Ficus microcarpa (Indian laurel tree)
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 List
- Biology and Ecology
- Climate
- Soil Tolerances
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Impact Summary
- Economic Impact
- Social Impact
- Risk and Impact Factors
- Uses
- Uses List
- Prevention and Control
- References
- Links to Websites
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Ficus microcarpa L. f.
Preferred Common Name
- Indian laurel tree
Other Scientific Names
- Ficus microcarpa var. hillii (F.M.Bailey) Corner
- Ficus microcarpa var. saffordii (Merr.) Corner
- Ficus retusa auct. non L.
International Common Names
- English: Chinese banyan; Chinese banyan fig; curtain fig; fig; Hill's weeping fig; Indian laurel fig; Indian-laurel; laurel fig; laurel fig tree; Malay banyan; Malayan banyan; small-fruit fig
- Spanish: laurel de la India
- French: arbre de l'Intendance; laurier d'Inde
- Chinese: rong shu
Local Common Names
- Dominican Republic: arbol de Washington; laurel; laurel de India; laurel de la India
- Germany: Lorbeer Feigenbaum
- Guam: nunu
- Indonesia/Java: bibis; bulu; kowang; wunut
- Japan: gajumaru
- Lesser Antilles: evergreen
- Malaysia: ara jejawi
- Micronesia, Federated states of: au au
- Northern Mariana Islands: nunu
- Palau: lulk
- Puerto Rico: jaguey
EPPO code
- FIUMI (Ficus microcarpa)
Summary of Invasiveness
Top of pageF. microcarpa is a high-risk, aggressively invasive, strangling fig or banyan tree native to Asia but cultivated pantropically (Center for Australian National Biodiversity Research, 2010; PIER, 2014). It is reportedly invasive to some places where its specialist pollinator wasp has also been introduced, including Hawaii, Florida, Bermuda, French Polynesia, Guam, the Bonin Islands, and parts of the West Indies, Central and South America (Randall, 2012; PIER, 2014; USDA-ARS, 2014). In a risk assessment prepared for Hawaii, the species received a high risk score of 10, indicating its likely threat to native flora (PIER, 2014). The species is listed as “agricultural weed, cultivation escape, environmental weed, garden thug, naturalised, noxious weed, sleeper weed, weed” in the Global Compendium of Weeds (Randall, 2012), and was included on the Florida Exotic Pest Plant Council’s Invasive Plant List (Florida Exotic Pest Plant Council, 2013). It is known to have escaped from cultivation, produces a large number of viable seeds which are ingested and spread by birds and animals and which are capable of growing in a wide range of conditions, and outcompetes native flora by strangling its host plant with its aerial roots during its early life as an epiphyte, as well as by shading when its large, dense canopy develops (Little and Skolmen, 1989; Randall, 2012).
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Urticales
- Family: Moraceae
- Genus: Ficus
- Species: Ficus microcarpa
Notes on Taxonomy and Nomenclature
Top of page
Often called the mulberry family, Moraceae consists of about 40 genera and 1000 species of trees, shrubs, lianas, or rarely herbs, nearly all with milky sap, and mainly of tropical or subtropical origin (University of Hawaii, 2014). The milky sap of various Moraceae species contain ‘heart poisons’ that are used as dart poisons in some cultures; other plant parts such as leaves and fruit juices have also been reported to cause allergic and toxic reactions in humans and livestock (Frohne and Pfa¨nder, 2005). Many genera of this family are well-known as food crops and include Artocarpus, the tropical food staple breadfruit and jackfruit genus, Ficus, the fig genus, and Morus, the mulberry genus.
Ficus is a large genus of about 800-1000 tree and shrub species native to the tropics and subtropics that are often cultivated beyond their native range for their edible figs or as ornamentals. Members of this genus are difficult to distinguish by their flowers, but can be differentiated by habit, whether they are banyans or not, by leaf shape, and by their figs (Whistler, 2000).
The species name F. microcarpa refers to the species’ small-sized figs, about 8 mm in diameter (Little and Skolmen, 1989). The name has been misapplied to Ficus retusa and Ficus nitida, and these species reportedly all have the common name ‘laurel de la India’ (Acevedo-Rodriguez and Strong, 2012; Oviedo-Prieto et al., 2012; Missouri Botanical Garden, 2014). Several species are currently being reviewed as synonyms of F. microcarpa, and infraspecific taxa under review include F. microcarpa var. hillii (F.M.Bailey) Corner and F. microcarpa var. naumannii (Engl.) Corner (Missouri Botanical Garden, 2014).
Description
Top of pageVariable in habit, often epiphytic, subscandent shrubs when young, in maturity spreading evergreen trees with large branches and numerous aerial roots hanging from the trunk and branches, these sometimes reaching the soil to form pillar-like roots. Leaves: variable, coriaceous, oblong, elliptic to broadly elliptic or obovate, usually 5-8 cm long, 3-5 cm wide, glabrous, margins entire, petioles 0.6-2 cm long. Flowers: synconia sessile, arising among or just below the leaves, depressed-globose, 6-10 mm in diameter, subtended by 3 broadly ovate, ± persistent bracts.
Distribution
Top of pageF. microcarpa is native to China, eastern Asia, the Indian subcontinent, Indo-China, Malesia, Australia, and the southwestern Pacific region, but has been introduced to and cultivated in the Americas including the West Indies and the United States (Wiersema and Leon, 1999; Acevedo-Rodriguez and Strong, 2012).
Some discrepancies in the reported distribution were found among sources. F. microcarpa has been reported as both introduced and native to Kosrae Island and the Marshall Islands in Micronesia, as well as in Guam and New Caledonia (PIER, 2014). The species is known to be of Old World origin and an introduction to the West Indies (Acevedo-Rodriguez and Strong, 2012), but Broome et al. (2007) report this species as native to the Caribbean region.
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: 25 Feb 2021Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Cabo Verde | Present | ||||||
Madagascar | Present | ||||||
Réunion | Present, Only in captivity/cultivation | Introduced | |||||
Seychelles | Present | ||||||
Asia |
|||||||
Bhutan | Present | Native | |||||
Cambodia | Present | Native | |||||
China | Present | Native | |||||
-Fujian | Present | Native | |||||
-Guangdong | Present | Native | |||||
-Guangxi | Present | Native | |||||
-Guizhou | Present | Native | |||||
-Hainan | Present | Native | |||||
-Yunnan | Present | Native | |||||
-Zhejiang | Present | Native | |||||
Cocos Islands | Present | Native | |||||
India | Present | Native | |||||
-Andhra Pradesh | Present | ||||||
-Tamil Nadu | Present | ||||||
Indonesia | Present | Native | |||||
-Irian Jaya | Present | Native | |||||
-Java | Present | Native | |||||
-Lesser Sunda Islands | Present | Native | Lesser Sunda Is. | ||||
-Maluku Islands | Present | Native | |||||
-Sumatra | Present | Native | |||||
Iraq | Present | Introduced | ‘introduced and cultivated’ | ||||
Japan | Present | Introduced | Invasive | Ogasawara (Bonin) Is. | |||
-Ryukyu Islands | Present | Ryukyu Is. | |||||
Laos | Present | Native | |||||
Malaysia | Present | Native | |||||
Myanmar | Present | Native | |||||
Nepal | Present | ||||||
Pakistan | Present | Introduced | ‘introduced and cultivated’ | ||||
Philippines | Present | Native | |||||
Singapore | Present | Native | ‘common’ | ||||
Sri Lanka | Present | Native | |||||
Taiwan | Present | Native | |||||
Thailand | Present | Native | |||||
Vietnam | Present | Native | |||||
Europe |
|||||||
France | Present | central | |||||
Italy | Present | Present based on regional distribution. | |||||
-Sicily | Present | Introduced | |||||
Montenegro | Present | ||||||
Portugal | Present | Present based on regional distribution. | |||||
-Azores | Present | ||||||
-Madeira | Present | ||||||
Spain | Present | Present based on regional distribution. | |||||
-Canary Islands | Present | ||||||
United Kingdom | Present | ||||||
North America |
|||||||
Antigua and Barbuda | Present | Native | Antigua | ||||
Barbados | Present | Native | |||||
Canada | Present | ||||||
Dominican Republic | Present | Introduced | |||||
El Salvador | Present | Introduced | |||||
Haiti | Present | Introduced | |||||
Honduras | Present | Introduced | |||||
Mexico | Present | Introduced | |||||
Montserrat | Present | Native | |||||
Nicaragua | Present | Introduced | |||||
Panama | Present | Introduced | |||||
Puerto Rico | Present | Introduced | |||||
Saint Kitts and Nevis | Present | Native | |||||
Saint Lucia | Present | Native | |||||
Trinidad and Tobago | Present | ||||||
U.S. Virgin Islands | Present | Introduced | St. Croix | ||||
United States | Present | All but northeastern USA | |||||
-California | Present | ||||||
-Florida | Present | Introduced | Invasive | ||||
-Hawaii | Present | Introduced | Naturalized | ‘naturalized’ | |||
Oceania |
|||||||
Australia | Present | Native | |||||
-Queensland | Present | Native | Cape York Peninsular, northeast Queensland | ||||
Christmas Island | Present | Native | |||||
Federated States of Micronesia | Present | Native | |||||
French Polynesia | Present | Introduced | Invasive | ||||
Guam | Present | ||||||
Marshall Islands | Present | var. microcarpa:; Original citation: Wagner et al. (2014) | |||||
New Caledonia | Present | ||||||
New Zealand | Present | ||||||
Northern Mariana Islands | Present | ||||||
Palau | Present | ||||||
Papua New Guinea | Present | Native | |||||
Solomon Islands | Present | Native | |||||
Tonga | Present | Introduced | Invasive | ||||
U.S. Minor Outlying Islands | Present | Introduced | Invasive | Midway Atoll | |||
South America |
|||||||
Argentina | Present | ||||||
Bolivia | Present | Introduced | ‘Cultivated’. Beni; Original citation: Bolivia Checklist (2014) | ||||
Brazil | Present | Present based on regional distribution. | |||||
-Acre | Present | ||||||
-Sao Paulo | Present | ||||||
Chile | Present | ||||||
Colombia | Present | ‘Valle del Cauca’ | |||||
Ecuador | Present | Guayas | |||||
-Galapagos Islands | Present | ||||||
Paraguay | Present | Central | |||||
Peru | Present | Introduced | ‘disturbed areas’ Loreto, Maynas | ||||
Venezuela | Present | Introduced | Margarita (offshore island) |
History of Introduction and Spread
Top of pageF. microcarpa is native to the Old World tropics but has been widely cultivated pantropically, and, in many places where its species-specific pollinator wasp has been introduced, F. microcarpa has naturalized or in some cases become invasive. In the US state of Florida, the species was said to have first been planted by Thomas Edison in Fort Meyers as a gift from Harvey Firestone, and has been present since at least 1912 (Kaufman and Kaufman, 2007); it began spreading by seed in the 1970s after an apparently accidental introduction of its species-specific pollinating wasp, and is now known to be invasive in Florida (IFAS, 2014).
Similarly, in the West Indies the species was not listed in Britton’s work on Bermuda (1918) but is now known to be a notorious invasive species there following the accidental introduction of its wasp sometime in the 1980s (Starr et al., 2003; Randall, 2012; Bermuda Department of Conservation Services, 2014). Date of the species’ introduction to the West Indies region is uncertain, but, based on its exclusion from Britton’s work on Bermuda (1918) and Bello’s (1881; 1883) work on Puerto Rico, it may have occurred relatively recently. Britton did collect specimens in 1903 from Cuba and in 1925 from Puerto Rico that are now held in the New York Botanical Garden herbarium.
In Hawaii, the pollinator wasp was intentionally introduced in 1938, and since then F. microcarpa has become a high-risk major invasive species across the islands (PIER, 2014). The species has become an established alien species in Sicily, Italy (DAISIE, 2014). In Pakistan, the species is occasionally planted in gardens and nurseries in Karachi and Lahore (Flora of Pakistan, 2014). In other places, the species has been cultivated as a common ornamental but does not appear to have naturalized due to the absence of its pollinator wasp.
Risk of Introduction
Top of pageF. microcarpa is a very high-risk species, and was given a high risk score of 10 (score of 6 or greater = likely to pose threat to native ecosystem) in a risk assessment prepared for Hawaii (PIER, 2014).
In Florida, F. microcarpa is a Category I invasive species on the Florida Exotic Pest Plant Council's 2013 List of Invasive Plant Species, defined as “invasive exotics that are altering native plant communities by displacing native species, changing community structures or ecological functions, or hybridizing with natives”, based on “the ecological damage caused”. Invaded habitats include pine rockland, hardwood forests, and disturbed places (Weber, 2003).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | Productive/non-natural |
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 | 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 | Natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Natural |
Littoral | Coastal areas | Present, no further details | Natural |
Biology and Ecology
Top of pageReproductive Biology
The species is capable of producing a fig-like fruit that contains about 150 seeds, and a single tree may produce up to 100,000 fruit which are eaten by birds and spread both locally and long-distance (Bermuda Department of Conservation Services, 2014).
Physiology and Phenology
Like many other Ficus species, F. microcarpa often begins life as an epiphyte, surrounding its host tree with its roots and eventually strangling it. The species also creates dense, impenetrable thickets that will shade out and kill any flora beneath it (Motooka et al., 2003; Weber, 2003; Bermuda Department of Conservation Services, 2014).
Associations
Each member of the Ficus genus has a symbiotic relationship with an agaonid wasp; just as each Ficus species requires a specific wasp in order to pollinate, the wasp will only lay eggs within its associated Ficus species (Starr et al., 2003). The wasp associated with F. microcarpa is Eupristinaverticillata.
Environmental Requirements
F. microcarpa generally grows at lower elevations and within tropical and temperate climate zones. In Queensland, Australia, for example, the species occurs in tropical rainforest climate and has a reported altitudinal range of 0-400 m (Centre for Australian National Biodiversity Research, 2010). In Bolivia and Peru, it is reported for 0-500 m (Bolivia Checklist, 2014; Peru Checklist, 2014) and in Panama, 0-1000 m (Panama Checklist, 2014), while in China it has been recorded for mountain and plain regions below 1900 m (PIER, 2014).
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])) | |
Aw - Tropical wet and dry savanna climate | Preferred | < 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25]) | |
Cf - Warm temperate climate, wet all year | Preferred | Warm average temp. > 10°C, Cold average temp. > 0°C, wet all year |
Notes on Natural Enemies
Top of pageF. microcarpa is highly susceptible to attack by dry-wood termites (Little and Skolmen, 1989). A number of insects attack the species in Hawaii, including the Cuban laurel thrip (Gynaikothrips ficorum) and the banyan leaf gall wasp (Josephiella sp.) (Starr et al., 2003).
Means of Movement and Dispersal
Top of pageF. microcarpa is dispersed by several different vectors. Seeds are spread both locally and long distance by over 200 vertebrate species that reportedly consume the synconia figs, mainly birds and some fruit bats, as well as dispersal by ants (Shanahan et al., 2001; Starr et al., 2003). In Florida, seeds are dispersed by ants attracted to an oily tissue coating the seed (Nadel et al., 1991).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Digestion and excretion | Seeds of this species are known to be dispersed by over 200 vertebrate species including birds and b | Yes | Yes | Shanahan et al., 2001; Starr et al., 2003 |
Escape from confinement or garden escape | Yes | Randall, 2012 | ||
Horticulture | Has been introduced and cultivated beyond its native range for use as an ornamental and shade tree | Yes | Yes | Hanelt et al., 2001; PIER, 2014; Randall, 2012; USDA-ARS, 2014 |
Landscape improvement | Has been introduced and cultivated beyond its native range for use as an ornamental and shade tree | Yes | Yes | Hanelt et al., 2001; PIER, 2014; USDA-ARS, 2014 |
Medicinal use | Yes | Yes | Hanelt et al., 2001; USDA-ARS, 2014 | |
Ornamental purposes | Yes | Yes | Hanelt et al., 2001; PIER, 2014; USDA-ARS, 2014 |
Economic Impact
Top of pageF. microcarpa is known to negatively impact native flora and ecosystems by not only strangling and replacing host trees during its early life as an epiphyte, but by forming dense canopies that shade out native flora. The extensive root systemst can damage infrastructure and anything else in the ground surrounding the tree.
Social Impact
Top of pageSeedlings of F. microcarpa can sprout almost anywhere that a seed lands, including walls, roofs and gutters of buildings. The root systems can be very damaging to buildings and stonework. In Bermuda, the plant is therefore considered a threat to historic buildings as well as to the natural environment (Bermuda Department of Conservation Services, 2014). In Hawaii, it damages concrete ditches which transport water (Starr et al., 2003).
Risk and Impact Factors
Top of page- Invasive in its native range
- Proved invasive outside its native range
- Abundant in its native range
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
- Pioneering in disturbed areas
- Tolerant of shade
- Fast growing
- Has high reproductive potential
- Has propagules that can remain viable for more than one year
- Damaged ecosystem services
- Host damage
- Infrastructure damage
- Competition - shading
- Competition - strangling
- Parasitism (incl. parasitoid)
- Rapid growth
- Rooting
- Highly likely to be transported internationally deliberately
- Difficult to identify/detect as a commodity contaminant
Uses
Top of pageF. microcarpa has been introduced and cultivated pantropically for use an ornamental plant (Wiersema and Leon, 1999). In southern India the species is reportedly cultivated as a shade tree in coffee plantations, and it is abundantly planted in southeast Asia and other tropical regions as an ornamental tree, as well as for its use in traditional medicine in India, Malaysia, and southern China (Hanelt et al., 2001). The species is grown as both an indoor house plant and as a shade tree in Puerto Rico, where it has now become persistent (Liogier and Martorell, 2000).
Uses List
Top of pageEnvironmental
- Landscape improvement
General
- Ornamental
Medicinal, pharmaceutical
- Traditional/folklore
Ornamental
- Potted plant
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.
Prevention
Like all members of the Ficus genus, the species requires a specialist pollinator wasp in order to set viable seed. Especially in places where F. microcarpa has been introduced but has not yet become invasive, it is a high priority to prevent the wasp from entering non-native areas in order to prevent the species’ spread.
Chemical Control
Chemical control has been used for Ficus species, as they are sensitive to triclopyr herbicides as a basal or stump treatment (Starr et al., 2003; Weber, 2003).
Physical Control
The species can be physically controlled by pruning to prevent the plant from maturing into a woody shrub or tree-like form.
Biological Control
Non-pollinating fig wasps have been suggested as possible biocontrol agents for invasive Ficus spp. At least 43 fig wasps utilize F. microcarpa figs, with more than 20 species present in the plant’s introduced range (Wang, 2014). A large galler species, Meselatus bicolor, is independent of the pollinator and can suppress both male and female reproductive successes of figs via competition for nutrients and preventing pollinators from entering figs, making it a potential biocontrol agent (Wang, 2014). Wang et al. (2015) reported the presence of this species in the Mediterranean region. M. bicolor prevents seeds and pollinators from developing in the figs it occupies, and has only been recorded from F. microcarpa, giving it the potential to be a valuable biological control agent in other countries outside the Mediterranean where F. microcarpa has become invasive (Wang et al., 2015).
References
Top of pageAcevedo-Rodríguez P; Strong MT, 2012. Catalogue of the Seed Plants of the West Indies. Smithsonian Contributions to Botany, 98:1192 pp. Washington DC, USA: Smithsonian Institution. http://botany.si.edu/Antilles/WestIndies/catalog.htm
Bello D, 1883. [English title not available]. (Apuntes para la flora de Puerto Rico. Segunda parte. Monoclamídeas.) Anales de la Sociedad Española de Historia Natural, 12:103-130.
Bello Espinosa D, 1881. [English title not available]. (Apuntes para la flora de Puerto Rico. Primera parte.) Anal. Soc. Española de Hist. Nat, 10:231-304.
Bermuda Department of Conservation Services, 2014. Indian Laurel (Ficus microcarpus.). http://www.conservation.bm/indian-laurel/
Bolivia Checklist, 2014. Catalogue of the Vascular Plants of Bolivia, Tropicos website. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://tropicos.org/NameSearch.aspx?projectid=13
Britton NL, 1918. Flora of Bermuda. New York, USA: Charles Scribner's Sons. 585 pp.
Broome R; Sabir K; Carrington S, 2007. Plants of the Eastern Caribbean. Online database. Barbados: University of the West Indies. http://ecflora.cavehill.uwi.edu/index.html
Centre for Australian National Biodiversity Research, 2010. Australian tropical rainforest plants. http://www.anbg.gov.au/cpbr/cd-keys/rfk/index.html
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. http://lkcnhm.nus.edu.sg/nus/pdf/PUBLICATION/LKCNH%20Museum%20Books/LKCNHM%20Books/flora_of_singapore_tc.pdf
DAISIE, 2014. Delivering Alien Invasive Species Inventories for Europe. European Invasive Alien Species Gateway. www.europe-aliens.org/default.do
Flora Mesoamericana, 2014. Flora Mesoamericana. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/FM
Flora of Nicaragua, 2014. Flora of Nicaragua, Tropicos website. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://tropicos.org/NameSearch.aspx?projectid=7
Flora of Pakistan, 2014. Flora of Pakistan/Pakistan Plant Database (PPD). Tropicos website St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.tropicos.org/Project/Pakistan
Florida Exotic Pest Plant Council, 2013. Florida Exotic Pest Plant Council's 2013 List of Invasive Plant Species. http://www.fleppc.org/list/2013/index.htm
Frohne D; Pfander HJ, 2005. Poisonous plants: A handbook for doctors, pharmacists, toxicologists, biologists and veterinarians. 2nd Edition. Portland, OR, USA: Timber Press, 469 pp.
Hanelt P; Buttner R; Mansfeld R, 2001. Mansfeld's Encyclopedia of Agricultural and Horticultural Crops (except Ornamentals). Berlin, Germany: Springer.
IFAS, 2014. Center for Aquatic and Invasive Plants. Gainesville, Florida, USA: University of Florida. http://plants.ifas.ufl.edu/
Langeland KA; Cherry HA; McCormick CA; Craddock Burks KA, 2008. Identification and biology of nonnative plants in Florida's natural areas. Second edition. Gainesville, FL, USA: University of Florida-IFAS, 210 pp.
Langeland KA; Ferrell JA; Sellers B; MacDonald GE; Stocker RK, 2014. Integrated management of nonnative plants in natural areas of Florida. University of Florida-IFAS Extension Publication, SP-242. Gainesville, FL, USA: University of Florida-IFAS, 27 pp. http://edis.ifas.ufl.edu/pdffiles/WG/WG20900.pdf
Liogier HA; Martorell LF, 2000. Flora of Puerto Rico and adjacent islands: a systematic synopsis, 2nd edition revised. San Juan, Puerto Rico: La Editorial, University of Puerto Rico, 382 pp.
Missouri Botanical Garden, 2014. Tropicos database. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/
Oviedo Prieto R; Herrera Oliver P; Caluff MG, et al. , 2012. National list of invasive and potentially invasive plants in the Republic of Cuba - 2011. (Lista nacional de especies de plantas invasoras y potencialmente invasoras en la República de Cuba - 2011). Bissea: Boletín sobre Conservación de Plantas del Jardín Botánico Nacional de Cuba, 6(Special Issue 1):22-96.
Panama Checklist, 2014. Flora of Panama Checklist, Tropicos website. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://tropicos.org/Project/PAC
Peru Checklist, 2014. The Catalogue of the Flowering Plants and Gymnosperms of Peru. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/PEC
PIER, 2014. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Randall RP, 2012. A Global Compendium of Weeds. Perth, Australia: Department of Agriculture and Food Western Australia, 1124 pp. http://www.cabi.org/isc/FullTextPDF/2013/20133109119.pdf
Starr F; Starr K; Loope L, 2003. Ficus microcarpa (Chinese banyan). Maui, Hawaii, USA: United States Geological Survey- Biological Resources Division, Haleakala Field Station. http://www.hear.org/pier/pdf/pohreports/ficus_microcarpa.pdf
University of Hawaii, 2014. Department of Botany Vascular Plant Family Access Page: Moraceae. Honolulu, USA: University of Hawaii. http://www.botany.hawaii.edu/faculty/carr/mor.htm
USDA-ARS, 2014. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx
Wagner WL; Herbst DR; Lorence DH, 2014. Flora of the Hawaiian Islands website. Washington DC, USA: Smithsonian Institution,. http://botany.si.edu/pacificislandbiodiversity/hawaiianflora/index.htm
Wagner WL; Herbst DR; Tornabene MW; Weitzman A; Lorence DH, 2014. Flora of Micronesia website. Washington DC: Smithsonian Institution. http://botany.edu/pacificislandbiodiversity/micronesia/index.htm
Wang R, 2014. The fig wasps associated with Ficus microcarpa, an invasive fig tree. Leeds, UK: University of Leeds. http://etheses.whiterose.ac.uk/6918/
WBN Flora Database, 2014. WBN Flora Database. St Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/Weda%20Bay
Whistler WA, 2000. Tropical ornamentals. Portland, Oregon, USA: Timber Press.
Distribution References
Broome R, Sabir K, Carrington S, 2007. Plants of the Eastern Caribbean., Barbados: University of the West Indies. http://ecflora.cavehill.uwi.edu/index.html
CABI, Undated. Compendium record. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
CABI, Undated b. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Centre for Australian National Biodiversity Research, 2010. Australian tropical rainforest plants., http://www.anbg.gov.au/cpbr/cd-keys/rfk/index.html
DAISIE, 2014. Delivering Alien Invasive Species Inventories for Europe. http://www.europe-aliens.org/
Flora Mesoamericana, 2014. Flora Mesoamericana., St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/FM
Flora of Nicaragua, 2014. Flora of Nicaragua, Tropicos website., St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://tropicos.org/NameSearch.aspx?projectid=7
Flora of Pakistan, 2014. Flora of Pakistan/Pakistan Plant Database (PPD)., St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.tropicos.org/Project/Pakistan
Florida Exotic Pest Plant Council, 2013. Florida Exotic Pest Plant Council's 2013 List of Invasive Plant Species., http://www.fleppc.org/list/2013/index.htm
IFAS, 2014. Center for Aquatic and Invasive Plants., Gainesville, Florida, USA: University of Florida. http://plants.ifas.ufl.edu/
Liogier HA, Martorell LF, 2000. Flora of Puerto Rico and adjacent islands: a systematic synopsis, 2nd edition revised., San Juan, Puerto Rico: La Editorial, University of Puerto Rico. 382 pp.
PIER, 2014. Pacific Islands Ecosystems at Risk., Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Randall RP, 2012. A Global Compendium of Weeds., Perth, Australia: Department of Agriculture and Food Western Australia. 1124 pp. http://www.cabi.org/isc/FullTextPDF/2013/20133109119.pdf
USDA-ARS, 2014. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysimple.aspx
WBN Flora Database, 2014. WBN Flora Database., St Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/Weda%20Bay
Whistler W A, 2000. Tropical Ornamentals. Portland, Oregon, USA: Timber Press.
Links to Websites
Top of pageWebsite | URL | Comment |
---|---|---|
Flora of Micronesia website | http://botany.si.edu/pacificislandbiodiversity/micronesia/index.htm | |
Flora of Pakistan/Pakistan Plant Database (PPD). Tropicos website | http://www.tropicos.org/Project/Pakistan | |
Flora of the Hawaiian Islands | http://botany.si.edu/pacificislandbiodiversity/hawaiianflora/index.htm | |
Flora of the West Indies | http://botany.si.edu/antilles/WestIndies/ | |
Hawaiian Ecosystems at Risk Project (HEAR) | http://www.hear.org/ | |
PIER | http://www.hear.org/pier/index.html |
Contributors
Top of page18/12/2014 Original text by:
Marianne Jennifer Datiles, Department of Botany-Smithsonian NMNH, Washington DC, USA
Pedro Acevedo-Rodríguez, Department of Botany-Smithsonian NMNH, Washington DC, USA
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