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Journal of East African Natural History 98(1): 141–145 (2009) WARNECKEA MELINDENSIS (MELASTOMATACEAE), A NEW COMBINATION FOR AN EAST AFRICAN COASTAL FOREST ENDEMIC R. Douglas Stone School of Biological and Conservation Sciences, University of KwaZulu-Natal Private Bag X01, Pietermaritzburg 3209, South Africa stonerd@ukzn.ac.za Quentin Luke The East African Herbarium, National Museums of Kenya P.O. Box 45166, 00100 Nairobi, Kenya Centre for Tropical Plant Conservation, Fairchild Tropical Botanic Garden 11935 Old Cutler Road, Coral Gables, FL 33156-4242 USA quentin.luke@swiftkenya.com ABSTRACT Results of recent morphological and molecular analyses necessitate the transfer of the species originally described as Memecylon melindense A.Fern. & R.Fern. to the genus Warneckea Gilg. A new combination, Warneckea melindensis (A.Fern. & R.Fern.) R.D.Stone & Q.Luke is proposed, and an IUCN status of Endangered is assessed for this regional endemic of coastal forests in Kenya and Tanzania. There is no evidence of hybridisation between W. melindensis and the closely related W. sansibarica (Taub.) Jacq.-Fél., even in sites where the two species are sympatric. Keywords: Warneckea, Melastomataceae, plant taxonomy, Kenya, Tanzania. INTRODUCTION Following the treatment of Melastomataceae for the Flora of Tropical East Africa (Wickens, 1975), further morphological and molecular studies have shown that the genus Warneckea Gilg is distinct from Memecylon L. (Jacques-Félix, 1978; Stone, 2006). The two genera can be readily distinguished by the strongly trinervate leaves of the former versus the apparently uninervate leaves of the latter. From the genus Lijndenia Zoll. & Moritzi, which also has trinervate leaves, Warneckea can be separated by its smooth leaf surfaces with conspicuous network of reticulate-areolate veinlets; by the tufts of bristles in the leaf-axils of some species (e.g., W. amaniensis Gilg); by its imperfectly 2-loculed ovary; and by its fleshy cotyledons. Lijndenia has leaves ± granular in dried material (owing to the presence of massive, ramiform sclereid cells in the mesophyll), and its uppermost inflorescence bracts are fused to form a cupule immediately subtending each flower (Jacques-Félix, 1985a). Seven East African species of Warneckea were recognised by Borhidi (1993), but his transfers of 142 R.D. Stone & Q. Luke W. jasminoides (Gilg) Jacq.-Fél. and W. bequaertii (De Wild.) Jacq.-Fél. to Lijndenia were made without analysis of taxonomic characters and should be rejected. Warneckea sansibarica (Taub.) Jacq.-Fél. (= Memecylon sansibaricum Taub. in Wickens, 1975) is the most widely distributed species of Warneckea in East Africa, being found mainly in the coastal forests of southernmost Somalia, Kenya, Tanzania, and northern Mozambique with outliers in the southern African interior and Madagascar (Wickens, 1975; Fernandes & Fernandes, 1978; Jacques-Félix, 1985b; Thulin, 1993; Coates-Palgrave, 2002). While it may be convenient to refer the coastal populations of W. sansibarica to one subspecies or variety and the inland populations to another, such treatment (cf. Wickens, 1975) appears to under-represent the morphological and genetic diversity in this complex. For example, recent investigations have revealed that W. sousae (A.Fern. & R.Fern.) A.E. van Wyk, which was placed by Wickens (1975) as a synonym of W. sansibarica, is really quite distinct (Vollesen, 1980; Stone & Andreasen, in press). When the taxon Memecylon melindense A.Fern. & R. Fern. was first described, it was compared with several other species having small, trinervate leaves, namely M. schliebenii Markgr. [= Warneckea schliebenii (Markgr.) Jacq.-Fél.], M. mouririifolium Brenan [= W. mouririifolia (Brenan) Borhidi], M. uniflorum Exell [= W. bebaiensis (Gilg ex Engl.) Jacq.-Fél.], and M. microphyllum Gilg [= W. microphylla (Gilg) Borhidi] (Fernandes & Fernandes, 1955). The same authors later recognized the affinity of M. melindense and M. buchananii Gilg [= W. sansibarica subsp. buchananii (Gilg) Borhidi], with the much smaller leaves of the former being mentioned as the only difference (Fernandes & Fernandes, 1960). In placing M. melindense as a synonym of M. sansibaricum [= W. sansibarica], Wickens (1975) noted it as “a small-leaved … shrub or possibly juvenile form” although “further gatherings and field studies may prove the two forms to be separable.” In December 2001, the first author observed plants referable to M. melindense to be locally common at their type locality in the Arabuko-Sokoke Forest, Kenya. These smallleaved shrubs were often seen growing in close association with larger-leaved trees of W. sansibarica, but without any morphological intermediates that might indicate hybridisation. The two morphotypes were subsequently found to differ at the molecular level, as indicated by uncorrected genetic distances in the spacer regions of nuclear ribosomal DNA (ITS sequence divergence = 1.9%; average divergence among cloned ETS alleles = 2.2%; cf. Stone & Andreasen, in press). That M. melindense is readily discernible from W. sansibarica is further suggested by field work at additional sites in Kenya and Tanzania (Vollesen, 1980; Luke, 2005). The available evidence warrants the recognition of M. melindense and its transfer to the genus Warneckea, necessitating a new combination. TAXONOMIC TREATMENT Warneckea melindensis (A.Fern. & R.Fern.) R.D.Stone & Q.Luke, comb. nov. Memecylon melindense A.Fern. & R.Fern., Bol. Soc. Brot., sér. 2, 29: 62, tab. 16 (1955). Type: Kenya, Kilifi District, Arabuko, fls., Oct 1937, Dale 3835 (holotype PRE!; isotypes BR!, EA!, K!, P!, S!). Distribution Kenya, K7 (Kilifi and Kwale Districts) and Tanzania, T8 (Kilwa and Liwale Districts). See figure 1. Warneckea melindensis, new combination 143 Figure 1. The geographic distribution of Warneckea melindensis. Known localities are indicated by black dots. Additional specimens examined. Kenya. Kilifi District, Sokoke, fls., s.d., Gisau EA 10987 & 11490 (EA, K); same locality, ster., s.d., Graham 1951 (EA, K); Arabuko, fls., Oct. 1929, Graham 2163 (EA, K, PRE); same locality, fl. buds, Feb 1932, MacNaughtan 153 (EA, G, K); Dida, fls., 14 Apr 1947, Jeffery 570 (EA, K); Sokoke, fl. buds, 14 Apr 1954, Trump 138 (EA, K); 0.5 km NE of Sokoke Forest Station on Kilifi-Vitengeni road, ster., 24 Aug 1971, Faden 71/751 (EA, K); Jilore, SW of Malindi, 3°11'S, 39°54'E, ster., 17 Mar 1973, Sangai EA 15711 (EA); Arabuko-Sokoke Forest, east and south of Jilore Forest Station, frs., 12 Jun 1973, Musyoki & Hansen 1036 (EA, K); Mangea Hill (Sita), 3°17'S, 39°44'E, fls., 24 Apr 1989, Luke & Robertson 1793 (EA, K); Arabuko-Sokoke, base of small nyari, 3°20'S, 39°51'E, ster., 6 Dec 1990, Luke & Robertson 2607 (EA, K); Arabuko-Sokoke Forest, along unpaved road from Mida to Jilore Forest Station, ca. 0.2 km N of intersection with Elephant Track, 3°17'02"S, 39°55'49"E, ster., 31 Dec 2001, Stone & Gitau 2427 (CAS, EA); Kwale District, Shimba Hills, Mwalugange Forest Reserve, 4°06'S, 39°28'E, ster., 6 Jan 1997, Luke 4574A (Ukunda herb.). Tanzania. Selous Game Reserve, without locality, fls., 21 Jun 1975, Ludanga & Vollesen MRC 2464 (EA); Kilwa District, Selous Game Reserve, Nakilala 144 R.D. Stone & Q. Luke thicket, 8°35'S, 38°15'E, fls., 23 Nov 1969, Rodgers 801 (EA, K); Liwale District, Selous Game Reserve, Malemba thicket, fls., 23 Dec 1975, Vollesen MRC 3129 (EA); same locality, 8°40'S, 38°25'E, fls., 11 Jan 1977, Vollesen MRC 4308 (EA, K). Habitat Coastal forest and thicket; altitude 30–400 m. Conservation status Warneckea melindensis is known from five sites, three of which are in Kenya and two in Tanzania. Most of the collections are from the Arabuko-Sokoke Forest Reserve which is the largest (417 km2) fragment of coastal forest remaining in East Africa. Using the Kew algorithm in ArcView, the EOO is calculated as 15 000 km2, much of this being part of the Indian Ocean and thus a major area of discontinuity, however, properly included in the calculation (Gaston & Fuller, 2009). The grid size was selected as 3.16 km (a practice adopted by the East Africa Plant Red List Authority on the advice of George Schatz and Craig Hilton-Taylor so as to reasonably cover plant dispersal around a point locality and at the same time not exclude the categories CR and EN for one or five localities under B2). This gives an AOO of just under 100 km2, well below the 500 km2 limit for the Endangered threat category (IUCN, 2001). Additional considerations are that two localities have been almost totally cleared: Mangea Hill for human settlement; and the Mwaluganje site, in Kwale District, by an overpopulation of elephant. This more than outweighs the fact that the remaining populations are reasonably secure within the protected areas of the Selous GR and Arabuko Sokoke FR. Thus our assessment is EN B2a,b (ii,iii,iv), Endangered. Notes Warneckea melindensis is most closely related to W. sansibarica (cf. Stone & Andreasen, in press) but is readily distinguished by its much smaller leaves (1.4–3.7 cm long and 1.2–2.3 cm wide vs. 5–10 cm long and 2.5–5 cm wide). In the type region (Arabuko-Sokoke) it is a spreading understorey shrub to 2 m high (rarely to 3.6 m), while W. sansibarica is an erect tree to 5 m with the brownish outer bark of the trunk and older branches exfoliating in patches to reveal whitish inner bark. At the Tanzanian localities, W. melindensis can be a shrub or small tree to 5 m, but it reportedly differs from W. sansibarica in leaf-size as well as in habitat, bark characteristics, flower-colour, and fruit-size (Vollesen, 1980). Further evaluation of W. melindensis awaits a comprehensive revision of the W. sansibarica complex. As for the curious disjunction of W. melindensis between K7 and T8, its cause is unknown although there are several other coastal forest endemics with similar distributions, including Karomia gigas (Faden) Verdc. 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