(Mart.) Solms, Pontederiaceae |
|
Present on Pacific Islands? yes
Primarily a threat at high elevations? no
Risk assessment results: High risk, score: 26 (Go to the risk assessment)
Common name(s): [more details]
Chinese: feng yan lan |
English: Nile lily, lilac-devil, water hyacinth |
Fijian: bekabekairaga, dabedabe ne ga, mbekambekairanga, ndambendambe ni nga |
French: jacinthe d'eau, pensée d'eau |
Hindi: jal khumbe |
Japanese: hoteiaoi |
Maori (Cook Islands): riri vai |
Palauan: bung el ralm |
Samoan: lili vai |
Spanish: aguapey, buchon, calamote, jacinto aquático, jacinto de agua, jacinto de rio, lechuguilla, liro de agua, tarulla |
Habit: aquatic herb
Description: "A perennial aquatic herb; stems short, floating or rooting in mud, rhizomatous or stoloniferous, rooting from the nodes; roots long, sometimes dark because of their purple anthocyanin, pendant; leaves in a rosette; petioles spongy, in young specimens short and with a one-sided swelling or inflation but up to 30 cm long when older, tapering and narrowing from the bulbous base to the point of attachment with the lamina; lamina circular to kidney-shaped, glossy smooth, 4 to 15 cm long and wide, acting as a sail in the wind; inflorescence in spikes with about eight flowers, long peduncled, bibracteate, the lower bract with long sheath and small lamina, the upper almost entirely included within the sheath of the lower one, tubular with a small pointed tip (apiculate); flower-bearing part of the rachis up to 15 cm or less long; entire scape may be 30 cm; perianth six-lobed, united below into a narrow tube, lilac, bluish purple or white, the upper lobe bearing a violet blotch with yellow center; stamens six, three long, three shorter, attached to the tube; capsule membranous, three-locular, dehiscent, many-seeded, as many as 50 or so per capsule; seed ovoid, ribbed, 0.5 to 1 mm. The species is distinguished by the almost one-sided swelling or inflation of the petiole, its long peduncled bibracteate spike, and its upper perianth blotched with yellow at the center" (Holm et al., 1977; p. 72).
"Rooted only at flowering time by long slender roots; otherwise floating, with thick, fleshy, more or less horizontal roots; leaves clustered, on bulbously inflated petioles, blades rounded or oblong, up to 3-4 inches wide; flowers showy, pale violet with a spot of bright yellow on the large upper lobe, some forms with pink and yellow flowers, all parts edible" (Stone, 1970; p. 116).
Habitat/ecology: Freshwater lakes, ponds, marshes, ditches, canals, slow-moving streams. "It is an aquatic floating weed. It does not tolerate brackish water (Holm et al., 1977; pp. 72-77) and salinity can limit or modify its distribution. For example, water hyacinth, which accumulates in the coastal lagoons of West Africa during the wet season, is reduced in those areas which become saline during the dry season. Growth by water hyacinth is favored by nutrient rich water, in particular by nitrogen, phosphorus and potassium" (Ecoport). "High growth rates mean populations can quickly form thick mats on the water surface. This makes passage by boats difficult, chokes irrigation channels, pollutes water and provides breeding grounds for disease-carrying insects. The natural beauty of areas is also degraded as native plants, birds and fish are displaced." (Smith, 2002; p. 82).
In Hawaii, "introduced as an ornamental, now naturalized and locally abundant in standing or slow-moving water such as ponds and sluggish streams at low elevations" (Wagner et al., 1999; pp. 1604-1606). In Fiji, "a locally abundant adventive, occurring near sea level (but elsewhere up to an elevation of 1,600 m or higher)" (Smith, 1979; pp. 175-176). In New Caledonia, "peu cultivée à présent, existe en masses serrées là où des rivières à courant faible ou des mares lui offerent des stations favorables mais n'obstrue pas les cours d'eau autant qu'en d'autres pays tropicaux" (MacKee, 1994; p. 118). In New Zealand, "An established escape from ponds and aquaria, now eradicated from many localities. E. crassipes was originally introduced as an ornamental, but it both accidentally escaped from cultivation and was deliberately planed, and by 1950 was established and troublesome in dams, ponds, swamps, slow-moving streams and river cut-offs in the Auckland Province" Possession of the plant in New Zealand is illegal (Healy & Edgar, 1980; p. 60).
Propagation: "Water hyacinth reproduces vegetatively by means of stolons which, together with solitary plants or drifting mats, are readily distributed by water currents, wind, boats and rafts. The plant also produces vast quantities of long-lived seed and persistence and spread by this means can be very significant (Sculthorpe 1971)." (Ecoport). "Spread throughout its range by intentional introductions as an ornamental" (Smith, 2002; p. 82).
Native range: Brazil, French Guian, Guyana, Suriname, Venezuela; cultivated and widely naturalized in the tropics and subtropics (GRIN).
Presence:
Pacific | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
American Samoa
Tutuila Islands |
Tutuila Island |
introduced
invasive |
Space, James C./Flynn, Tim (2000) (p. 35) |
Australia (Pacific offshore islands)
Norfolk Islands |
Norfolk Island |
introduced
invasive |
Orchard, Anthony E., ed. (1994) (p. 12)
"Common in open fresh-water habitats". Sight record, 1983, P.S. Green. |
Commonwealth of the Northern Mariana Islands (US)
Northern Mariana Islands |
Rota Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 99) |
Commonwealth of the Northern Mariana Islands (US)
Saipan |
Saipan Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 99) |
Cook Islands
Southern Cook Islands |
Mangaia Island | McCormack, Gerald (2013) | |
Cook Islands
Southern Cook Islands |
Rarotonga Island |
introduced
invasive |
Meyer, Jean-Yves (2000) (p. 89) |
Cook Islands
Southern Cook Islands |
Rarotonga Island | McCormack, Gerald (2013) | |
Federated States of Micronesia
Chuuk Islands |
Chuuk Islands |
introduced
|
Space, James C./Waterhouse, Barbara/Denslow, Julie S./Nelson, Duane/Mazawa, Thomas R. (2000) (p. 27) |
Federated States of Micronesia
Kosrae Island |
Kosrae Island |
introduced
cultivated |
Lorence, David H./Flynn, Timothy (2010) (p. 11)
"Apparently not yet naturalized". |
Federated States of Micronesia
Kosrae Island |
Kosrae Island |
introduced
invasive |
Sanney, Jacob A. (2013) (p. 19) |
Federated States of Micronesia
Pohnpei Islands |
Pohnpei Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 99) |
Federated States of Micronesia
Pohnpei Islands |
Pohnpei Island |
introduced
invasive |
Meyer, Jean-Yves (2000) (p. 90) |
Federated States of Micronesia
Pohnpei Islands |
Pohnpei Island |
introduced
|
Glassman, S. F. (1952) (pp. 107-108)
Voucher cited: Glassman 2553 (US) |
Federated States of Micronesia
Pohnpei Islands |
Pohnpei Island |
introduced
cultivated |
Herrera, Katherine/Lorence, David H./Flynn, Timothy/Balick, Michael J. (2010) (p. 62)
Vouchers cited: F.R. Fosberg 26257 (BISH), S.F. Glassman 2553 (BISH), L. Stemmermann 2979 (BISH), M. Takamatsu 908 (BISH), M. Takamatsu 910 (BISH) |
Federated States of Micronesia
Yap Islands |
Yap (Waqab) Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 99) |
Fiji
Fiji Islands |
Viti Levu Island |
introduced
invasive cultivated |
Smith, Albert C. (1979) (pp. 175-176)
Vouchers cited: Greenwood 184, Vaughan 3161, DA 11013, DA 9462, DA 3991, DA 3992, DA 6085, DA 3481 |
French Polynesia
Marquesas Islands |
Ua Pou (Huapu, Uapou, Uapu) Island |
introduced
invasive |
Lorence, David H./Wagner, Warren L. (2013)
Voucher cited: S. P. Perlman, E. Vogt 15889 (PTBG) |
French Polynesia
Marquesas Islands |
Ua Pou (Huapu, Uapou, Uapu) Island |
introduced
invasive |
Florence, J./Chevillotte, H./Ollier, C./Meyer, J.-Y. (2013)
Naturalisée |
French Polynesia
Society Islands |
Raiatea (Havai) Island |
introduced
invasive |
Welsh, S. L. (1998) (p. 376) |
French Polynesia
Society Islands |
Raiatea (Havai) Island |
introduced
invasive |
Florence, J./Chevillotte, H./Ollier, C./Meyer, J.-Y. (2013)
Naturalisée |
French Polynesia
Society Islands |
Tahiti Island |
introduced
invasive |
Welsh, S. L. (1998) (p. 376)
Vouchers cited: Setchell & Parks 238, Florence 2557, BRY 25445 |
French Polynesia
Society Islands |
Tahiti Island |
introduced
invasive |
Florence, J./Chevillotte, H./Ollier, C./Meyer, J.-Y. (2013)
Voucher cited: J. Florence 2557 (PAP) Naturalisée. Peu envahissant. |
French Polynesia
Society Islands |
Tetiaroa Atoll |
introduced
cultivated |
Sachet, M.-H./Fosberg, F. R. (1983) (p. 64) |
French Polynesia
Austral (Tubuai) Islands |
Tubuai Island |
introduced
invasive |
Florence, J./Chevillotte, H./Ollier, C./Meyer, J.-Y. (2013)
Naturalisée |
Guam
Guam Island |
Guam Island |
introduced
invasive |
Stone, Benjamin C. (1970) (p. 116)
Voucher cited: Stone 4915 (GUAM) |
Guam
Guam Island |
Guam Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 99) |
Guam
Guam Island |
Guam Island |
introduced
invasive |
Meyer, Jean-Yves (2000) (p. 95) |
State of Hawaii
Hawaiian Islands |
Hawaii (Big) Island |
introduced
invasive |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (pp. 1604-1606) |
State of Hawaii
Hawaiian Islands |
Kauai Island |
introduced
invasive |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (pp. 1604-1606) |
State of Hawaii
Hawaiian Islands |
Maui Island |
introduced
invasive |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (pp. 1604-1606) |
State of Hawaii
Hawaiian Islands |
Oahu Island |
introduced
invasive |
Wagner, Warren L./Herbst, Derral R./Sohmer, S. H. (1999) (pp. 1604-1606) |
Marshall Islands
Ralik Chain |
Kwajalein (Kuwajleen) Atoll |
introduced
cultivated |
Whistler, W. A./Steele, O. (1999) (p. 105) |
Marshall Islands
Ratak Chain |
Arno Atoll |
introduced
cultivated |
Vander Velde, Nancy/Vander Velde, Brian (2007) (p. 4)
"Rare; few plants observed in container by private residence in Ine; could pose serious environmental threat if introduced into wetlands". |
Marshall Islands
Ratak Chain |
Majuro (Mãjro) Atoll |
introduced
cultivated |
Vander Velde, Nancy (2003) (p. 55) |
Nauru
Nauru Island |
Nauru Island |
introduced
invasive cultivated |
Thaman, R. R./Fosberg, F. R./Manner, H. I./Hassall, D. C. (1994) (p. 74)
Voucher cited: Hassall 255 (SUVA) |
New Caledonia
New Caledonia |
New Caledonia Islands |
introduced
invasive |
Meyer, Jean-Yves (2000) (p. 100) |
New Caledonia
New Caledonia |
New Caledonia Islands |
introduced
invasive cultivated |
Gargominy, Oliver/Bouchet, Philipe/Pascal, Michel/Jaffre, Tanguy/Tourneu, Jean-Christophe (1996) (p. 382)
Esiste en masses serrées dans les mares ou les rivières à faible courant mais n'obstrue pas les cours d'eau autant qu'en d'autres pays tropicaux. |
New Caledonia
New Caledonia Archipelago |
Île Grande Terre |
introduced
invasive cultivated |
MacKee, H. S. (1994) (p. 118)
Vouchers cited: Sarasin 299 (Z), Compton 1602 (BM), Baumann & Guillaumin 9570, MacKee 4318, Jérémie & Tirel 1647 |
Palau
Palau (Belau ) (main island group) |
Babeldaob Island |
introduced
cultivated |
Space, James C./Waterhouse, Barbara/Miles, Joel E./Tiobech, Joseph/Rengulbai, Kashgar (2003) (pp. 12, 85) |
Palau
Palau (Belau ) (main island group) |
Koror (Oreor) Island |
introduced
|
Fosberg, F. R./Sachet, Marie-Hélène/Oliver, Royce (1987) (p. 99) |
Palau
Palau (Belau ) (main island group) |
Koror (Oreor) Island |
introduced
cultivated |
Space, James C./Waterhouse, Barbara/Miles, Joel E./Tiobech, Joseph/Rengulbai, Kashgar (2003) (pp. 12, 80) |
Palau
Palau (Belau ) (main island group) |
Koror (Oreor) Island |
introduced
cultivated |
Lorence, David H./Flynn, Tim (2010) (p. 18) |
Palau
Palau (Belau ) (main island group) |
Koror (Oreor) Island |
Beleu National Museum (Republic of Palau. Koror.) (1966) (voucher ID: BNM 195)
Taxon name on voucher: Eichhornia crassipes (Mart. & Zecc.) Solms |
|
Palau
Palau (Belau ) (main island group) |
Ngerkebesang Island |
introduced
cultivated |
Space, James C./Waterhouse, Barbara/Miles, Joel E./Tiobech, Joseph/Rengulbai, Kashgar (2003) (p. 12) |
Papua New Guinea
Papua New Guinea (eastern New Guinea Island) |
Papua New Guinea (eastern New Guinea Island) |
introduced
|
Henty, E. E./Pritchard, G. H. (1975) (p. 46)
Introduced and eliminated several times [as of date of publication]. |
Papua New Guinea
Papua New Guinea (eastern New Guinea Island) |
Papua New Guinea (eastern New Guinea Island) | Waterhouse, D. F. (1997) (p. 61) | |
Philippines
Philippine Islands |
Philippine Islands |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Philippines
Philippine Islands |
Philippine Islands |
introduced
invasive cultivated |
Merrill, Elmer D. (1925) (p. 200)
Introduced about 1912 as an ornamental, now very abundant in shallow water of lakes and in slow streams. |
Samoa
Western Samoa Islands |
Upolu Island |
introduced
invasive |
Space, James C./Flynn, Tim (2002) (p. 9)
Voucher: Flynn 6972 (PTBG, SAMOA) |
Samoa
Western Samoa Islands |
Upolu Island |
National Tropical Botanical Garden (U.S.A. Hawaii. Kalaheo.) (2002) (voucher ID: PTBG 306)
Taxon name on voucher: Eichhornia crassipes |
|
Solomon Islands
Solomon Islands |
Solomon Islands | Swarbrick, John T. (1997) (p. 91) | |
Solomon Islands
Solomon Islands |
Solomon Islands |
introduced
|
Hancock, I. R./Henderson, C. P. (1988) (p. 70) |
Solomon Islands
Solomon Islands |
Solomon Islands |
introduced
invasive cultivated |
Shine, C./Reaser, J. K./Gutierrez, A. T., eds. (2003) (p. 165)
Dominant invader. |
United States (other Pacific offshore islands)
Wake Islands |
Wake Island |
introduced
cultivated |
Fosberg, F. R. (1959) (p. 11)
One plant seen in 1952. |
United States (other Pacific offshore islands)
Wake Islands |
Wake Island |
introduced
|
Fosberg, F. R./Sachet, M.-H. (1969) (p. 7)
Not seen in 1961 or 1963. |
Vanuatu
New Hebrides Islands |
Vanuatu (Republic of) |
introduced
invasive |
Meyer, Jean-Yves (2000) (p. 106) |
Vanuatu
New Hebrides Islands |
Vanuatu (Republic of) |
introduced
invasive |
Shine, C./Reaser, J. K./Gutierrez, A. T., eds. (2003) (p. 179) |
Pacific Rim | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
Australia
Australia (continental) |
Northern Territory |
introduced
invasive |
Smith, Nicholas M. (2002) (p. 82)
All infestations eradicated except for Fogg Dam where isolated outbreaks are under control. |
Australia
Australia (continental) |
Queensland |
introduced
invasive |
Smith, Nicholas M. (2002) (p. 82) |
Cambodia
Cambodia |
Cambodia (Kingdom of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Central America
Central America (Pacific rim) |
Costa Rica (Republic of) | Holm, Leroy/Pancho, Juan V./Herberger, James P./Plucknett, Donald L. (1979) (p. 136) | |
Central America
Central America (Pacific rim) |
Honduras (Republic of) | Holm, Leroy/Pancho, Juan V./Herberger, James P./Plucknett, Donald L. (1979) (p. 136) | |
Central America
Central America (Pacific rim) |
Nicaragua (Republic of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 74, 77) |
Central America
Central America (Pacific rim) |
Panama (Republic of) | Holm, Leroy/Pancho, Juan V./Herberger, James P./Plucknett, Donald L. (1979) (p. 136) | |
China
China |
China (People's Republic of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
China
China |
Hong Kong |
introduced
invasive cultivated |
Wu, Te-lin (2001) (p. 356)
In ponds and rivers. |
Indonesia
Indonesia |
Indonesia (Republic of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Japan
Japan |
Japan |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Japan
Japan |
Japan |
introduced
|
Mito, Toshikazu/Uesugi, Tetsuro (2004) (p. 191) |
South Korea
South Korea |
South Korea (Republic of) | Holm, Leroy/Pancho, Juan V./Herberger, James P./Plucknett, Donald L. (1979) (p. 136) | |
Malaysia
Malaysia |
Malaysia (country of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Mexico
Mexico |
Mexico (United Mexican States) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (p. 75) |
Negara Brunei Darussalam
Brunei |
Brunei (Negara Brunei Darussalam) |
introduced
invasive |
Waterhouse, D. F. (1993) (pp. 65, 77) |
New Zealand
New Zealand |
New Zealand (country) |
introduced
invasive |
Healy, A. J./Edgar, E. (1980) (p. 60)
Voucher cited: N. T. Moar 445 (CHR 64900) |
Singapore
Singapore |
Singapore (Republic of) |
introduced
invasive |
Waterhouse, D. F. (1993) (pp. 65, 77) |
Singapore
Singapore |
Singapore (Republic of) |
introduced
invasive |
Chong, Kwek Yan/Tan, Hugh T. W./Corlett, Richard T. (2009) (p. 38)
Naturalised |
South America (Pacific rim)
South America (Pacific rim) |
Colombia |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 74, 76) |
Taiwan
Taiwan Island |
Taiwan Island |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Thailand
Thailand |
Thailand (Kingdom of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
United States (west coast)
United States (west coast states) |
USA (California) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Vietnam
Vietnam |
Vietnam (Socialist Republic of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Indian Ocean | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
Australia (Indian Ocean offshore islands)
Christmas Island Group |
Christmas Island |
introduced
cultivated |
Swarbrick, J. T. (1997) (p. 113) |
La Réunion (France)
La Réunion Island |
La Réunion Island |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
La Réunion (France)
La Réunion Island |
La Réunion Island |
introduced
invasive |
Lavergne, Christophe (2006)
"Envahissant" |
Maldives
Maldive Islands |
Maldive Islands |
introduced
invasive |
Pallawatta, Nirmalie/Reaser, Jamie K./Gutierrez, Alixis T./eds. (2003) (p. 62) |
Mauritius
Mautitius Islands (Mauritius and Rodrigues) |
Mauritius Island |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Seychelles
Seychelles Islands |
Seychelles Islands |
introduced
|
Weber, Ewald (2003) (p. 148) |
Seychelles
Seychelles Islands |
Seychelles Islands |
introduced
|
Invasive Species Specialist Group (2017) |
Also reported from | |||
Country/Terr./St. & Island group |
Location |
Cited status &
Cited as invasive & Cited as cultivated & Cited as aboriginal introduction? |
Reference &
Comments |
South Africa
South Africa |
South Africa (Republic of) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
United States (continental except west coast)
United States (other states) |
USA (Florida) |
introduced
invasive |
Holm, Leroy G./Plucknett, D. L./Pancho, J. V./Herberger, J. P. (1977) (pp. 72-77) |
Comments: Can become so thick that it chokes lakes and rivers (Florida and Australia). A declared noxious weed in Western Australia, the Northern Territory and Queensland (Smith, 2002; p. 82). A Class A (eradicate) noxious weed in New Zealand. Can be used for pig feed, but this may aid in its spread.
Planting of this species in the State of Florida (U.S.) is prohibited by Florida Department of Environmental Protection (Hunsberger, 2001).
Control: See "Biology and control of aquatic plants: A best management practices handbook" for control information (large file, PDF format). Additional control information from the Bugwood Wiki.
Physical: Hand pulling, dragline or specially designed harvesting machine.
Permanent drainage to dry out a pond or lake will control water hyacinth (Smith et al.1984).
Chemical: Herbicidal control of large infestations of water hyacinth growing under favorable conditions has been attempted only rarely (Scott et al. undated) and even when enormous resources have been invested, as in Sudan, has had little effect. However, this method has been successful for controlling small infestations accessible by land or boat (Smith et al. 1984; Jamieson et al. 1977) and eradicating small infestations in regions that are climatically unfavorable to growth of this plant. The herbicides most commonly used have been 2,4-D and Glyphosate, the first of these being by far the most widely used as it is relatively inexpensive.
The proliferation of water hyacinth in its exotic range is determined largely by two factors; nutrient supply and the absence of natural enemies of the weeds. To be fully effective, control strategies must address both watershed management and direct weed control.
The effects which the management of watersheds can have on the nutrient level of rivers, lakes and other wetlands has already been referred to. Watersheds must be managed to control water hyacinth and other floating aquatic weeds, provide a sustainable, acceptable life-style for the human population living in the watershed, and conserve the ecology and biodiversity. (GPPIS).
Biological: "There have been many attempts at biological control, with a steadily increasing record of substantial successes, although these have generally been slow in emerging. The most important natural enemies include two weevils (Neochetina eichhorniae and N. bruchi), two moth larvae (Sameodes albiguttalis and Haimbachia infusella), a mite (Orthogalumna terebrantis) and a fungus (Cercospora rodmanii). However there are many other natural enemies that could be investigated if required. Experience in a number of countries indicates that the establishment of several of the above organisms is highly likely to bring about a significant reduction in the abundance of water hyacinth. Control is generally slow in developing and, in some situations, all of the above organisms (and perhaps even others) may be required to provide an adequate level of suppression" (Waterhouse, 1994; p. 69).
The biological control agents which have been most successful are two weevils, Neochetina bruchi Hustache and N. eichhorniae Warner, and a moth Sameodes albiguttalis (Warren). However, optimal control has not been achieved in all situations and additional agents are being evaluated, including the moth Aeigona infusella.
Biological control information from the publication "Biological control of invasive plants in the eastern United States".
Waterhouse (1994, pp. 73-83) lists natural enemies, promising biological control agents, and a summary of attempts at biological control by country.