Ker Gawl., Zingiberaceae |
Present on Pacific Islands? yes
Primarily a threat at high elevations? no
Risk assessment results:
Hawaii/Pacific: High risk, score: 19 (Go to the risk assessment)
Risk assessment from the Government of Queensland, Australia (PDF format)
Common name(s): [more details]
English: Himalayan ginger, Kahili ginger, ginger-lily, kāhili ginger, kahili ginger-lily, wild ginger, yellow ginger |
Fijian: cevuga dromodromo |
French: gingembre-douleur, longose, longose de Gardner |
Hawaiian: awapuhi kahili, kāhili |
Maori (Cook Islands): kōpī |
Pohnpeian: sinter weitahta |
Habit: herb
Description: "Coarse herbs with leafy shoots 1-2 m tall. Leaves ovate-elliptic, 20-45 cm long, 10-15 cm wide, glabrous or sparsely pubescent along midrib on lower surface, apex short-acuminate, petioles 1-2 cm long, ligules membranous, 1.5-3 cm long, entire or very shallowly 2-lobed, glabrate, sheaths glabrous or glabrate. Inflorescences erect, cylindrical, 16-30 (-45) cm long, primary bracts widely spaced, ovate-elliptic, spreading or obliquely ascending, enfolding the cincinni, much shorter than the floral tube, 3-5 cm long, glabrous, rachis glabrous, exposed, cincinni 2-flowered; calyx cylindrical, 3-lobed, 3-3.5 cm long; corolla yellow, the tube longer than the primary bract, 5-5.5 cm long, the lobes greenish yellow, linear, 3.5-5 cm long; labellum centrally tinged orange, 2.5-3 cm long; stamen bright reddish orange, far exceeding labellum, ca. 6.5 cm long; lateral staminodes yellow, ca. 3 cm long; ovary glabrous. Capsules oblong, ca. 1.5 cm long, the valves orange within. Seed red, 5-6 mm long" (Wagner et al., 1999; p. 1623).
Habitat/ecology: "Forests and forest edges, moist places. This tall herb spreads rapidly and may become dominant over large areas, especially under canopy openings or in cleared areas. It forms dense thickets that penetrate into undisturbed forests and impede the growth and regeneration of native plants. Seedlings of shrubs and trees are unable to establish in stands of this plant. Once established, the plant is shade-tolerant and very persistent" (Weber, 2003; p. 194). See also H. coronarium and H. flavescens.
The plant grows in wet habitats between sea level and 1,700 m (Smith, 1985; pp. 191-192). In New Zealand, "spreading on roadsides and damp places, very common about Auckland" (Healy & Edgar, 1980; p. 42).
Propagation: By stolons where already established. Conspicuous, fleshy, red seeds are dispersed by frugivorous birds as well as man. Even small root fragments will regrow (Smith, 1985; pp. 191-192).
Native range: Bhutan, India (Assam, Sikkim), Nepal; naturalized elsewhere; widely cultivated in tropics (GRIN).
Presence:
Pacific | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
Cook Islands
Southern Cook Islands |
Mangaia Island |
cultivated
|
McCormack, Gerald (2013) |
Cook Islands
Southern Cook Islands |
Mangaia Island |
introduced
cultivated |
Space, James C./Flynn, Tim (2002) (p. 86) |
Cook Islands
Southern Cook Islands |
Rarotonga Island |
cultivated
|
McCormack, Gerald (2013) |
Cook Islands
Southern Cook Islands |
Rarotonga Island |
Bishop Museum (Honolulu) (1990) (voucher ID: BISH 664890)
Taxon name on voucher: Hedychium gardnerianum Ker Gawl. |
|
Federated States of Micronesia
Pohnpei Islands |
Pohnpei Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 113) |
Federated States of Micronesia
Pohnpei Islands |
Pohnpei Island |
introduced
cultivated |
Herrera, Katherine/Lorence, David H./Flynn, Timothy/Balick, Michael J. (2010) (p. 63) |
Fiji
Fiji Islands |
Viti Levu Island |
introduced
cultivated |
Smith, Albert C. (1979) (p. 198)
Voucher cited: DA 12338 |
French Polynesia
Society Islands |
Tahiti Island |
introduced
|
Fosberg, F. R. (1997) (p. 154) |
French Polynesia
Society Islands |
Tahiti Island |
introduced
cultivated |
Florence, J./Chevillotte, H./Ollier, C./Meyer, J.-Y. (2013)
Cultivée |
State of Hawaii
Hawaiian Islands |
Hawaii (Big) Island |
introduced
invasive cultivated |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (p. 1623)
Voucher cited: Fagerlund & Mitchell 743 |
State of Hawaii
Hawaiian Islands |
Kauai Island |
introduced
invasive cultivated |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (p. 1623) |
State of Hawaii
Hawaiian Islands |
Lānai Island |
introduced
invasive cultivated |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (p. 1623) |
State of Hawaii
Hawaiian Islands |
Maui Island |
introduced
invasive cultivated |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (p. 1623) |
State of Hawaii
Hawaiian Islands |
Oahu Island |
introduced
invasive |
Staples, George W./Herbst, Derral R./Imada, Clyde T. (2006) (p. 9)
Vouchers cited: B. Kennedy et al. 42 (BISH), C. Imada et al. 2004-58 (BISH) |
New Caledonia
New Caledonia Archipelago |
Île Grande Terre |
introduced
cultivated |
MacKee, H. S. (1994) (p. 142)
Voucher cited: MacKee 34886 |
Pacific Rim | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
Australia
Australia (continental) |
New South Wales |
introduced
invasive |
National Herbarium of New South Wales (2013)
Naturalised |
Australia
Australia (continental) |
Australia (continental) |
introduced
invasive |
National Herbarium of New South Wales (2013)
Naturalised |
Australia
Australia (continental) |
Queensland |
introduced
invasive |
Queensland Herbarium (2002) (p. 4) |
China
China |
Hong Kong |
introduced
cultivated |
Wu, Te-lin (2001) (p. 353)
Ornamental. |
New Zealand
New Zealand |
New Zealand (country) |
introduced
invasive |
Healy, A. J./Edgar, E. (1980) (p. 42)
Voucher cited: Lloyd (AK 25040) |
New Zealand
New Zealand |
New Zealand (country) |
introduced
invasive |
Owen, S. J. (1997) |
Indian Ocean | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
La Réunion (France)
La Réunion Island |
La Réunion Island |
introduced
invasive |
MacDonald, I. A. W./Thebaud, C./Strahm, W. A./Strasberg, D. (1991) (pp. 51-61) |
La Réunion (France)
La Réunion Island |
La Réunion Island |
introduced
invasive |
Lavergne, Christophe (2006)
"Très envahissant" |
La Réunion (France)
La Réunion Island |
La Réunion Island |
introduced
invasive |
Baret, Stephane/Rouget, Mathieu/Richardson, David M./Lavergne, Christophe/Egoh, Benis/Dupont, Joel/Strasberg, Dominique (2006) (p. 758) |
Mascarene Islands
Mascarene Islands (Mauritius, La Reunion, Rodrigues) |
Mascarene Islands |
introduced
|
U.S. Dept. Agr., Agr. Res. Serv. (2013) |
Comments: A major invader of native forests in New Zealand. Also a problem species in South Africa and La Réunion.
Control:
Physical: Dig out, pull seedlings and regrowth. Do not compost roots.
Chemical: Treat with herbicide. Escort 25 gm/100 l water + 0.1% Pulse; Roundup 2% +0.2% Pulse; Amitrole (Timmins and Mackenzie, 1995; pp. 127-129.
"1. Cut down and paint stump (all year round): cut above
pink 'collar' at base and apply or glyphosate (250ml/L) or metsulferon-methyl
600g/kg (1g /L). Leave stems and leaves on site to rot down.
2. Dig or pull out small plants (all year round). Don't compost, leave on site
to rot down or hang rhizomes in trees, as they survive indefinitely. Dispose of
rhizomes at a refuse transfer station or by drying out and burning.
3. Spray (all year round): metsulferon-methyl 600g/kg (5g/10L knapsack). Add
penetrant in winter. For dense patches keep spray away from roots of vulnerable
plants. Don't replant sprayed sites for 6 months" (Weedbusters New Zealand).
Biological: In Hawaii, "Anderson and Gardner (1999) have studied a strain of Ralstonia solanacearum (E.F.Smith) Yabuuchi et al. (Bacteria, Pseudomonaceae) that attacks kahili ginger. They expressed considerable optimism that this fungus has the potential to bring about long term control of this pest including the suppression of seedling establishment. The slow-acting nature of this pathogen may be beneficial in that native species will have a chance to recover before weeds overwhelm them. The establishment of the bacterium is somewhat difficult generally requiring physical damage. Nevertheless, the bacterium has been established in some populations in the Islands. Evidence suggests that the density of plants in these areas is declining. Perhaps the most encouraging aspect of this disease is that seeds do not germinate or damp off soon thereafter where the bacterium is present in the soil. EPA approval may be required before the fungus can be broadcast as a biocide. In the meanwhile, use of this pathogen is limited to local application only though experiments on mass culture, optimal dosage, and alternative inoculation techniques are underway. A potential conflict of interest is that it attacks edible ginger (Zingiber officinele Roscoe - Zingiberales, Zingiberaceae). The difficulty of dissemination and establishment of the bacterium suggests that this concern is not a significant problem. The infestations of kahili ginger are well above the areas were ginger is grown commercially" (Smith et al., 2002; p. 95).