Invasive Species Compendium

Detailed coverage of invasive species threatening livelihoods and the environment worldwide


Asclepias syriaca
(common milkweed)



Asclepias syriaca (common milkweed)


  • Last modified
  • 20 November 2019
  • Datasheet Type(s)
  • Invasive Species
  • Host Plant
  • Preferred Scientific Name
  • Asclepias syriaca
  • Preferred Common Name
  • common milkweed
  • Taxonomic Tree
  • Domain: Eukaryota
  •   Kingdom: Plantae
  •     Phylum: Spermatophyta
  •       Subphylum: Angiospermae
  •         Class: Dicotyledonae
  • Summary of Invasiveness
  • A. syriaca can be an aggressive and persistent weed and contains several poisonous glucosidic substances (cardenolides) known to be poisonous to sheep, cattle, and occasionally horses (

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Preferred Scientific Name

  • Asclepias syriaca Blanco, 1837

Preferred Common Name

  • common milkweed

Other Scientific Names

  • Asclepias cornuti Decne.
  • Asclepias intermedia Vail
  • Asclepias kansana Vail
  • Asclepias syriaca L. var. kansana (Vail) Palmer & Steyermark

International Common Names

  • English: broadleaf milkweed; butterfly flower; cotton weed; silkweed; silky milkweed; silky swallow-wort; Virginia silkweed milkweed; wild cotton
  • Spanish: asclepia; vencetosigo comun
  • French: asclepiade; asclepiade de Syrie; cotonnier; petit-cochon

Local Common Names

  • Germany: Gehoernte Seidenpflanze
  • Netherlands: zijdeplant

EPPO code

  • ASCSY (Asclepias syriaca)

Summary of Invasiveness

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A. syriaca can be an aggressive and persistent weed and contains several poisonous glucosidic substances (cardenolides) known to be poisonous to sheep, cattle, and occasionally horses (Anderson, 1999).

Taxonomic Tree

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  • Domain: Eukaryota
  •     Kingdom: Plantae
  •         Phylum: Spermatophyta
  •             Subphylum: Angiospermae
  •                 Class: Dicotyledonae
  •                     Order: Gentianales
  •                         Family: Asclepiadaceae
  •                             Genus: Asclepias
  •                                 Species: Asclepias syriaca

Notes on Taxonomy and Nomenclature

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Louis Hebert sent seeds of Asclepias syriaca from Quebec City, Canada to Paris and Cornut’s treatise published in 1635: ‘Canadensium plantarum aliarumque nondum editarum Historia, describes both A. syriaca L. and A. incarnata L. A. syriaca was first identified as Apocynum majus syriacum rectum; Linnaeus then classified it as A. syriaca L. in 1753 (Gaertner, 1979).

Asclepias is a widespread genus with 76 species and 91 accepted taxa overall. There are 14 species of milkweed native in Canada (White, 1996). A. syriaca is the most widespread and locally abundant species of the genus (Hartzler and Buhler, 2000); it occurs in 38 states of North America.

According to Endress and Bruyns (2000) Asclepiadaceae is now treated as sub-family Asclepiadoideae in the family Apocynaceae.


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A. syriaca (common milkweed) is a perennial herb with long-spreading rhizomes. Stems stout, erect, to 2 m tall, with short downy hairs and milky juice; leaves opposite, smooth margined, oblong, 10-20 cm long and 5-11 cm wide, with prominent veins; upper surface smooth, lower covered with short white hairs. Flowers sweet-smelling, pink to white, in large, many-flowered (the number per inflorescence varies greatly, from less than 10 to more than 120) axillary and apical bell-like clusters. The long-lived flowers produce copious amounts of nectar (Wyatt and Broyles, 1994), flowering from June to August, depending on initial growth, climate, and location (Anderson, 1999). Seed brown, flat, oval, 6 mm long, 5 mm wide, with a tuft of silky white hairs apically. All plant parts contain latex; shoots from established plants arise from adventitious root buds, emerging in April and May. The root system is composed of horizontal and vertical roots. In established stands, vertical roots may penetrate the soil to depths of 3.8 m (Anderson, 1999).

Plant Type

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Seed propagated
Vegetatively propagated


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Contrary to its specific name, A. syriaca is native to northeastern, north central and southeastern United States and adjacent areas of Canada, and has spread to cultivated areas (Hartzler Buhler, 2000). This plant grows throughout the Great Plains ecoregion from southern Canada south to northeastern Oklahoma, northwestern Georgia, and Texas; and east from North Carolina to Maine (USDA-NRCS, 2010). It is naturalized in cultivated ground and dry grassland in various parts of central and southern Europe (IENICA, 2003).

Distribution Table

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The distribution in this summary table is based on all the information available. When several references are cited, they may give conflicting information on the status. Further details may be available for individual references in the Distribution Table Details section which can be selected by going to Generate Report.

Last updated: 17 Feb 2021
Continent/Country/Region Distribution Last Reported Origin First Reported Invasive Reference Notes


JapanPresentPresent based on regional distribution.
-Ryukyu IslandsPresent


Bosnia and HerzegovinaPresent
CzechiaPresent, Few occurrences
DenmarkPresent, Localized
NetherlandsPresent, Few occurrences
SwitzerlandPresent, Few occurrences
UkrainePresent, Localized

North America

CanadaPresentPresent based on regional distribution.
-ManitobaPresent, Few occurrencesNativeInvasive
-New BrunswickPresent, Few occurrencesNative
-Nova ScotiaPresent, Few occurrencesNativeInvasive
-OntarioPresent, WidespreadNativeInvasive
-QuebecPresent, Few occurrencesNativeInvasive
-SaskatchewanPresent, Few occurrencesNativeInvasive
United StatesPresentPresent based on regional distribution.
-IowaPresent, WidespreadNative
-NebraskaPresent, WidespreadNative
-New HampshirePresent, WidespreadNative
-New JerseyPresentNative
-New YorkPresentNative
-North CarolinaPresentNative
-North DakotaPresentNative
-Rhode IslandPresentNative
-South CarolinaPresentNative
-South DakotaPresentNative
-West VirginiaPresentNative
-WisconsinPresent, WidespreadNative


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A. syriaca colonizes a variety of communities from woodlands to cleared grasslands and marshlands. It grows in clumps or patches in meadows, fencerows, roadsides, railways, waste places, reduced-tillage fields, and other open habitats.

Habitat List

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Terrestrial ManagedCultivated / agricultural land Principal habitat Harmful (pest or invasive)
Terrestrial ManagedManaged grasslands (grazing systems) Present, no further details Harmful (pest or invasive)
Terrestrial ManagedDisturbed areas Principal habitat Harmful (pest or invasive)
Terrestrial ManagedRail / roadsides Principal habitat Harmful (pest or invasive)
Terrestrial Natural / Semi-naturalNatural grasslands Present, no further details Harmful (pest or invasive)

Hosts/Species Affected

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The crops most affected by this species are soybeans, corn, peanuts and grain sorghum (Anderson, 1999) and maize (Konstantinovic et al., 2008). Canadian studies of competition between common milkweed and oats found up to 20% yield loss of grain (Bhowmik, 1982).

Host Plants and Other Plants Affected

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Plant nameFamilyContextReferences
Avena sativa (oats)PoaceaeMain
    Glycine max (soyabean)FabaceaeMain
      Medicago sativa (lucerne)FabaceaeMain
        Sorghum bicolor (sorghum)PoaceaeMain
          Triticum aestivum (wheat)PoaceaeMain
            Zea mays (maize)PoaceaeMain

              Biology and Ecology

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              A. syriaca is genetically self-incompatible, although low-levels of self-compatibility have been reported (Wyatt and Broyles, 1994), and this species has an unusual late-acting form of ovarian rejection. Flowers are self-sterile and insect-pollinated (Anderson, 1999), and pollen dispersal via a pollinium results with a fruit sharing the same outcrossed paternal parent (Hochwender, 2000). Only around 2% of the flowers produce mature pods, with an average plant producing 4-6 pods, containing approx. 150-425 seeds.

              Reproductive Biology

              A. syriaca has a pollen delivery system whereby packets of pollen (pollinia) are transferred as a single unit during pollination; this method of reproduction is only seen elsewhere in some members of the Orchidaceae (Pleasants, 1991).The vegetative habit and weedy reproductive strategy A. syriaca makes it one of the most distinct milkweeds (Wilbur, 1976).

              In a study using isozyme polymorphisms to study multiple paternity in A. syriaca, Gold and Shore (1995) found no statistical evidence for multiple paternity within fruits but extensive multiple paternity between fruits on the same ramet, suggesting potential choice of mates through selective fruit abortion.

              Physiology and Phenology

              A. syriaca grows as a colony of plants and each colony develops from a single plant arising from a seed or root segment, it has underground rootstocks that develop adventitious buds which give rise to new individuals; a large clonal group can comprise several thousand stems (Wilbur, 1976).

              Vertebrate herbivores browse A. syriaca and results from a study by Hochwender (2000), showed that in low nutrient conditions, this species allocates resources to the storage organ, providing greater biomass when damaged; therefore an ability to compensate for damage might be important for this species.

              Environmental Requirements

              A. syriaca is adapted to wide range of climatic and edaphic conditions and will tolerate soil conditions in any textural group, but is most commonly found on well-drained soils of loamy texture and grows best in full sunlight or light shade. It does not tolerate excessive moisture. A. syriaca has been found to be the most abundant invasive species in open sand grasslands (Botta-Dukat, 2008).


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              C - Temperate/Mesothermal climate Preferred Average temp. of coldest month > 0°C and < 18°C, mean warmest month > 10°C

              Soil Tolerances

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              Soil drainage

              • free

              Soil reaction

              • acid
              • alkaline
              • neutral

              Soil texture

              • heavy
              • light
              • medium

              Natural enemies

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              Natural enemyTypeLife stagesSpecificityReferencesBiological control inBiological control on
              Aphis nerii Herbivore to genus
              Danaus plexippus Herbivore to genus
              Labidomera clivicollis Herbivore to genus
              Liriomyza asclepiadis Herbivore to genus
              Lygaeus kalmii Herbivore to genus
              Rhyssomatus lineaticollis Herbivore to genus
              Tetraopes tetrophthalmus Herbivore to genus

              Notes on Natural Enemies

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              Approximately 12 species of herbivore consume A. syriaca in eastern North America and nearly all are specialists of Asclepias spp. because of particular mandibular structures, feeding modes, and the way they avoid the defensive latex production of this species (Van Zandt and Agrawal, 2004).

              Means of Movement and Dispersal

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              Natural Dispersal (Non-Biotic)

              Only 3% of A. syriaca flowers produce seed pods, as most fall from the inflorescence approximately 10 days after opening (Anderson, 1999). A. syriaca spreads mainly by seeds which are wind pollinated and are dispersed on tufts of floss(Bhowmik, 1982). A. syriaca can produce large numbers of seeds, especially compared to other milkweed species, which facilitates dispersal over a long distance (White, 1996). Contrary to this, however, Pleasants (1991) found that much pollen dispersal in this species was short-distance.

              Pathway Causes

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              CauseNotesLong DistanceLocalReferences
              Research Yes Gaertner, 1979, publ. 1980

              Pathway Vectors

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              VectorNotesLong DistanceLocalReferences
              Wind Yes Yes Bhowmik, 1982; Pleasants, 1991

              Impact Summary

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              Environment (generally) Positive and negative

              Economic Impact

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              Losses due to this species have been recorded in Sorghum production as A. syriaca populations increased (NAPPO, 2003). The floss attached to seeds also tends to clog air intake devices on combines during harvest (Anderson, 1999).

              Environmental Impact

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              Impact on Biodiversity

              A. syriaca can be an aggressive and persistent weed and contains several poisonous glucosidic substances (cardenolides) known to be poisonous to sheep, cattle, and occasionally horses (Anderson, 1999). All parts of the plant contain the potentially toxic substances and A. syriaca is toxic to poultry; some milkweeds have been declared ‘noxious weeds’ in some North America states (White, 1996).

              The specialist herbivores Tetraopes tetraophthalmus and Danaus plexippus have developed adaptations that allow them to sequester plant-generated cardenolides to defend themselves against predators (Hochwender et al., 2000).

              Populations of the plant are thought to be beneficial as a source of nectar for butterflies, bees and other insects and A. syriaca plays an important part in the life cycle of the monarch butterfly (Danaus plexippus). Since D. plexippus requires A. syriaca as a larval food (Urquhart and Urquhart, 1979), D. plexippus might be at risk in Canada if noxious weed legislation were to be enforced and resulted in the elimination of milkweed (Hartzler and Buhler, 2000).

              Risk and Impact Factors

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              • Invasive in its native range
              • Proved invasive outside its native range
              • Has a broad native range
              • Abundant in its native range
              • Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
              • Pioneering in disturbed areas
              • Has high reproductive potential
              • Reproduces asexually
              Impact outcomes
              • Negatively impacts agriculture
              • Negatively impacts animal health
              Impact mechanisms
              • Allelopathic
              • Causes allergic responses


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              Economic Value

              A. syriaca is considered medicinal in the USA and foliage or latex is used as a remedy for cancer, tumours and warts. It is also thought to be beneficial in treating asthma, catarrh and cough. Good quality fibre is obtained from the inner bark of the stem and can be used to make twine.

              Uses List

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              • Wildlife habitat

              Human food and beverage

              • Oil/fat
              • Vegetable


              • Fibre
              • Rubber/latex

              Medicinal, pharmaceutical

              • Traditional/folklore

              Similarities to Other Species/Conditions

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              A. speciosa (showy milkweed) is similar to A. syriaca but it has broad, oval and rounded or heart-shaped leaves, densely woolly stalks, and fewer and longer flowers. Apocynum cannabinum (hemp dogbane) could be confused with A. syriaca but can be distinguished by its narrow, elliptical leaves 5-12 cm long, which are not hairy (Anderson, 1999). A. tuberosa (butterfly-weed) can also be mistaken for A. syriaca; it looks similar but it has orange flowers and the sap is not as milky.

              Prevention and Control

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              Due to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.


              Physical/mechanical control

              Removal of stalks by cutting can aggravate the problem as this stimulates growth from underground buds, and when cultivated, the resulting small root fragments will grow into a new plant.

              Chemical control

              Seedlings can be controlled with selected herbicides as pre-emergence treatments Bhowmik (1982). Aboveground plant parts may be destroyed by herbicides including 2, 4-D, mecoprop, dicamba and MCPA, but growth of adventitious roots is stimulated by this action. Amitrole-T and glyphosate will kill top growth and result in restricted regrowth during the following season. Glyphosate seems to be most effective overall and may reduce A. syriaca occurrence in crop fields (NAPPO, 2003).


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              Anderson WP, 1999. Perennial weeds. Characteristics and identification of selected herbaceous species. Iowa, USA: Iowa State University Press, 228 pp.

              Bhowmik PC, 1982. Herbicide control of common milkweed (Asclepias syriaca). Weed Science, 30:349-351.

              Botta-Dukát Z, 2008. Invasion of alien species to Hungarian (semi-)natural habitats. Acta Botanica Hungarica, 50(Supplementum):219-227.

              DAISIE, 2010. European Invasive Alien Species Gateway. European Invasive Alien Species Gateway.

              Endress ME; Bruyns PV, 2000. A revised classification of the Apocynaceae s.l. Botanical Review, 66(1):1-56.

              Gaertner EE; 1979, publ. 1980. The history and use of milkweed (Asclepias syriaca L.). Economic Botany, 33(2):119-123.

              GBIF, 2010. Global Biodiversity Information Facility. Global Biodiversity Information Facility. GBIF.

              Gold JJ; Shore JS, 1995. Multiple paternity in Asclepias syriaca using a paired-fruit analysis. Canadian Journal of Botany, 73(8):1212-1216.

              Hartzler RG; Buhler DD, 2000. Occurrence of common milkweed (Asclepias syriaca) in cropland and adjacent areas. Crop Protection, 19(5):363-366.

              Hochwender CG; Marquis RJ; Stowe KA, 2000. The potential for and constraints on the evolution of compensatory ability in Asclepias syriaca. Oecologia, 122(3):361-370.

              IENICA, 2003. Milkweed, Interactive European Network for Industrial Crops and their Applications (IENICA). Milkweed, Interactive European Network for Industrial Crops and their Applications (IENICA).

              Jeffery LS; Robison LR, 1971. Growth characteristics of common milkweed. Weed Science, 19(3):193-6.

              Konstantinovic B; Meseldzija M; Mandic N, 2008. Distribution of Asclepias syriaca L. on the territory of Vojvodina and possibilities of its control. Herbologia, 9(2):39-46.

              NAPPO, 2003. Pest fact sheet Asclepias syriaca L. North American Plant Protection Organization (NAPPO).

              Pleasants JM, 1991. Evidence for short-distance dispersal of pollinia in Asclepias syriaca L. Functional Ecology, 5(1):75-82.

              Timmons FL, 1946. Studies of the distribution and floss yield of Common Milkweed (Asclepias syriaca L.) in Northern Michigan. Ecology, 27(3):212-225.

              USDA-NRCS, 2010. The PLANTS Database. The PLANTS Database. Baton Rouge, USA: National Plant Data Center.

              White DJ, 1996. Status, distribution, and potential impact from noxious weed legislation. Report prepared for the Canadian Wildlife Service, Ottawa, Canada. Status, distribution, and potential impact from noxious weed legislation. Report prepared for the Canadian Wildlife Service, Ottawa, Canada.

              Wilbur HM, 1976. Life history evolution in seven milkweeds of the genus Asclepias. Journal of Ecology, 64(1):223-240.

              Wyatt R; Broyles SB, 1994. Ecology and evolution of reproduction in milkweeds. Annual Review of Ecological Systematics, 25:423-441.

              Zandt PAvan; Agrawal AA, 2004. Community-wide impacts of herbivore-induced plant responses in milkweed (Asclepias syriaca). Ecology, 85(9):2616-2629.

              Distribution References

              Anderson W P, 1999. Perennial weeds. Characteristics and identification of selected herbaceous species. Iowa, USA: Iowa State University Press. 228 pp.

              Babić G, Trkulja V, 2017. Distribution mapping of selected invasive weed species in north western area of Republic of Srpska (Bosnia and Herzegovina). In: VIII International Scientific Agriculture Symposium, "Agrosym 2017", Jahorina, Bosnia and Herzegovina, October 2017. Book of Proceedings [VIII International Scientific Agriculture Symposium, "Agrosym 2017", Jahorina, Bosnia and Herzgovina, October 2017. Book of Proceedings.], [ed. by Kovačević D]. Istocno Sarajevo, Bosnia-Herzegovina: Faculty of Agriculture, University of East Sarajevo. 1524-1530.

              Botta-Dukát Z, 2008. Invasion of alien species to Hungarian (semi-)natural habitats. Acta Botanica Hungarica. 50 (Supplementum), 219-227. DOI:10.1556/ABot.50.2008.Suppl.11

              CABI, Undated. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI

              EPPO, 2020. EPPO Global database. In: EPPO Global database, Paris, France: EPPO.

              GBIF, 2010. Global Biodiversity Information Facility.

              Konstantinović B, Meseldžija M, Mandić N, 2008. Distribution of Asclepias syriaca L. on the territory of Vojvodina and possibilities of its control. Herbologia. 9 (2), 39-46.

              Konstantinović B, Meseldžija M, Samardžić N, Konstantinović B, 2012. Distribution of invasive weeds on the territory of AP Vojvodina. In: Proceedings of the International Symposium on Current Trends in Plant Protection, Belgrade, Serbia, 25-28th September, 2012. [ed. by Marisavljević D]. Belgrade, Serbia: Institute for Plant Protection and Environment. 44-48.

              Scheffer S J, Lonsdale O, 2018. A survey of Agromyzidae (Diptera) reared from leafmines on Long Island, New York; host associations, distribution data, and the description and host association of a new species. Zootaxa. 4450 (1), 77-90. DOI:10.11646/zootaxa.4450.1.5

              Stobbs L W, Greig N, Weaver S, Shipp L, Ferguson G, 2009. The potential role of native weed species and bumble bees (Bombus impatiens) on the epidemiology of Pepino mosaic virus. Canadian Journal of Plant Pathology. 31 (2), 254-261.

              Vuković N, Miletić M, Milović M, Jelaska S D, 2014. Grime's CSR strategies of the invasive plants in Croatia. Periodicum Biologorum. 116 (3), 323-329.

              White D J, 1996. Status, distribution, and potential impact from noxious weed legislation. Report prepared for the Canadian Wildlife Service, Ottawa, Canada. In: Status, distribution, and potential impact from noxious weed legislation. Report prepared for the Canadian Wildlife Service, Ottawa, Canada,


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              01/03/10 Original text by:

              Claire Teeling, Consultant, UK

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