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  • Flowers of Clidemia hirta
  • General appearance of Clidemia hirta
  • Leaves of Clidemia hirta
  • Leaves and flowers of Clidemia hirta at Marihat in northern Sumatra, Indonesia (Photo: Colin Wilson)
  • Leaf and flower of Clidemia hirta at Marihat in northern Sumatra, Indonesia (Photo: Colin Wilson)
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Common name
kauresinga (English), kaurasiga (English), mbona na mbulamakau (English), ndraunisinga (English), roinisinga (English), vuti (English), soap bush (English), Hirten-Schwarzmundgewaechs (German), Koster's curse (English), faux vatouk (English), clidemia, kúi
Synonym
Melastoma hirtum , L.
Similar species
Summary
The invasive shrub Clidemia hirta is a problem in tropical forest understories in its introduced range, where it invades gaps in the forest, preventing native plant species from regenerating. The spread of Clidemia hirta has been linked to soil disturbances, particularly that caused by the wild pig, another invasive species. It has proven to negatively effect native ecosystems and is difficult to control in the Hawaiian archipelago. It is feared it will have a similar effect in other regions where it has been introduced such as in various Indian Ocean Islands (Seychelles), the Malaysian Peninsula and parts of Micronesia (Palau).
Species Description
Koster’s curse is a coarse perennial shrub up to 2m tall. The stems are covered with red bristles that lighten with age. The leaves are opposite, simple and petiolate. The ovate-to-oblong leaf blades are hairy with crenate margins. The surfaces appear pleated. Five major veins originate at the base of the leaf and extend to the apex. The inflorescence is a panicle that can be terminal or axillary. The calyx has five hairy linear lobes atop a long urceolate hypanthium. The corolla consists of five small white petals. The fruit is a hairy ovoid many seeded bluish-black berry (Weedy Plants of the US Undated).
Notes
Prolific in high rainfall areas, slow growing and poor fruiting in dry areas or dense shade.
Habitat Description
Clidemia hirta does not occur in forest in its native range (however, see below) but is a vigorous invader of tropical forest in its introduced range. For C. hirta, its absence from forest understory in its native range likely results in part from the strong pressures of natural enemies (DeWalt Denslow and Ickes 2004). In the lowlands of Central and South America and Caribbean Islands (where it is native) it colonises naturally and anthropogenically disturbed open areas such as pastures, riversides, roadsides, and tree plantations (DeWalt Denslow and Ickes 2004). In its introduced range C. hirta is abundant in open areas and gaps in the understory of old-growth forest (Smith 1992, Rejmánek 1996, Strahm 1999, in DeWalt Denslow and Ickes 2004). C. hirta appears to be more shade tolerant in its introduced range (Wester and Wood 1977, in DeWalt Denslow and Ickes 2004). \r\n
The following notes are taken from reports of the plant in its native range (from Peters 2001). In La Mucuy National Park in Venezuela, a montane tropical rain forest (ca 2200m elevation; mean annual rainfall ca1800mm), all C. Hirta plants in primary forest were beneath closed canopies. It was particularly prevalent along steep embankments with exposed soil. Even plants near trails were extensively shaded. Several gaps were searched but no C. Hirta plants were located, although other Clidemia species were found. At Caparo Forest Reserve, a lowland tropical deciduous forest (ca 150m elevatopm; mean annual rainfall ca 1200mm) in Venezuela, C. Hirta occurs primarily along trails, but also in the undisturbed understory, and seldom in full sunlight. In another part of its native habitat, Trinidad, it is most common in wet, partially shaded sites, and prevalent along trails and roads, and at the sides of clearings (Taylor 1928, Cook 1929, in Peters 2001). A study conducted in 1994 north of Manaus, Brazil, found C. Hirta in the understory of young secondary forest (K. Ickes, pers. Comm.). Extensive searches for C. Hirta in Costa Rica have located the plant only in highly disturbed sites, such as roadsides, pastures, and tree plantations, but never in forest gaps at La Selva. (K. Ickes Pers. Comm., in Peters 2001).
Reproduction
Each fruit contains over 100 seeds and a mature plant produces in excess of 500 fruits each season. The seeds can remain dormant for up to four years in the soil (Smith Undated).
Flowering and fruiting occur throughout the year with prolific production of seeds (Peters 2001). Continuous flowering has been observed in areas where the rainfall exceeds 2 500mm/yr with no dry season. However in areas where rainfall is as low as 1 000mm/yr and where there is a dry season the plant does not fruit or flower much after the dry season has begun. Leaves fall off, growth ceases and some death of shoot tips occurs. As long as the drought does not last more than six months plants recover and resume reproduction within a short time (Smith Undated).
Pathway
The long-distance routes and methods of Clidemia hirta invasion are unknown, but it probably is introduced accidentally by people (Cronk and Fuller 1995, in Peters 2001). In Hawai'i spread of clidemia is thought to be due to people who work in or use forests (from Smith Undated). No one group is entirely responsible for the spread. Some abandoned clearings previously used to grow marijuana suggest that in West Maui, Hawai'i, marijuana growers are partly responsible for its spread. In other areas (O'ahu, Moloka'i and the Nounou and Na Pali Coast invasions on Kaua'i) invasions were observed along forest trails first suggesting that hikers were responsible. Vehicle spread was thought to be the method of spread of the weed to the Kilauea East Rift zone on Hawai'i island and the Wai'anae mountains on O'ahu. Yet other infestations are thought to be due to spread by pig hunters.Most alien populations of this plant are probably the result of deliberate ornamental introductions.

Principal source:

Compiler: Dr. Justin Gerlach, The Nature Protection Trust of Seychelles, Cambridge, UK & IUCN/SSC Invasive Species Specialist Group (ISSG)

Review: Dr. Justin Gerlach, The Nature Protection Trust of Seychelles, Cambridge, UK.

Publication date: 2006-07-24

Recommended citation: Global Invasive Species Database (2016) Species profile: Clidemia hirta. Downloaded from http://www.iucngisd.org/gisd/species.php?sc=53 on 10-12-2016.

General Impacts
Invasive plants present a major problem to conservationists because of their tendency to replace diverse natural vegetation with exotic monocultures (Cronk and Fuller 1995, Rejmánek 1996, in Peters 2001). Plant invasion poses a serious threat to forests because of its potential to reduce biodiversity and lead to the extinction of native flora and fauna (Usher 1991, in Peters 2001). Invasions may precipitate species extinction through either the direct displacement of native species by aliens or through the indirect effects of alien species on the ecosystem (Phillips 1997, in Peters 2001).\r\n
C. hirta may be present in a location without causing observable changes in an ecosystem for up to 30 years. For example, in both Hawaii and Fiji, ca 30 years elapsed between the first sighting of the species and the time that it was recognised as a conservation problem (Wester and Wood 1977, in Peters 2001). In Hawaiian communities, C. hirta may be replacing endemic species that formerly predominated, threatening their extinction (Wester and Wood 1977, in Peters 2001). The impact of this weed on native species and ecosystems is devastating and the rate at which it spread throughout the islands is alarming (Smith Undated). Its invasion into Hawaiian forests is apparently aided by a release from these herbivores and pathogens (DeWalt Denslow and Ickes 2004). It is a highly invasive shrub in the montane rain forests and cloud forests of Samoa, Fiji, Wallis and Futuna, and the Hawaiian Islands (Meyer 2000, in Binggeli Hall and Healey Undated). While C. hirta has not yet had the far-reaching ecological consequences at the Pasoh Forest Reserve (on the Malaysian peninsula) that have been documented in Fiji and Hawaii, some modification of the natural ecosystem seems likely, especially if the recent increase in disturbance continues. The results of at least one study have implied that by competing with native species in gaps, the C. hirta invasion in the Pasoh Forest Reserve, a previously undisturbed continental tropical forest, has the potential to alter forest regeneration. A survey on the status of invasive woody plant species in the western Indian Ocean found that the major environmental impact of invasive species in the region is the reduction of the native regeneration through competition by exotic species (Mauremootoo 2003). This becomes most apparent with thicket-forming species such as C. hirta (and also including Chrysobalanus icaco, Lantana camara, Psidium cattleianum, Ravenala madagascariensis, Rubus alceifolius and Syzygium jambos) (Mauremootoo 2003). The survey also rated C. hirta as one of the most problematic invasive species in the Comoros Archipelago and Réunion and as one of the main invasive species on Mauritius and the Seychelles (Mauremootoo 2003).
Management Info
Preventative measures: A Risk assessment of Clidemia hirta for the Pacific region was prepared by Pacific Island Ecosystems at Risk (PIER) using the Australian risk assessment system (Pheloung, 1995). The result is a score of 27 and a recommendation of: reject the plant for import (Australia) or species likely to be a pest (Pacific).\r\n

\r\nPhysical: Manual weeding may be effective for small populations. In healthy ecosystems Clidemia hirta's dominance is a temporary phenomenon with forest trees overshading it within 7 years.\r\n

\r\nGround disturbance created by feral pigs (Sus scrofa) plays a major role in the establishment of C. hirta and other populations of alien species in Hawaii (Smith 1993, Stone et al. 1993, in Peters 2001). These pigs are native to North Africa and Eurasia, including Malaysia, but are currently found on many oceanic islands and all continents except Antarctica (Lever 1985, in Peters 2001). They are omnivorous and obtain a substantial portion of their food by grubbing for roots, bulbs, fungi, invertebrates, and other belowground material (Aplet et al. 1991, Fensham 1993, Kotanen 1995, in Peters 2001). Severely grubbed areas may extend for more than a hectare, but are typically composed of many small (ca 1 m2) patches of ground disturbance. Through trampling, rooting, and preferential feeding, feral pigs in Hawaii have disturbed natural plant communities dramatically (Aplet et al. 1991, Stone 1993, in Peters 2001). Wild pigs may also act as agents of dispersal for introduced species including C. hirta(Stone and Loope 1987, in Peters 2001). Because of this link the possibility exists of controlling C. hirta by managing pig populations, especially at places where the link between soil disturbance and invasive plant spread has been established, such as at the Pasoh Forest Reserve (Malaysian peninsula).\r\n

\r\nDisturbance is a key element in the establishment and invasion of C. hirta. Wildfires, landslides, windstorms and other forms of soil disturbance (such as pig rooting) accelerate the dominance of this weed (Smith Undated; Peters 2001). In its native environment plants are confined to open areas and only become dominant about twelve months after disturbance, such as in slash-and-burn agricultural areas (Burkhart Pers. Comm, in Smith Undated). All new range extensions in Hawaii begin along the open edges of trails or other disturbed areas. In order to keep the weed out of an area the primary management objective should be to minimise and prevent disturbance (Smith Undated). \r\n

\r\nAll efforts to eradicate newly established populations of C. hirta in Hawaii failed when they were not initiated before first fruit set (Smith Undated). There have been many well-meaning attempts by volunteer groups to control the spread of C. hirta through pulling it by hand, unfortunately the effort is likely to fail. The seed bank produced by these plants is colossal over a very short period of time (Smith Undated). In order to effectively control an infested area by mechanical means eradication efforts must be conducted at least once a year for up to 10 years. Only two instances of successful control, Kamakou (Moloka'i) and Pu'u Kukui trail (Maui) are known (Smith Undated). Clidemia is susceptible to a number of herbicides but will regenerate unless further applications are made. Chemical control does not appear to be practical in Hawaii's native ecosystems, particularly those difficult to access (Smith Undated).\r\n

\r\nClick here for Information about remote sensing for understory invasive plants and documenting the spread of weeds.

Countries (or multi-country features) with distribution records for Clidemia hirta
Informations on Clidemia hirta has been recorded for the following locations. Click on the name for additional informations.
Lorem Ipsum
Location Status Invasiveness Occurrence Source
Details of Clidemia hirta in information
Status
Invasiveness
Arrival date
Occurrence
Source
Introduction
Species notes for this location
Location note
Management notes for this location
Impact
Mechanism:
Outcome:
Ecosystem services:
Impact information
Invasive plants present a major problem to conservationists because of their tendency to replace diverse natural vegetation with exotic monocultures (Cronk and Fuller 1995, Rejmánek 1996, in Peters 2001). Plant invasion poses a serious threat to forests because of its potential to reduce biodiversity and lead to the extinction of native flora and fauna (Usher 1991, in Peters 2001). Invasions may precipitate species extinction through either the direct displacement of native species by aliens or through the indirect effects of alien species on the ecosystem (Phillips 1997, in Peters 2001).\r\n
C. hirta may be present in a location without causing observable changes in an ecosystem for up to 30 years. For example, in both Hawaii and Fiji, ca 30 years elapsed between the first sighting of the species and the time that it was recognised as a conservation problem (Wester and Wood 1977, in Peters 2001). In Hawaiian communities, C. hirta may be replacing endemic species that formerly predominated, threatening their extinction (Wester and Wood 1977, in Peters 2001). The impact of this weed on native species and ecosystems is devastating and the rate at which it spread throughout the islands is alarming (Smith Undated). Its invasion into Hawaiian forests is apparently aided by a release from these herbivores and pathogens (DeWalt Denslow and Ickes 2004). It is a highly invasive shrub in the montane rain forests and cloud forests of Samoa, Fiji, Wallis and Futuna, and the Hawaiian Islands (Meyer 2000, in Binggeli Hall and Healey Undated). While C. hirta has not yet had the far-reaching ecological consequences at the Pasoh Forest Reserve (on the Malaysian peninsula) that have been documented in Fiji and Hawaii, some modification of the natural ecosystem seems likely, especially if the recent increase in disturbance continues. The results of at least one study have implied that by competing with native species in gaps, the C. hirta invasion in the Pasoh Forest Reserve, a previously undisturbed continental tropical forest, has the potential to alter forest regeneration. A survey on the status of invasive woody plant species in the western Indian Ocean found that the major environmental impact of invasive species in the region is the reduction of the native regeneration through competition by exotic species (Mauremootoo 2003). This becomes most apparent with thicket-forming species such as C. hirta (and also including Chrysobalanus icaco, Lantana camara, Psidium cattleianum, Ravenala madagascariensis, Rubus alceifolius and Syzygium jambos) (Mauremootoo 2003). The survey also rated C. hirta as one of the most problematic invasive species in the Comoros Archipelago and Réunion and as one of the main invasive species on Mauritius and the Seychelles (Mauremootoo 2003).
Red List assessed species 6: CR = 6;
Management information
Preventative measures: A Risk assessment of Clidemia hirta for the Pacific region was prepared by Pacific Island Ecosystems at Risk (PIER) using the Australian risk assessment system (Pheloung, 1995). The result is a score of 27 and a recommendation of: reject the plant for import (Australia) or species likely to be a pest (Pacific).\r\n

\r\nPhysical: Manual weeding may be effective for small populations. In healthy ecosystems Clidemia hirta's dominance is a temporary phenomenon with forest trees overshading it within 7 years.\r\n

\r\nGround disturbance created by feral pigs (Sus scrofa) plays a major role in the establishment of C. hirta and other populations of alien species in Hawaii (Smith 1993, Stone et al. 1993, in Peters 2001). These pigs are native to North Africa and Eurasia, including Malaysia, but are currently found on many oceanic islands and all continents except Antarctica (Lever 1985, in Peters 2001). They are omnivorous and obtain a substantial portion of their food by grubbing for roots, bulbs, fungi, invertebrates, and other belowground material (Aplet et al. 1991, Fensham 1993, Kotanen 1995, in Peters 2001). Severely grubbed areas may extend for more than a hectare, but are typically composed of many small (ca 1 m2) patches of ground disturbance. Through trampling, rooting, and preferential feeding, feral pigs in Hawaii have disturbed natural plant communities dramatically (Aplet et al. 1991, Stone 1993, in Peters 2001). Wild pigs may also act as agents of dispersal for introduced species including C. hirta(Stone and Loope 1987, in Peters 2001). Because of this link the possibility exists of controlling C. hirta by managing pig populations, especially at places where the link between soil disturbance and invasive plant spread has been established, such as at the Pasoh Forest Reserve (Malaysian peninsula).\r\n

\r\nDisturbance is a key element in the establishment and invasion of C. hirta. Wildfires, landslides, windstorms and other forms of soil disturbance (such as pig rooting) accelerate the dominance of this weed (Smith Undated; Peters 2001). In its native environment plants are confined to open areas and only become dominant about twelve months after disturbance, such as in slash-and-burn agricultural areas (Burkhart Pers. Comm, in Smith Undated). All new range extensions in Hawaii begin along the open edges of trails or other disturbed areas. In order to keep the weed out of an area the primary management objective should be to minimise and prevent disturbance (Smith Undated). \r\n

\r\nAll efforts to eradicate newly established populations of C. hirta in Hawaii failed when they were not initiated before first fruit set (Smith Undated). There have been many well-meaning attempts by volunteer groups to control the spread of C. hirta through pulling it by hand, unfortunately the effort is likely to fail. The seed bank produced by these plants is colossal over a very short period of time (Smith Undated). In order to effectively control an infested area by mechanical means eradication efforts must be conducted at least once a year for up to 10 years. Only two instances of successful control, Kamakou (Moloka'i) and Pu'u Kukui trail (Maui) are known (Smith Undated). Clidemia is susceptible to a number of herbicides but will regenerate unless further applications are made. Chemical control does not appear to be practical in Hawaii's native ecosystems, particularly those difficult to access (Smith Undated).\r\n

\r\nClick here for Information about remote sensing for understory invasive plants and documenting the spread of weeds.

Management Category
Eradication
Control
None
Unknown
Bibliography
29 references found for Clidemia hirta

Managment information
Hivert, J. 2003. Plantes exotiques envahissantes - Etat des m�thodes de lutte mise en oeuvre par l Office National des For�ts � La R�union. ONF R�union.
Summary: Synth�se des m�thodes de lutte employ�es par l ONF � la R�union contre une vingtaine de plantes exotiques envahissantes.
Julien, M. H. (ed.) 1992. Biological control of weeds: a world catalogue of agents and their target weeds (3rd edition). CAB International, Wallingford, UK. 28pp.
Kueffer, C. and Mauremootoo, J., 2004. Case Studies on the Status of Invasive Woody Plant Species in the Western Indian Ocean. 3. Mauritius (Islands of Mauritius and Rodrigues). Forest Health & Biosecurity Working Papers FBS/4-3E. Forestry Department, Food and Agriculture Organization of the United Nations, Rome, Italy.
Peters, H.A. 2001. Clidemia hirta Invasion at the Pasoh Forest Reserve: An Unexpected Plant Invasion in an Undisturbed Tropical Forest, Biotropica 33(1): 60 - 68.
PIER (Pacific Island Ecosystems at Risk), 2002. Clidemia hirta
Summary: Ecology, synonyms, common names, distributions (Pacific as well as global), management and impact information.
Available from: http://www.hear.org/pier/species/clidemia_hirta.htm [Accessed 5 February 2003].
Smith, C.W. Undated. Distribution, Status, Phenology, Rate of Spread, and Management of Clidemia in Hawaii.
Summary: Available from: http://www.botany.hawaii.edu/faculty/duffy/book/1992_chap/11.pdf [Accessed April 19 2006]
Varnham, K. 2006. Non-native species in UK Overseas Territories: a review. JNCC Report 372. Peterborough: United Kingdom.
Summary: This database compiles information on alien species from British Overseas Territories.
Available from: http://www.jncc.gov.uk/page-3660 [Accessed 10 November 2009]
Wilson, Colin, Wildlife Management Officer, Department of Infrastructure, Planning and Environment, Parks & Wildlife Service, Northern Territory, Australia.
Summary: Compilor of original GISD profile of Chromoleana odorata.
General information
Baret, S., Rouget, M., Richardson, D. M., Lavergne, C., Egoh, B., Dupont, J., & Strasberg, D. 2006. Current distribution and potential extent of the most invasive alien plant species on La R�union (Indian Ocean, Mascarene islands). Austral Ecology, 31, 747-758.
Summary: L objectif de ce papier est d identifier les zones prioritaires en mati�re de gestion des invasions biologiques � La R�union en mod�lisant la distribution actuelle et potentiellle d une s�lection de plantes parmi les plus envahissantes.
Binggeli, P. 2000. The East Usambaras (Tanzania) - The pearl of Africa. Aliens 10 (14-15).
Binggeli, P, Hall, J.B. and Healey, J.R. Undated. Invasive Woody Plants, The Overstory 89.
Summary: Available from: http://www.agroforestry.net/overstory/overstory89.html [Accessed April 19 2006]
Conservatoire Botanique National De Mascarin (BOULLET V. coord.) 2007. - Clidemia hirta Index de la flore vasculaire de la R�union (Trach�ophytes) : statuts, menaces et protections. - Version 2007.1 (mise � jour 12 juin 2007).
Summary: Base de donn�es sur la flore de la R�union. De nombreuses informations tr�s utiles.
Available from: http://flore.cbnm.org/index2.php?page=taxon&num=fc6709bfdf0572f183c1a84ce5276e96 [Accessed 26 March 2008]
DeWalt, S.J., Denslow, J.S. and Ickes, K. 2004. Natural-Enemy Release Facilitates Habitat Expansion of the Tropical Shrub Clidemia hirta, Ecology 85(2): pp. 471 - 483.
Fournet, J. 2002. Flore illustr�e des phan�rogames de guadeloupe et de Martinique. CIRAD-Gondwana editions.
Gerlach, J. 1993. Invasive Melastomataceae in Seychelles. Oryx 27: 22-26.
Gerlach, J. 1996. The effects of habitat domination by invasive Melastomataceae. Phelsuma 4: 19-26.
Invasive Woody Plants in the Tropics. Undated.
Summary: Available from: http://members.lycos.co.uk/WoodyPlantEcology/docs/w-inv3.rtf [Accessed April 19 2006]
ITIS (Integrated Taxonomic Information System), 2004. Online Database Clidemia hirta
Summary: An online database that provides taxonomic information, common names, synonyms and geographical jurisdiction of a species. In addition links are provided to retrieve biological records and collection information from the Global Biodiversity Information Facility (GBIF) Data Portal and bioscience articles from BioOne journals.
Available from: http://www.itis.gov/servlet/SingleRpt/SingleRpt?search_topic=TSN&search_value=27703 [Accessed December 31 2004]
Joshi, C., de Leeuwa, J., van Durena, I.C. Undated. Remote Sensing and GIS Applications for Mapping and Spatial Modelling of Invasive Species.
Summary: Available from: http://www.isprs.org/istanbul2004/comm7/papers/132.pdf [Accessed April 19 2006]
Kueffer, C. & Lavergne, C. 2004. Case studies on the status of invasive woody plant species in the Western Indian Ocean. R�union. FAO. 36 p
Summary: Available from: http://www.fao.org/forestry/webview/media?mediaId=6842&langId=2 [Accessed 26 March 2008]
Macdonald, I.A.W., Th�baud, C., Strahm, W.A., & Strasberg, D. 1991. Effects on alien plant invasions on native v�g�tation remnants on La Reunion (Mascarene Islands, Indian Ocean). Environmental Conservation, 18, 51-61.
Summary: Cet article est le premier � proposer une hi�rarchisation des plantes les plus envahissantes de La R�union. 33 plantes ont �t� ainsi class�es en utilisant une m�thode d�velopp�e en Afrique du Sud. Les bases d une strat�gie de lutte contre les plantes exotiques envahissantes sont �galement formul�es.
Space, J.C and Falanruw, M. Undated. Observations on invasive plant species in Micronesia.
Summary: Available from: http://www.hear.org/pier/pdf/micronesia_report.pdf [Accessed April 19 2006]
Tassin, J., Lavergne, C., Muller, S., Blanfort, V., Baret, S., Le Bourgeois, T., Triolo, J., & Rivi�re, J.-N. 2006. Bilan des connaissances sur les cons�quences �cologiques des invasions de plantes � l��le de La R�union (archipel des Mascareignes, oc�an Indien). Revue d�Ecologie (La Terre et la Vie). 61, 35-51.
Summary: Cet article propose un bilan des m�thodes et des r�sultats relatifs aux �tudes traitant de la connaissance des cons�quences �cologiques des invasions de plantes exotiques.
Wester, L. L. and Wood, H. B. 1977. Koster s curse (Clidemia hirta), a weed pest in Hawaiian forests. Environmental Conservation 4(1): 35-41.
Whistler, W. A. 1992. Vegetation of Samoa and Tonga. Pacific Science 46(2): 172.
Contact
The following 7 contacts offer information an advice on Clidemia hirta
Baret,
St�phane
Geographic region: Indian Ocean
Ecosystem: Terrestrial
Organization:
Parc national de La R�union, Charg� de mission flore
Address:
112 rue Ste Marie - 97400 St Denis
Phone:
02 62 90 79 06
Fax:
02 62 90 11 39
Barthelat,
Fabien
Organization:
Assistant Technique Union Internationale pour la Conservation de la Nature Initiative Cara�bes
Address:
C/O Parc National de Guadeloupe Habitation Beausoleil, Mont�ran 97120 Saint-Claude, Guadeloupe
Phone:
(+590) (0)590 80 86 00
Fax:
(+590) (0)590 80 05 46
Gerlach,
Justin
Clidemia hirta
Organization:
The Nature Protection Trust of Seychelles
Address:
133 Cherry Hinton Road, Cambridge CB1 7BX, UK
Phone:
+44 122 3246875
Fax:
Lavergne,
Christophe
Geographic region: Indian Ocean
Ecosystem: Terrestrial
Organization:
Conservatoire Botanique National de Mascarin
Address:
2 rue du P�re Georges Domaine des Colima�ons 97436 SAINT LEU
Phone:
(33) 02 62 24 92 27
Fax:
Le Bourgeois,
Thomas
Geographic region: Africa; Indian Ocean; Southest Asia
Ecosystem: Terrestrial, Freshwater
Organization:
Centre de coop�ration internationale en recherche agronomique pour le d�veloppement
Address:
Cirad UMR AMAP, TA A51/PS2, Boulevard de la Lironde, F34398 Montpellier C�dex 5, France
Phone:
33 (0)4 67 61 59 10
Fax:
Meyer,
Jean-Yves
Geographic region: Pacific, Indian Ocean
Ecosystem: Terrestrial
Expert in the botany of French Polynesia and the Pacific Islands, and has worked on ecology and biological control of Miconia calvescens in French Polynesia.
Organization:
D�l�gation � la Recherche
Address:
D�l�gation � la Recherche, Gouvernement de Polyn�sie fran�aise. B.P. 20981, 98713 Papeete, Tahiti, Polyn�sie fran�aise
Phone:
689 47 25 60
Fax:
Triolo,
Julien
Geographic region: Indian Ocean
Ecosystem: Terrestrial
Organization:
Office National des For�ts
Address:
ONF. Domaine Forestier de la Providence, 97488 Saint Denis cedex
Phone:
692345283
Fax: