(DRAFT) - Taxonomy
                               Species BIDENS, CUNEATE
                                Species Id ESIS701026
                                   Date 13 MAR 96



TAXONOMY

NAME - BIDENS, CUNEATE OTHER COMMON NAMES - BIDENS and CUNEATE ELEMENT CODE - CATEGORY - Angiosperm PHYLUM AND SUBPHYLUM - MAGNOLIOPHYTA, CLASS AND SUBCLASS - MAGNOLIOPSIDA, ORDER AND SUBORDER - ASTERALES, FAMILY AND SUBFAMILY - ASTERACEAE, GENUS AND SUBGENUS - BIDENS, SPECIES AND SSP - CUNEATA, SCIENTIFIC NAME - BIDENS CUNEATA AUTHORITY - TAXONOMY REFERENCES - COMMENTS ON TAXONOMY - Cuneate Bidens Bidens cuneata Sherff KINGDOM: Plant GROUP: Angiosperm DIVISION: Magnoliophyta CLASS: Magnoliopsida ORDER: Asterales FAMILY: Asteraceae Decumbent, spreading herb generally less than 1 m ht. Leaves simple, rhomboidovate, toothed, acute at apex, 2.5 - 5 cm long, 1 - 2.5 cm wide. Flower heads yellow, solitary on peduncles 7-19 cm long Ray florets about 7-10, 17-25 mm long, 9-11 mm wide. Disc florets generally 13-33. Achenes straight, black, wingless, glabrous or slightly hairy on margin, 6-12 mm long (01,02). Bidens cuneata was described by E.E. Sherff in 1920 (03). It closely resembles B. mauiensis and B. molokaiensis because of its sprawling habit, simple leaves and solitary flower heads, but can be distinguished from the former by its wingless achenes, and from the latter by leaf shape and serration. Recent experiments in hybridization by Gillett and Lim (04) have shown that interspecific hybrids among Hawaiian Bidens can be readily induced and the resulting highly fertile progeny is indicative of a general lack of genetic barriers within the group. They concluded that B. cuneata was a Taxonomy - 1 (DRAFT) - Taxonomy Species BIDENS, CUNEATE Species Id ESIS701026 Date 13 MAR 96 natural hybrid between B. molokaiensis and the simple leaf form of B. mauiensis (var. cuneatoides) despite the fact that one parent occurs on Molokai, the other on Maui and the presumed hybrid on Oahu. Thus it was proposed that B. cuneata be reduced to hybrid status with the hybrid formula B. mauiensis var. cuneatoides x B. molokaiensis (05). Alternatively, the taxon may be simply denoted as B. x cuneata (06). More recently, extensive hybridization experiments, chemotaxonomic analyses and greenhouse observations attendant to a monographic revision of the Hawaiian Bidens have revealed that Bidens cuneata is in fact identical to B. molokaiensis (07). After numerous repetitions of Gillett's crosses between the two presumed parents and close examination of his experimental vouchers, it was concluded that Gillett's presumed hybrids upon which his conclusions were formulated were mostly accidental self-fertilizations. In addition, the supposed differences between "B. cuneata" and B. molokaiensis disappear when grown under the same conditions. The status of B. molokaiensis was listed by Fosberg & Herbst (08) as "uncertain" with insufficient information for formal status determination. It subsequently has never been proposed for Endangered or Threatened status by USFWS. In addition to the very small population on Diamond Head, small populations occur on the sea cliffs on the north coast of Molokai from Hoolehua east to Halawa (02,07). One specimen has been seen from Kahoolawe (02). It is believed that the population(s) on Kahoolawe is (are) probably as precarious as the one on Diamond Head (02). Although no formal survey has been conducted to determine the size, extent and status of the Molokai populations, repeated visits to several sites in conjunction with the monographic treatment presently in progress indicate that perhaps a "Threatened" status for B. molokaiensis may be appropriate. Type Specimen: Oahu, Diamond Head. Bryan, sn (BISH) Additional Specimens: 1 Oahu, Diamond Head, on arid, windswept crest of NW rim. Elev. 400' C. Lamoureax, E. Ozaki & K. Kosaki. 8 April 1955 (HAW). 2 Oahu, Diamond Head, on outer north slope just below crater rim. C. Lamoureax. 5 March 1969 (HAW). 3 Oahu, Diamond Head, 200 m north of highest peak at west end of crater. Elev. 700'. C. Lamoureaux, D. Herbst & H. St. John. 7 March 1969 (HAW). 4 Oahu, Diamond Head, inside portion of crater rim, sw portion of Leahi Peak. Elev. 700'. K.M. Nagata. 1 March 1971 (HLA). 5 Oahu, Diamond Head, interior slope of seaward crest on steep, rocky incline exposed to strong winds. G.W. Gillett. 28 July 1971 (BISH HLA). References: (04,05,07,09,10,11). Taxonomy - 2
                                  (DRAFT) - Status
                               Species BIDENS, CUNEATE
                                Species Id ESIS701026
                                   Date 13 MAR 96



STATUS

Coded Status E: Federal Endangered COMMENTS ON STATUS - U.S. STATUSES AND LAWS: Cuneats biden< (Bidens cuneata$ ha< bee$ designateS a$ Endangered species pursuant to the Endangered Species Act of 1973 (50 CFR 17.12; P.L. 93-205, 87 Stat. 884; 16 U.S.C. 1531-1540), as amended. The species has this status wherever found including the State of Hawaii. This species is protected by the Lacey Act (P.L. 97-79, as amended; 16 U.S.C. 3371 et seq.) which makes it unlawful to possess any wild plant (including roots, seeds, and other parts) within U.S. territorial or special maritime jurisdiction (as defined in 18 U.S.C. 7); or to import, export, transport, sell, receive, acquire, or purchase in interstate or foreign commerce any wild plant (including roots, seeds, and other parts) taken, possessed, transported, or sold in violation of any State law or regulation. It is also unlawful to import, export, transport, sell, receive, acquire, or purchase any wild plant (including roots, seeds, and other parts) taken or possessed in violation of any U.S. law, treaty, or regulation or in violation of Indian tribal law. RESPONSIBLE FEDERAL AGENCIES: USFWS -Responsible for the management/recovery, listing, and law enforcement/protection of this species. All Federal agencies have responsibility to ensure that any action authorized, funded, or carried out by that agency is not likely to jeopardize the continued existence of the species or result in the destruction or adverse modification of Critical Habitat (50 CFR 402), and to utilize their authorities to carry out programs for the conservation of the species. STATE STATUSES AND LAWS: STATE: Hawaii DESIGNATED STATUS: Endangered ADMINISTRATIVE AGENCY: State Dept. of Land and Natural Resources STATE STATUTE: Hawaii Rev. Stat., Chapter 195D INTERNATIONAL STATUSES, TREATIES, AND AGREEMENTS: None. ECONOMIC STATUSES: None known. Status - 1 (DRAFT) - Status Species BIDENS, CUNEATE Species Id ESIS701026 Date 13 MAR 96 75/07/01:40 FR 27823/27924 - Notice of review 76/06/16:41 FR 24523/24572 - Proposed rule 78/04/26:43 FR 17909/17916 - Summary of comments on proposed rule 79/12/10:44 FR 70796/70797 - Withdrawal of proposed rule 82/08/23:47 FR 36675/36678 - Reproposed as endangered 84/02/17:49 FR 06099/06101 - Final rule 85/09/27:50 FR 39526/39527 - Notice of Review Status - 2
     

HABITAT ASSOCIATIONS

HABITAT - TERRESTRIAL TERRESTRIAL LAND USE - Bare Exposed Rock COMMENTS ON HABITAT ASSOCIATIONS - The single remaining population of Bidens cuneata is found near the crest of the north-facing inner slopes of the southwest wall of Diamond Head crater at approximately 700 ft (213 m) elevation. The soils of Diamond Head have been classified as "rock land" which is characterized by extensive rock outcrops, steep to precipitous slopes that are well drained or excessively drained and the presence of only very shallow soil (12). The colony is situated in a pocket of very shallow soil on a very steep slope with excessive drainage (02). Although few other shrubs grow in the habitat area, those species that are able to survive are well adapted for arid conditions and are aggressive. Scrubby Leucaena leucocephala and Waltheria americana are the predominant shrubs and Tridax procumbens, Sonchus oleraceus and Pennisetum setaceum comprise the herb layer (01,02). Vegetational cover during the rainy season may approach 100 percent in vegetated areas but during prolonged dry spells most of the plants are dessicated and defoliated. Bidens cuneata constitutes less than 1 percent of the vegetation in the habitat (02). Bidens cuneata is easily grown under greenhouse conditions with no special attention other than maximum sunlight and adquate drainage indicating minimal edaphic and climatological requirements (02). Habitat Associations - 1
                                (DRAFT) - Food Habits
                               Species BIDENS, CUNEATE
                                Species Id ESIS701026
                                   Date 13 MAR 96



FOOD HABITS

TROPHIC LEVEL - AUTOTROPH Food Habits - 1
                         (DRAFT) - Environment Associations
                               Species BIDENS, CUNEATE
                                Species Id ESIS701026
                                   Date 13 MAR 96



ENVIRONMENTAL ASSOCIATIONS

G = General A = Adult LIM = Limiting RA = Resting Adult J = Juvenile FA = Feeding Adult RJ = Resting Juvenile BA = Breeding Adult FJ = Feeding Juvenile P = Pupae L = Larvae E = Egg RL = Resting Larvae FL = Feeding Larvae
LIFESTAGE ENVIRONMENTAL ASSOCIATIONS G Coastal Features: Vegetated offshore islands G Terrestrial Features: Bottomland G Terrestrial Features: Cliffs/ledges G Terrestrial Features: Rock outcrops G Environment Associations - 1
                               (DRAFT) - Life History
                               Species BIDENS, CUNEATE
                                Species Id ESIS701026
                                   Date 13 MAR 96



LIFE HISTORY

HABIT: Bidens cuneata is a shrub (01,02,03,07,09,10,11). LIFE CYCLE: Perennial (02). TYPE OF REPRODUCTION: Sexual (02). REPRODUCTIVE PHENOLOGY: Germination, leafing, and budding dates are unknown. Flowering, fruiting and seed/fruit dispersal occur between December and July (01). SEX OR SPORE STATUS: Monoecious (01). POLLINATION, SPORE AND SEED DISSEMINATION: Pollen dissemination is accomplished through insects. Seed dissemination is due to the wind (01,02). SEED BIOLOGY: Not known, although seed germination of most Hawaiian species of Bidens is not known to be difficult under greenhouse conditions (02). Seedlings have been observed in the wild but survival is minimal (01, 02). POPULATION BIOLOGY: A single extant colony is known from the steep inside slopes of Diamond Head crater. Only two census of the population are known to have been conducted. In February 1979, 10 established individuals and 16 seedlings were counted in an area appoximately 15 m in diameter. In May 1980 less than 10 established plants and no seedlings were counted in a strip 1.5 m in length (01). Although the factors responsible for the population dynamics and seedling mortality have not been identified, seasonal drought and encroachment by aggressive exotic species are believed to be involved (02). Collections of B. cuneata have been made in other sites along the crater rim and herbarium labels indicate that these colonies were generally larger than the one presently known. These facts suggest a pattern of general decline but the overall impression obtained from available sources of information is that the total population has always been small and highly localized (01). The extent of its reproductive success and recovery potential appears minimal because of the extirpation of historically known colonies, the fact that B. cuneata has never been found outside its historic range, and the fact that the population has always been small (01). ECOLOGICAL/EDAPHIC FACTORS: The soils of Diamond Head have been classified as "rock land" by the USDA (12). Diamond Head soils consist largely of former volcanic Life History - 1 (DRAFT) - Life History Species BIDENS, CUNEATE Species Id ESIS701026 Date 13 MAR 96 ash and lapilli altered to palagonite and also talus breccia (13). Thin pockets of eroded ash and accumulated litter are found on ledges and outcrops on the steep crater walls. The colony is situated at approximately 215 m elevation on the steep north-facing slope exposed to the prevailing trade winds. Although the region receives an annual rainfall of approximately 76 m (14) the available soil moisture is thought to be correspondingly less because of excessive drainage and thin soils. Most of the rainfall occurs during the winter and early spring with only 5-10 cm occurring between April and September (15). The environmental impacts of dessicating prevailing winds, low rainfall with severe summer drought and relatively little available soil moisture are profound, especially during the summer when the temperature is generally highest. Although the average annual temperature at Waikiki approximately one mile west of Diamond Head is 24.5 degrees Celsius (16) the actual temperature inside the crater is probably higher due to insolation and large doses of incident radiation unimpeded by topographic or vegetative interception. TROPHIC STATUS: Phototrophic (02). CHARACTERISTIC DOMINANCE: Component (02). COMMUNITY ECOLOGY: Almost nothing is known of the ecology of the associated plant community. The vegetation is composed of common, exotic, drought resistant species (01). No successional trends have been determined. SPECIES INTERRELATIONSHIPS: None. OTHER LIFE HISTORY DESCRIPTORS: None. Life History - 2
                           (DRAFT) - Management Practices
                               Species BIDENS, CUNEATE
                                Species Id ESIS701026
                                   Date 13 MAR 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Beneficial Suppressing wildfire Beneficial Restricting/regulating human disturbance of populations Beneficial Maintaining Early Stages of Succession Beneficial Maintaining Sperm/Seed Banks Beneficial Stocking captive-reared wild-strain animals Beneficial Transplanting Wild Eggs/Wild Seeds Beneficial Restricting Poaching Adverse Incidental Capturing/Killing Existing Incidental Capturing/Killing Adverse Collecting Existing Collecting Adverse Hiking/Camping Existing Hiking/Camping Adverse Low Gene Pool Existing Low Gene Pool Adverse Soil compaction by heavy equipment in mine areas Existing Soil compaction by heavy equipment in mine areas Adverse Competition Existing Competition Adverse Exotic/Feral/Introducted Species Existing Exotic/Feral/Introducted Species Adverse Erosion Existing Erosion Adverse Vegetation Composition Changes Existing Vegetation Composition Changes COMMENTS ON MANAGEMENT PRACTICES - Direct, man-induced threats were probably not significant until after 1906, due to the relative isolation of the habitat. In subsequent years, however, extensive military construction occurred in the habitat area and although the direct impact of these activities is unknown, it is plausible that uncharted populations may have been destroyed and aggressive weed species proliferated because of such disturbance. In more recent times a popular hiking trail has been established around the rim of the crater. The presence of this trail remains a constant and significant threat to the population as all reported sightings of B. cuneata has occurred at or near the crest of the crater rim and along the trail. Thus, habitat deterioration due to trampling of plants, soil compaction and promotion of erosion, rockfall and landslide remains a constant threat to the population. Encroachment by aggressive exotic species also represents a possible threat to the population. Only one species found in association with B. cuneata is native. The most recent census (1980) indicates that the taxon is restricted to a single colony of less than 10 established plants (01). The gene pool is thus severely limited and it is doubtful whether the remaining population possesses sufficient diversity to enable it to survive a serious environmental challenge. Finally, over collecting by zealous professional botanists and amateur Management Practices - 1 (DRAFT) - Management Practices Species BIDENS, CUNEATE Species Id ESIS701026 Date 13 MAR 96 naturalists may also threaten the integrity of the colony. Judging from the few collections available, the evidence seems to be to the contrary. However, the collections of amateurs and unscrupulous collectors do not usually find their way into herbaria (01,02). No future potential threats are perceived at this time. UNAPPROVED PLAN: At the present time, there is no approved recovery plan. Management actions that are recommended for the recovery of the Cuneate Bidens include: 1) protection of the plant from accidental or intentional damage due to trampling by hikers or vandalism; 2) artificial propagation to increase its numbers; 3) establishment of several other populations along the rim of Diamond Head crater; 4) maintenance of early successional stages of the transplants until they become established; 5) development of a plan to protect the new colonies against trampling vandalism, and fires; 6) monitor the species; 7) maintain a representative sample of the gene pool in the form of a cultivated population and/or stored seed; and 8) Restrict poaching of existing and future populations. The State Division of Forestry and Wildlife plans to propagate the plant and establish new populations on Diamond Head. As the species is presently being cultivated at the University of British Columbia, parent stock is available and propagation techniques are known. Management Practices - 2
                                   (DRAFT) - References
                                 Species BIDENS, CUNEATE
                                  Species Id ESIS701026
                                      Date 13 MAR 96



     

References

References - 1 (DRAFT) - References Species BIDENS, CUNEATE Species Id ESIS701026 Date 13 MAR 96 ***** REFERENCES FOR ALL NARRATIVES EXCEPT N-OCCURRENCE ***** 01 Takeuchi, W. 1980. Unpublished status report on Bidens cuneata Sherff. U.S. Fish and Wildl. Serv., Honolulu, HI. 02 Nagata, K.M. Pers. observ. Lyon Arboretum, Honolulu, HI 96822. 03 Sherff, E.E. 1920. Studies in the genus Bidens V. Bot. Gaz. 70:102. 04 Gillett, G.W. and E. Lim. 1970. An experimental study of the genus Bidens (Asteraceae) in the Hawaiian Islands. Univ. Cal. Publ. Bot. 56:1-63. 05 Gillett, G.W. 1975. The diversity and history of Polynesian Bidens section Campylotheca. Harold L. Lyon Arboretum, Honolulu, HI. 32 pp. 06 St. John, H. 1973. List and summary of the flowering plants in the Hawaiian Islands. Pac. Trop. Bot. Gard. Memoir No. 1. Lawai. 519 pp. 07 Ganders, F.R. and K.M. Nagata. In prep. Monograph of the Hawaiian species of the genus Bidens. 08 Fosberg, F.R. and D. Herbst. 1975. Rare and endagered species of Hawaiian vascular plants. Allertonia 1(1):1-72. 09 Sherff, E.E. 1937. The genus Bidens. Field Mus. Nat. Hist. Publ. 388. Chicago. 163 pp. 10 Degener, O. 1940. Flora Hawaiiensis Fam. 344. Bidens cuneata. 11 Kimura, B. and K.M. Nagata. 1980. Hawaii's vanishing flora. Orietal Publ. Co. Honolulu, HI. 88 pp. 12 Foote, D.E., et al. 1972. Soil survey of the islands of Kauai, Oahu, Maui, Molokai, and Lanai, State of Hawaii. USDA. 13 Macdonald, G.A. and A.T. Abbott. 1970. Volcanoes in the sea. Univ. Press of Hawaii. Honolulu. 441 pp. 14 State of Hawaii. 1973. Climatologic stations in Hawaii. Dept. of Land and Natural Resources. Report R42. 187 pp. 15 State of Hawaii. 1959. Rainfall of the Hawaiian Islands. Hawaii Water Authority. n.p. 16 United States. 1983. Climatoligical data. Annual summary. Hawaii and the Pacific. NOAA 79(13). ***** REFERENCES FOR N-OCCURRENCE NARRATIVE ONLY ***** 01 Takeuchi, W. 1980. Unpublished status report on Bidens cuneata Sherff. U.S. Fish and Wildl. Serv., Honolulu, HI. 02 Sherff, E.E. 1920. Studies in the genus Bidens V. Bot. Gaz. 70:102. 03 Gillett, G.W. and E. Lim. 1970. An experimental study of the genus Bidens (Asteraceae) in the Hawaiian Islands. Univ. Cal. Publ. Bot. 56:1-63. 04 Sherff, E.E. 1937. The genus Bidens. Field Mus. Nat. Hist. Publ. 388. Chicago, IL. 163 pp. 05 Degener, O. 1940. Bidens cuneata. Flora Hawaiiensis Fam. 344. 06 Kimura, B. and K.M. Nagata. 1980. Hawaii's vanishing flora. Oriental Publ. Co., Honolulu, HI. 88 pp. References - 2