Regional ecosystem details for 12.11.3
| Regional ecosystem | 12.11.3 |
|---|---|
| Vegetation Management Act class | Least concern |
| Wetlands | Not a Wetland |
| Biodiversity status | No concern at present |
| Subregion | 3, 7, 5, (6), (1), (2), (4), (9), (8) |
| Estimated extent1 | Pre-clearing 150000 ha; Remnant 2021 99000 ha |
| Short description | Eucalyptus siderophloia, E. propinqua +/- E. microcorys, Lophostemon confertus, Corymbia intermedia, E. acmenoides open forest on metamorphics +/- interbedded volcanics |
| Structure code | Open Forest |
| Description | Eucalyptus siderophloia and E. propinqua open forest +/- E. microcorys, Lophostemon confertus, Corymbia intermedia, E. biturbinata, E. acmenoides, E. tereticornis, E. moluccana, Angophora leiocarpa, Syncarpia verecunda with vine forest species and E. grandis or E. saligna in gullies. Eucalyptus pilularis and E. tindaliae sometimes present e.g. mid D'Aguilar Range, Conondale Range. Occurs predominantly on hills and ranges of Palaeozoic and older moderately to strongly deformed and metamorphosed sediments and interbedded volcanics. Not a Wetland. (BVG1M: 9a). Vegetation communities in this regional ecosystem include: 12.11.3a: Lophostemon confertus +/- Eucalyptus microcorys, E. carnea, E. propinqua, E. major, E. siderophloia woodland. Occurs in gullies and exposed ridges of Palaeozoic and older moderately to strongly deformed and metamorphosed sediments and interbedded volcanics. Not a Wetland. (BVG1M: 9a). 12.11.3b: Eucalyptus pilularis tall open forest. Other frequently occurring species include Eucalyptus microcorys, E. saligna, E. siderophloia, E. carnea, Corymbia intermedia and E. propinqua. Occurs on higher altitude (>300m) subcoastal hills and ranges of Palaeozoic and older moderately to strongly deformed and metamorphosed sediments and interbedded volcanics. Not a Wetland. (BVG1M: 8b). |
| Supplementary description | Ryan, T.S. (ed.) (2012); Bean et al. (1998), I12, G23, H8 |
| Protected areas | D'Aguilar NP, Conondale NP, Wrattens NP, Springbrook NP, Maleny NP, Bellthorpe NP, Mount Barney NP, Woondum NP, Samford CP, Oakview NP, Moggill CP, Nerang NP, Tuchekoi NP, Tamborine NP, Grongah NP, Bunyaville CP, Wrattens RR, Clear Mountain CP, Wararba Cr |
| Special values | 12.11.3: Habitat for threatened plant species including Corchorus cunninghamii, Marsdenia coronata and Sophora fraseri. This ecosystem is known to provide suitable habitat for koalas (Phascolarctos cinereus). 12.11.3a: Habitat for threatened flora species including Corchorus cunninghamii, Marsdenia coronata and Sophora fraseri. This ecosystem is known to provide suitable habitat for koalas (Phascolarctos cinereus). 12.11.3b: Habitat for threatened plant species including Corchorus cunninghamii, Marsdenia coronata and Sophora fraseri. This ecosystem is known to provide suitable habitat for koalas (Phascolarctos cinereus). |
| Fire management guidelines | SEASON: Summer to winter. INTENSITY: Plan for low to moderate. Unplanned occasional high intensity wildfire will occur. INTERVAL: 4-8 years maintains a healthy grassy system. 8-20 years for shrubby elements of understorey. INTERVAL_MIN: 4. INTERVAL_MAX: 20. STRATEGY: Aim for 40-60% mosaic burn. Needs disturbance to maintain RE structure (eucalypt overstorey with open understorey of predominantly non-rainforest species). Any moist sclerophyll that is relatively open with a mixture of grasses and shrubs should be a priority for fire management to retain RE structure. ISSUES: Frequent fire is needed to maintain understorey integrity, keeping more mesic species low in the profile of the understorey so that other species can compete. A grassy system is especially important for species such as the eastern bristlebird and its habitat. It is essential that wildfires are not the sole source of fire in this ecosystem. High intensity fires occur periodically through time, however frequent low to moderate intensity fires will create the disturbance required to keep the understorey diverse. A follow-up burn soon after a high intensity wildfire can be considered to reduce germinating/resprouting mesic species. |
| Comments | 12.11.3: This type develops a dense understorey of Araucarian vine forest species in the absence of fire. Subject also to weed invasion by Lantana camara. 12.11.3a: This type develops a dense understorey of Araucarian vine forest species in the absence of fire. Subject also to weed invasion by Lantana camara. 12.11.3b: Mid D'Aguilar Range and Conondale Range. Subject also to weed invasion by Lantana camara. |
1 Estimated extent is from version 13 pre-clearing and 2021 remnant regional ecosystem mapping. Figures are rounded for simplicity. For more precise estimates, including breakdowns by tenure and other themes see remnant vegetation in Queensland.
