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UPDATED DA - Attachment 6 - Bushfire Management Plan
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INTERVAL: Heath 8-12 years, Sedge 12-20 frequently due to the additional moisture
years, Mixed grass/shrub 6-20 years. present in melaleuca communities.
INTERVAL_MIN: 6. INTERVAL_MAX: 20.
12.3.13 -Closed or wet heathland.
STRATEGY: Aim for a 25-70% burn
Characteristic species include Melaleuca
mosaic (in association with surrounding
thymifolia, Banksia robur, Xanthorrhoea
ecosystems, as melaleuca ecosystems
fulva, Hakea actites, Leptospermum spp.
often just occur in patches or along
and Baeckea frutescens. Occurs on
natural drainage lines). Fires may,
seasonally waterlogged Quaternary
depending on the conditions and type of
alluvial plains along coastal lowlands.
vegetation, burn areas larger than just
Palustrine. (BVG1M: 29a).
the melaleuca ecosystem. Ensure secure
boundaries from non fire-regime adapted Fire management guidelines –
ecosystems. Consider the needs of
SEASON: Late summer to winter.
melaleuca ecosystems based on
understorey (i.e., heath dominated, sedge INTENSITY: Moderate (to high; due to the
dominated or mixed grass/shrub) when inherent characteristics of highly flammable
planning burns. High soil moisture (or vegetation).
presence of water on the ground) is INTERVAL: 8-20 years. INTERVAL_MIN: 8.
required, as avoidance of peat-type fires INTERVAL_MAX: 20.
must be maintained.
STRATEGY: Aim for a burn mosaic of 40-
ISSUES: Fire regimes for melaleuca 80%. Ensure planned burn conditions are
ecosystems require further fire research. conducive to maintaining integrity of the
Melaleuca forests are fire-adapted, but landscape (i.e., use good soil moisture,
too high an intensity or frequent fire will recent rainfall and standing water on the
slow or prevent regeneration and lead to ground).
lower species richness (since these
communities contain numerous obligate ISSUES: Intervals at the upper end (12-20
seed regenerating species that require years) of the recommended regime may be
sufficient fire intervals to produce seed). desirable to counteract detrimental impacts
High intensity fires may kill trees and of a high intensity fire over 100% of
lead to whipstick regeneration. Too landscape. This vegetation often contains
frequent fire may result in a net loss of obligate seed regenerating species and as
nutrients over time from an already such, the application of frequent fire may
nutrient poor system. Fire associations reduce species richness if the intervals
are significantly influenced by between fire are not sufficient for plants to
understorey composition. Melaleuca produce seed.
communities with a heath understorey
should burn in a similar way to coastal 12.5.3 – Eucalyptus racemosa subsp.
heath (8-12 years). Sedge understorey racemosa woodland with Corymbia
communities will burn in association with intermedia, E. siderophloia +/- E.
the surrounding ecosystems (so will tindaliae, E. resinifera, E. pilularis, E.
often burn with them but sometimes not, microcorys, Angophora leiocarpa.
such that these communities have a Melaleuca quinquenervia is often a
slightly less fire frequency). Mixed prominent feature of lower slopes. Minor
understorey communities burn in a patches (<1ha) dominated by Corymbia
similar way to dry sclerophyll, in citriodora subsp. variegata sometimes
association with the surrounding dry occur. Occurs on complex of remnant
sclerophyll, though somewhat less Tertiary surfaces +/- Cainozoic and
RFA24-059 – Noosa Land Fill and Waste Management Facility – Bushfire Management Plan
Rob Friend & Associates Pty Ltd 10th of October 2024
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