Regional ecosystem details for 12.5.13
| Regional ecosystem | 12.5.13 |
|---|---|
| Vegetation Management Act class | Endangered |
| Wetlands | Not a Wetland |
| Biodiversity status | Endangered |
| Subregion | 6, (8), (9), (5), (7), (2), (11.22), (4) |
| Estimated extent1 | Pre-clearing 55000 ha; Remnant 2021 6000 ha |
| Short description | Microphyll to notophyll vine forest +/- Araucaria cunninghamii on remnant Tertiary surfaces |
| Structure code | Closed Forest |
| Description | Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Araucaria cunninghamii, Cupaniopsis parvifolia, Dendrocnide photiniphylla, Rhodosphaera rhodanthema, Flindersia australis, F. schottiana, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Argyrodendron trifoliolatum sometimes present especially in subregion 6. Occurs on remnant Tertiary surfaces especially lateritised basalt. Not a Wetland. (BVG1M: 5a). Vegetation communities in this regional ecosystem include: 12.5.13a: Microphyll to notophyll vine forest +/- Araucaria cunninghamii. Characteristic species include Araucaria cunninghamii, Cupaniopsis parvifolia, Dendrocnide photiniphylla, Rhodosphaera rhodanthema, Flindersia australis, F. schottiana, F. xanthoxyla, Drypetes deplanchei, Olea paniculata, Diospyros geminata, Gossia bidwillii, Excoecaria dallachyana and Vitex lignum-vitae. Argyrodendron trifoliolatum sometimes present especially in subregion 6. Occurs on remnant Tertiary surfaces especially lateritised basalt. Not a Wetland. (BVG1M: 5a). 12.5.13b: Microphyll/notophyll vine forest. Characteristic species include Cupaniopsis anacardioides, Acronychia imperforata, Flindersia schottiana, Alectryon coriaceus, Elaeocarpus obovatus, Polyalthia nitidissima, Diospyros spp., Pleiogynium timorense and Mallotus discolor. Melaleuca spp. and eucalypt emergents may be present, e.g. Melaleuca dealbata and Corymbia tessellaris. Occurs on coastal remnant Tertiary surfaces. Not a Wetland. (BVG1M: 5a). 12.5.13c: Low microphyll vine forest and semi-evergreen vine thicket +/- Araucaria cunninghamii. Characteristic species include Brachychiton rupestris, Flindersia collina, F. australis, Alectryon diversifolius, A. subdentatus, Elattostachys xylocarpa, Erythroxylum sp. (Splityard Creek L.Pedley 5360), Psydrax odorata forma buxifolia, Diospyros geminata, Planchonella cotinifolia, Croton insularis, Bridelia exaltata and Bursaria incana. Melaleuca bracteata is often present along watercourses. Occurs on remnant Tertiary surfaces especially lateritised basalt. (Land zone 5). Not a Wetland. (BVG1M: 7a). |
| Supplementary description | Bean et al. (1998), G9, G13, G18 |
| Protected areas | Tarong NP, Cooroibah CP, Mount Binga NP, Boat Mountain CP 1, The Palms NP, Jack Smith Scrub CP, Boat Mountain CP 2, Ravensbourne NP, Great Sandy CP, Burrum Coast NP, Mount Binga FR |
| Special values | 12.5.13: Habitat for threatened plant species including Alectryon ramiflorus, Sarcochilus weinthalii, Cossinia australiana. 12.5.13a: Habitat for threatened plant species including Alectryon ramiflorus, Sarcochilus weinthalii, Cossinia australiana. 12.5.13b: Habitat for threatened plant species including Acronychia littoralis and near threatened species including, Xylosma ovata and Dansiea elliptica. 12.5.13c: Habitat for near threatened plant species including Callitris baileyi and Cryptocarya floydii. |
| Fire management guidelines | INTERVAL: Fire return interval not relevant. INTERVAL_MIN: 100. INTERVAL_MAX: 100. STRATEGY: Do not burn deliberately. Protection relies on broad-scale management of surrounding country. May need active protection from wildfire in extreme conditions or after prolonged drought. Planned burns should not create a running fire into vine forest. Ensuring conditions of good soil moisture and moisture of litter in surrounding communities will limit fire behaviour/intensity. ISSUES: Fire sensitive and not normally flammable. There may be issues with lantana and other weeds from fire and other disturbance. Remnants may be limited by frequent fire at the margins; this requires further research. |
| Comments | 12.5.13: Characteristic localities for the RE are Yarraman-Tarong-Boat Mountain. Cleared for agriculture and hoop pine plantation. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. 12.5.13a: Characteristic localities for the RE are Yarraman-Tarong-Boat Mountain. Cleared for agriculture and hoop pine plantation. Remnants can be degraded by weed infestation in conjunction with wildfire damage on margins. 12.5.13b: Deepwater Creek catchment. Mostly cleared for horticultural production. Only persists as small remnants that can be degraded by weed infestation in conjunction with wildfire damage. 12.5.13c: Mostly restricted to western margins of central part of bioregion in the vicinity of Barambah Creek extending westward into the Brigalow Belt. Remnants require intensive management because of invasion by weeds and fire damage on margins. |
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.
