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2021-06-14 General Committee Meeting Minutes
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GENERAL COMMITTEE MEETING MINUTES 14 JUNE 2021
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GENERAL COMMITTEE MEETING MINUTES 14 JUNE 2021
Protected areas Great Sandy NP, Poona NP, Bribie Island NP, Noosa NP, Glass
House Mountains NP, Deepwater NP, Mooloolah River NP,
Tewantin NP, Burrum Coast NP, Pumicestone NP, Pipeclay
NP, Beerwah FR, Toorbul CP, Cooloola (Noosa River) RR,
Weyba Creek CP, Ningi Creek CP
Special values Habitat for threatened fauna species including the wallum
froglet Crinia tinnula. This ecosystem is known to provide
suitable habitat for koalas (Phascolarctos cinereus). 12.3.4a:
Habitat for threatened fauna species including the wallum
froglet Crinia tinnula. This ecosystem is known to provide
suitable habitat for koalas (Phascolarctos cinereus).
Fire management SEASON: Late summer to mid-winter (after rain).
guidelines INTENSITY: Planned and occasional unplanned burns
(typically of higher intensity) influence the ecology of
melaleuca ecosystems. INTERVAL: Heath 8-12 years, Sedge
12-20 years, Mixed grass/shrub 6-20 years. STRATEGY: Aim
for a 25-70% burn mosaic (in association with surrounding
ecosystems, as melaleuca ecosystems often just occur in patches
or along natural drainage lines). Fires may, depending on the
conditions and type of vegetation, burn areas larger than just the
melaleuca ecosystem. Ensure secure boundaries from non fire-
regime adapted ecosystems. Consider the needs of melaleuca
ecosystems based on understorey (i.e., heath dominated, sedge
dominated or mixed grass/shrub) when planning burns. High
soil moisture (or presence of water on the ground) is required,
as avoidance of peat-type fires must be maintained. ISSUES:
Fire regimes for melaleuca ecosystems require further fire
research. Melaleuca forests are fire-adapted, but too high an
intensity or frequent fire will slow or prevent regeneration and
lead to lower species richness (since these communities contain
numerous obligate seed regenerating species that require
sufficient fire intervals to produce seed). High intensity fires
may kill trees and lead to whipstick regeneration. Too frequent
fire may result in a net loss of nutrients over time from an
already nutrient poor system. Fire associations are significantly
influenced by understorey composition. Melaleuca communities
with a heath understorey should burn in a similar way to coastal
heath (8-12 years). Sedge understorey communities will burn in
association with the surrounding ecosystems (so will often burn
with them but sometimes not, such that these communities have
a slightly less fire frequency). Mixed understorey communities
burn in a similar way to dry sclerophyll, in association with the
surrounding dry sclerophyll, though somewhat less frequently
due to the additional moisture present in melaleuca
communities.
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