and slope APZ Setback (0º) 8 VHC 8.1 North to west (3º) 20.4* 9 VHC 8.1 North to west (3º) 20.4* 12 VHC 8.1 North to east (8º) 25.4* * Source – Flamesol Minimum Distance calculator The building envelopes within Lot 8 and Lot 9 are separated from the Very High Potential Bushfire Intensity area by a minimum of 75m of mowed/grazed grass and therefore have been provided adequate separation from the hazardous VHC 8.1 open forest to achieve compliance with Assessment Benchmark 4. The building envelope within Lot 12 is separated from the Very High Potential Bushfire Intensity area by a minimum of 39m of mowed/grazed grass and therefore has been provided adequate separation from the hazardous VHC 8.1 open forest to achieve compliance with Assessment Benchmark 4. 6.2.3 Asset Protection Zone Design To reduce the potential for bushfire impact to buildings, structures and occupants as a result of future landscaping, regrowth and fuel load accumulation within the site, the identified APZ setbacks in Table 5 above are to be established and maintained according to the following criteria: • APZ’s are maintained as a low threat zone dominated by maintained grass to a nominal 100mm height which is regularly mowed to reduce fuel loads and the risk of a grassfire encroaching toward the building; • Any landscaping within the APZ satisfies the low threat vegetation criteria prescribed in section 2.2.3.2 of AS 3959:2018 or later iterations thereof, where applicable, and be planted as discrete isolated clumps of low flammability vegetation aligned parallel to the building to aid in interception of ember and smoke attack and not perpendicular and in a manner which could transmit fire toward the building; • No woody mulch is to be used within 2m of buildings; • No non-rainforest trees are to be planted within 10m of the building and no non-rainforest tree limbs extend to within 6m of the roof line; • Future landscaping works/plantings maximise the use of locally indigenous, low flammability species and or low density plantings of suitable open forest /woodland species with low bark shedding characteristics. Site managers should consult their local native plant nursery for suitable species selection; and • Surface fuels and woody regrowth be controlled in the APZ to maintain a low fuel load environment. Roof tops, roof gutters and other areas of the building and including ancillary infrastructure such as garden sheds be regularly inspected, and debris removed to reduce the risk of spot fires developing in the properties during a bushfire event; and © 2022 23
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