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#75 This Action Statement was first published in 1996 and remains current. This Northern Sandalwood version has been prepared for web publication. It Santalum lanceolatum retains the original text of the action statement, although contact information, the Preamble distribution map and the This Action Statement forms a key step in Early authorities referred to only two illustration may have been localities - the Warby Range State Park east updated. the Flora and Fauna Guarantee program. It follows the listing of the Northern of Wangaratta, and Boundary Bend south- © The State of Victoria, Sandalwood under the Flora and Fauna east of Robinvale (Cochrane et al. 1968; Willis Department of Guarantee Act 1988, and outlines action to 1972; Cheal 1980 and Costermans 1986). Sustainability and be taken to ensure the long-term survival of However, Beauglehole (1986) recognised a Environment, 2003 the species. third locality, on Murphy's Island near Torrumbarry, west of Echuca. Four Published by the Description and Distribution Department Northern Sandalwood Santalum lanceolatum additional localities have been recorded in of Sustainability and R. Br., also known as Plumbush (in South recent times: one near Springhurst (about 30 Environment, Victoria. Australia) or Cherry Bush and Native Plum km north-east of the Warby Range locality) 8 Nicholson Street, (in Queensland), is a tall shrub or small in 1989, and the other three in the Mt Meg East Melbourne, tree, 2-8 m high. It is noted for its highly area (13 km south-west of the Warby Range Victoria 3002 Australia aromatic wood and dark, furrowed bark, population) in 1994-95. This publication may be of which is persistent to the smaller, The Warby Range, Springhurst and three Mt assistance to you but the pendulous branches. The thick grey-green Meg populations are associated with rocky, State of Victoria and its leaves are 5-12 cm long, opposite, hairless generally northern slopes, which in the employees do not guarantee and tapering to a short petiole. Flowering Warby Range case is particularly steep (30° that the publication is occurs throughout the year but is most or more). Outcropping granite boulders without flaw of any kind or prominent in spring and summer. The characterise the Springhurst site, while well- is wholly appropriate for white-yellow flowers (7-10 mm long) are in drained granite soils are a feature of all. your particular purposes and therefore disclaims all short terminal or axillary panicles. The Associated vegetation consists of low open- liability for any error, loss mature fruit is a 6-9 mm wide dark-blue woodland dominated by Blakely's Red Gum or other consequence which drupe. The sweet flesh is edible, as is the (Eucalyptus blakelyi) and Red Stringybark may arise from you relying central 'stone' (endocarp), which can be (Eucalyptus macrorhyncha), and taller wattles, on any information in this deeply pitted (Black 1963; Willis 1972 and Lightwood (Acacia implexa) and Currawang publication. Cheal 1980). In Australia, Northern (Acacia doratoxylon). The two remaining Sandalwood is found in the interior of all localities, at Boundary Bend and ISSN 1448-9902 mainland states and the Northern Territory Torrumbarry, are associated with sandy (Willis 1972). The species is widespread, alluvial soils and White Cypress-pine but not abundant, throughout arid and (Callitris glaucophylla) woodland on the semi-arid Australia (Cheal 1980), and Murray River floodplain. At Boundary Bend occurs in a wide range of woodland the associated vegetation consists of Hooked communities, ranging from sandhills to Needlewood (Hakea tephrosperma), Cooba rocky hills (Cunningham et al. 1981). (Acacia ligulata) and chenopod sub-shrubs Northern Victoria represents the southern (Sluiter pers. comm.), while Willow Wattle edge of the species' range. Seven widely (Acacia salicina) is present at the Torrumbarry separated localities are known in Victoria. site. #75 Conservation Status to China, that it became exterminated from many of its former Queensland haunts'. Current Status By far the single most significant threat to the remaining CNR (1994) Endangered in Victoria Victorian populations is removal of plants under 1 m high and Northern Sandalwood has been listed as a threatened taxon the inhibition of seedling and sucker recruitment through under Schedule 2 of the Flora and Fauna Guarantee Act 1988. grazing. Cheal (1980) recognised that persistent grazing of Reasons for Conservation Status seedlings across the species Australian range had, at that time, Four of the seven known populations occur on Crown seriously hampered regeneration and resulted in the species Land: Warby Range State Park and Mt. Meg Flora and becoming rare. Fauna Reserve (two populations) are managed primarily In its final recommendations , the Scientific Advisory for nature conservation, while the Boundary Bend Committee (SAC 1992) determined that the Northern population occurs on 'River Murray Reserve' (LCC 1989), Sandalwood is:. which is managed for a variety of public purposes. The - significantly prone to future threats which are likely to three remaining populations occur on private land. result in extinction; and All known populations have, in the past, been represented - very rare in terms of abundance and distribution by only a few individuals. Although a substantial increase in numbers has been recorded recently at three of the Major Conservation Objectives localities, the overall Victorian population size of 258 plants The major conservation objectives are to:. is still very small. - protect and enhance all known Northern Sandalwood The Warby Range population has been documented for habitats; more than 30 years. Cochrane et al. (1968) and Garnet (1974) - develop successful seed and cutting propagation refer to only one old tree, with Garnet adding that, 10 years techniques; earlier, two ancient trees and two struggling seedlings were - establish four new stands in appropriate and secure public recorded. Cheal (1980) recorded nine individuals. The land sites by 1999; and Warby Range population now totals 65 (1.5 ha), of which - increase the overall population from 258 to 450 within the about half are 2 m or less in height. Although a real increase next 10 years. in the number of individuals is apparent, Cheal (pers. comm.) hypothesises that the majority, if not all, are likely to Management Issues have progressively risen from root suckers originating from Ecological Issues Specific to the Taxon the oldest specimens. Like all members of the Sandalwood family Santalaceae, Before the erection of protective fencing in June 1990, the Northern Sandalwood is parasitic on the roots of other plants Springhurst population consisted of nine mature to (Cunningham et al. 1981, Costermans 1986). However, there is senescent individuals (3.5-6 m high). It now numbers 70 (0.3 not enough knowledge of specific host relationships, and it is ha). The additional plants, up to 2.5 m high have suckered not known whether the species is an obligate parasite for all or vegetatively from roots of parent plants up to 20 m away. only part of its life cycle. Cheal (1980) refers to 'perhaps no more than two Grazing of smaller plants and the associated inhibition of individuals' at the Boundary Bend locality. The population recruitment is the most significant ongoing threat to Northern now numbers 40 (0.5 ha), including about 13 under 2.5 m Sandalwood. The impact of grazing is best documented for the high, the majority definitely being suckers (Pickering pers. Warby Range population. Garnet (1967) and (1974) indicated comm.). that rabbit and sheep grazing there had prevented all regeneration. Cheal (1980) noted an increase in Northern The Torrumbarry population consists of four individuals (1 Sandalwood numbers after the phasing-out of sheep in the ha): two mature plants and another under 2.5 m high. 1970s and their total removal in 1976. Feral goats preferentially Mt Meg Flora and Fauna Reserve supports two populations grazed and caused significant damage to Northern approximately 2 km apart, consisting of 60 (1 ha) and 3 (0.1 Sandalwood until eradicated in 1982 (Hall pers. comm.). The ha) plants. The private land locality, 1 km east of the further increase in the Warby Range Sandalwood population is smaller population, supports 16 plants (0.5 ha), consisting attributed to the increased rabbit control within the Park. of three mature to old (but healthy) trees and the remainder At the Springhurst site, exclusion of stock and rabbit grazing young shrubs. through the erection of protective fencing has produced an Historically, Northern Sandalwood was thought to be once eight-fold increase in Sandalwood numbers. However, grazing more common throughout north central and north-eastern pressure has prevented regeneration at the Torrumbarry site Victoria, and to be more widespread on rocky faces in the (Woodward 1991). At the Warby Range site in particular, Warby Ranges. Much of the decline occurred late last another potential (although minor) threat, is grazing by century, after the gold rush, when out-of-work miners kangaroos and wallabies, which might be more pronounced in apparently exported consignments of the highly fragrant extended dry periods. timber to Asia (Hall pers. comm.). Indeed, Brown (1953) The apparent low rate or absence of sexual reproduction is a refers to 'such large quantities being exported, principally considerable threat to Northern Sandalwood. Although buds 2 #75 and flowers form annually at all sites, fruit were not Fleshy Mistletoe (Amyema miraculosum) has been recorded on recorded at any of the known Victorian populations until Northern Sandalwood in the Warby Range and at Boundary May 1992, when considerable numbers were observed at Bend. Fleshy Mistletoe occurs throughout northern Victoria the Warby Range site. Flower wasps (Scolia spp., family and parasitises only members of the Santalaceae and Scoliidae) have been observed feeding on Northern Loranthaceae (Mistletoe) families. Jim Willis first recorded four Sandalwood flowers (pers. obs.), but the role of invertebrate plants of Fleshy Mistletoe on Northern Sandalwood in the (or vertebrate) pollinators, and their possible absence due to Warby Range in 1971.
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  • Adelaide Botanic Gardens

    Adelaide Botanic Gardens

    JOURNAL of the ADELAIDE BOTANIC GARDENS AN OPEN ACCESS JOURNAL FOR AUSTRALIAN SYSTEMATIC BOTANY flora.sa.gov.au/jabg Published by the STATE HERBARIUM OF SOUTH AUSTRALIA on behalf of the BOARD OF THE BOTANIC GARDENS AND STATE HERBARIUM © Board of the Botanic Gardens and State Herbarium, Adelaide, South Australia © Department of Environment, Water and Natural Resources, Government of South Australia All rights reserved State Herbarium of South Australia PO Box 2732 Kent Town SA 5071 Australia J. Adelaide Bot. Gard. 19: 75-81 (2000) DETECTING POLYPLOIDY IN HERBARIUM SPECIMENS OF QUANDONG (SANTALUM ACUMINATUM (R.Br.) A.DC.) Barbara R. Randell 7 Hastings Rd., Sth Brighton, South Australia 5048 e-mail: [email protected] Abstract Stomate guard cells and pollen grains of 50 herbarium specimens were measured, and the results analysed. There was no evidence of the presence of two size classes of these cell types, and thus no evidence suggesting the presence of two or more ploidy races. High levels of pollen sterility were observed, and the consequences of this sterility in sourcing and managing orchard stock are discussed. Introduction In arid areas of Australia, the production of quandong fniit for human consumption isa developing industry. This industry is hampered by several factors in the breeding system of this native tree (Santalum acuniinatum (R.Br.) A. DC.- Santalaceae). In particular, plants grown from seed collected from trees with desirable fruit characters do not breed true to the parent tree. And grafted trees derived from a parent with desirable fruit characters are not always self-pollinating. This leads to problems in sourcing orchard trees with reliable characteristics, and also problems in designing orchards to provide pollen sources for grafted trees.