Howell Shrublands in the New England Tableland and Nandewar Bioregions - Determination to make a minor amendment to Part 3 of Schedule 1 of the Threatened Species Conservation Act
The Scientific Committee, established by the Threatened Species Conservation Act, has made a Determination to make a minor amendment to Part 3 of Schedule 1 (Endangered ecological communities) of the Act by inserting the Howell Shrublands in the New England Tableland and Nandewar Bioregions (as described in the determination of the Scientific Committee under Division 5 Part 2 published in the Gazette on 2 December 2011) and as a consequence to omit reference to the Howell Shrublands in the New England Tableland and Nandewar Bioregions (as described in the determination of the Scientific Committee under Division 5 Part 2) which was published on pages 2723 to 2726 in the NSW Government Gazette No. 43 dated 18 April 2008. Minor amendments to the Schedules are provided for by Division 5 of Part 2 of the Act.
The Scientific Committee is of the opinion that the amendment is necessary or desirable to correct minor errors or omissions in the Determination in relation to the Thackway and Cresswell (1995) reference.
NSW Scientific Committee - final determination
The Scientific Committee has found that:
1. The Howell Shrublands in the New England Tableland and Nandewar Bioregions is the name given to the ecological community that is characterised by the following assemblage of species;
Acacia falciformis | Acacia granitica |
Acacia neriifolia | Acacia triptera |
Acacia viscidula | Actinotus gibbonsii |
Actinotus helianthi | Aristida jerichoensis |
Aristida vagans | Arthropodium milleflorum |
Austrodanthonia bipartita | Austrodanthonia monticola |
Babingtonia densiflora | Blechnum cartilagineum |
Boronia granitica | Brachyscome stuartii |
Bulbostylis pyriformis | Caesia calliantha |
Calandrinia eremaea | Callitris endlicheri |
Calytrix tetragona | Cassinia laevis |
Cassinia quinquefaria | Centrolepis strigosa |
Cheilanthes sieberi | Cheistochloa rigida |
Chenopodium pumilio | Chrysocephalum semipapposum |
Commelina cyanea | Cotula australis |
Crassula sieberiana | Cryptandra amara |
Cryptandra amara subsp. floribunda | Cyathea australis |
Cymbopogon refractus | Cyperus fulvus |
Cyperus gracilis | Dianella caerulea |
Dichopogon fimbriatus | Digitaria breviglumis |
Drosera peltata | Echinopogon caespitosus |
Einadia hastata | Entolasia stricta |
Eragrostis brownii | Eucalyptus caleyi |
Eucalyptus dealbata | Eucalyptus mckieana |
Eucalyptus prava | Euchiton sphaericus |
Eulalia aurea | Ficus rubiginosa |
Fimbristylis dichotoma | Gahnia aspera |
Glycine clandestina | Gonocarpus micranthus |
Gonocarpus tetragynus | Gonocarpus teucrioides |
Goodenia belledifolia | Hibbertia kaputarensis |
Homoranthus prolixus | Hovea lanceolata |
Hydrocotyle peduncularis | Hypericum gramineum |
Isotoma anethifolia | Isotoma axillaris |
Laxmannia compacta | Laxmannia gracilis |
Leionema rotundifolium | Lepidosperma laterale |
Leptospermum brevipes | Leptospermum novae-angliae |
Leucopogon melaleucoides | Leucopogon muticus |
Leucopogon neo-anglicus | Lobelia gracilis |
Lomandra multiflora | Microlaena stipoides |
Micromyrtus sessilis | Monotaxis macrophylla |
Murdannia graminea | Notelaea microcarpa |
Olearia elliptica | Opercularia hispida |
Oxalis chnoodes | Ozothamnus obcordatus |
Paspalidium constrictum | Patersonia sericea |
Persoonia cornifolia | Phebalium rotundifolium |
Philotheca myoporoides subsp. conduplicata | Plectranthus parviflorus |
Pleurosorus subglandulosus | Poa sieberiana |
Pomax umbellata | Portulaca bicolor |
Portulaca filifolia | Portulaca oleracea |
Prostanthera nivea | Pterostylis setifera |
Ranunculus sessiliflorus | Rumex brownii |
Sigesbeckia orientalis | Solanum cinereum |
Solanum opacum | Solenogyne bellioides |
Stackhousia viminea | Stypandra glauca |
Trachymene incisa | Tripogon loliiformis |
Urtica incisa | Vittadinia sulcata |
Wahlenbergia communis | Zieria odorifera ms |
2. The total species list of the community is considerably larger than that given above, with many species present in only one or two sites or in low abundance. The species composition of a site will be influenced by the size of the site, recent rainfall or drought condition and by its disturbance (including fire) history. The number of species, and the above ground relative abundance of species will change with time since fire, and may also change in response to changes in fire regime (including changes in fire frequency). At any one time, above ground individuals of some species may be absent, but the species may be represented below ground in the soil seed banks or as dormant structures such as bulbs, corms, rhizomes, rootstocks or lignotubers. The list of species given above is of vascular plant species; the community also includes micro-organisms, fungi, cryptogamic plants and a diverse fauna, both vertebrate and invertebrate. These components of the community are poorly documented.
3. Howell Shrublands has been recorded primarily around Copeton Dam and Goonoowigal near Inverell with a small occurrence (about 10 ha) at Warrabah. These occurrences are within the New England Tableland and Nandewar Bioregions. Bioregions are defined in Thackway and Cresswell (1995).
4. Howell Shrublands are dominated by low shrubs particularly Homoranthus prolixus and Babingtonia densifolia. Occasionally all shrubs may be absent giving a grassland structure or Callitris endlicheri and various eucalypts such as Eucalyptus dealbata and Eucalyptus prava may be present giving the appearance of a low open woodland. Howell Shrublands have been described in Hunter, J. & Clarke, P. (1998) Cunninghamia 5(3) :547-618.
5. Howell Shrublands occur on granitic outcrops and has been recorded on Gilgai Granite (undifferentiated), leucoadamellite and Tingha Granite. The area covered by granite outcrops is likely to be about 500-800 ha of which Howell Shrublands community is likely to actually cover about 100-200 ha.
6. Rare and threatened species in Howell Shrublands include Homoranthus prolixus, Boronia granitica, Eucalyptus mckieana, Monotaxis macrophylla, Leionema rotundifolium and Acacia granitica.
7. The main occurrence of the Howell Shrublands areas are not known to be conserved in any National Parks though it may possibly occur in Copeton State Recreation Area. Part of the small southern occurrence (about 2ha) is conserved in Warrabah National Park.
8. The most significant threat to the Howell Shrublands is grazing by goats. There are large herds throughout the area occupied by the Howell Shrublands community. Rabbits also cause substantial modification to the community. Other impacts are from sheep grazing and clearing, weed invasion, roadworks and powerline constructions. Increased mining activity and inappropriate fire regimes are potential threats.
9. In view the above, the Scientific Committee is of the opinion that Howell Shrublands in the New England Tableland and Nandewar Bioregions is likely to become extinct in nature unless factors threatening its survival or evolutionary development cease to operate and that listing as an endangered ecological community is warranted.
Dr Richard Major
Chairperson
Scientific Committee
Proposed Gazettal date: 02/12/11
Exhibition period: 2/12/11 – 03/02/12
Reference :
Thackway R, Cresswell ID (1995) An interim biogeographic regionalisation for Australia: a framework for setting priorities in the National Reserves System Cooperative Program. (Version 4.0. Australian Nature Conservation Agency: Canberra.)