Solanum angustum
stage missing = ploidy missing = chrom_num missing = voucher missing =
Solanum angustum is endemic to Queensland and known only from the type and two other collections. The label of the only recent collection indicated that the species was growing in “low eucalypt woodland with shallow clay soil”.
Solanum angustum is a typical member of Solanum subgenus Leptostemonum. It is placed into the S. ellipticum group (Group 27) by Bean (2004) on morphological grounds; its phylogenetic position has not been investigated using molecular data.
Symon, D.E. 1981. A revision of Solanum in Australia.
J. Adelaide Bot. Gard. 4: 1-367.
IUCN Species Survival Commision 2001. IUCN Red List Categories and Criteria: Version 3.1.
Gland, Switzerland and Cambridge, UK: IUCN.
Bean, A.R. 2004. The taxonomy and ecology of Solanum subg. Leptostemonum (Dunal) Bitter (Solanaceae) in Queensland and far north-eastern New South Wales.
Austrobaileya 6 (4): 639-816.
The affinities of this species are not known with any certainty, and it is only tentatively placed in the S. ellipticum group.
Symon (1981) considered S. angustum to be a synonym of S. parvifolium and stated: “The type specimen consists of three leafy portions, one with a fruit attached and a second detached fruit present. From the photograph, the plant is obviously closely related to S. parvifolium R. Br. and to a lesser extent S. ferocissimum Lindl. The type locality of S. angustum is at the northern extremity of the distribution of S. parvifolium. The berry of S. angustum was described as 1.5 cm diam., which is larger than usual for S. parvifolium. However, the seeds of S. angustum, which have been examined, are very similar to those of the two related species. I therefore prefer to consider S. angustum Domin as an extreme form of S. parvifolium until further specimens are collected.”
Conservation status: S. angustum has been collected just four times, in 1908, 1910, 1939 and 1992. A recent visit to the 1992 collection site failed to find the species. It has not been seen since 1992, despite deliberate searches during the summer months, especially in the Chillagoe-Walsh River area. Although there are no known extant populations, a presumption of extinction is premature. There would appear to be much available habitat within the extent of occurrence, although the required habitat for the species is still not known.
Applying the IUCN guidelines (IUCN, 2001), and using the 1992 location as an existing location, a category of “Endangered” is recommended (EN C2a(ii); D).