Potentially Misidentified Species:
In Florida, Eichhornia crassipes may be confused with the floating form of a
somewhat similar appearing native aquatic plant, frog's bit (Limnobium
spongia). The presence of small,
white flowers and petioles that are not bulbous or inflated aid in
distinguishing the native plant from water hyacinth (Langeland and Burks 1998).
II. HABITAT AND DISTRIBUTION
Eichhornia crassipes can be found in all types of Florida freshwater habitats.
The species is native to the Amazon Basin of Brazil but has been introduced to
tropical and subtropical regions around the world (Langeland and Burks 1998).
Holm et al. (1977) noted that at the time of publication 56 countries including
the United States had reported it as a noxious weed.
Within the U.S., E. crassipes occurs throughout the southeast north to
Virginia and west to Texas, as well as in California and Hawaii. Seasonal
escapes from cultivation are reported from New York, Kentucky, Tennessee and
Missouri, but populations apparently do not survive through winter. The plant
previously occurred in Arizona, Arkansas, and Washington State but is now
considered eradicated in these locations (Ramey 2001).
E. crassipes occurs in all but a handful of counties in the Florida
peninsula and about half the counties in the panhandle and north Florida
Eichhornia crassipes is a freashwater species that is widespread in all six
counties within the IRL watershed.
III. LIFE HISTORY AND POPULATION BIOLOGY
Age, Size, Lifespan:
Aerial portions of Eichhornia crassipes generally grow to 0.5 m in height, although individuals in some Asian populations may reach nearly 1 m (Gopal 1987).
Water hyacinth mats are capable of attaining incredibly high plant density and
biomass. A single hectare of dense E. crassipes mat can contain more
than 360 metric tons of plant biomass. Exhaustive management efforts in
Florida over the last 20 years have considerably reduced the amount of aquatic
habitat choked by this invader (UF/IFAS 2001).
Water hyacinth is capable of sexual and asexual reproduction and both modes are
important to the species' success as a pernicious aquatic invader. In mild
climates, plants can flower year-round, and from early spring to late fall
elsewhere. They can produce an abundance of seeds (Flora of North America 2003,
Langeland and Burks 1998). A study by Barrett (1980b) confirmed that tropical
E. crassipes populations produced twice as many seeds as did temperate
populations and attributed the difference to higher rates of pollinating insect
visitation in the tropics. Seed germination tends to occur when water levels
are down and the seedlings can grow in saturated soils.
Vegetative reproduction occurs via the breaking off of rosettes of clonal
individuals. The stolons (horizontal shoots capable of forming new shoots and
adventitious roots from nodes) are easily broken by wind or wave action and
floating clonal plants and mats are readily transported via wind or water
movement (Barrett 1980a, Langeland and Burks 1998).
E. crassipes produces a thin walled, capsule-like fruit that is
protected within structures that form from the perianth, the outer whorls of
the flowers. Each capsule can hold as many as four hundred-fifty 4-mm long x 1-mm thick seeds
(Gopal 1987). Germination typically occurs in wet soil.
IV. PHYSICAL TOLERANCES
Although Eichhornia crassipes is excluded from cold climates due to temperature
limitations, it does exhibit a degree of freeze tolerance. Aerial portions of
the plant killed back by moderate freeze events can quickly regrow from
submerged stem tips protected from freezing by water (Langeland and Burks
Holm et al. (1977) indicate that water hyacinth is intolerant of brackish
conditions. Experimental studies by de Casabianca and Laugier (1995)
demonstrated an inverse relationship between salinity and Eichhornia crassipes
plant yield; no plant production and cankerous plants resulted at salinities
above 6 ppt and irreversible physiological damage occurred above 8 ppt. Water
hyacinth is capable of growing in low salinity coastal lagoon habitats, e.g.,
in West Africa during the rainy season (ISSG).
V. COMMUNITY ECOLOGY
Small forage fish utilize the floating mats and suspended root masses as a
refuge, although anthocyanins and other soluble plant pigments in the roots may
protect them from herbivores (Gopal 1987).
VI. INVASION INFORMATION
The U.S. invasion history of water hyacinth is well documented. The Brazil
native was first introduced to the U.S. as an ornamental aquatic plant at a New
Orleans, LA exposition in 1884. Eichhornia crassipes escaped from cultivation to
arrive in Florida by 1890, and over the ensuing 60 years, dense mats of this
highly invasive plant had taken over more than 50,000 ha of Florida freshwater
habitat (Gopal and Sharma 1981, Schmitz et al. 1993).
The amount of Florida aquatic habitat choked by dense water hyacinth mats is
currently much less than during the first 100 years after the arrival of the
species. Waterways are kept clear of dense infestations only through
extraordinary management efforts involving field crews engaged in full time
mechanical removal and biocidal control of E. crassipes. Complete
eradication from Florida is impossible.
Potential to Compete With Natives:
Water hyacinth is a Category 1 invasive exotic in Florida, capable of altering
native plant communities by displacing native species and changing community
structures or ecological functions (FLEPPC).
Holm et al. (1977) describe Eichhornia crassipes as one of the worst weeds in
The capacity of water hyacinth to invade and overtake aquatic habitat is
astounding. Growth rates are explosive and vegetative population doubling can
take place in 1-3 weeks (Mitchell 1976, Wolverton and McDonald 1979,
Langeland and Burkes 1998).
The species can quickly dominate natural areas and can dramatically alter the
species composition, structure, and function of native plant and animal
communities (Langeland and Burks 1998).
The suspended root system may account for up to half of the plant biomass. The
adventitious roots are clonal plants that break off of the parent to
immediately thrive on their own and are also capable of taking root in moist
soil in low water conditions.
Possible Economic Consequences of Invasion:
Large, dense Eichhornia crassipes mats can degrade water quality and can choke
waterways. Plant respiration and biomass decay can result in oxygen depletion
and fish kills (FDEP undated).
The documented negative economic impacts of water hyacinth invasion worldwide
have included the clogging of irrigation channels, choking off of navigational
routes, smothering of rice paddies, loss of fishing areas, increase in breeding
habitat available to disease-transmitting mosquitoes, and others (Room and
Fernando 1992, ISSG).
associated with removal and maintenance control of water hyacingth are
Barrett S.C.H. 1980a. Sexual reproduction in Eichhornia crassipes (water
Hyacinth). 1. Fertility of clones from diverse regions. Journal of Applied
Barrett S.C.H. 1980b. Sexual reproduction in Eichhornia crassipes (water
hyacinth). II. Seed production in natural populations. The Journal of Applied
de Casabianca M.-L. and T. Laugier. 1995. Eichhornia crassipes
production on petroliferous wastewaters: effects of salinity. Bioresource
Flora of North America. 2003. 26:39-41. Published online.
Florida Department of Environmental Protection. Undated. Water hyacinth
management - A good example of maintenance control in Florida. FDEP Bureau of
Invasive Plant Management Circular 19. 3 p.
Gopal B. and Sharma K.P. 1981. Water-hyacinth (Eichhornia crassipes),
most troublesome weed of the world. Hindasia Publications, Delhi, India. 219 p.
Gopal B. 1987. Water hyacinth. Elsevier Science Publishers, Amsterdam. 471 p.
Holm LG, Plucknett DL, Pancho JV, Herberger JP. 1977. The world's worst weeds:
Distribution and biology. Honolulu: University Press of Hawaii. 609 pp.
Langeland KA, and KC Burks (Eds.). 1998. Identification and Biology of
Non-Native Plants in Florida's Natural Areas. UF/IFAS. 165 p.
Mitchell D.S. 1976. The growth and management of Eichhornia crassipes
and Salvinia spp. In their native environment and in alien situations.
In: Varshney C.K. amd J. Rzoska (Eds.). Aquatic weeds in southeast Asia. W.
Junk Publishers, Netherlands. 396 p.
Ramey V. 2001. Non-Native Invasive Aquatic Plants in the United States:
Eichhornia crassipes. Center for Aquatic and Invasive Plants, University
of Florida and Sea Grant. Available online.
Room P.M. and I.V.S. Fernando. 1992. Weed invasions countered by biological
control: Salvinia molesta and Eichhornia crassipes in Sri Lanka,
Aquatic Botany 42:99-107.
Schmitz D.C., Schardt J.D., Leslie A.J., Dray F.A., Osbourne J.A. and B.V.
Nelson. 1993. The ecological impact and management history of three invasive
alien aquatic plant species in Florida. In: McKnight (Ed.). Biological
pollution-The control and impact of invasive exotic species. Indiana Academy
of Science, Indianapolis. 261 p.
Wolverton B.C. and and R.C. McDonald. 1979. Waterhyacinth (Eichhornia
crassipes) productivity and harvesting studies. Economic Botany 33:1-10.
J. Masterson, Smithsonian Marine Station
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Page last updated: June 30, 2007