Clerodendrum chinense (Chinese glory bower)
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
- Biology and Ecology
- Climate
- Rainfall Regime
- Soil Tolerances
- Natural enemies
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Environmental Impact
- Risk and Impact Factors
- Uses
- Uses List
- Prevention and Control
- Gaps in Knowledge/Research Needs
- References
- Links to Websites
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Clerodendrum chinense (Osbeck) Mabberley
Preferred Common Name
- Chinese glory bower
Other Scientific Names
- Clerodendrum fragrans Willd.
- Clerodendrum fragrans Willd. f. pleniflorum (Schauer) Standl. & Steyerm
- Clerodendrum fragrans Willd. var. pleniflorum Schauer.
- Clerodendrum philippinum Schauer.
- Ovieda fragrans Willd.
- Volkameria fragrans Vent.
International Common Names
- English: fragrant clerodendrum; fragrant glory bower; glory bower; stickbush; wild jasmine
- Spanish: flor de muerto; hortensia; jazmín de muerto; jazmín de perro
- French: herbe à madame villaret
- Chinese: chong ban xiu mo li
Local Common Names
- Bahamas: wild jasmine
- Cook Islands: pitate mama; tiare tupapaku
- Cuba: avispero; cógelo todo; jazmín trasminador; juan grande; mil flores; mil rosas; yerba hedionda
- Jamaica: julius plague; Lady Nugent's rose
- Lesser Antilles: moselle; pain killer; stick-bush; wez alba
- Micronesia, Federated states of: Honolulu rose; rohsen onoluhlu (Pohnpei)
- Puerto Rico: jazmín hediondo; yapaná
- Samoa: losa fiti; Losa Honolulu
- USA/Hawaii: pikake hohono; pikake pilau; pikake wauke
Summary of Invasiveness
Top of pageC. chinense is a highly invasive weed in tropical and subtropical ecosystems. This species has the capacity to move into a habitat and reproduce aggressively by root suckers. C. chinense is classified as a “major weed” in Hawaii, Fiji, Western Samoa, and America Samoa (PIER, 2012) where it grows commonly along roadsides and as an ornamental shrub in gardens. This species rapidly invades pastures and plantations wherever it is planted forming dense thickets that exclude other species (Space and Flynn, 2002; Motooka et al., 2003). In the West Indies, C. chinense is included in lists of invasive species in Cuba, Puerto Rico, and US Virgin Islands (Acevedo-Rodríguez and Strong, 2012; González et al., 2012) and is classified as a widespread exotic plant in the Lesser Antilles (including Antigua, Barbados, Dominica, Grenada, Guadeloupe, Martinique, Montserrat, St. Lucia, and St. Vincent; Broome et al., 2007).
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Lamiales
- Family: Lamiaceae
- Genus: Clerodendrum
- Species: Clerodendrum chinense
Notes on Taxonomy and Nomenclature
Top of pageThe family Lamiaceae includes mostly herbs or shrubs, comprising about 236 genera and 7173 species (Stevens, 2012). Species within this family commonly are aromatic plants with quadrangular stems and verticillate inflorescences. Leaves are opposite or whorled, and are simple or occasionally pinnately compound; stipules are absent. Flowers are bisexual and zygomorphic. Currently, the genus Clerodendrum is classified in the subfamily Ajugoideae, being one of several genera reassigned from Verbenaceae to Lamiaceae in the 1990s, based on phylogenetic analysis of morphological and molecular data. The genus Clerodendrum includes about 150 species that are distributed worldwide in tropical and subtropical areas (Stevens, 2012).
Description
Top of pageShrubs up to 3 m tall, finely pubescent throughout, branches and stems quadrangular. Leaves membranous, broadly ovate to triangular-ovate, 6-25 cm long, 5-25 cm wide, both surfaces sparsely to moderately strigillose, margins coarsely and irregularly dentate, apex acute, and base cordate to truncate. Inflorescences terminal, cymose, densely many-flowered, subsessile or short-pendulate, often subtended by a pair of foliaceous bracts, bracteoles numerous, oblong or elliptic, 1.5-3 cm long, strigillose, especially along the margins. Flowers are fragrant; calyx purple or red, sometimes with white spots, campanulate, 10-15 mm long, 5-lobed, the lobes anceolate, apex acuminate; corolla pale pink, usually doubled by petaloid stamens; stamens and ovary usually modified into extra petals. Fruits are rarely developed (Liogier, 1995; Wagner et al., 1999).
Distribution
Top of pageC. chinense is native to southern Asia (probably China and Vietnam). The invasive nature of this species has allowed it to become established in numerous tropical and subtropical areas throughout North America (Florida, Hawaii and Mexico), Central America, South America, West Indies, and the Pacific Islands.
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 |
---|---|---|---|---|---|---|---|
Asia |
|||||||
China | Present | Present based on regional distribution. | |||||
-Fujian | Present | Native | |||||
-Guangdong | Present | Native | |||||
-Guangxi | Present | Native | |||||
-Guizhou | Present | Native | |||||
-Yunnan | Present | Native | |||||
Hong Kong | Present | Native | |||||
Indonesia | Present | Introduced | |||||
Japan | Present | Introduced | |||||
Malaysia | Present | Introduced | |||||
Singapore | Present | Introduced | Cultivated | ||||
Taiwan | Present | Native | |||||
Thailand | Present | Introduced | |||||
Vietnam | Present | Native | |||||
North America |
|||||||
Anguilla | Present, Widespread | Introduced | |||||
Bahamas | Present | Introduced | Reported in a 1920 collection made by Britton & Millspaugh | ||||
Barbados | Present, Widespread | Introduced | |||||
Belize | Present | Introduced | Ornamental | ||||
Bermuda | Present | Introduced | Reported in a 1918 collection made by N.L. Britton | ||||
Costa Rica | Present | Introduced | Ornamental | ||||
Cuba | Present | Introduced | 1900 | Invasive | Date of introduction is taken from collections housed in the Smithsonian Herbarium | ||
Dominica | Present, Widespread | Introduced | |||||
Dominican Republic | Present | Introduced | 1920 | Date of introduction is taken from collections housed in the Smithsonian Herbarium | |||
El Salvador | Present | Introduced | |||||
Grenada | Present, Widespread | Introduced | |||||
Guadeloupe | Present, Widespread | Introduced | |||||
Guatemala | Present | Introduced | Ornamental | ||||
Haiti | Present | Introduced | 1920 | Date of introduction is taken from collections housed in the Smithsonian Herbarium | |||
Honduras | Present | Introduced | Ornamental | ||||
Jamaica | Present | Introduced | 1904 | Date of introduction is taken from collections housed in the Smithsonian Herbarium | |||
Martinique | Present, Widespread | Introduced | |||||
Mexico | Present | Introduced | Chiapas | ||||
Montserrat | Present, Widespread | Introduced | |||||
Nicaragua | Present | Introduced | Ornamental | ||||
Panama | Present | Introduced | Ornamental | ||||
Puerto Rico | Present | Introduced | 1901 | Invasive | Date of introduction is taken from collections housed in the Smithsonian Herbarium | ||
Saint Lucia | Present, Widespread | Introduced | |||||
Saint Vincent and the Grenadines | Present, Widespread | Introduced | |||||
U.S. Virgin Islands | Present | Introduced | Invasive | St. Thomas | |||
United States | Present | Present based on regional distribution. | |||||
-Florida | Present | Introduced | Cultivated | ||||
-Hawaii | Present | Introduced | 1865 | Invasive | Found in wet pastures and forests on all main islands except Ni’ihau (Motooka et al., 2003) | ||
Oceania |
|||||||
Australia | Present | Present based on regional distribution. | |||||
-Queensland | Present | Introduced | Cultivated | ||||
Cook Islands | Present | Introduced | Invasive | Aitutaki Atoll and Rarotanga Islands | |||
Federated States of Micronesia | Present | Introduced | Invasive | Kosrae, Chuuk and Pohnpei Islands. Under eradication on Pohnpei | |||
Fiji | Present | Introduced | Invasive | Rotuma, Taveuni, Vanua Levu, and Viti Levu Islands | |||
French Polynesia | Present | Introduced | Invasive | Tahiti, Moore, Havai, Maketea and Raevavae Islands | |||
Niue | Present, Widespread | Introduced | Invasive | ||||
Papua New Guinea | Present | Introduced | Invasive | Cultivated | |||
Samoa | Present | Introduced | Invasive | Ofu, Olosega, Ta’u and Tutuila Islands; Original citation: Space and Flynn (2002) | |||
South America |
|||||||
Chile | Present | Introduced | Cultivated | ||||
Colombia | Present | Introduced | Antioquia | ||||
Ecuador | Present | Introduced | |||||
-Galapagos Islands | Present | Introduced | St. Cruz and St. Cristobal Islands | ||||
Peru | Present | Introduced | Cultivated |
History of Introduction and Spread
Top of pageIn Hawaii, C. chinense was first collected in 1864-1865 and currently is an invasive weed that can be found in wet pastures and forests on all main islands except on Ni’ihau (Motooka et al., 2003). In the West Indies, this species was probably introduced as an ornamental plant in the nineteenth century. The first records of this species from Puerto Rico come from the collections of A.P. Garber in 1880 and from P.E. Sintenis in 1885 (Urban, 1911; Smithsonian Herbarium). In Puerto Rico this species was reported by Britton and Wilson (1925) as escaped from cultivation in lower and middle elevations and Vélez (1950) as one of the worst weeds in coffee plantations. Later, this species has been collected in Cuba (1900), Jamaica (1904), Dominican Republic and Haiti (1920). Currently, C. chinense is becoming “widespread” in the Lesser Antilles on the islands of Antigua, Barbados, Dominica, Grenada, Guadeloupe, Martinique, Montserrat, St. Lucia, and St. Vincent (Broome et al., 2007). In American Samoa and the Pacific Islands (Cook Islands, Fiji, Niue, Tonga, and Western Samoa) since 2002 this species is classified as a ‘weed” that has to be monitored closely (Space and Flynn, 2002; PIER et al., 2012).
Risk of Introduction
Top of pageThe risk of introduction of C. chinense is high. This species is commonly planted as an ornamental mainly for its foliage and showy flowers, but it produces large amounts of root suckers which can rapidly spread the plant to form dense thickets. The risk of introduction of stems and/or roots as a contaminant of garden soils remains high in those countries where this species is planted. Additionally, C. chinense is still sold in the nursery and landscape trade in many countries and thus it is available for further dispersal. The use of this species for nurseries, gardens, and landscaping should be discouraged and it should be monitored closely for spread.
Habitat
Top of pageC. chinense is a rapidly growing shrub that can be found planted in gardens and has the potential to rapidly invade pastures, forest edges, roadsides, and waste grounds. This species prefers to grow in moist environments, full sunlight, with fertile soils, but it can tolerate shade and grow in disturbed areas. In Hawaii, it can be found forming dense canopies in pastures, along streams, and along forest edges, shading out the understory (Motooka et al., 2003). In Fiji, C. chinense is cultivated as an ornamental from near sea level to an elevation of about 900 m, and it is a common element in thickets, coconut plantations, and along roadsides (Smith, 1991).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | ||||
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Disturbed areas | Principal habitat | Natural |
Terrestrial | Managed | Rail / roadsides | Principal habitat | Natural |
Terrestrial | Managed | Urban / peri-urban areas | Principal habitat | Natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Wetlands | Present, no further details | Harmful (pest or invasive) |
Biology and Ecology
Top of pageGenetics
There are no specific genetic studies on this species. However, for many Clerodendrum species, studies available indicate that they are polyploids with a high chromosome number (2n = 46, 48, or 52; Yuan et al., 2010).
Reproductive Biology
Species in the genus Clerodendrum have an unusual pollination syndrome which avoids self-pollination. The mating system in this genus combines dichogamy and herkogamy. Clerodendrum species have flowers that are protandrous. In these flowers, the stamens and the style are curled upwards tightly inside the flower bud. When the flowers open, the filaments and style start uncoiling. While the filaments project to the centre, the style continues to bend down towards the lower side of the flower. This is the functional male phase. After pollen has been released, the filaments curl back sideways and the style with its receptive stigma (female phase) projects back to the centre, taking the position occupied by the stamens in the male phase (Yuan et al., 2010).
Physiology and Phenology
C. chinense has been collected in flower throughout the year in the West Indies (Smithsonian US Herbarium). In North America, the flowering phase has been reported from late spring to early summer.
Longevity
C. chinense is a rapidly growing perennial shrub.
Environmental Requirements
C. chinense grows in moist environments (annual rainfall greater than 1000 mm) in tropical and sub-tropical climates. This species prefers to grow in areas with full sunlight exposure and fertile soils (pH 5-7). However, C. chinense is also a shade-tolerant and thus it is able to grow in the understory.
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
Af - Tropical rainforest climate | Preferred | > 60mm precipitation per month | |
Am - Tropical monsoon climate | Tolerated | Tropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25])) | |
Aw - Tropical wet and dry savanna climate | Tolerated | < 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25]) | |
Cf - Warm temperate climate, wet all year | Tolerated | Warm average temp. > 10°C, Cold average temp. > 0°C, wet all year |
Soil Tolerances
Top of pageSoil drainage
- free
- seasonally waterlogged
Soil reaction
- acid
- neutral
Soil texture
- light
- medium
Special soil tolerances
- saline
- shallow
Natural enemies
Top of pageNatural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Phyllocharis undulata | Herbivore | Adults | to genus | Hawaii and Pacific Islands |
Notes on Natural Enemies
Top of pagePhyllocharis undulata is a species of leaf-eater beetle found in Laos, Cambodia, Vietnam, Peninsular Malaysia, Singapore, Java, Lombok and Timor. This species feeds on various species of Clerodendrum, including C.inerme, C. chinense, and C. calamitosum. It has been considered as a biological control agent against C. chinense (Julien, 1992). Further studies are needed to determine if this beetle species is adequately host-specific and the viability of its application as a biological control agent.
Means of Movement and Dispersal
Top of pageC. chinense is primarily dispersed by root suckers. These root suckers can grow rapidly and when they find suitable environmental conditions they develop and establish new trees. Seeds and fruits are rarely produced (Liogier, 1995).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Medicinal use | Use in traditional Chinese medicine | Yes | Flora of China Editorial Committee (2012) | |
Ornamental purposes | Common in gardens | Yes | Yes | PIER (2012) |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Debris and waste associated with human activities | Species produces root suckers | Yes | ||
Sold in the nursery and landscape trade | Yes | Yes | ||
Plants or parts of plants | Yes | Yes | PIER (2012) | |
Soil, sand and gravel | Yes | Yes | PIER (2012) |
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Negative |
Environment (generally) | Negative |
Environmental Impact
Top of pageC. chinense has been identified as an invasive weed. This is a very aggressive shrub that grows rapidly and form dense thickets along roadsides, waste grounds, streams, and forest edges. The invasive nature of this species has allowed it to become dominant in areas where it was planted and consequently it has the potential to out-compete native vegetation.
Risk and Impact Factors
Top of page- Invasive in its native range
- Proved invasive outside its native range
- Has a broad native range
- Abundant in its native range
- Highly adaptable to different environments
- Tolerant of shade
- Highly mobile locally
- Fast growing
- Has high reproductive potential
- Reproduces asexually
- Altered trophic level
- Damaged ecosystem services
- Ecosystem change/ habitat alteration
- Loss of medicinal resources
- Modification of fire regime
- Monoculture formation
- Negatively impacts tourism
- Reduced native biodiversity
- Threat to/ loss of endangered species
- Threat to/ loss of native species
- Competition - monopolizing resources
- Competition - shading
- Rapid growth
- Rooting
- Highly likely to be transported internationally accidentally
- Highly likely to be transported internationally deliberately
Uses
Top of pageRoots and leaves of C. chinense have been used in traditional Chinese medicine for the treatment of rheumatism, asthma, and inflammatory diseases.
This species is still sold in the nursery and landscape trade. People frequently utilize this plant in gardens because it is attractive to bees, butterflies, and birds.
Uses List
Top of pageGeneral
- Botanical garden/zoo
Medicinal, pharmaceutical
- Traditional/folklore
Ornamental
- Potted plant
- Propagation material
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.
Physical/Mechanical Control
Mechanical control is difficult: continual slashing will slow spread but not prevent it. Vertical barriers in the soil may prevent further spread if deep enough (PIER, 2012).
Biological Control
The chrysomelid beetle Phyllocharis undulata is a prospective biocontrol agent (Julien, 1992; PIER, 2012). Further studies in this area are needed.
Chemical Control
The use of chemicals to control C. chinense has to be performed very carefully. Herbicides containing triclopyr butoxyethyl ester are suggested as possible herbicides for Western Samoa. Work carried out in Western Samoa has shown that metsulfuron-methyl ester produces effective control. It has been recommended that the plants be cut and the new growth sprayed with herbicide (Waterhouse, 1993). Young plants can be sprayed with a herbicide such as 3,5,6-trichloro-2-pyridinyloxyacetic acid butoxyethyl ester (PIER, 2012). Motooka et al. (2003) suggested that hormone-type herbicides in timely repeat applications will control this weed.
Gaps in Knowledge/Research Needs
Top of page1) Studies on environmental requirements for establishment.
2) Genetic studies to determine variability.
3) Studies assessing the impact of this exotic species on native plants are needed.
4) Recommendations for management and control (biological and chemical control) in invaded areas.
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
Adams CD, 1972. Flowering Plants of Jamaica. University of the West Indies, 267.
Britton NL, 1918. Flora of Bermuda. New York, USA: Charles Scribner's Sons. 585 pp.
Britton NL; Millspaugh CF, 1920. The Bahama Flora. New York, USA: NL Britton & CF Millspaugh.
Britton NL; Wilson P, 1925. Botany of Porto Rico and the Virgin Islands. Scientific Survey of Porto Rico & Virgin Islands, Volume 6
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
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
Davidse G; Sousa Sánchez M; Knapp S; Chiang Cabrera F, 2012. Rubiaceae a Verbenaceae. Flora Mesoamericana, 4:1-533.
Englberger K, 2009. Invasive weeds of Pohnpei: A guide for identification and public awareness. Kolonia, Federated States of Micronesia: Conservation Society of Pohnpei, 29 pp.
Flora of China Editorial Committee, 2012. Flora of China Web. Cambridge, USA: Harvard University Herbaria. http://flora.huh.harvard.edu/china/
González-Torres LR; Rankin R; Palmarola A (eds), 2012. Invasive plants of Cuba. (Plantas Invasoras en Cuba.) Bissea: Boletin sobre Conservacion de Plantad del Jardin Botanico Nacional, 6:1-140.
Idárraga-Piedrahita A; Ortiz RDC; Callejas Posada R; Merello M, 2011. [English title not available]. (Flora de Antioquia.) Catálogo de las Plantas Vasculares, vol. 2. Listado de las Plantas Vasculares del Departamento de Antioquia:939 pp.
Liogier HA, 1995. Descriptive flora of Puerto Rico and adjacent islands: Spermatophyta, Volume IV. Melastomataceae to Lentibulariaceae. San Juan, Puerto Rico: La Editorial, UPR.
PIER, 2012. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Smith AC, 1991. Flora Vitiensis nova: A new flora of Fiji. Lawai, Kauai, Hawai`i. National Tropical Botanical Garden, Volume 5, 626 pp.
Space JC; Flynn T, 2000. Report to the Government of Niue on invasive plant species of environmental concern. USDA Forest Service, Honolulu, 34.
Space JC; Flynn T, 2002a. Report to the Government of Samoa on invasive plant species of environmental concern. Honolulu, USA: USDA Forest Service, 83 pp.
Space JC; Waterhouse B; Denslow J; Nelson D; Waguk EE, 2000. Invasive plant species on Kosrae, Federated States of Micronesia. Honolulu, USA: USDA Forest Service, 43 pp.
Stevens PF, 2012. Angiosperm Phylogeny Website. http://www.mobot.org/MOBOT/research/APweb/
Urban I, 1911. Verbenaceae. Symbolae Antillanae Seu Fundamenta Florae Indiae Occidentalis, 4(538).
USDA-ARS, 2012. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx
USDA-NRCS, 2012. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/
Velez I, 1950. Plantas Indeseables en los Cultivos Tropicales. Rio Piedras, Puerto Rico: Editorial Universitaria.
Wagner WL; Herbst DR; Sohmer SH, 1999. Manual of the Flowering Plants of Hawaii, Revised ed. Honolulu, USA: University of Hawaii Press.
Wunderlin RP; Hansen BF, 2003. Atlas of Florida Vascular Plants. Institute for Systematic Biology, University of South Florida, Tampa, USA. http://www.plantatlas.usf.edu/.
Zuloaga FO; Morrone O; Belgrano MJ; Marticorena C; Marchesi E, 2008. [English title not available]. (Catálogo de las Plantas Vasculares del Cono Sur (Argentina, Sur de Brasil, Chile, Paraguay y Uruguay).) Monographs in Systematic Botany from the Missouri Botanical Garden, 107:1-3348.
Distribution References
Adams C D, 1972. Flowering plants of Jamaica. Mona, Jamaica: University of the West Indies. 848 pp.
Britton N L, 1918. Flora of Bermuda. New York, USA: C. Scribner's Sons.
Britton N L, Millspaugh C F, 1920. The Bahama Flora. New York, USA: NL Britton & CF Millspaugh.
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
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
Davidse G, Sousa Sánchez M, Knapp S, Chiang Cabrera F, 2012. (Rubiaceae a Verbenaceae). In: Flora Mesoamericana, 4 1-533.
Flora of China Editorial Committee, 2012. Flora of China Web., Cambridge, USA: Harvard University Herbaria. http://flora.huh.harvard.edu/china/
González-Torres LR, Rankin R, Palmarola A, 2012. Invasive plants of Cuba. (Plantas Invasoras en Cuba). In: Bissea: Boletin sobre Conservacion de Plantad del Jardin Botanico Nacional, 6 [ed. by González-Torres LR, Rankin R, Palmarola A]. 1-140.
Idárraga-Piedrahita A, Ortiz RDC, Callejas Posada R, Merello M, 2011. [English title not available]. (Flora de Antioquia). In: Catálogo de las Plantas Vasculares, 2 Listado de las Plantas Vasculares del Departamento de Antioquia. 939 pp.
Liogier HA, 1995. Descriptive flora of Puerto Rico and adjacent islands: Spermatophyta, Volume IV. Melastomataceae to Lentibulariaceae., San Juan, Puerto Rico: La Editorial, UPR.
PIER, 2012. Pacific Islands Ecosystems at Risk., Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Space JC, Flynn T, 2000. Report to the Government of Niue on invasive plant species of environmental concern., Honolulu, USDA Forest Service. 34.
Wagner WL, Herbst DR, Sohmer SH, 1999. Manual of the Flowering Plants of Hawaii, Revised ed., Honolulu, USA: University of Hawaii Press.
Wunderlin RP, Hansen BF, 2003. Atlas of Florida Vascular Plants., Tampa, USA: Institute for Systematic Biology, University of South Florida. http://www.plantatlas.usf.edu/
Links to Websites
Top of pageWebsite | URL | Comment |
---|---|---|
Flora of the West Indies | http://botany.si.edu/antilles/WestIndies/ | |
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gateway | https://doi.org/10.5061/dryad.m93f6 | Data source for updated system data added to species habitat list. |
Pacific Island Ecosystems at Risk (PIER) | http://www.hear.org/Pier/index.html | |
Plants of the Eastern Caribbean | http://ecflora.cavehill.uwi.edu/index.html | |
USDA Germplasm Resources Information Network | http://www.ars-grin.gov/ |
Contributors
Top of page21/09/12 Original text by:
Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH, Washington DC, USA
Pedro Acevedo-Rodríguez, Department of Botany-Smithsonian NMNH, Washington DC, USA
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