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Technical Information about Polygonum cuspidatum (Japanese Knotweed) Description and Variation
Economic Importance Detrimental - Japanese knotweed is a very aggressive species (Hitchcock and Cronquist 1964) that is capable of crowding out all other vegetation (Ahrens 1975); Hickman (1993) lists the species as a noxious weed. In addition, the plant can create a fire hazard in the dormant season (Ahrens 1975). Japanese knotweed is an escaped ornamental that is becoming increasingly common along stream corridors and rights-of-way in Washington. The species forms dense stands that crowd out all other vegetation, degrading native plant and animal habitat. This perennial plant is difficult to control because it has extremely vigorous rhizomes that form a deep, dense mat. In addition, the plant can resprout from fragments; along streams, plant parts may fall into the water to create new infestations downstream. Beneficial - The plant is sometimes grown as an ornamental (Hitchcock and Cronquist 1964; Muenscher 1955). Geographic Distribution: As its name indicates, Japanese knotweed is a native of Japan (Hickman 1993). However, it has become naturalized in North America, where it is found from Newfoundland and many parts of the northeastern U.S. (Muenscher 1955), west to California (Hickman 1993) and the Pacific Northwest (Hitchcock and Cronquist 1964). Habitat An escaped ornamental, Japanese knotweed is often found in waste places, neglected gardens, roadsides, and along streambanks (Muenscher 1955; Figueroa 1989). Because Japanese knotweed often grows along riparian corridors, we are considering it to be an invasive freshwater weed. History A native of Asia, this species was introduced to England in 1825 for use as an ornamental (Patterson 1976). Japanese knotweed was subsequently introduced to the U.S. for use in ornamental hedges and for erosion control (Pridham and Bing 1975). Growth, Development, and Reproduction Japanese knotweed is a perennial plant. This species spreads by seed and by long, stout rhizomes (Muenscher 1955). However, colonies rarely establish from seed. Primary spread of the species is reported to be through mechanical movement of plant parts (Figueroa 1989). Management Methods: See the information at these sites for current control
methods http://www.co.clark.wa.us/weed/documents.html Biocontrol Potential No information is available References Ahrens, J.F. 1975. Preliminary results with glyphosate for control of Polygonum cuspidatum. Proceedings of the Northeastern Weed Science Society 29: 326. Figueroa, P.F. 1989. Japanese knotweed herbicide screening trial applied as a roadside spray. Proceedings of the Western Society of Weed Science 42: 288-293. Hickman, J.C., ed. 1993. The Jepson Manual: Higher Plants of California. University of California Press, Berkeley. Hitchcock, C.L. and A. Cronquist. 1964. Vascular Plants of the Pacific Northwest. Part 2: Salicaceae to Saxifragaceae. University of Washington Press, Seattle. Muenscher, W.C. 1955. Weeds, Second Edition. Cornell University Press, Ithaca, NY. Patterson, D.T. 1976. The history and distribution of five exotic weeds in North Carolina. Castanea 41: 177-180. Pridham, A.M.S. and A. Bing. 1975. Japanese-bamboo. Plants-Gard. 31: 56-57. Scott, R. and R.H. Marrs. 1984. Impact of Japanese knotweed and methods of control. Aspect Appl. Biol., 291-296. Home | Brazilian Elodea | Eurasian Watermilfoil | Fanwort | Fragrant Water Lily | Hydrilla | Parrotfeather | Swollen Bladderwort | Water Hyacinth | Water Primrose | Yellow Floating Heart | Garden Loosestrife | Giant Hogweed | Hairy Willow-Herb | Indigobush | Japanese Knotweed | Purple Loosestrife | Reed Canarygrass | Salt Cedar |