Canadian fleabane (Erigeron canadensis) essential oil in a clear glass vial
Erigeron canadensis (synonymConyza canadensis) is an annual plant native throughout most of North America and Central America. It is also widely naturalized in Eurasia and Australia. Common names include horseweed, Canadian horseweed, Canadian fleabane, coltstail, marestail, and butterweed. It was the first weed to have developed glyphosate resistance, reported in 2001 from Delaware.
Erigeron canadensis is an annual, herbaceous plant growing to 1.5 metres (5 feet) tall, with sparsely hairy stems. The leaves are unstalked, slender, 2–10 centimetres (0.8–3.9 inches) long, and up to 1cm (0.4in) wide, with a coarsely toothed margin. They grow in an alternate spiral up the stem, and the lower ones wither early. The flower heads are produced in dense inflorescences and are 1cm (0.4in) in diameter. Each individual flower has a ring of white or pale purple ray florets and a centre of yellow disc florets. The fruit is a cypsela tipped with dirty white down.[2]
Erigeron canadensis can easily be confused with Erigeron sumatrensis, which may grow to a height of 2m (6.6ft), and the more hairy Erigeron bonariensis, which does not exceed 1m (3.3ft). E.canadensis is distinguished by bracts that have a brownish inner surface with no red dot at the tip, and are free (or nearly free) of the hairs found on the bracts of the other species.[3][4][5]
Distribution and habitat
Horseweed originated in North America and Central America and is widespread in its native range.[6] It has spread to inhabited areas of most of the temperate zone of Asia,[7] Europe,[2][8] and Australia.[9] It is found in Britain from northern Scotland to Cornwall, growing as a weed of arable land and man-made environments. It is considered invasive in China.[10]
Horseweed can grow in a range of natural habitats, from sand dunes to old fields, as well as in gardens and other disturbed areas.[11] It is an indicator for disturbance because it often colonizes disturbed areas in which it was sparse or absent prior to the disturbance.[12] Horseweed is a common pest of agricultural fields, and can tolerate a range of acidic to neutral soils (pH 4.8 to 7.2).[13]
Weed status
Horseweed is commonly considered a weed, and in Ohio, Oregon, and some other locations,[14] it has been declared a noxious weed.[15][16] It was the first weed to have developed glyphosate resistance, reported in 2001 from Delaware.[17]
It can be found in fields, meadows, and gardens throughout its native range. Horseweed infestations (specifically of 105 plants per 10ft2) have reduced soybean yields by as much as 83%,[18] with one estimate claiming it can reduce yields by up to 90%.[19] Severe infestations have reduced sugar beet yields by 64%.[18]
Horseweed produces a large amount of seeds that are dispersed by wind, allowing it to easily colonize disturbed soils.[13]
The seeds can germinate at any time of year with sufficient moisture and proper temperatures. With fall germination, it overwinters as a rosette and bolts in the spring to flower in the summer. With spring germination, it spends less time as a rosette before bolting to flower.[13] The seeds can persist in the seedbank of disturbed and non-disturbed sites, though it is more prevalent in disturbed sites.[23]
The seeds are capable of persisting in the seedbank after a fire,[24] and the plant increases in frequency in response to more frequent fire regimes.[25]
↑ Wu, Bingde; Zhang, Huanshi; Jiang, Kun; Zhou, Jiawei; Wang, Congyan (2019). "Erigeron canadensis affects the taxonomic and functional diversity of plant communities in two climate zones in the North of China". Ecological Research. 34 (4): 535–547. Bibcode:2019EcoR...34..535W. doi:10.1111/1440-1703.12024. S2CID198244222.
↑ Weakley, A. S. (2015). Flora of the Southern and Mid-Atlantic States. Chapel Hill, NC, University of North Carolina Herbarium.
↑ Kruger, Greg R.; Davis, Vince M.; Weller, Stephen C.; Johnson, William G. (2010). "Growth and Seed Production of Horseweed (Conyza canadensis) Populations after Exposure to Postemergence 2,4-D". Weed Science. 58 (4): 413–419. doi:10.1614/WS-D-10-00022.1. S2CID55366555.
↑ Cohen, Susan; Braham, Richard; Sanchez, Felipe (December 2004). "Seed Bank Viability in Disturbed Longleaf Pine Sites". Restoration Ecology. 12 (4): 503–515. doi:10.1111/j.1061-2971.2004.00382.x.
↑ Creech, M. N., et al. (2012). "Alteration and Recovery of Slash Pile Burn Sites in the Restoration of a Fire-Maintained Ecosystem." Restoration Ecology 20(4): 505-516.
↑ Burton, J. A. (2009). Fire frequency effects on vegetation of an upland old growth forest in eastern Oklahoma. Environmental Science. Stillwater, Oklahoma, Oklahoma State University. Bachelor: 78.
↑ Stevenson, Matilda Coxe 1915 Ethnobotany of the Zuni Indians. SI-BAE Annual Report #30 (p.55).
↑ Rafinesque, C. S. (1828). Medical flora; or Manual of the medical botany of the United States of North America.
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