Regional ecosystem details for 7.11.19
| Regional ecosystem | 7.11.19 |
|---|---|
| Vegetation Management Act class | Of concern |
| Wetlands | Contains Palustrine |
| Biodiversity status | Of concern |
| Subregion | 7, 8, 9, (9.6), (3), (4), (5), (1) |
| Estimated extent1 | Pre-clearing 8000 ha; Remnant 2021 6000 ha |
| Short description | Corymbia intermedia and/or Lophostemon suaveolens open forest to woodland on uplands on metamorphics |
| Structure code | Open Forest |
| Description | Corymbia intermedia (pink bloodwood) and/or Lophostemon suaveolens (swamp mahogany) open forest to woodland. Uplands on metamorphics. Contains Palustrine. (BVG1M: 9c). Vegetation communities in this regional ecosystem include: 7.11.19a: Corymbia intermedia, Eucalyptus tereticornis, Allocasuarina torulosa, A. littoralis and Lophostemon suaveolens open forest, low open forest and woodland with Acacia cincinnata, A. flavescens, Banksia aquilonia and Xanthorrhoea johnsonii. Uplands on metamorphics. Not a Wetland. (BVG1M: 9c). 7.11.19b: Corymbia intermedia, Allocasuarina torulosa and Lophostemon suaveolens open forest to woodland. Uplands on metamorphics, of the moist rainfall zone. Not a Wetland. (BVG1M: 9c). 7.11.19c: Lophostemon suaveolens woodland and open forest. Uplands on metamorphics. Contains Palustrine. (BVG1M: 9c). |
| Supplementary description | Stanton and Stanton (2005), M14d, M91, Q91, M16e in part (Qld Herbarium and WTMA (2005) M250a), CM16e in part (Qld Herbarium and WTMA (2005) CM250a), Q16e in part (Qld Herbarium and WTMA (2005) Q250a); Tracey and Webb (1975), 14d, 16e |
| Protected areas | Little Mulgrave NP, Kuranda NP, Wooroonooran NP, Daintree NP (CYPAL), Gadgarra NP, Dinden NP, Danbulla South FR, Barron Gorge NP, Dinden CP, Paluma Range NP, Dinden West FR, Mount Peter CP, Danbulla NP, Kuranda FR, Little Mulgrave FR |
| Special values | 7.11.19: Potential habitat for NCA listed species: Marsdenia rara, Randia audasii. |
| Fire management guidelines | SEASON: Cool, dry season (June-Sep). INTENSITY: Low to moderate. INTERVAL: 2-5 years. INTERVAL_MIN: 2. INTERVAL_MAX: 5. STRATEGY: Mosaic burn < 30%. Begin burning early in the fire season, with progressive patch fires burnt through the year. Stop burning when the network of fires and other breaks is sufficient to impede fire spread later in the year. Storm-burning may be used to add further diversity to the fire mosaic. ISSUES: Ignition is most likely during hot, dry season (Oct - Jan). These fires are typically high intensity fires that can be difficult to control. Maintaining a fire mosaic will ensure protection of animal habitats and mitigate against wildfires. |
| Comments | 7.11.19: Distinguished from 7.11.43 and 7.11.51 by the dominance of Corymbia intermedia instead of C. clarksoniana (usually higher altitude and/or wetter zones than 7.11.43 and 7.11.51). Distinguished from 7.11.16 by the occurrence on sub-coastal ranges as opposed to headlands and near coastal foothills. Widespread in the bioregion along the central ranges. |
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.
