Livistona chinensis (Chinese fan palm)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Description
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat
- Habitat List
- Hosts/Species Affected
- Biology and Ecology
- Climate
- Air Temperature
- Rainfall
- Soil Tolerances
- Natural enemies
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Environmental Impact
- Threatened Species
- Risk and Impact Factors
- Uses
- Uses List
- Similarities to Other Species/Conditions
- Prevention and Control
- References
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Livistona chinensis (Jacq.) R. Br. ex C. Mart.
Preferred Common Name
- Chinese fan palm
Other Scientific Names
- Chamaerops biroo Siebold ex Mart.
- Latania chinensis Jacq.
- Livistona japonica Nakai ex Masam.
- Livistona oliviformis (Hassk.) Mart.
- Livistona subglobosa (Hassk.) Mart.
- Saribus chinensis (Jacq.) Blume
- Saribus oliviformis Hassk.
- Saribus subglobosus Hassk.
International Common Names
- English: Chinese fountain palm; fountain palm
- Spanish: livistona de China; palma abanico; palma china
- French: palmier éventail de Chine
- Chinese: pu kui
- Portuguese: falsa-latânia; palmeira-leque-da-China
Local Common Names
- French Polynesia: palmier fontaine
- Italy: palma da capelli
- Japan: biro
EPPO code
- LIVCH (Livistona chinensis)
Summary of Invasiveness
Top of pageLivistona chinensis is a palm tree that has been widely introduced into tropical and warm temperate regions of the world to be used as ornamental. It has escaped from cultivation and become naturalized in disturbed sites, but also in undisturbed natural areas. L. chinensis produces a large amount of fruits and has high germination rates. It grows by forming dense thickets that can crowd out and overshadow native species. Currently, it is listed as invasive in Hawaii, Florida, Bermuda, Mauritius, Reunion and New Caledonia. In Florida, L. chinensis is listed as a category II invasive plant, a category designed for species with the potential to disrupt native plant communities.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Monocotyledonae
- Order: Arecales
- Family: Arecaceae
- Genus: Livistona
- Species: Livistona chinensis
Notes on Taxonomy and Nomenclature
Top of pageThe family Arecaceae includes 188 genera and 2585 species of perennial climbers, shrubs and trees (commonly known as palm trees) distributed across the tropics and warm temperate regions of the world (Stevens, 2012). The genus Livistona is included in the subfamily Coryphoideae and is one of the most ecologically diverse and widespread genera of palms. Livistona is distributed across Africa and southern Arabia, southeastern and eastern Asia, Malesia and Australia. Because of this extensive distribution, Livistona has received uneven taxonomic attention at the species level. Livistona is also a genus of major horticultural and economic importance, and thus many species have been moved by humans over long distances (Dowe, 2001; 2009; Starr et al., 2003).
Description
Top of pageStems to 15 m tall, 20-30 cm in diameter, rough with leaf scars. Leaves are palmate; petioles to 1.8 m, with green or black recurved spines along margins, spines denser proximally, fewer distally on petioles; hastula to 3 cm; blades almost circular in outline, 1.2-1.8 m wide, green on both surfaces, regularly divided to c. half their length into 50-90 segments, these split and pendulous at apices. Inflorescences are 1-1.2 m, branched to three orders, with six or seven partial inflorescences; rachillae 10-18 cm; flowers hermaphroditic, borne in clusters of 4-7, white or yellow, 2-2.5 mm. Fruits are green or blue-green, globose to ellipsoid or pear-shaped, 1.5-2.6 x 0.9-1.8 cm (Flora of China Editorial Committee, 2016).
Distribution
Top of pageL. chinensis is native to Eastern Asia including China, Japan (i.e., Ryukyu Islands, Bonin Islands) and Taiwan (USDA-ARS, 2016). The species is widely cultivated as an ornamental and can be found naturalized in the West Indies, tropical America and on many islands in the Indian and Pacific Oceans (Wagner et al., 1999; Meyer et al., 2008; Flora of China Editorial Committee, 2016; Govaerts, 2016; PIER, 2016).
Distribution Table
Top of pageThe distribution in this summary table is based on all the information available. When several references are cited, they may give conflicting information on the status. Further details may be available for individual references in the Distribution Table Details section which can be selected by going to Generate Report.
Last updated: 17 Dec 2021Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Mauritius | Present | Introduced | Invasive | ||||
Réunion | Present | Introduced | Invasive | ||||
South Africa | Present | Introduced | |||||
Asia |
|||||||
China | Present | Native | Based on regional distribution | ||||
-Guangdong | Present | Native | |||||
-Hainan | Present | Native | |||||
Hong Kong | Present | Introduced | Cultivated | ||||
India | Present | Introduced | Based on regional distribution | ||||
-Andaman and Nicobar Islands | Present | Introduced | |||||
Indonesia | Present | Introduced | Based on regional distribution | ||||
-Java | Present | Introduced | |||||
Japan | Present | Native | Based on regional distribution | ||||
-Kyushu | Present | Native | |||||
-Ryukyu Islands | Present | Native | |||||
-Shikoku | Present | Native | |||||
Singapore | Present | Introduced | Cultivated | ||||
Taiwan | Present | Native | |||||
Vietnam | Present | Introduced | |||||
North America |
|||||||
Antigua and Barbuda | Present | ||||||
Bermuda | Present | Introduced | Invasive | ||||
Costa Rica | Present | Introduced | |||||
Dominican Republic | Present | Introduced | Cultivated | ||||
El Salvador | Present | Introduced | Cultivated | ||||
Haiti | Present | Introduced | Cultivated | ||||
Puerto Rico | Present | Introduced | Cultivated | ||||
United States | Present | Introduced | Invasive | Based on regional distribution | |||
-Florida | Present | Introduced | Invasive | ||||
-Hawaii | Present | Introduced | Invasive | ||||
Oceania |
|||||||
Australia | Present | Introduced | 1912 | ||||
Federated States of Micronesia | Present | Introduced | |||||
Fiji | Present | Introduced | |||||
French Polynesia | Present | Introduced | |||||
Guam | Present | Introduced | |||||
Kiribati | Present | Introduced | |||||
Marshall Islands | Present | Introduced | |||||
Nauru | Present | Introduced | |||||
New Caledonia | Present | Introduced | Invasive | ||||
Northern Mariana Islands | Present | Introduced | |||||
Palau | Present | Introduced | |||||
Wallis and Futuna | Present | Introduced | |||||
South America |
|||||||
Bolivia | Present | Introduced | Cultivated | ||||
Colombia | Present | Introduced |
History of Introduction and Spread
Top of pageIn Mauritius, L. chinensis was introduced in 1785 and is now widely naturalized and invasive in native and secondary forests across the island (Meyer et al., 2008). In Hawaii, it was probably introduced in the 1800s and is cultivated as an ornamental tree, persisting after cultivation, and sparingly naturalized in areas where previously cultivated (Wagner et al., 1999).
Risk of Introduction
Top of pageBecause L. chinensis is widely commercialized as an ornamental palm in the horticultural trade, the risk of new introductions of this species is very high. It has the potential to escape from cultivation and become naturalized in disturbed sites, but also in undisturbed natural forests (Wagner et al., 1999; Starr et al., 2003; Meyer et al., 2008; ISSG, 2016).
Habitat
Top of pageL. chinensis grows in coastal and secondary moist forests at elevations between 1 and 600 m (Starr et al., 2003; Dowe, 2009; Palmweb, 2016). In China, it grows in coastal forests, often on sandy soils (Flora of China Editorial Committee, 2016). In Florida, it can be found growing on disturbed hammocks and mesic woodlands (Flora of North America Editorial Committee, 2016). In Mauritius, it is widely naturalized in native and secondary forests, and in Reunion it has spread in streambeds, shady understorey of disturbed secondary forests and coastal areas (Meyer et al., 2008). In Hawaii, it is especially prolific in moist areas, where numerous seedlings are often observed in ditches, waterways, streambeds, gulches and shady understory of disturbed secondary forests (Starr et al., 2003). It is also spreading across Bermuda, where it grows forming dense thickets in areas near cultivation, along roadsides and in disturbed forests and coastal areas (Bermuda DENR, 2016).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Disturbed areas | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Disturbed areas | Present, no further details | Natural |
Terrestrial | Managed | Disturbed areas | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Urban / peri-urban areas | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Productive/non-natural |
Littoral | Coastal areas | Present, no further details | Harmful (pest or invasive) | |
Littoral | Coastal areas | Present, no further details | Natural | |
Littoral | Coastal areas | Present, no further details | Productive/non-natural |
Hosts/Species Affected
Top of pageL. chinensis negatively impacts Acanthophoenix rubra, a critically endangered palm endemic to Mauritius (Maunder et al., 2001).
Biology and Ecology
Top of pageGenetics
The chromosome number of L. chinensis is 2n = 36 (Flora of North America Editorial Committee, 2016; Palmweb, 2016).
Reproductive Biology
As other palm species, L. chinensis is probably pollinated by wind and a variety of insects and animals such as beetles, bees, flies, ants and bats (Dehgan, 1998). This species is hermaphrodite and predominantly autogamous, while an evolutionary trend towards dioecy is displayed in other members of the genus (Dowe, 2009).
Physiology and Phenology
In Asia, L. chinensis flowers from February to April and fruits from April to September (Dowe, 2009). In Florida and Bermuda, it has been recorded flowering during the spring and summer (Gilman and Watson, 1993).
Environmental Requirements
L. chinensis grows in any moist area at elevations below 600 m. Plants are adapted to a wide range of soil conditions including clay, loam, sand, acidic and alkaline soils, but it prefers well-drained soils. Seedlings and young plants can thrive in open sunny areas, as well as in dense shady forested areas (Starr et al., 2003; Dowe, 2009; Palmweb, 2016).
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
Af - Tropical rainforest climate | Preferred | > 60mm precipitation per month | |
Am - Tropical monsoon climate | Preferred | Tropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25])) | |
As - Tropical savanna climate with dry summer | Preferred | < 60mm precipitation driest month (in summer) and < (100 - [total annual precipitation{mm}/25]) | |
Aw - Tropical wet and dry savanna climate | Preferred | < 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25]) |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Mean annual rainfall | 1800 mm | >3000 mm | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
Soil reaction
- acid
- alkaline
- neutral
Soil texture
- light
- medium
Natural enemies
Top of pageNatural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Aleurotrachelus atratus | ||||||
Candidatus Phytoplasma palmae | Pathogen | Other|All Stages | not specific | Dehgan (1998) | ||
Paysandisia archon | ||||||
Raoiella indica | Pathogen | |||||
Rhynchophorus ferrugineus |
Notes on Natural Enemies
Top of pageL. chinensis appears to be susceptible to lethal yellowing disease caused by Candidatus Phytoplasma palmi (Dehgan, 1998) and some other pathogens.
Means of Movement and Dispersal
Top of pageNatural Dispersal
L. chinensis spreads by seeds. Fruits fall to the ground and sprout below the parent tree. Fruits can also be spread by birds and other animals (Bermuda DENR, 2016). In Hawaii, it is possible that plants are also spread in water, as seedlings are often observed germinating along ditches (Starr et al., 2003). Dispersal by sea currents has been suggested for the northerly spread of L. chinensis (as var. subglobosa) from the Ryukyu Archipelago to Shikoku, Japan (Yoshida et al., 2000).
Intentional Introduction
L. chinensis is primarily spread over long distances by humans. It is often planted as ornamental and used in landscaping (Starr et al., 2003; Flora of China Editorial Committee, 2016; USDA-ARS, 2016).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Botanical gardens and zoos | Planted in botanical gardens | Yes | Yes | Meyer et al. (2008) |
Disturbance | Naturalized along roadsides and disturbed forests | Yes | Yes | ISSG (2016) |
Escape from confinement or garden escape | Seeds escaped from cultivation | Yes | Yes | Meyer et al. (2008) |
Garden waste disposal | Seeds escaped from cultivation | Yes | Yes | Meyer et al. (2008) |
Intentional release | Ornamental palm | Yes | Yes | Meyer et al. (2008) |
Internet sales | Seeds and seedlings | Yes | Yes | |
Landscape improvement | Widely commercialized as ornamental | Yes | Yes | USDA-ARS (2016) |
Nursery trade | Widely commercialized as ornamental | Yes | Yes | USDA-ARS (2016) |
Ornamental purposes | Widely commercialized as ornamental | Yes | Yes | USDA-ARS (2016) |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Debris and waste associated with human activities | Seeds escaped from cultivation | Yes | Yes | Meyer et al. (2008) |
Water | seeds | Yes | Yes | Starr et al. (2003) |
Wind | seeds | Yes | Yes | ISSG (2016) |
Impact Summary
Top of pageCategory | Impact |
---|---|
Cultural/amenity | Positive |
Economic/livelihood | Positive and negative |
Environment (generally) | Negative |
Environmental Impact
Top of pageImpact on Habitats
L. chinensis is listed as invasive in Hawaii, Florida, Bermuda, Mauritius, Reunion and New Caledonia, where it negatively impacts vegetation on coastal areas, mesic woodlands and secondary moist forests (Starr et al., 2003; Meyer et al., 2008; FLEPPC, 2015; Bermuda DENR, 2016; ISSG, 2016; PIER, 2016).
Impact on Biodiversity
L. chinensis produces a large number of fruits and has high germination rates. Fallen berries germinate at the base of the parent tree, forming dense thickets that smother and outcompete native vegetation (Bermuda DENR, 2016). In Mauritius, it has become invasive and is threatening the critically endangered endemic palm Acanthophoenix rubra (Maunder et al., 2001).
Threatened Species
Top of pageThreatened Species | Conservation Status | Where Threatened | Mechanism | References | Notes |
---|---|---|---|---|---|
Acanthophoenix rubra | CR (IUCN red list: Critically endangered) | Mauritius | Competition - monopolizing resources; Competition - shading; Competition - smothering | Maunder et al. (2001) | IUCN critically endangered species |
Risk and Impact Factors
Top of page- Proved invasive outside its native range
- Has a broad native range
- Abundant in its native range
- Highly adaptable to different environments
- Is a habitat generalist
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
- Pioneering in disturbed areas
- Benefits from human association (i.e. it is a human commensal)
- Long lived
- Gregarious
- Ecosystem change/ habitat alteration
- Modification of successional patterns
- Monoculture formation
- Reduced native biodiversity
- Threat to/ loss of endangered species
- Threat to/ loss of native species
- Competition - monopolizing resources
- Competition - shading
- Competition - smothering
- Produces spines, thorns or burrs
- Highly likely to be transported internationally deliberately
Uses
Top of pageL. chinensis is widely planted as an ornamental throughout tropical and subtropical areas of the world. It is often planted in gardens, parking lots, parks and avenues (Gilman and Watson, 1993; USDA-ARS, 2016). In Asia, leaves are used for making hats, fans, brooms and raincoats (Dowe, 2009; Flora of China Editorial Committee, 2016).
Uses List
Top of pageEnvironmental
- Amenity
General
- Botanical garden/zoo
Materials
- Baskets
- Fibre
Ornamental
- garden plant
Similarities to Other Species/Conditions
Top of pageL. chinensis looks similar to the Bermuda endemic palm Sabal bermudana, but can be distinguished by the following traits (Bermuda DENR, 2016): L. chinensis has thorns on the leaf stem, while S. bermudana never has thorns; and L. chinensis has a uniformly green leaf, hard oval grey-blue berries and the leaf meets the stem in a ‘C’ shape when viewed from above.
Prevention and Control
Top of pageDue to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.
Control
Physical/mechanical control
Seedlings of L. chinensis can be pulled by hand. Larger saplings are more difficult to pull and can be dug out with a fork, but will re-grow if broken. Larger plants can be cut back to ground level (Bermuda DENR, 2016; ISSG, 2016).
Chemical control
In Bermuda, the herbicide glyphosate has been used to control L. chinensis. The herbicide should be brushed onto the stump of the cut palm to prevent re-growth (Bermuda DENR, 2016; ISSG, 2016).
References
Top of pageAcevedo-Rodríguez P, Strong MT, 2012. Catalogue of the seed plants of the West Indies. Smithsonian Contributions to Botany, No. 98. Washington DC, USA: Smithsonian Institution Scholarly Press, 1192 pp.
Berendsohn WG, Gruber AN, Salomón JM, Molina JG, 2012. Nova Silva Cuscatlanica. Native and introduced trees of El Salvador, Part 2: Angiospermae - Families M to P and Pteridophyta. (Nova Silva Cuscatlanica. Árboles nativos e introducidos de El Salvador, Parte 2: Angiospermae - Familias M a P y Pteridophyta). Englera No. 29(2). Berlin-Dahlem, Germany: Botanischer Garten und Botanisches Museum, 300 pp.
Bermuda DENR, 2016. List of invasive plant species. Paget, Bermuda: Department of Environment and Natural Resources (DENR). http://environment.bm/
Chong KY, Tan HTW, Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species. Singapore: Raffles Museum of Biodiversity Research, National University of Singapore, 273 pp.
Dehgan B, 1998. Landscape plants for subtropical climates. Gainesville, USA: University of Florida Press, 638 pp.
Dowe JL, 2001. Studies in the genus Livistona (Coryphoideae: Arecaceae). PhD Thesis. Queensland, Australia: James Cook University.
FLEPPC, 2015. List of Invasive Plant Species. Fort Lauderdale, Florida, USA: Florida Exotic Plant Pest Council. http://www.fleppc.org/
Flora of China Editorial Committee, 2016. Flora of China. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.efloras.org/flora_page.aspx?flora_id=2
Flora of North America Editorial Committee, 2016. Flora of North America North of Mexico. St Louis, Missouri and Cambridge, Massachussets, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.efloras.org/flora_page.aspx?flora_id=1
Florence J, Chevillotte H, Ollier C, Meyer JY, 2013. Botanical database of the Nadeaud Herbarium of French Polynesia. (Base de données botaniques Nadeaud de l'Herbier de la Polynésie Française (PAP)). http://www.herbier-tahiti.pf
Gilman EF, Watson DG, 1993. Livistona chinensis, Chinese fan palm. Fact Sheet ST-365. Gainesville, USA: Environmental Horticulture Department, Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida. http://hort.ufl.edu/database/documents/pdf/tree_fact_sheets/livchia.pdf
Govaerts R, 2016. World Checklist of Arecaceae. London, UK: Royal Botanic Gardens, Kew. http://apps.kew.org/wcsp/
Holdridge LR, Poveda LJ, 1975. Trees of Costa Rica. (Arboles de Costa Rica). San Jose, Costa Rica: Centro Cientifica Tropical.
Idárraga A, Ortiz RC, Callejas R, Merello M, 2011. [English title not available]. (Flora de Antioquia: catálogo de las plantas vasculares. Vol. II). Programa Expedición Antioquia-2103. Series Biodiversidad y Recursos Naturales. Bogotá, Colombia: Universidad de Antioquia, Missouri Botanical Garden & Oficina de planeación departamental de la gobernación de Antioquia, Editorial D’Vinni, 939 pp.
ISSG, 2016. Global Invasive Species Database (GISD). Livistona chinensis. Invasive Species Specialist Group of the IUCN Species Survival Commission. http://www.iucngisd.org/gisd/species.php?sc=1645
Jørgensen PM, Nee MH, Beck SG, 2015. Catalogue of the vascular plants of Bolivia. (Catalogo de plantas vasculares de Bolivia). Monographs in Systematic Botany, Vol. 127(1-2). St. Louis, USA: Missouri Botanical Garden Press, 1744 pp.
Palmweb, 2016. Palmweb: Palms of the world online. London, UK: Royal Botanical Gardens, Kew. http://www.palmweb.org/node/2
PIER, 2016. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Starr F, Starr K, Loope L, 2003. Livistona chinensis, Chinese fan palm, Arecaceae. Alien species in Hawaii. Honolulu, USA: Hawaii Ecosystems at Risk (HEAR), University of Hawaii. http://www.hear.org/starr/hiplants/reports/pdf/livistona_chinensis.pdf
Stevens PF, 2012. Angiosperm Phylogeny Website. St Louis, Missouri, USA: University of Missouri and Missouri Botanical Garden. http://www.mobot.org/MOBOT/research/APweb/
USDA-ARS, 2016. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx
Wu T, 2001. Check List of Hong Kong Plants. Hong Kong Herbarium and the South China Institute of Botany. Hong Kong: Agriculture, Fisheries and Conservation Department. http://www.hkflora.com/v2/flora/plant_check_list.php
Distribution References
Berendsohn WG, Gruber AN, Salomón JM, Molina JG, 2012. Nova Silva Cuscatlanica. Native and introduced trees of El Salvador, Part 2: Angiospermae - Families M to P and Pteridophyta. (Nova Silva Cuscatlanica. Árboles nativos e introducidos de El Salvador, Parte 2: Angiospermae - Familias M a P y Pteridophyta). In: Englera, 29 (2) Berlin-Dahlem, Germany: Botanischer Garten und Botanisches Museum. 300 pp.
Bermuda DENR, 2016. List of invasive plant species., Paget, Bermuda, Department of Environment and Natural Resources (DENR). http://environment.bm/
CABI, Undated. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Chong KY, Tan HTW, Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species., Singapore: Raffles Museum of Biodiversity Research, National University of Singapore. 273 pp.
FLEPPC, 2015. List of Invasive Plant Species., Fort Lauderdale, Florida, USA: Florida Exotic Plant Pest Council. http://www.fleppc.org/
Florence J, Chevillotte H, Ollier C, Meyer JY, 2013. Botanical database of the Nadeaud Herbarium of French Polynesia. (Base de données botaniques Nadeaud de l'Herbier de la Polynésie Française (PAP))., http://www.herbier-tahiti.pf
Govaerts R, 2016. World Checklist of Arecaceae., London, UK: Royal Botanic Gardens, Kew. http://apps.kew.org/wcsp/
Holdridge LR, Poveda LJ, 1975. Trees of Costa Rica. (Arboles de Costa Rica)., San Jose, Costa Rica: Centro Cientifica Tropical.
Idárraga A, Ortiz RC, Callejas R, Merello M, 2011. [English title not available]. (Flora de Antioquia: catálogo de las plantas vasculares). In: Programa Expedición Antioquia-2103. Series Biodiversidad y Recursos Naturales, II Bogotá, Colombia: Universidad de Antioquia, Missouri Botanical Garden & Oficina de planeación departamental de la gobernación de Antioquia, Editorial D’Vinni. 939 pp.
Jørgensen PM, Nee MH, Beck SG, 2015. Catalogue of the vascular plants of Bolivia. (Catalogo de plantas vasculares de Bolivia). In: Monographs in Systematic Botany, 127 (1–2) St. Louis, USA: Missouri Botanical Garden Press. 1744 pp.
Palmweb, 2016. Palmweb: Palms of the world online., London, UK: Royal Botanical Gardens, Kew. http://www.palmweb.org/node/2
PIER, 2016. Pacific Islands Ecosystems at Risk., Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.htm
USDA-ARS, 2016. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysimple.aspx
Wu T, 2001. Check List of Hong Kong Plants. In: Hong Kong Herbarium and the South China Institute of Botany, Hong Kong: Agriculture, Fisheries and Conservation Department. http://www.hkflora.com/v2/flora/plant_check_list.php
Contributors
Top of page11/01/17 Original text by:
Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH, Smithsonian Institution, Washington DC, USA
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