Datasheet
Callisia fragrans (basketplant)
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Pictures
Top of page| Picture | Title | Caption | Copyright |  | Title | Habit |
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| Caption | Callisia fragrans ground cover in disturbed dry forest. Saint Lucia, West Indies. January 2009. |
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| Copyright | ©Roger Graveson-2009 |
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| Habit | Callisia fragrans ground cover in disturbed dry forest. Saint Lucia, West Indies. January 2009. | ©Roger Graveson-2009 |
 | Title | Habit, showing flowers and foliage |
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| Caption | Callisia fragrans showing flowers and foliage, Saint Lucia, West Indies. January 2009. |
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| Copyright | ©Roger Graveson-2009 |
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| Habit, showing flowers and foliage | Callisia fragrans showing flowers and foliage, Saint Lucia, West Indies. January 2009. | ©Roger Graveson-2009 |
Identity
Top of pagePreferred Scientific Name
- Callisia fragrans (Lindl.) Woodson (1942)
Preferred Common Name
Other Scientific Names
- Rectanthera fragrans (Lindl.) O. Deg
- Spironema fragrans Lindl.
International Common Names
- English: chain plant; inch plant; fragrant inch plant
Local Common Names
- Australia: purple succulent
- English: spironema
Summary of Invasiveness
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Callisia fragrans is a reasonably common cultivated, ornamental, perennial herb. It can be grown as a pot or basket plant or as ground cover in tropical or subtropical climates. In these warm climates, parts of the plant may break off or be spread by gardeners and start to grow. Occasionally considered invasive, it is established on Gros Piton, a World Heritage Site in Saint Lucia. In this habitat, its rapid spread is beginning to threaten native forest and displace many indigenous species.
Taxonomic Tree
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- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Monocotyledonae
- Order: Commelinales
- Family: Commelinaceae
- Genus: Callisia
- Species: Callisia fragrans
Notes on Taxonomy and Nomenclature
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The basionym is Spironema fragrans Lindl. published in Edwards's Botanical Register 26: pl. 47. 1840. A synonym is Rectanthera fragrans (Lindl.) O. Deg. published in Flora Hawaiiensis 1: 62. 1932. However the accepted name is Callisia fragrans (Lindl.) Woodson published in Annals of the Missouri Botanical Garden 29(3): 154. 1942.
Description
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Wagner et al. (1999) describes the plant as a "perennial herb; stems fleshy, up to 1 m long, branched, with long stolons at base. Leaves clustered toward the ends of the stem, scattered below, elliptic-lanceolate, 18-25 cm long, 3.5-4 cm wide, base prominently veined, clasping, ciliate, often striped with purple. Flowers in compact pairs of cymes arranged in panicles up to 0.6 m long, each cyme pair subtended by 3-toothed bracts 10-15 mm long; sepals white-transparent, scarious, lanceolate, 5-6 mm long; petals glossy, white-transparent, thin, wilting by noon, narrowly ovate, erose, ca 6 mm long; stamens 6".
Plant Type
Top of pageHerbaceous
Perennial
Vegetatively propagated
Distribution
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Native to Mexico, C. fragrans is a popular pot plant and is cultivated throughout Europe, Asia and the Americas. It also appears to be cultivated as a herbal medicinal plant in Russia (see http://www.callisia.org/). Countries in which it is only present as a cultivated plant are mostly not recorded in the following table. GBIF (2013) has 66 records from Mexico, 48 from USA, 8 from Puerto Rico, 4 from US Virgin Islands and only 1 or 2 from the remaining 10 countries.
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.
| Country | Distribution | Last Reported | Origin | First Reported | Invasive | References | Notes | ASIA |
| Singapore | Present only in captivity/cultivation | | Introduced | | Not invasive | Chong et al., 2009 | |
NORTH AMERICA |
| Mexico | Present | | Native | | Not invasive | USDA-ARS, 2011 | |
| USA | | | | | | | |
| -Florida | Present | | Introduced | | | Atlas of Florida Vascular Plants, 2012 | |
| -Hawaii | Present | | Introduced | | Invasive | Wagner et al., 1999; Starr et al., 2003 | Kaua‘i Island, Maui Island, O‘ahu Island |
| -Louisiana | Present | | Introduced | | | USDA-NRCS, 2012 | |
CENTRAL AMERICA AND CARIBBEAN |
| Barbados | Present only in captivity/cultivation | | Introduced | | Not invasive | CMS Sean, University of the West Indies, Barbados, personal communication | |
| British Virgin Islands | Present only in captivity/cultivation | | Introduced | | Not invasive | Acevedo-Rodriguez & Strong, 2012 | |
| Curaçao | Present only in captivity/cultivation | | Introduced | | Not invasive | A van den Bos, www.botanypictures.com, personal communication, 2012 | |
| Dominican Republic | Present only in captivity/cultivation | | Introduced | | Not invasive | Acevedo-Rodriguez & Strong, 2012 | |
| Guadeloupe | Restricted distribution | | Introduced | | | Fabien Barthelat, IUCN, personal communication, 2013 | Commonly cultivated, escaped and naturalized in dry parts of Guadeloupe mainland, Marie-Galante, Les Saintes, Saint Martin and Saint Barth |
| Haiti | Present only in captivity/cultivation | | Introduced | | Not invasive | Acevedo-Rodriguez & Strong, 2012 | |
| Jamaica | Present only in captivity/cultivation | | Introduced | | Not invasive | Jamalco South Manchester EIA, 2012 | |
| Netherlands Antilles | Present only in captivity/cultivation | | Introduced | | Not invasive | Madden, http://www.natureonstatia.com, personal communication, 2012 | Statia |
| Puerto Rico | Present | | Introduced | | | USDA-NRCS, 2012 | |
| Saint Lucia | Localised | | Introduced | | Invasive | Graveson, 2012 | Invasive on Gros Piton |
| Saint Vincent and the Grenadines | Widespread | | Introduced | | Not invasive | Fr de Silva M, Church of the Immaculate Conception, Mayreau, personal communication, 2012 | Bequia and Mustique |
| United States Virgin Islands | Present only in captivity/cultivation | | Introduced | | Not invasive | Acevedo-Rodriguez & Strong, 2012; USDA-NRCS, 2012 | |
SOUTH AMERICA |
| Ecuador | Present only in captivity/cultivation | | Introduced | | Not invasive | Charles Darwin Foundation, 2008 | San Cristóbal Island |
OCEANIA |
| Australia | | | | | | | |
| -Lord Howe Is. | Present | | Introduced | | | Queensland Government, 2013 | |
| -New South Wales | Present | | Introduced | | | Queensland Government, 2013 | |
| -Queensland | Present | | Introduced | | Invasive | Csurhes & Edwards, 1998 | SE Queensland |
| Cook Islands | Present only in captivity/cultivation | | Introduced | | Not invasive | Space & Flynn, 2002 | Aitutaki Atoll, Atiu Island |
| French Polynesia | Present only in captivity/cultivation | | Introduced | | Not invasive | Lorence & Wagner, 2008 | Hiva Oa Island, Ua Pou Island |
| Marshall Islands | Present only in captivity/cultivation | | Introduced | | Not invasive | Vander, 2003 | Majuro (Mãjro) Atoll |
| Micronesia, Federated states of | Present only in captivity/cultivation | | Introduced | | Not invasive | Lorence & Flynn, 2010 | Kosrae Island |
| Palau | Present only in captivity/cultivation | | Introduced | | Not invasive | Space et al., 2009 | Ngercheu Island |
Risk of Introduction
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Although the plant is not yet cultivated in all tropical and subtropical countries, it is likely to spread from where it is found; escaping into waste land around houses and more than likely establishing itself among native vegetation.
Habitat List
Top of page| Category | Habitat | Presence | Status | | Terrestrial-managed |
| Disturbed areas | Present, no further details | |
| Terrestrial-natural/semi-natural |
| Natural forests | Present, no further details | Harmful (pest or invasive) |
| Rocky areas / lava flows | Present, no further details | |
Biology and Ecology
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Reproductive Biology
Flowers are formed in late winter or early spring but spread seems to be by vegetative reproduction, with individual plants removed from the colony-forming roots. This can be accidental or more commonly, as a result of gardening activities. Some species of Callisia are wind-pollinated, but the flowers of C. fragrans are strongly scented, as the name suggest, and are presumably insect-pollinated (Kubitski et al. 1998). The fruit are small, three-celled, capsules.
Longevity
A colony in a vacant plot at Massade, Gros Islet, Saint Lucia has been present and increasing in size for ten years. It managed to survive a 5-month drought during 2009/2010 (R. Graveson, Saint Lucia, personal observation, 2012).
Population Size and Density
Large perennial drought-resistant colonies are formed.
Nutrition
The rosette pattern of leaves and the dense colony may result in little rainwater entering the soil as most is collected by the plant.
Environmental Requirements
C. fragrans needs full or at least partial sunlight, relatively high temperatures (US Hardiness Zones 10b-11) and a more-or-less neutral soil (pH 6.1-7.8) (Dave’s Garden, 2013).
Climate
Top of page| Climate | Status | Description | Remark | | A - Tropical/Megathermal climate | Preferred | Average temp. of coolest month > 18°C, > 1500mm precipitation annually | |
| 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]) | |
Means of Movement and Dispersal
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Natural Dispersal (Non-Biotic)
Possibly by viable fruits but there is no record of this in the literature.
Intentional Introduction
Gardeners introduce C. fragrans to new areas as a garden ground-cover ornamental. Local spread is by individuals breaking off and rooting.
Impact Summary
Top of page| Category | Impact | | Environment (generally) | Negative |
Environmental Impact
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Impact on Habitats
Globally C. fragrans tends to grow in disturbed secondary forest and moist semi-open areas. Where it has become invasive in the World Heritage Site in Saint Lucia, it grows on the steep middle slopes of Gros Piton. In this seasonal, semi-open, native deciduous forest it forms carpets on large rocks and the ground in between. The main populations of C. fragrans have established close to the main trail to the summit (Graveson, 2012).
Impact on Biodiversity
As it forms carpets it replaces indigenous species such as Callisia repens, Peperomia trifolia, P. myrtifolia and Gibasis geniculata (Graveson, 2012).
Social Impact
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Globally there is no information, except for Saint Lucia.
In Saint Lucia the Gros Piton trail is an important source of income to the Fonds Gens Libres community. It is conceivable that if C. fragrans comes to dominate the ground cover in the middle elevations, the publicity given to that may negatively affect tourist numbers. In addition, it is likely that eradication of C. fragrans will affect the community financially, as they may have to use income generated from the guided walks to tourists to fund the eradication programme (Graveson, 2012).
Risk and Impact Factors
Top of pageInvasiveness
- Fast growing
- Gregarious
- Long lived
- Proved invasive outside its native range
- Reproduces asexually
- Tolerant of shade
Likelihood of entry/control
- Highly likely to be transported internationally deliberately
- Highly likely to be transported internationally illegally
Uses List
Top of pageMedicinal, pharmaceutical
- Source of medicine/pharmaceutical
Ornamental
- Potted plant
- Propagation material
Prevention and Control
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SPS Measures
Prohibition of planting as an ornamental in high-risk areas would be a useful measure.
Public Awareness
This species is easily recognizable in the wild as it forms conspicuous colonies. If reported early, the patch can be physically removed with little difficulty. Thus, public awareness in high risk areas will aid in preventing this species from establishing itself in the wild.
Eradication
Despite C. fragrans being reported as invasive in some countries, little information is available on its prevention and control. It may be that its impact is not major enough to warrant prevention and control measures. Its size, semi-succulent texture and growth habit are similar to the invasive Tradescantia spathacea and methods used to control this plant may be suited to control C. fragrans.
Containment/Zoning
Technique suitable for eradication will also be appropriate for containment and zoning where complete eradication is not possible.
Physical/Mechanical Control
Hand pulling of small areas of C. fragrans infestation is possible but re-growth may still occur. Careless removal may cause further spreading of the basketplant.
Movement Control
Discouragement of planting in areas where there is a high risk of spread into native forest would be a useful measure.
Chemical Control
Larger areas need herbicide spraying with follow-up spraying for re-growth. Spraying two to three times over several months is effective with glyphosate (MEPA, 2013). The Australian Government (2013) also suggests glyphosate with or without metsulfuron.
Gaps in Knowledge/Research Needs
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A pilot scheme is required to look into details of a protocol for eradication, involving a mix of physical and chemical measures.
Research is required to investigate whether the formation of carpets of C. fragrans changes soil conditions in a manner which might affect tree seedlings.
In addition, studies are required to investigate the extent to which carpets of C. fragrans prevent water from entering the soil.
References
Top of pageAcevedo-Rodríguez PT, Strong MT, 2012. Catalogue of seed plants of the West Indies. Washington DC, USA: Smithsonian Institution Scholarly Press, 1221 pp.
Atlas of Florida Vascular Plants, 2012. Atlas of Florida Vascular Plants. Florida, USA: University of South Florida. http://www.florida.plantatlas.usf.edu/
Australian Government, 2013. Permit to allow minor use of an agnet chemical product for control of various environmental weeds using helicopter spot-spraying equipment, Permit Number PER12363., Australia: Australian Government. http://www.farmoz.au/Permit/FARMOZ/PER12363
Charles Darwin Foundation, 2008. Database inventory of introduced plant species in the rural and urban zones of Galapagos. Galapagos, Ecuador: Charles Darwin Foundation.
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
Csurhes S, Edwards R, 1998. Potential environmental weeds in Australia: candidate species for preventive control. Canberra, Australia: Biodiversity Group, Environmental Australia, 202 pp. http://www.environment.gov.au/biodiversity/invasive/weeds/publications/books/pubs/potential.pdf
Dave's Garden, 2013. PlantFiles: Basket Plant, Chain Plant, Inch Plant. Callisia fragrans. Dave's Garden. http://davesgarden.com/guides/pf/go/54577/
GBIF, 2012. Global Biodiversity Information Facility. Global Biodiversity Information Facility (GBIF). http://data.gbif.org
Graveson RS, 2012. Survey of invasive alien plant species on Gros Piton, Saint Lucia. Project No. GFL / 2328- 2713-4A86, GF-1030-09-03. Project No. GFL / 2328- 2713-4A86, GF-1030-09-03, GFL / 2328- 2713-4A86, GF-1030-09-03. Catsries, Saint Lucia: Department of Forestry.
HEAR, 2012. Alien species in Hawaii. Hawaii ecosystems at risk. Honolulu, Hawaii: University of Hawaii. http://www.hear.org/AlienSpeciesInHawaii/index.html
Howard RA, 1974. Flora of the Lesser Antilles, 1-6. Jamaica Plain, MA, USA: Arnold Arboretum of Harvard University.
Jamalco South Manchester EIA, 2012. Description of the Environment. Kingston, Jamaica: Conrad Douglas & Associates Ltd, 62. http://www.nepa.gov.jm/eias/Manchester/South%20Manchester/Final%20Report%20South%20Manchester%20EIA%20Jamalcopart2.pdf
Kubitzki K, Huber H, Rudall P, Stevens PS, 1998. Flowering Plants. Monocotyledons: Alismatanae and Commelinanae (except Gramineae). New York, USA: Sprinnger-Verlag, 511 pp.
Lorence DH, Flynn T, 2010. Checklist of the plants of Kosrae. Unpublished checklist. National Tropical Botanical Garden. Lawai, Hawaii: National Tropical Botanical Garden, 26.
Lorence H, Wagner DWL, 2008. Flora of the Marquesas islands. Flora of the Marquesas islands. National Tropical Botanical Garden and the Smithsonian Institution., unpaginated.
MEPA, 2013. MEPA Weed Control: Callisia fragrans. Queensland, Australia: Mt. Nero and Mt Glorious Environmental Protection Association. http://www.gloriousnebo.org.au/MEPA/psucculent.pdf
Mount Gravatt Environmental Group, 2012. Purple succulent Callisia fragrans. Queensland, Australia: Mount Gravatt Environmental Group. http://megoutlook.wordpress.com/tag/purple-succulent-callisia-fragrans/
Orchard AE, 1994. Flora of Australia. Oceanic islands 1, 49. Canberra, Australia: Australian Government Publishing Service.
PIER, 2012. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Queensland Government, 2013. Weeds of Australia. Queensland Biosecurity Edition. Purple Succulent Callisia fragrans. Queensland, Australia: Queensland Government. http://keyserver.lucidcentral.org/
Schvoong, 2012. Callisia fragrans family doctor plants. New York, USA: Schvoong.com. http://www.shvoong.com/medicine-and-health/dentistry-oral-medicine/2239832-callisia-fragrans-family-doctor-plant/
Space JC, Flynn T, 2002. Report to the Government of the Cook Islands on invasive plant species of environmental concern. Honolulu, USA: USAL USDA Forest Service, 146 pp.
Space JC, Lorence DH, LaRosa AM, 2009. Report to the Republic of Palau: 2008 update on Invasive Plant Species. Hilo, Hawaii, USA: USDA Forest Service, 227. http://www.sprep.org/att/irc/ecopies/countries/palau/48.pdf
Starr F, Martz K, Loope LL, 2003. New plant records from the Hawaiian Archipelago. Part 2: Notes. In: Records of the Hawaii Biological Survey for 2001-2002. Part 2: Notes. Bishop Museum Occasional Papers, 74 [ed. by Evenhuis, N. L. \Eldredge, L. G.]. Honolulu, Hawaii, USA: Bishop Museum Press, 23-34. http://www.hear.org/starr/publications/new_plant_records_2001.pdf
USDA-ARS, 2011. Germplasm Resources Information Network (GRIN). Online Database. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, USA: National Germplasm Resources Laboratory. http://www.ars-grin.gov/
USDA-NRCS, 2012. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/
Vander VN, 2003. The vascular plants of Majuro Atoll, Republic of the Marshall Islands. Atoll Research Bulletin, 503:1-141.
Wagner WL, Herbst DR, Sohmer SH, 1999. Manual of the flowering plants of Hawaii. Revised edition. Honolulu, Hawaii, USA: University of Hawaii Press/Bishop Museum Press, 1919 pp.
Contributors
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01/06/12 Original text by:
Roger Graveson, Consultant, Saint Lucia
Distribution Maps
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- = Present, no further details
- = Evidence of pathogen
- = Widespread
- = Last reported
- = Localised
- = Presence unconfirmed
- = Confined and subject to quarantine
- = See regional map for distribution within the country
- = Occasional or few reports