Melicope oppenheimeri K.R. Wood, Appelhans & W.L. Wagner, 2016
publication ID |
https://dx.doi.org/10.3897/phytokeys.69.8844 |
persistent identifier |
https://treatment.plazi.org/id/153A842B-D5AC-5255-8B30-8D3AD331C3F9 |
treatment provided by |
|
scientific name |
Melicope oppenheimeri K.R. Wood, Appelhans & W.L. Wagner |
status |
sp. nov. |
Melicope oppenheimeri K.R. Wood, Appelhans & W.L. Wagner sp. nov. Figs 1 View Figure 1 , 4 View Figure 4 , 5 View Figure 5
Diagnosis.
Differs from Hawaiian congeners by its combination of leaves having 7-10 pair of secondary veins; cymes to 3 cm long; peduncles 5-6.5 mm long; flowers perfect; carpels basally connate 1/5, narrowed into a strongly reflexed beak 10-15 mm long, capsules 4-9 × 40-52 mm; and ovary appressed densely short-sericeous.
Type.
United States of America. Hawaiian Islands , West Maui : Wailuku District, Waihe‘e Valley, Metrosideros polymorpha var. glaberrima - Cheirodendron trigynum wet forest , 20°54.15'N; 156°33.95'W, 770 m elev., 12 Sep 2006, Hank Oppenheimer & Jill Miller H90609 View Materials (holotype: PTBG-070667; isotypes: BISH, GoogleMaps US)
Description.
Trees 3-4 m tall, bark medium brown, young branchlets light brown, glabrate, 3-6 mm wide in third internode, terminal branchlets yellowish brown tomentose with a waxy scurf. Leaves opposite, unifoliolate, coriaceous, the blade obovate to broadly elliptic, occasionally orbicular, 5-17.5 × 3.5-8.5 cm, the margin entire, the base rounded to obtuse, the apex rounded, obtuse to acute, or emarginate, secondary veins usually 7-10 pairs, connected by a moderately arched vein 2-11 mm from margin with higher order venation reticulate, both surfaces glabrous, occasionally glabrate along midrib of abaxial surface, young leaves glabrate to sparsely puberulent on lower surface; petiole shallowly canaliculate, 10-30 × 1-3 mm at middle, glabrate. Flowers: perfect, 3-5 in axillary cymes up to 3 cm long, peduncles 5-6.5 mm long, sparsely short-puberulent, pedicles 5-8 mm, short-puberulent, bracteoles 1.5-3 mm long, sepals broadly ovate, tip short acuminate, externally sparsely short-puberulent, glabrous within, 3 × 2.5-2.8 mm, connate basally 1/4 to 1/3 of length; petals tinged purple, narrowly ovate, lanceolate, 6-8 × 2.5-3 mm, glabrous internally and externally, tips recurved, nectary disk with sparsely scattered hairs; ovary densely appressed short-sericeous; style ca. 1.7 mm long, with finely appressed hairs; stigma capitate, four lobed, glabrous; stamens 8, filaments glabrous, the antesepalous ones 5-7 mm long, antepetalous ones 4-5 mm long, all with pollen. Capsules purple tinged when fresh, 4-9 × 40-52 mm, carpels connate basally for ca. 1/5 their length, narrowed into a strongly reflexed beak 10-15 mm long, exocarp glabrate with few hairs widely spaced over surface, endocarp sparsely to evenly puberulent. Seeds 2 per carpel, ovoid, 5-9 mm long.
Phenology.
To date, Melicope oppenheimeri has been observed with flower buds in January and August, with flowers at anthesis during September, and with fruit during January, February, May, August, September, and November.
Etymology.
We are pleased to name this new species in honor of Hank Oppenheimer, botanist with the Maui Nui Plant Extinction Prevention Program, who collected the type specimen and has made many valuable contributions to the understanding and conservation of the Hawaiian flora.
Specimens examined.
United States. Hawaiian Islands, West Maui: Wailuku District, Waihe‘e Valley, south side, below and north of Kahoolewa Ridge , 20°54.15'N; 156°33.95'W, 770 m elev., 8 Aug 1998, Wood & Perlman 7408 (BISH, PTBG, US) GoogleMaps ; loc. cit., 9 Aug 1998, Perlman & Wood 16,338 (CANB, PTBG) GoogleMaps ; loc. cit., 10 AUG 1998, Wood & Perlman 7419 (BISH, PTBG, US) GoogleMaps ; loc. cit., 15 Feb 2005, Oppenheimer & Hansen H 20,505 (BISH, PTBG, US) GoogleMaps ; loc. cit., 19 May 2009, Perlman & Oppenheimer 21,642 (PTBG) GoogleMaps .
The following couplets can be inserted into the existing key to Hawaiian Melicope (treated as Pelea ) by Stone, Wagner, and Herbst (in Wagner et al. 1999, pp. 1179-1182) to accommodate Melicope oppenheimeri .
19(18) | Exocarp sparsely to densely puberulent or tomentose, at least toward base or along suture | 20 |
19 | Exocarp glabrous or glabrate, sometimes with a few hairs widely spaced over surface (49). | 49 |
49(19) | Endocarp densely and uniformly short-villous; K | Melicope cruciata |
49 | Endocarp glabrous or sparsely puberulent, especially along suture | 50 |
50(49) | Leaves ternate; O | Melicope lydgatei |
50 | Leaves opposite. | 51 |
51(50) | Most petioles 0-10 mm long | 52 |
51 | Most petioles over 10 mm long | 58 |
58(51) | Ovary sparsely to densely puberulent or tomentulose, but exocarp glabrate or nearly so in fruit | 59 |
58 | Ovary and exocarp glabrous | 60 |
59(58) | Flowers perfect, carpels narrowed into a reflexed beak 10-15 mm long; WM | Melicope oppenheimeri |
59 | Flowers unisexual, carpels straight or somewhat reflexed, apex not beaked | 59a |
59a(59) | Capsules (16-)25-40(-50) mm wide, carpels connate 1/4-1/3 their length; pedicels 5-20 mm long; L, EM, H | Melicope volcanica |
59a | Capsules 11-20 mm wide, carpels connate (1/3-)1/2 their length or more; pedicels 2-5 mm long; K, O | Melicope wawraeana |
Distribution and ecology.
Although seven trees of Melicope oppenheimeri have been documented since its discovery in 1998, only three trees are still surviving in the upper headwaters of Waihe‘e Valley, West Maui (Figures 2 View Figure 2 , 3 View Figure 3 ). No trees have yet been located outside of the type locality and access to the site has only been by helicopter.
The plant communities of upper Waihe‘e Valley are varied and merge together in and around the 0.25 km2 cliff-base plateau region where trees of Melicope oppenheimeri occur. The plateau itself represents a relictual low statured Metrosideros Banks ex Gaertn. ( Myrtaceae )- Cheirodendron Nutt. ex Seem. ( Araliaceae ) lowland wet forest community. Other relic native components of the plateau include ferns such as Asplenium lobulatum Mett. ( Aspleniaceae ), Cibotium glaucum (Sm.) Hook. & Arn. ( Cibotiaceae ), Ctenitis latifrons (Brack.) Copel. ( Dryopteridaceae ), Diplazium sandwichianum (C. Presl) Diels ( Athyriaceae ), two endemic genera of ferns, namely Adenophorus Gaudich. ( Polypodiaceae ) and Sadleria Kaulf. ( Blechnaceae ), along with herbs, shrubs, and small trees including Antidesma platyphylla H. Mann ( Phyllanthaceae ), Broussaisia arguta Gaudich. ( Hydrangeaceae ), Coprosma pubens A. Gray ( Rubiaceae ), Dubautia plantaginea Gaudich. ( Asteraceae ), Peperomia hirtipetiola C. DC. ( Piperaceae ), and various species of Clermontia Gaudich., Cyanea Gaudich. (both Campanulaceae ), and Cyrtandra J.R. Forst. & G. Forst. ( Gesneriaceae ). Steeper ridges and slopes that edge the plateau are dominated by matting ferns of Dicranopteris Bernh.( Gleicheniaceae ) ( Wood 1997).
Unfortunately, past habitat degradation by introduced pigs ( Sus scrofa L.) has altered the plant composition of the plateau, which is now being dominated by a succession of invasive weeds, which threaten Melicope oppenheimeri , especially Ageratina adenophora (Spreng.) R.M. King & H. Rob. ( Asteraceae ), Buddleja asiatica Lour. ( Scrophulariaceae ), Clidemia hirta (L.) D. Don ( Melastomataceae ), Erigeron karvinskianus DC. ( Asteraceae ), and Tibouchina herbacea (DC.) Cogn. ( Melastomataceae ) ( Wood 1997).
Towering over the plateau and most outstanding, are vertical caldera-like basalt cliffs dominated by a native sedge and grass association called Machaerina Vahl ( Cyperaceae )- Deschampsia P. Beauv. ( Poaceae ) wet cliff community. The cliffs are seeping with springs and waterfalls and strata of past volcanic flows are clearly evident. Additional components of this Waihe‘e cliff community include Sadleria pallida Hook. & Arn., Pipturus albidus (Hook. & Arn.) A. Gray ( Urticaceae ), Eragrostis grandis Hillebr., Isachne distichophylla Munro ex Hillebr. (both Poaceae ), and Dubautia scabra (DC.) D.D. Keck.
Superb examples of Metrosideros - Cheirodendron montane wet forest dominate above these cliffs in association with windswept wet shrublands and occasional bog communities in and around the locality known as Kaho‘olewa Ridge ( Wood 1997). At the base of the cliffs, which enclose the southern perimeter of the plateau lie heaps of basalt talus with accumulated substrates which are moderately deep in sections and appear to be fine textured brown silty clay.
The forests spreading below the plateau are composed of Metrosideros mixed lowland riparian vegetation, which are closed to open in canopy and dissected by deeply carved streams with steep banks 10-30 m in height. The native flora of this lower riparian community has similarities to the cliff-base plateau but with a greater diversity, including Ilex anomala Hook. & Arn. ( Aquifoliaceae ), Perrottetia sandwicensis A. Gray ( Dipentodontaceae ), Polyscias oahuensis (A. Gray) Lowry & G.M. Plunkett ( Araliaceae ), and Pritchardia forbesiana Rock ( Arecaceae ), along with species of Kadua Cham. & Schltdl. ( Rubiaceae ), Myrsine L. ( Primulaceae ), and Psychotria L. ( Rubiaceae ) ( Wood 1997). Notable observations of native birds in the upper Waihe‘e region include nesting seabird colonies of dark-rumped petrels ( Pterodroma sandwichensis Ridgeway) along with native forest birds such as 'apapane ( Himatione sanguinea Gmelin), and 'amakihi ( Chlorodrepanis virens wilsoni Rothschild).
Phylogenetic placement.
Melicope oppenheimeri , like all Hawaiian Melicope , falls into section Pelea , which has a distribution ranging from Taiwan, the Philippines, and Borneo eastward to the Hawaiian and Marquesas Islands, and south to New Caledonia. Only Melicope triphylla (Lam.) Merr. is distributed in the Southeast Asian areas mentioned above, and the remainder of sect. Pelea is restricted to New Guinea and Pa cific archipelagos ( Hartley 2001). Section Pelea proved to be polyphyletic in molecular phylogenetic analyses, and monophyly can be reached if the New Caledonian species are excluded and the Hawaiian endemic genus Platydesma is included in the section ( Appelhans et al. 2014b). Hartley (2001, pp. 31, 139-140) stated that the Hawaiian species mostly resemble the New Caledonian species - especially Melicope vieillardii - based on several “primitive” characters including bisexual flowers, persistent sepals and petals, apically acute staminal filaments, basally connate carpels, glabrous endocarp, and Type A seed attachment, however, a close phylogenetic relationship of the Hawaiian and the New Caledonian species could not be verified ( Appelhans et al. 2014b). The Hawaiian species of Melicope have been treated under the genus Pelea by Wagner et al. (1990) and the authors divided the taxon into the four sections Apocarpa B. Stone; Cubicarpa B. Stone; Megacarpa B. Stone; and Pelea . If the Hawaiian groups are to continue to be recognized, they would need to be treated as subsections. Only the latter of these sections, which consists of three species, proved to be monophyletic ( Appelhans et al. 2014b, c). Two specimens of Melicope oppenheimeri (the paratypes Wood & Perlman 7408 and Wood & Perlman 7419) have been included in phylogenetic research ( Appelhans et al. 2014b, c) and they are listed under the original determination Melicope reflexa (H. St. John) T.G. Hartley & B.C. Stone in these studies. The two specimens are part of a largely unresolved clade consisting of representatives of Cubicarpa and Megacarpa . The closest relatives of Melicope oppenheimeri could not be determined due to the low genetic variation in the sampled nuclear and plastid markers. We are currently working on resolving phylogenetic relationships of Hawaiian Melicope using Next-generation sequencing.
Morphology and related taxa.
Although beaked fruit have evolved in a few species of Melicope belonging to sections Melicope and Vitiflorae ( Hartley 2001, p. 19), this character is unique to Melicope oppenheimeri within sect. Pelea (Figure 1C View Figure 1 , 5B View Figure 5 ). Beaked fruit have also evolved in Hawaiian Platydesma sect. Cornutia B.C. Stone, which is nested within Melicope sect. Pelea , but which is not an immediate relative of Melicope oppenheimeri .
Morphologically, Melicope oppenheimeri resembles the Moloka‘i endemic species Melicope reflexa , with both having reflexed carpels that are coherent at base. Significant differences between Melicope oppenheimeri and Melicope reflexa include capsules connate 1/5, 4-9 × 40-52 mm (vs. capsules connate 1/4, 10-17 × 20-33 mm); endocarp sparsely to evenly puberulent (vs. endocarp glabrous); ovary appressed densely short-sericeous (vs. ovary glabrous); pedicles 5-8 mm (vs. pedicles15-20 mm); and flowers perfect, 3-5, on robust peduncles (vs. flowers unisexual, 1-3, on delicate peduncles).
Two other morphologically similar Hawaiian Melicope , also with carpels coherent at base include Melicope molokaiense (Hillebr.) T.G. Hartley & B.C. Stone and Melicope volcanica (A. Gray) T.G. Hartley & B.C. Stone. Melicope molokaiense , which is known from Molokai and Maui, differs from Melicope oppenheimeri in having capsules connate 1/4, 10-17 × 21-39 mm; endocarp glabrous; ovary glabrous; and flowers unisexual. Melicope volcanica , which is known from Lana‘i, Moloka‘i, East Maui, and the big island of Hawai‘i, similarly differs with capsules connate 1/3-1/4, and flowers unisexual, yet also differs with leaves having 10-20 pair of secondary veins; cymes ca. 6 cm long; and peduncles 7-38 mm long. Melicope oppenheimeri has leaves with 7-10 pair of secondary veins; cymes ca. 3 cm long; and peduncles 5-6.5 mm long.
Melicope species are generally either exclusively hermaphroditic or dioecious, yet there are a few recorded exceptions ( Hartley 2001, p. 10). Although Melicope oppenheimeri is apparently hermaphroditic, we cannot make a definitive statement on the breeding system of this rare narrow endemic, having only six collections for study, and limited flowering material.
Conservation status.
Plant and animal endemics from isolated oceanic islands are often endangered or critically endangered ( Kreft et al. 2008, Sakai et al. 2002). The ongoing decline of native pollinators ( Kearns et al. 1998) and seed dispersers ( Milberg and Tyrberg 1993), in combination with other primary extrinsic factors such as invasive non-native plants, predation by introduced vertebrates, loss and fragmentation of natural habitats, and devastation by severe storms, are leading to an increase in extinctions throughout the islands of Oceania ( Sakai et al. 2002, Wood 2007, 2012, Kingsford et al. 2009). Other prominent factors such as strict habitat requirements, very low historic population densities and narrow geographic range increase the risk of extinction. ( Sakai et al. 2002, Wood 2007, 2015). It is currently unclear how many of the estimated 10,000 native Hawaiian insect species have gone extinct, but at this point in time the Hawaiian Islands have lost 79 of its native bird species and are left with only 32 ( James and Olson 1991, Olson and James 1991, Burney et al. 2001, Boyer 2008). The authors maintain a checklist of endemic Hawaiian vascular plant taxa that have no known wild individuals remaining. Of the estimated 1191 native vascular plant species in Hawai‘i, 130 taxa are now presumed extinct. Evidently 41 of these possible extinctions have occurred in the Hawaiian lobeliads ( Campanulaceae ), a family renowned for their co-evolution with Hawai‘i’s unique forest birds, the honeycreepers, in the endemic subfamily Drepanidinae of the Fringillidae or finch family ( Wood 2014, 2015). The Lamiaceae or mint family falls second in this severe category, with 22 species that are presumed extinct. With two-thirds of the surviving forest bird species in Hawai‘i being critically endangered and a continued decline in native arthropods, there is grave concern for the endangered Hawaiian flora and for their unique insular relationships with biodiversity as a whole. Even today, little is known about the life cycles, breeding system variations, and habitat preferences found in the Hawaiian flora ( Sakai et al. 2002, Wood 2015), but it is known that Melicope rely on insects for pollination and birds for dispersal ( Hartley 2001). Within Hawaiian Melicope five species are currently presumed extinct, 19 are federally listed as endangered, and with the inclusion of Melicope oppenheimeri , ten species fall into the Plant Extinction Prevention Program (PEPP) category, meaning there are 50 or fewer individuals remaining (see Table 1 View Table 1 ). Members of Hawaiian Rutaceae are currently in the process of being evaluated according to IUCN categories and criteria.
IUCN Red List Category. When evaluated using the World Conservation Union (IUCN) criteria for endangerment (IUCN 2001), Melicope oppenheimeri falls into the Critically Endangered (CR) category, which designates this species as facing a very high risk of extinction in the wild. Our formal evaluation can be summarized by the following IUCN hierarchical alphanumeric numbering system of criteria and subcriteria: CR B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C2a(ii); D; which reflects a severely limited Extent of Occurrence (EOO) and Area of Occupancy (AOO) of less than 1 km2 and a wild population of only three individuals. It should be noted that seed collections of Melicope oppenheimeri have been made by Maui PEPP staff during routine monitoring and there is currently a single cultivated individual being grown at the Olinda Rare Plant Facility on East Maui.
No known copyright restrictions apply. See Agosti, D., Egloff, W., 2009. Taxonomic information exchange and copyright: the Plazi approach. BMC Research Notes 2009, 2:53 for further explanation.
Kingdom |
|
Phylum |
|
Class |
|
Order |
|
Family |
|
Genus |