Mugwort

Origin

Native to Europe and eastern Asia

Discovered

16th century by Jesuit missionaries in Canada

Impact

Displace native species, and can delay or disrupt succession in natural ecosystems

Mugwort

Origin

Native to Europe and eastern Asia

Discovered

16th century by Jesuit missionaries in Canada

Impact

Displace native species, and can delay or disrupt succession in natural ecosystems
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Background

Mugwort  (Artemesia vulgaris) is an invasive perennial forb that is widespread throughout North America, though it is most common in the eastern United States and Canada. It is a weed of nurseries, turfgrass, vineyards, waste areas, forest edges, and roadsides. Mugwort spreads aggressively through an extensive rhizome system and will readily form large, mono-specific stands.

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Origin and Expansion

Mugwort is native to Europe and eastern Asia, where it has historically been used as a medicinal herb. Seed may have been first introduced to North America as early as the 16th century by Jesuit missionaries in Canada. It was also introduced throughout the continent as a contaminant in ship ballast and nursery stock.

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Biology

Mugwort is a perennial with an extensive rhizome system. Shoots emerge during the spring, and flowering occurs from July to late September. A single plant can, depending on its environment, produce up to 200,000 seeds.  The small seeds (~1mm in diameter) are largely wind dispersed. Seed production does not seem to be a major factor in the spread of mugwort populations, however, and some biotypes do not produce viable seed.  Instead, mugwort spreads largely through vegetative expansion and the anthropogenic dispersal of root propagules. The root system is extensive though shallow (to 20 cm in depth), with numerous branching rhizomes up to 1 cm in diameter. Plants can regenerate from rhizome fragments as small as 2 cm (Klingeman et al. 2004).

Identify
Characteristics and Identification

The rarely-seen seedlings have oblong cotyledons without petioles. Adult stems are smooth and longitudinally ridged, with numerous axillary branches towards the upper portions of the plant. The stems become somewhat woody as they age. The leaves are alternate, densely covered with wooly, silver-white hairs on the underside, and slightly hairy on the upper surface. Leaf morphology is variable throughout the plant. The lower leaves are petiolate, with stipules at the base, and generally coarsely toothed and pinnately lobed. The upper leaves are sessile and lanceolate with smooth or toothed margins. The numerous ray and disk flowers are small (5 mm), green, and grow in racemes and clusters at the end of stems and branches. The foliage is aromatic and slightly pungent.

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Impact

Mugwort is a problematic weed in nurseries, where small root fragments can easily contaminate nursery stock. It is also a major weed in turf grass, field-grown ornamental crops, and orchards. Stands of mugwort displace native species, and can delay or disrupt succession in natural ecosystems (Barney and DiTommaso 2003). Mugwort produces several terpenoid potential allellochemicals, and decaying mugwort foliage has been shown to inhibit the growth of red clover in laboratory experiments (Inderjit and Foy 1999). Mugwort pollen is a common cause of hay fever.

Prevention
Prevention, Control, and Management

The dense root system of mugwort can make it difficult to control. Pulling is ineffective, and may even promote growth by leaving residual rhizome fragments in the soil. Mugwort tolerates mowing, and even sustained mowing over two years will not fully eradicate mugwort stands. The relatively shallow roots make mugwort vulnerable to repeated cultivation in agricultural systems, though this practice risks spreading root propagules.

Chemical control of mugwort can have limited effectiveness. Though non-specific broadleaf herbicides such as glyphosate or dicamba can effectively control mugwort, the rates required for adequate suppression are rarely economical (Bradley and Hagood 2002). For small infestations, multiple spot-treatments of glyphosate can be effective (Bing 1983).

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New York Distribution Map

This map shows confirmed observations (green points) submitted to the NYS Invasive Species Database. Absence of data does not necessarily mean absence of the species at that site, but that it has not been reported there. For more information, please visit iMapInvasives.

References

Barney, J.N. and A. DiTommaso. 2003. The biology of Canadian weeds. 118. Artemisia vulgaris L. Canadian Journal of Plant Science 83:205-215.

Bing, A. 1983. Problems in mugwort control in lawns. Proc. Of 40th Northeastern Weed Sci. Soc. 40: 376

Bradley K.W. and Hagood E.S. 2002. Evaluations of Selected Herbicides and Rates for Long-Term Mugwort (Artemisia vulgaris) Control. Weed Technology 16:164-170.

Inderjit and Foy C.L. 1999. Nature of the interference mechanism of mugwort (Artemisia vulgaris). Weed Technology 13:176-182.

Klingeman, W.E., Robinson, D.K., McDaniel, G.L.  2004. Regeneration of mugwort (Artemisia vulgaris) from rhizome sections in sand, pine bark, and soil substrates. J. Environ. Hort. 22:139–143.

Weston, L.A., J.N. Barney, and A. DiTommaso. 2005. A review of the biology and ecology of three invasive perennials in New York State : Japanese knotweed (Polygonum cuspidatum), mugwort (Artemisia vulgaris) and pale swallow-wort (Vincetoxicum rossicum). Plant and Soil 277 (1-2):53-69.