Caladenia callitrophila - NSW Threatened Species Scientific Committee Preliminary Determination: Critically endangered
Caladenia callitrophila D.L.Jones, an orchid – proposed Critically endangered species listing - Preliminary Determination open for comment until 28 February 2025.
The NSW Threatened Species Scientific Committee assesses which species are eligible for listing as threatened.
The exhibition of the Preliminary Determination provides an opportunity for the community to comment or provide additional information relevant to the assessment.
Have your say on the Preliminary Determination.
Extract from the Preliminary determination (PDF 319KB)
Caladenia callitrophila is endemic to the southern Riverina region of New South Wales (NSW). It is currently known to exist in three small, isolated subpopulations located within state forests between the towns of Berrigan and Balldale at altitude range of 120-170 m ASL (Copeland and Backhouse 2022). The subpopulations are separated by 16-50 km of cultivated farmland. This species occurs in woodland of Callitris glaucophylla (white cypress pine), Eucalyptus melliodora (yellow box) and Eucalyptus microcarpa (western grey box), with a grassy and sparsely shrubby understorey, on red-brown sandy or sandy-loam soils. Most of the plants have been found in 3-4 m tall white cypress pine regrowth (G. Robertson in litt. Feb 2021).
There is a very low number of mature individuals of Caladenia callitrophila. The total number of C. callitrophila flowering plants recorded during the 2020 season, after good winter rain, was around 183 flowering plants, with the majority of those (>90%) occurring at one site (G. Robertson in litt. Feb 2021; DCCEEW unpubl. data). Following the much drier winter of 2023 only 14 flowering plants were recorded (DCCEEW unpubl data; L. Carrigan unpubl data; G. French unpubl data).
It is difficult to estimate the current total population size of C. callitrophila as plants observed flowering in one season that did not reemerge in the following season are not necessarily dead. Some may remain dormant underground, a common ecological strategy observed in orchids with a similar life history (Dixon and Tremblay 2009). Emergent numbers fluctuate primarily due to rain and soil moisture, and the underground population is probably capable of persisting for some years without emergence (Dixon and Tremblay 2009). However, given the season in 2020 was considered a year with good conditions for flowering, the population size is likely no more than 250.
Little is known of the specific details of the biology of Caladenia callitrophila however it is believed to be very similar to other spider orchids. Caladenia species are deciduous and die back to a dormant, fleshy tuber over summer (NSW DEC 2004; Dixon and Tremblay 2009). In Caladenia, tubers are generally replaced annually by a single daughter tuber on a vertical dropper, but few species appear to reproduce vegetatively by this means (Jones 2021). The tuber sprouts following sufficient late autumn/winter rains, with a single leaf developing above ground. Once the leaf is fully extended, a single flower may be produced. C. callitrophila flowers in September to October if conditions are suitable and flowers persist for about a month depending on the seasonal conditions (NSW DEC 2004; Copeland and Backhouse 2022). The prominent calli on the labellum of C. callitrophila suggest that is likely pollinated by nectar-foraging thynnid wasps (Zaspilothynnus sp.) (Reiter et al. 2019).
Acacia chrysotricha - NSW Threatened Species Scientific Committee Preliminary Determination: Critically endangered
Acacia chrysotricha Tindale, a tree – proposed Critically endangered species listing – Preliminary Determination open for comment until 17 April 2025.
The NSW Threatened Species Scientific Committee assesses which species are eligible for listing as threatened.
The exhibition of the Preliminary Determination provides an opportunity for the community to comment or provide additional information relevant to the assessment.
Have your say on the Preliminary Determination.
Extract from the Preliminary determination (PDF 298KB):
Acacia chrysotricha was found to be eligible for listing as Critically Endangered under the IUCN Criteria B1ab(iii).
The main reasons for this species being eligible are: 1) Acacia chrysotricha has a very highly restricted Extent of Occurrence (EOO) of 28 km2, 2) Acacia chrysotricha is known from a single threat-defined location; and 3) continuing decline has been observed and is expected to continue in the quality of habitat due the combined effects of weed invasion and logging activities.
Acacia chrysotricha Tindale (Figure 1; Newry golden wattle, Bellinger River wattle) is a conventionally accepted species (CHAH 2006) in the Fabaceae family. Acacia chrysotricha is described in PlantNET (2004) as an “Erect tree usually 6–15 m high; bark finely or deeply fissured, grey to red-brown; branchlets ± terete with low ridges, densely yellowish-hairy at first, later the hairs greyish or fawn. Leaves ± sessile on pulvinus, with petiole to 0.1 cm long above pulvinus; rachis 5–14 cm long, densely hairy, circular jugary glands irregularly present at the lowest 1–3 pairs and/or upper 1–3 pairs of pinnae, interjugary glands absent or rarely an odd one present; pinnae 8–18 pairs, 1–4.7 cm long; pinnules mostly 12–25 pairs (6 or more on basal pinnae),oblong to narrowly oblong, elliptic-oblong or ± lanceolate, recurved when dry, mostly 3–4.5 mm long and 1–1.5 mm wide, with fine white or golden hairs mainly on margins and midvein. Inflorescences in axillary and terminal racemes and panicles; peduncles 3–6 mm long, golden-hairy; heads globose, 15–30-flowered, 4–7 mm diam., bright yellow. Pods straight to slightly curved, ± flat, mostly barely to slightly constricted between seeds, 3–10 cm long, 4–6 mm wide, firmly papery thinly leathery, with long fine hairs; seeds longitudinal; funicle ± encircling the seed. Flowering July-August”.
The first collection of Acacia chrysotricha was made in 1910. It was first described by Tindale in 1966 based on the following type specimen: “Connell's Creek, on Compt. 24 of Newry SF, just south of Urunga, on a side gully 40 to 50 ft. high, 8 inches indiam. at the base, one tree 70 ft. high, 12 inches in diam., A. Floyd 7.1961 (NSW 34451), located in the National Herbarium of New South Wales, Sydney" (Hunter 2017). The name “Newry golden wattle” refers to the golden hairs on the branchlets (PlantNET 2004). It can be distinguished from similar co-occurring Acacia species (e.g., A. mearnsii and A. oshanesii) by features such as the colour and fissuring of the bark, densely hairy branchlets, shorter petiole length, position of jugary and interjugary glands, typically fewer pairs of pinnae and pinnules and the bright yellow flowers (PlantNET 2004).
Acacia chrysotricha trees are typically described as growing approximately 6 to 20 m tall (PlantNET 2004; Richards 2011), however, a few individuals have been observed with estimated heights as tall as 25–40 m in undisturbed habitats (Smith 2012).
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Acacia chrysotricha fruit. Image Credit: Gavin Phillips/DCCEEW
Caladenia rileyi - NSW Threatened Species Scientific Committee Preliminary Determination: Endangered
Caladenia rileyi D.L.Jones, an orchid – proposed Endangered species listing – Preliminary Determination open for comment until 17 April 2025.
Preliminary determination (PDF 280KB)
Conservation assessment report using the common assessment method (PDF 340KB)
The NSW Threatened Species Scientific Committee assesses which species are eligible for listing as threatened.
The exhibition of the Preliminary Determination provides an opportunity for the community to comment or provide additional information relevant to the assessment.
Have your say on the Preliminary Determination.
Extracts from the Preliminary determination (PDF 280KB):
The main reasons for this species being eligible are (i) it has highly restricted geographic distribution (EOO is 327 km2 and AOO is 36 km2); (ii) it has low population size (plausibly less than 2 500 mature individuals); (iii) it is severely fragmented and has a small number of threat based locations; (iv) there is a continuing decline in the area, extent and/or quality of habitat and the number of mature individuals due to threats from habitat loss and destruction, forestry activities, herbivory (grazing and browsing), weed incursion, and climate change.
The NSW Threatened Species Scientific Committee has found that:
1. Caladenia rileyi D.L.Jones (family Orchidaceae) was described by (Jones 2021) as “Leaf linear-lanceolate, 40–100 x 6–8mm. Flower stem 80–250mm tall, wiry, 1–flowered. Flowers 40–50mm across, yellowish-green with red central stripes;sepals and petals with thickish brown clubs 6–25 x 3 mm, petal clubs shorter than sepals. Dorsal sepal erect, 40–55 x 2–3 mm, incurved. Lateral sepals obliquely deflexed, 40–55 x 3–3.5 mm, more or less parallel. Petals obliquely deflexed, 30–40 x 1.5–2mm. Labellum delicately hinged, 17–20 x 18–20 mm, pale green with a white central patch and maroon apex; basal margins with 4–6 pairs of erect combteeth to 6mm long; midlobe margins with 5–8 pairs short blunt teeth to apex; tip recurved. Basal calli c.4mm long. Lamina calli to 3mm long, maroon, in 4 crowded rows onto base of maroon patch. Column 12–14 x 5.5–6.5 mm, transparent with pink to red flecks and striae; basal glands obovoid, c.3 mm long, yellow with a reddish basal stalk shiny. Flowers: September to October.”
2. Caladenia rileyi is endemic to the southern inland plains of New South Wales (NSW) and is restricted to a small area near the town of Narrandera, at 100-200m elevation (Copeland and Backhouse 2022). The species is currently known to exist in only four subpopulations, all located on crown land. Two of these subpopulations are in state forests, one is a Travelling Stock Reserve (TSR) north of Narrandera, and one is found along a roadside site just east of Narrandera. These four sites are small and isolated patches of habitat (10-55 km apart), separated from one another by cultivated farmland. This species grows in woodland habitats dominated by Callitris glaucophylla (white cypress pine), with a sparse understory of grasses and forbs on red-brown sandy soils or sandy clay loams (Jones 2021). Caladenia rileyi has been recorded in Callitris glaucophylla - Eucalyptus melliodora (yellow box) woodlands, Callitris glaucophylla – Allocasuarina verticillata (drooping sheoak) woodlands and woodlands dominated by a mixture of Callitris glaucophylla, E. dwyeri (Dwyer’s red gum) and Acacia doratoxylon (currawang) (ALA 2024; G. Robertson in litt. Feb 2021).
3. The habitat of this species may occur within 'Inland Grey Box Woodland in the Riverina, NSW South Western Slopes, Cobar Peneplain, Nandewar and Brigalow Belt South Bioregions’ an Endangered Ecological Community (EEC) under the NSW BC Act (NSW SC 2011). This EEC most likely corresponds with Plant Community Type (PCT) ‘Western Grey Box - White Cypress Pine tall woodland on loam soil on alluvial plains of NSW South Western Slopes Bioregion and Riverina Bioregion (PCT 80). This species may also occur in PCT ‘Dwyer's Red Gum - White Cypress Pine - Currawang shrubby woodland mainly in the NSW South Western Slopes Bioregion’ (PCT 185), but may not be restricted to these specific PCTs (NSW DPE 2023).
Eucalyptus oresbia - NSW Threatened Species Scientific Committee Preliminary Determination: Endangered
Eucalyptus oresbia J.T.Hunter & J.J.Bruhl, a tree – proposed Endangered species listing – Preliminary Determination open for comment until 17 April 2025.
Preliminary determination (PDF 311KB)
Conservation assessment report using the common assessment method (PDF 929KB)
The NSW Threatened Species Scientific Committee assesses which species are eligible for listing as threatened.
The exhibition of the Preliminary Determination provides an opportunity for the community to comment or provide additional information relevant to the assessment.
Have your say on the Preliminary Determination.
Extract from the Preliminary determination (PDF 311KB):
Eucalyptus oresbia J.T.Hunter & J.J.Bruhl as was found to be Endangered in accordance with the following provisions in the Biodiversity Conservation Regulation 2017: Clause 4.2(1 b)(2 c) and Clause 4.3(b)(d)(e i,iii) because: 1) the species is suspected to have undergone a large population reduction of >50% over a three generation period of 306 years due to historical clearing for agriculture and pine plantations; 2) the species has a highly restricted area of occupancy (44 km2 ) and extent of occurrence (420 km2); 3) the species is known from 3–4 threat-defined locations; and 4) continuing decline is inferred in the area, extent and quality of habitat and the number of mature individuals due to conflicting land uses such as plantation forestry and agriculture in prime E. oresbia habitat, adverse fire regimes, the maintenance of tracks and trails, and the invasion of weeds such as blackberry and radiata pine.
The NSW Threatened Species Scientific Committee has found that:
1. Eucalyptus oresbia J.T.Hunter & J.J.Bruhl (family Myrtaceae) is described by Hunter and Bruhl (1999) as a “Tree to 30 m tall. Bark smooth white, yellow or cream, rarely grey, sock absent or rarely present on younger trees to 1 m. Juvenile stems and branchlets usually strongly quadrangular. Leaves: seedling leaves ovate to elliptic, 3–10 cm long, 1–3.5 cm wide, plane, opposite, apex acute to obtuse, base rounded or ± caudate, petiolate at first and then a few pairs sessile, concolorous; intermediate leaves ovate to lanceolate, 12–18 cm long, 3–6.5 cm wide, sub-opposite to alternate, apex acute to acuminate, ± hooked, base rounded to ± oblique; adult leaves lanceolate, falcate or ± plane, 9.5–18 cm long, 1.2–2.2 cm wide, alternate, conspicuously glossy and dark green, margins entire, apex acuminate and often hooked, base attenuate, acute or oblique, petiole terete to flattened, barely channelled above, 1–2 cm long; venation 30–45° to midrib, intramarginal vein 0.5–2 mm from the margin, midrib channelled above.
Inflorescence of axillary umbellasters. Flowers 6–7 per axil; peduncle 8–17 mm long, 2–5 mm wide; pedicel distinct in bud and fruit, 3–5 mm long in buds, 2–4.5 mm long in fruit; buds obloid to clavate, bulbous above and below the suture,± 1-ribbed, 6–9.5 mm long; calyptra peaked hemispherical, acutely obconical or ±rostrate, 2.5–5 mm long, 2–3.5 mm wide; hypanthium 2.5–5 mm long, 2–3.5 mm wide; style terete, 3–4 mm long; stamens with filaments 3.5–5 mm long, anthers dorsifixed, parallel, dehiscence longitudinal, 0.4–0.6 mm long, white, oil gland orbicular and abaxial. Fruit cupular, ± 1-ribbed, 4.5–8 mm long, 5–8 mm wide, often splitting on one side; disc level to descending, c. 1 mm wide; valves 3, ± level. Seeds red-brown to black. Cotyledons bilobed.”
2. Eucalyptus oresbia is a range-restricted species endemic to several small, disjunct sites near the town of Nundle on the New South Wales (NSW) Northern Tablelands (Hunter and Bruhl 1999; OEH 2021). Eucalyptus oresbia is currently known from four disjunct sites. The core area is around the type locality at Hanging Rock, due east of Nundle, with smaller outlying stands known from the Scotts Creek area near Murrurundi to the south, in the Dungowan Dam catchment area northeast of Nundle, and in Ben Halls Gap National Park southeast of Nundle. Given the minimum distance between these sites is approximately 11 km, each is considered a separate subpopulation per the IUCN (2024) definition.
3. The minimum estimated population size of Eucalyptus oresbia is 6,458-6,708 mature individuals. Approximately 92-96% of the known population occurs within the Hanging Rock subpopulation, and less than 1% of the known individuals occur on lands managed for conservation in the Ben Halls Gap and Dungowan Dam subpopulations.
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Eucalyptus oresbia. Image Credit: Gavin Phillips/DCCEEW
Tasmannia purpurascens - NSW Threatened Species Scientific Committee Preliminary Determination: Endangered
Tasmannia purpurascens (Vickery) A.C.Sm., a shrub – proposed Endangered species listing – Preliminary Determination open for comment until 17 April 2025.
The NSW Threatened Species Scientific Committee assesses which species are eligible for listing as threatened.
The exhibition of the Preliminary Determination provides an opportunity for the community to comment or provide additional information relevant to the assessment.
Have your say on the Preliminary Determination.
Extract from the Preliminary determination (PDF 338KB):
Tasmannia purpurascens (Vickery) A.C.Sm. was found to be Endangered in accordance with the following provisions in the Biodiversity Conservation Regulation 2017: Clause 4.3(b)(d)(e i,iii) because: 1) the species has a highly restricted geographic range with an area of occupancy (AOO) of 240–248 km2 and an extent of occurrence (EOO) of 550–1,199 km2; 2) it occurs in three threat-defined locations; and 3) there is an estimated and inferred continuing decline in the area, extent and quality of habitat and number of mature individuals due to habitat clearing, fragmentation, and degradation; dieback from Phytophthora cinnamomi infection; habitat degradation from feral animals; invasion by Cytisus scoparius (Scotch broom) and Rubus spp. (blackberry); and adverse fire regimes, particularly high frequency fire and high severity fire.
The NSW Threatened Species Scientific Committee has found that:
1. Tasmannia purpurascens (Vickery) A.C.Sm. (family Winteraceae) is a “shrub 1– 3 m high, apical buds and stems purplish. Leaves oblanceolate to ± obovate, mostly 8–18 cm long, 30– 50 mm wide, apex obtuse, glabrous, both surfaces green and purplish towards base; secondary veins forming angles of c. 45° with midvein; ± sessile, gradually tapered to base. Petals usually 2, 8–12 mm long, white. Carpels 2– 9 per flower. Ovary c. 2 mm long; stalk of carpel much shorter than the ovary. Berries ovoid to oblong, 10–15 mm long, blackish purple; usually 2–6 develop, each on stalk 1– 4 mm long, peduncle 20–40 mm long.” (Harden 1990).
2. The majority of Tasmannia purpurascens records are in the Barrington Tops and Gloucester Tops area of the NSW Northern Tablelands. The species is also recorded in Ben Halls Gap Nature Reserve (NR), approximately 40 km to the northwest. The distribution of T. purpurascens occurs on the traditional lands of the Geawegal and Kamilaroi peoples (AIATIS 2023).
3. The population size of Tasmannia purpurascens is estimated to exceed 100,000 individuals (OEH 2021). The species is dioecious (Smith 1969; Falster et al. 2021) but the proportion of males and females is unknown, as is the proportion of mature individuals. Tasmannia purpurascens is common on the Barrington Plateau (M. Saunders pers. obs. November 2023). There is no long-term monitoring information available for this species and there is no information on long-term population trends. Tasmannia purpurascens occurs across an estimated 1–3 subpopulations, as per the IUCN (2024) definition.
4. Tasmannia purpurascens has a highly restricted geographic range. The extent of occurrence (EOO) was calculated at 550–1,199 km2 and is based on a minimum convex polygon enclosing all mapped occurrences of the species, the method of assessment recommended by IUCN (2024). The area of occupancy (AOO) is estimated to be 240–248 km2 and was calculated using 2 x 2 km grid cells, the scale recommended by IUCN (2024).
5. Tasmannia purpurascens typically occurs in in tall, moist eucalypt, subalpine woodland, and cool temperate rainforest (OEH 2019; PlantNet 2023) at elevations ranging from 1,050–1,560 m above sea level. Tasmannia purpurascens occurs on freely draining soil with good moisture retention but can also grow on heavier soils (Casey 1983).
6. Tasmannia purpurascens is dioecious (Smith 1969; Falster et al. 2021) and flowers from October to November (Falster et al. 2021; OEH 2021; PlantNet 2023). Tasmannia purpurascens fruits from February to June (FOA 2022), with fruit maturing over several months, based on what is known about Tasmannia lanceolata (Read 2017). Tasmannia purpurascens seeds are dormant at the time of release. In situ fruit burial studies of Tasmannia stipitata, with which T. purpurascens co-occurs, have shown the species has a delayed germination of at least 2 months (Campbell et al. 2012) and up to 10 months (Campbell et al. 2016), suggesting T. purpurascens is likely to have similar delayed germination under real world conditions with the environmental conditions required to break dormancy and promote germination remaining unknown.
7. Tasmannia purpurascens is exposed to a broad range of threats, including habitat clearing, fragmentation, and degradation; dieback from Phytophthora cinnamomi infection; habitat degradation from feral animals; invasion by Cytisus scoparius (Scotch broom) and Rubus spp. (blackberry); and adverse fire regimes, particularly high frequency fire and high severity fire. Hybridisation with sympatric Tasmannia taxa is also occurring and appears to be an important evolutionary process among other taxa in the genus (Worth et al. 2010). Threats are concentrated in the Barrington Tops area, with Bens Halls Gap NR currently only affected by low densities of feral herbivores. ‘Clearing of native vegetation’, ‘Infection of native plants by Phytophthora cinnamomi’, ‘Predation, habitat degradation, competition and disease transmission by feral pigs (Sus scrofa)’, ‘Habitat degradation and loss by feral horses (brumbies, wild horses), Equus caballus Linnaeus 1758’, ‘Invasion and establishment of Cytisus scoparius (Scotch broom)’, ‘Loss and degradation of native plant and animal habitat by invasion of escaped garden plants, including aquatic plants’, and ‘High frequency fire resulting in the disruption of life cycle processes in plants and animals and loss of vegetation structure and composition’ are listed as Key Threatening Processes under the Act.
8. Tasmannia purpurascens occurs at three threat-defined locations as per the IUCN definition (IUCN 2024), due to the most serious plausible threats which result in the lowest number of locations being dieback from Phytophthora cinnamomi infection and adverse fire regimes.
9. Habitat disturbance, fragmentation, and degradation from logging operations has resulted in an estimated and inferred loss of mature individuals and a significant decline in habitat quality and extent. Targeted surveys undertaken in logging compartments in 2023 inferred logging to have resulted in or contributed to a circa 77–100% decline in the number of individuals (in all age classes) at 5–21 years after the logging events (NSW DCCEEW 2024).
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Tasmannia purpurascens. Image Credit: Matt Saunders