Emilia sonchifolia (red tasselflower)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Description
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Habitat
- Habitat List
- Hosts/Species Affected
- Host Plants and Other Plants Affected
- Biology and Ecology
- Climate
- Latitude/Altitude Ranges
- Air Temperature
- Rainfall
- Rainfall Regime
- Soil Tolerances
- Notes on Natural Enemies
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Economic Impact
- Environmental Impact
- Threatened Species
- Risk and Impact Factors
- Uses
- Uses List
- Similarities to Other Species/Conditions
- Prevention and Control
- References
- Links to Websites
- Contributors
- Distribution Maps
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Top of pageIdentity
Top of pagePreferred Scientific Name
- Emilia sonchifolia (L.) DC. ex DC.
Preferred Common Name
- red tasselflower
Other Scientific Names
- Cacalia sonchifolia Hort ex L.
- Crassocephalum sonchifolium (L.) Less.
- Emilia javanica (Burm.f.) C.B.Rob.
- Emilia purpurea Cass.
- Emilia rigidula DC.
- Emilia sinica Miq.
- Gynura ecalyculata DC.
- Senecio sonchifolius (L.) Moench
International Common Names
- English: consumption weed; cupid's paintbrush; cupid's shaving brush; Flora's paintbrush; lilac tasselflower; purple sow thistle; red groundsel; sow thistle
- Spanish: borlitas; brochita; clavel chino; huye que te cojo; pincel de amor; pincelillo de poeta; yebra socialista
- French: cacalie a feuilles de laiteron; émilie; herbe a lapin; manger lapin; salade a lapin
- Chinese: yi dian hong
- Portuguese: bela-emilia; serralha
Local Common Names
- Bahamas: purple emilia
- Brazil: brocha; falsa-serralha; pincel; serralha-mirim
- El Salvador: molendera; rabanillo; rabano falso
- Germany: purpur-quastenkoepfchen
- Indonesia: djombang; dwaji rowo
- Japan: usubeni-nigana
- Lesser Antilles: goutte de sang rouge; rabbit meat; ti léton
- Madagascar: tsiontsiona
- Malawi: kalimwendo; mambenawo
- Malaysia: ketumbit jantan; setumbak merah; tanbak-tambak merah; tetambak merah
- Philippines: cetim; kipot-kipot; lamlampka; tagiulinau; yagod-no-kang kang
- Puerto Rico: clavelito Colorado; clavelitos del cafetal
- Vietnam: co chua le
EPPO code
- EMISO (Emilia sonchifolia)
Summary of Invasiveness
Top of pageEmilia sonchifolia is an annual herb believed to be native to China and South-East Asia. Since spreading from its natural range, E. sonchifolia now has a pan-tropical distribution and is naturalized elsewhere in Asia, as well as in Australia, the Pacific Islands, Africa and the Americas. This species has been reported as a weed for a number of crops and has been shown to reduce yields and act as a reservoir for crop pathogens. Currently it is listed as invasive in India, Mexico, Brazil, Paraguay, Costa Rica, the Galapagos, Puerto Rico, the Virgin Islands, Dominican Republic, Trinidad and Tobago, Madeira, Réunion, Hawaii and on many other islands in the Pacific Ocean. Mechanical control has been shown to be effective, and chemical control has been effective in some annual and perennial crops.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Asterales
- Family: Asteraceae
- Genus: Emilia
- Species: Emilia sonchifolia
Notes on Taxonomy and Nomenclature
Top of pageWith 1,620 genera and more than 23,600 species, Asteraceae is one of the most diverse families of flowering plants (Stevens, 2019). Species within the Asteraceae are very variable in their growth form and habitat, but may be recognized by their “capitulate” and involucrate inflorescences in which numerous small flowers open first on the outside and are infrequently subtended by bracts. The anthers in this family are usually fused and form a tube through which the style extends before the two stigmatic lobes separate and become recurved. The rather small, single-seeded fruits usually have a plumose “pappus” and are frequently dispersed by wind (Pruski and Robinson, 2018; Stevens, 2019). The genus Emilia comprises approximately 100 species distributed mainly in tropical regions of the Old World (Pruski and Robinson, 2018).
Description
Top of pageEmilia sonchifolia is an erect to ascending, smooth or sparingly hairy, soft stemmed, slenderly branched annual herb, growing 20 to 70 cm tall with a branched taproot. The leaves are alternate. Those on the lower stem are deeply and irregularly toothed, being nearly round, kidney shaped, ovate, triangular-ovate or obovate, 4 to 16 cm long, 1 to 8 cm wide, with narrowly winged petioles. The upper, lanceolate leaves are sessile, with bases which encircle the stem. The inflorescence is terminal, usually dichotomously branched, flat-topped and composed of 3 to 6 stalked flower heads, each with a whorl of bracts beneath. Each urn-shaped flower head, a composite of numerous tubular florets which protrude by 1 mm above a single ring of outer green involucral bracts, is 12-14 mm long by 4-5 mm wide. There are 30-60 florets per head, the outer ones female and the inner ones with both stamens and stigmas. The flowers may be purple, scarlet, red, pink, orange, white or lilac. The fruit is an oblong dry indehiscent ribbed achene, 2.4-3 mm long, reddish brown or off-white with a pappus of white hairs up to 8 mm long.
Distribution
Top of pageThe exact native range of E. sonchifolia is still uncertain (USDA-ARS, 2018). It is considered native to Asia (China, Southeast Asia) but it now has a pan-tropical distribution and can be found naturalized in Africa, North, Central and South America, the West Indies, Oceania and several islands across the Pacific and the Indian Ocean (Pruski and Robinson, 2018; GRIIS, 2018; PIER, 2018; PROTA, 2018; USDA-ARS 2018).
Distribution Table
Top of pageThe 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: 25 Feb 2021Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Angola | Present | Introduced | Naturalized | Naturalized | |||
Congo, Democratic Republic of the | Present | Introduced | |||||
Côte d'Ivoire | Present | Introduced | Naturalized | Naturalized | |||
Equatorial Guinea | Present | Introduced | Naturalized | Naturalized | |||
Ghana | Present | Introduced | Naturalized | Naturalized | |||
Guinea | Present | Introduced | Naturalized | Naturalized | |||
Kenya | Present | Introduced | Naturalized | Naturalized | |||
Madagascar | Present | Introduced | |||||
Malawi | Present | ||||||
Mauritius | Present | Introduced | Naturalized | Naturalized | |||
Nigeria | Present | Introduced | Naturalized | Naturalized | |||
Réunion | Present | Introduced | Naturalized | Naturalized | |||
Senegal | Present | Introduced | Naturalized | Naturalized | |||
Seychelles | Present | ||||||
Sierra Leone | Present | Introduced | Naturalized | Naturalized | |||
Sudan | Present | ||||||
Tanzania | Present | Introduced | Naturalized | Naturalized | |||
Asia |
|||||||
Bangladesh | Present | ||||||
Bhutan | Present | Native | |||||
Brunei | Present | ||||||
Cambodia | Present | ||||||
China | Present | Native | |||||
-Anhui | Present | Native | |||||
-Fujian | Present | Native | |||||
-Guangdong | Present | Native | |||||
-Guizhou | Present | Native | |||||
-Hainan | Present | Native | |||||
-Hebei | Present | Native | |||||
-Henan | Present | Native | |||||
-Hubei | Present | Native | |||||
-Hunan | Present | Native | |||||
-Jiangsu | Present | Native | |||||
-Shaanxi | Present | Native | |||||
-Sichuan | Present | Native | |||||
-Yunnan | Present | Native | |||||
-Zhejiang | Present | Native | |||||
Hong Kong | Present | ||||||
India | Present | Introduced | Invasive | ||||
-Arunachal Pradesh | Present | Introduced | Invasive | ||||
-Assam | Present | Introduced | Invasive | ||||
-Himachal Pradesh | Present | Introduced | Invasive | ||||
-Jammu and Kashmir | Present | Introduced | Invasive | ||||
-Karnataka | Present | ||||||
-Manipur | Present | Introduced | Invasive | ||||
-Meghalaya | Present | Introduced | Invasive | ||||
-Mizoram | Present | Introduced | Invasive | ||||
-Nagaland | Present | Introduced | Invasive | ||||
-Odisha | Present | ||||||
-Sikkim | Present | Introduced | Invasive | ||||
-Tripura | Present | Introduced | Invasive | ||||
-Uttarakhand | Present | Introduced | Invasive | ||||
-West Bengal | Present | Introduced | Invasive | ||||
Indonesia | Present | ||||||
-Java | Present | ||||||
Japan | Present | Native | |||||
-Honshu | Present | Native | |||||
-Kyushu | Present | Native | |||||
-Ryukyu Islands | Present | Native | |||||
Laos | Present | ||||||
Malaysia | Present | Native | |||||
Maldives | Present | Introduced | |||||
Myanmar | Present | ||||||
Nepal | Present | Native | |||||
Philippines | Present | Native | |||||
Singapore | Present | ||||||
Sri Lanka | Present | Native | |||||
Taiwan | Present | Native | |||||
Thailand | Present | Native | |||||
Vietnam | Present | Native | |||||
Europe |
|||||||
Portugal | |||||||
-Madeira | Present, Only in captivity/cultivation | Introduced | Cultivated in gardens, appearing rarely outside | ||||
North America |
|||||||
Anguilla | Present | ||||||
Antigua and Barbuda | Present, Widespread | Introduced | |||||
Bahamas | Present | Introduced | |||||
Barbados | Present | ||||||
Belize | Present | Introduced | Naturalized | Naturalized | |||
British Virgin Islands | Present | Introduced | Invasive | ||||
Costa Rica | Present | Introduced | Invasive | ||||
Cuba | Present | Introduced | Listed as a weed | ||||
Dominica | Present, Widespread | Introduced | |||||
Dominican Republic | Present | Introduced | Invasive | ||||
Grenada | Present, Widespread | Introduced | |||||
Guadeloupe | Present, Widespread | Introduced | |||||
Guatemala | Present | Introduced | Naturalized | Naturalized | |||
Haiti | Present | Introduced | |||||
Honduras | Present | ||||||
Jamaica | Present | Introduced | |||||
Martinique | Present, Widespread | Introduced | |||||
Mexico | Present | Introduced | Invasive | ||||
Montserrat | Present, Widespread | Introduced | |||||
Netherlands Antilles | Present, Widespread | Introduced | |||||
Nicaragua | Present | Introduced | Naturalized | Naturalized | |||
Panama | Present | Introduced | Naturalized | Naturalized | |||
Puerto Rico | Present | Introduced | Invasive | ||||
Saint Kitts and Nevis | Present, Widespread | Introduced | |||||
Saint Lucia | Present, Widespread | Introduced | |||||
Saint Martin | Present, Widespread | Introduced | |||||
Saint Vincent and the Grenadines | Present, Widespread | Introduced | |||||
Trinidad and Tobago | Present | Introduced | Invasive | ||||
U.S. Virgin Islands | Present | Introduced | Invasive | ||||
United States | Present | Present based on regional distribution. | |||||
-California | Present | Introduced | |||||
-Florida | Present | Introduced | Naturalized | Naturalized | |||
-Georgia | Present | Introduced | Naturalized | Naturalized | |||
-Hawaii | Present, Widespread | Introduced | Invasive | ||||
-Louisiana | Present | Introduced | |||||
-Ohio | Present | Introduced | |||||
-South Carolina | Present | Introduced | Naturalized | Naturalized | |||
Oceania |
|||||||
American Samoa | Present | Introduced | Invasive | ||||
Australia | Present | Introduced | |||||
-Queensland | Present | ||||||
Cook Islands | Present | ||||||
Federated States of Micronesia | Present | Introduced | Invasive | ||||
-Chuuk | Present | Introduced | Invasive | ||||
-Pohnpei | Present | Introduced | Invasive | ||||
-Yap | Present | Introduced | Invasive | ||||
Fiji | Present | Introduced | Invasive | ||||
French Polynesia | Present | Introduced | Invasive | ||||
Guam | Present | Introduced | Invasive | ||||
Kiribati | Present | Introduced | |||||
Nauru | Present | Introduced | Invasive | ||||
New Caledonia | Present | Introduced | Invasive | ||||
Niue | Present | Introduced | Invasive | ||||
Northern Mariana Islands | Present | Introduced | Invasive | ||||
Palau | Present | Introduced | Invasive | ||||
Papua New Guinea | Present | Native | |||||
Samoa | Present | ||||||
Solomon Islands | Present | Introduced | |||||
Tonga | Present | Introduced | Invasive | ||||
Tuvalu | Present | Introduced | |||||
U.S. Minor Outlying Islands | Present | Introduced | Invasive | ||||
-Johnston Atoll | Present | Introduced | Invasive | ||||
Vanuatu | Present | Introduced | |||||
Wallis and Futuna | Present | Introduced | |||||
South America |
|||||||
Bolivia | Present | Introduced | |||||
Brazil | Present | Introduced | Invasive | ||||
-Alagoas | Present | ||||||
-Amazonas | Present | ||||||
-Bahia | Present | ||||||
-Ceara | Present | ||||||
-Espirito Santo | Present | ||||||
-Goias | Present | ||||||
-Maranhao | Present | ||||||
-Mato Grosso | Present | ||||||
-Minas Gerais | Present | ||||||
-Para | Present | ||||||
-Paraiba | Present | ||||||
-Parana | Present | ||||||
-Pernambuco | Present | ||||||
-Piaui | Present | ||||||
-Rio de Janeiro | Present | ||||||
-Rio Grande do Norte | Present | ||||||
-Rio Grande do Sul | Present | ||||||
-Santa Catarina | Present | ||||||
-Sao Paulo | Present, Widespread | ||||||
-Sergipe | Present | ||||||
Colombia | Present | Introduced | Naturalized | Naturalized | |||
Ecuador | Present | Introduced | Naturalized | Naturalized | |||
-Galapagos Islands | Present | ||||||
French Guiana | Present | Introduced | Naturalized | Naturalized | |||
Guyana | Present | Introduced | Naturalized | Naturalized | |||
Paraguay | Present | Introduced | Invasive | ||||
Peru | Present | ||||||
Suriname | Present | Introduced | Naturalized | Naturalized | |||
Venezuela | Present | Introduced | Naturalized | Naturalized |
History of Introduction and Spread
Top of pageIn Puerto Rico, E. sonchifolia was first recorded in a herbarium collection made in 1881 (Rojas-Sandoval and Acevedo-Rodríguez, 2015). On islands in the Pacific Ocean, it was apparently introduced early in the 20th century (Smith, 1991).
Habitat
Top of pageGrowing at elevations ranging from sea level up to 3000 m, E. sonchifolia thrives under a wide range of environmental conditions across tropical and subtropical regions. It is a common weed in open grasslands, waste areas, roadsides, arable crops, pastures, forest edges, coastal thickets, weedy slopes, riverbanks and paddy ridges. It also grows in partially shaded areas beneath coffee, oil palm and tea plantations (Pruski and Robinson, 2018; Flora of China, 2018).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Natural |
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Disturbed areas | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Disturbed areas | Present, no further details | Natural |
Terrestrial | Managed | Disturbed areas | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Productive/non-natural |
Littoral | Coastal areas | Present, no further details | Harmful (pest or invasive) | |
Littoral | Coastal areas | Present, no further details | Natural | |
Littoral | Coastal areas | Present, no further details | Productive/non-natural |
Hosts/Species Affected
Top of pageWithin and outside its natural distribution range, E. sonchifolia is a very common weed of field crops, and can be found in virtually any annual or perennial plantation crop.
Host Plants and Other Plants Affected
Top of pageBiology and Ecology
Top of pageGenetics
The chromosome number reported for E. sonchifolia is 2n=10 and 2n=20 (Xie et al., 2003; Flora of China, 2018).
Reproductive biology
The flowers of E. sonchifolia are hermaphrodites and are pollinated by insects (i.e. bees and flies) and by wind. This species is self-fertile (Pruski and Robinson, 2018; PFAF, 2018).
Physiology and phenology
In China, E. sonchifolia flowers from July to October (Flora of China, 2018). In Central America and Mexico, this species has been recorded flowering throughout the year (Pruski and Robinson, 2018; Vibrans, 2019). In the USA it produces flowers all year, but mostly from October to March (Flora of North America, 2018).
Longevity
Emilia sonchifolia is a fast-growing annual plant (Flora of China, 2018).
Activity patterns
As long as soil moisture is adequate, E. sonchifolia will germinate throughout the growing season in Nigeria (Holm et al., 1997) with plants completing their life cycle in about 90 days. Two types of seed may be distinguished by the colour of the achene. The female outer circle of florets of a flower head produce reddish-brown achenes while those from inner hermaphrodite florets are off-white (Marks and Akosim, 1984). A larger proportion of both types germinate at 27°C than at 30°C but only those which develop from outer florets germinate under deep shade. While low levels of germination (4%) will occur when seeds are buried as deep as 4 cm in the soil, plants will only emerge from seed near to the surface. Only 3% of seedlings germinating at a depth of 1 cm emerged in trials in Sri Lanka compared with 29% of those placed at 0.5 cm (Pemadasa and Kangatharalingam, 1977), suggesting that occasional deep tillage may be a useful control measure.
Environmental requirements
Emilia sonchifolia prefers to grow in moist tropical areas with temperatures ranging from 20°C to 30°C (but can tolerate 10-40°C) and mean annual rainfall of 1000-2000 mm. It prefers well-drained soils in a sunny position with a pH of 4.5-6.5. Plants are drought tolerant once established (Pruski and Robinson, 2018; Flora of China, 2018; PIER, 2018; Fern, 2019). It is particularly tolerant of acid conditions, and is an early colonizer of newly cleared peat soils in Malaysia (Wee, 1970).
Movement and Dispersal
Emilia sonchifolia spreads by seed. The fruit carries a pappus of capillary-like bristles that facilitates wind-dispersal. Seeds can be secondarily dispersed by water, as a contaminant in crop and pasture seeds, on soil and adhered to vehicles and agricultural machinery (Pruski and Robinson, 2018; Flora of China, 2018; Flora of North America, 2018; Fern, 2019).
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
Af - Tropical rainforest climate | Preferred | > 60mm precipitation per month | |
Am - Tropical monsoon climate | Preferred | Tropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25])) | |
As - Tropical savanna climate with dry summer | Preferred | < 60mm precipitation driest month (in summer) and < (100 - [total annual precipitation{mm}/25]) | |
Aw - Tropical wet and dry savanna climate | Preferred | < 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25]) | |
Cs - Warm temperate climate with dry summer | Tolerated | Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers | |
Cw - Warm temperate climate with dry winter | Tolerated | Warm temperate climate with dry winter (Warm average temp. > 10°C, Cold average temp. > 0°C, dry winters) |
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
30 | 45 |
Air Temperature
Top of pageParameter | Lower limit | Upper limit |
---|---|---|
Mean annual temperature (ºC) | 20 | 30 |
Mean maximum temperature of hottest month (ºC) | 40 | |
Mean minimum temperature of coldest month (ºC) | 10 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Mean annual rainfall | 1000 | 2000 | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
Soil reaction
- acid
- neutral
Soil texture
- heavy
- light
- medium
Notes on Natural Enemies
Top of pagePathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Disturbance | Weed of disturbed sites | Yes | Flora of China, 2018 | |
Horticulture | Sometimes planted as an ornamental | Yes | Yes | USDA-ARS, 2018 |
Medicinal use | Used in traditional Asian medicine | Yes | Yes | Flora of China, 2018 |
People foraging | Leaves eaten as a vegetable | Yes | Yes | USDA-ARS, 2018 |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Debris and waste associated with human activities | Seed dispersal | Yes | Yes | Fern, 2019 |
Machinery and equipment | Seed dispersal | Yes | Yes | Fern, 2019 |
Land vehicles | Seed dispersal | Yes | Yes | Fern, 2019 |
Water | Seed dispersal | Yes | Yes | Fern, 2019 |
Wind | Seed dispersal | Yes | Yes | Fern, 2019 |
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Positive and negative |
Environment (generally) | Positive and negative |
Human health | Positive |
Economic Impact
Top of pageEmilia sonchifolia has been reported as a weed of 29 crops but, although extremely common, Holm et al. (1997) do not consider it to be troublesome. However, they do report that the species as a serious or principal weed in some areas, for example in cassava in Brazil and India; cotton, maize and lowland rice in Brazil; oil palm and rubber in South East Asia; papaya, groundnut, sweet potato and tomato in Hawaii, USA; pineapple in Hawaii, USA and Malaysia; and taro (Colocasia esculenta) in Samoa. It has also been identified as one of the most problematic weeds in the cotton-producing areas of Nicaragua (Solis and de la Cruz, 1992). In other situations, E. sonchifolia is but one member of a diverse broadleaf flora. When uncontrolled, E. sonchifolia or Emilia coccinea can decrease the dry weight of lettuce and mustard cabbage (Brassica juncea) by 70 and 30% respectively (at 11 weeds per crop plant), while tomato fruit yield has been shown to be reduced by 18% by 80-120 weeds per plant. The more competitive, closely spaced crop of sweet corn was not affected by up to 150 weeds per crop plant (Floresca, 1976).
Emilia sonchifolia can be an alternative host, serving as a reservoir for crop pathogens. In Hawaii, USA, a wilt disease of pawpaw (Carica papaya), caused by Tomato spotted wilt virus (TSWV) is invariably associated with orchards which have numerous TSWV infected E. sonchifolia plants (Gonsalves and Truijillo, 1986). Other economically important pathogens for which E. sonchifolia is an alternative host are Xanthomonas campestris pv. phaseoli [X. axonopodis pv. phaseoli], which causes bacterial infection of beans (Phaseolus vulgaris) in Brazil and Cuba (Rodriguez et al., 1991; Valarini and Spadotto, 1995), the yellow spot virus of pineapple [Tomato spotted wilt virus] (Frohlich and Rodewald, 1970), and the nematode Rotylenchulus reniformis, found in bananas in Cuba (Blanco et al., 1982). It is also a host of Liriomyza huidobrensis, an insect pest of onion (Allium cepa) in Colombia (Hincapie et al., 1993).
Environmental Impact
Top of pageEmilia sonchifolia also behaves as an environmental weed with the potential to displace native vegetation and alter successional processes. It has been reported invading forest edges, secondary forests, coastal thickets and natural grasslands. It has been listed as invasive in India, Mexico, Brazil, Paraguay, Costa Rica, the Galapagos, Puerto Rico, the Virgin Islands, Dominican Republic, Trinidad and Tobago, Madeira, Réunion, Hawaii, and on many other islands in the Pacific Ocean (Lorenzi, 2000; Chacón and Saborío, 2003; Chandra, 2012; Ministerio de Medio Ambiente y Recursos Naturales, 2012; Rojas-Sandoval and Acevedo-Rodríguez, 2015; GRIIS, 2018; PIER, 2018; Vibrans, 2019).
Threatened Species
Top of pageThreatened Species | Conservation Status | Where Threatened | Mechanism | References | Notes |
---|---|---|---|---|---|
Vigna o-wahuensis (Oahu cowpea) | EN (IUCN red list: Endangered); USA ESA listing as endangered species | Hawaii | Ecosystem change / habitat alteration; Pest and disease transmission | US Fish and Wildlife Service, 2011 |
Risk and Impact Factors
Top of page- Invasive in its native range
- Proved invasive outside its native range
- Has a broad native range
- Abundant in its native range
- Highly adaptable to different environments
- Is a habitat generalist
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
- Pioneering in disturbed areas
- Tolerant of shade
- Highly mobile locally
- Benefits from human association (i.e. it is a human commensal)
- Fast growing
- Gregarious
- Ecosystem change/ habitat alteration
- Modification of successional patterns
- Monoculture formation
- Negatively impacts agriculture
- Reduced native biodiversity
- Threat to/ loss of native species
- Competition - monopolizing resources
- Rapid growth
- Highly likely to be transported internationally accidentally
- Highly likely to be transported internationally deliberately
- Difficult to identify/detect as a commodity contaminant
- Difficult to identify/detect in the field
Uses
Top of pageEmilia sonchifolia is sold in local markets across tropical Asia as food or for use in traditional medicine (Flora of China, 2018). The young leaves are used as a vegetable (Uphof, 1968; Martin and Ruberte, 1978), while the plants are considered of value medicinally in India and China (Duke and Ayensu, 1985).
Uses List
Top of pageGeneral
- Ornamental
Human food and beverage
- Vegetable
Medicinal, pharmaceutical
- Source of medicine/pharmaceutical
Similarities to Other Species/Conditions
Top of pageEmilia sonchifolia is most likely to be confused with Emilia coccinea, with which it can hybridize (Olorode and Olorunfemi, 1973). E. coccinea is also found in Brazil, the Caribbean, Colombia, Costa Rica, El Salvador, Honduras, Mexico, USA, Venezuela, Sri Lanka and much of West Africa (Adams, 1963; Holm et al., 1979; Fournet and Hammerton, 1991). In East and Central Africa both species occur in highland areas of Malawi (Banda and Morris, 1985), while E. coccinea is widespread throughout more humid areas of Kenya, Tanzania and Uganda (Blundell, 1992), and is also present in Angola, Mozambique, Zimbabwe and Zambia (Bolnick, 1995).
E. coccinea may be distinguished by having about 8 involucral bracts, somewhat less than the 15 found in E. sonchifolia. E. coccinea is recognized by yellow flowered forms in West Africa and scarlet flowered forms in East/Central Africa, while those of E. sonchifolia are mauve or rarely white (Adams, 1963). However, flower colour in E. sonchifolia varies greatly around the world and particular care needs to be taken when considering this character.
Emilia sonchifolia looks similar to E fosbergii and E. coccinea. These species can be distinguished based on the following vegetative and floral traits (Pruski and Robinson, 2018):
Emilia sonchifolia: Basal and lower leaves lyrate-pinnatifid; involucres narrow-cylindrical, corollas included to only slightly exserted; corollas usually pink or lavender, lobes 0.5-0.8 mm; disc floret styles indistinctly appendiculate, appendages to 0.1 mm, no longer than broad, convex.
Emilia coccinea: Basal and lower leaves shortly petiolate; involucres broad-cylindrical to hemispherical, corollas moderately to well-exserted; corollas lobes 1.1-2.2 mm; disc floret styles obviously appendiculate, appendages 0.2-0.3 mm, caudate. Leaf margins nearly subentire; involucres campanulate, about as long as broad, corollas well-exserted; corollas bright orange to red, lobes 1.6-2.2 mm.
Emilia fosbergii: Basal and lower leaves shortly petiolate; involucres broad-cylindrical to hemispherical, corollas moderately to well-exserted. Leaf margins usually coarsely dentate; involucres broad-cylindrical, (1-) 2× as long as broad, corollas moderately exserted; corollas usually pale red or pinkish-red, lobes 1.1-1.6 mm
Prevention and Control
Top of pageDue 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.
Emilia sonchifolia is easily controlled mechanically, while selective chemical control can be achieved in some annual and perennial crops. A co-formulated mixture of pretilachlor and dimethametryn, a mixture of piperophos with propanil or oxadiazon alone, all applied at 5 days after sowing provided 8-12 weeks control in upland rice in Nigeria (Enyinnia, 1992). Pre-emergence applications of cyanazine, metribuzin or imazaquin, or post-emergence application of a mixture of bentazone, fomesafen and sethoxydim allow selective control in soyabean (Barros, 1989; Barros et al., 1992). Sethoxydim applied alone has not provided control in trials with either cotton or soyabean in Brazil (Beltrao et al., 1983; Barros et al., 1992). A number of options are available for residual control in plum orchards including glyphosate mixtures with diuron, simazine or terbacil, MSMA mixed with diuron, or paraquat mixed with simazine (Almeida et al., 1987). For Eucalyptus grandis, oxyfluorfen provides control of E. sonchifolia for up to 180 days following application (Silva et al., 1995). Atrazine provides excellent control in sugarcane in Hawaii (Olney, 1971).
References
Top of pageAdams CD, 1963. Compositae. In: Hutchinson J, Dalziel JM, Hepper FN, eds. Flora of West Tropical Africa, Volume 2, Second edition. London, UK: Crown Agents
Banda AK, Morris B, 1985. Common Weeds of Malawi. Lilangwe, Malawi: University of Malawi
Berhaut J, 1967. Flore du Senegal. Dakar, Senegal: Editions Clairafrique
Blundell M, 1992. Wild Flowers of East Africa. London, UK: Harper Collins
Bolnick D, 1995. A Guide to the Common Wild flowers of Zambia and Neighbouring Regions. London, UK: Macmillan
Borges, RAX, Teles, AM, 2015. Emilia. In: Lista de Espécies da Flora do Brasil, Jardim Botânico do Rio de Janeiro.http://floradobrasil.jbrj.gov.br/jabot/floradobrasil/FB16105
Chacón E, Saborío G, 2003. San Jose, Costa Rica: Asociación para la Conservación y el Estudio de la Biodiversidad (ACEBIO).
Duke J, Ayensu E, 1985. Medical Plants of China. Algonac, Michigan, USA: Reference Publications Inc
Frohlich G, Rodewald W, 1970. Enfernedades y plagas de las plantas tropicales. Leipzig, Germany: Offizin Anderson Nexo
Gonzales GB, Webb ME, 1989. Manual Para la Identificacion y Control de Malezas en el Area Integrada de Santa Cruz. Santa Cruz, Bolivia: Centro Internacional de Agricultura Tropical
GRIIS, 2018. Global Register of Introduced and Invasive Species. http://www.griis.org/
Haslewood EL, Matter GG, 1966. Handbook of Hawaiian Weeds. Honolulu, Hawaii, USA: Hawaiian Sugar Planters Association
Holm L, Doll J, Holm E, Pancho J, Herberger J, 1997. World Weeds. Natural Histories and Distribution. New York, USA: John Wiley and Sons, Inc
IRRI, 1989. Weeds Reported in Rice in South and South East Asia. Manila, Philippines: International Rice Research Institute
Kasasian L, 1964. Common Weeds of Trinidad. St Agustine, Trinidad: University of the West Indies
Kleinschmidt HE, Johnson RW, 1977. Weeds of Queensland. Queensland, Australia: Department of Primary Industries
Labrada R, 2003. Important Weed Species in Crops and Countries, Caribbean, Cuba. Data stored from 59 developing countries. Rome, Italy: FAO.
Lorenzi H, 2000. Weeds of Brazil, terrestrial and aquatic, parasitic, poisonous and medicinal, (3rd) . Nova Odessa, Brazil: Plantarum Institute.
Martin F, Ruberte R, 1978. Survival and Subsistence in the Tropics. Mayaguez, Puerto Rico: Antillian College Press
Olney V, 1971. Development of weed control in Hawaiian sugarcane fields. Third Conference of the Asian-Pacific Weed Science Society, Kuala Lumpur, Malaysia: Asian Pacific Weed ScienceSociety, 35:1-6
Olorode O, Olorunfemi A, 1973. The hybrid origin of Emilia praetermissa Senecioneae: compositae. Annals of Botany, 37:185-191
Pancho JV, Vega MR, Plucknett DL, 1969. Some Common Weeds of the Philippines. Laguna, Philippines: Weed Science Society of the Philippines, University of the Philippines at Los Ba±os
Parham J, 1958. The Weeds of Fiji. Bulletin 35. Suva, Fiji: Department of Agriculture
Pemadasa M, Kangatharalingam N, 1977. Factors affecting germination of some Compositaes. Ceylon Journal of Agricultural Science, 12:157-168
Pruski JF, Robinson H, 2018. Flora Mesoamericana, 5(2) [ed. by Davidse G, Sousa Sánchez M, Knapp S, Chiang Cabrera F]. St. Louis, USA: Missouri Botanical Garden Press.1–608.
Remaudiere G, van Harten A, Ilharco FA, 1977. Some Aphidiodea of French Polynesia. Bulletin de la Societe Entomologique de France, 82(5-6):150-155
Robertson SA, 1989. Flowering Plants of Seychelles. Kew, UK: Royal Botanic Gardens
Silva da W, Silva da JF, Cardoso AA, Barros de NF, 1995. Use of trifluralin 600 and oxyfluorfen in the culture of Eucalyptus grandis. Revista Arvore, 19(1):1-17
Trinidad and Tobago Biodiversity, 2016. Lists of Invasive species in Trinidad and Tobago. http://www.biodiversity.gov.tt/home/trinidad-a-tobago-biodiversity/invasive-alien-species.html
Uphof J, 1968. Dictionary of Economic Plants. New York, USA: Cramer
USDA-NRCS, 2018. The PLANTS Database. Baton Rouge, USA: National Plant Data Center.
Velez I, van Overbeek J, 1950. Plantas Indeseables en los Cultivos Tropicales. Riuo Piedras, Puerto Rico: Universidad de Puerto Rico
Wang ZR, 1990. Farmland Weeds in China. Beijing, China: Agricultural Publishing House
Wee Y, 1970. Weed succession observations on arable peat land. Malayan Forester, 33:63-69
Xie ZY, Zheng CM, 2003. Cytological studies on 13 species of Compositae from Hainan, China. Journal of Systematics and Evolution, 41(6), 545–552.
Distribution References
Adams CD, 1963. Compositae. In: Flora of West Tropical Africa, 2 (Second) [ed. by Hutchinson J, Dalziel JM, Hepper FN]. London, UK: Crown Agents.
Banda AK, Morris B, 1985. Common Weeds of Malawi., Lilangwe, Malawi: University of Malawi.
Berhaut J, 1967. (Flore du Senegal)., Dakar, Senegal: Editions Clairafrique.
Borges RAX, Teles AM, 2015. Emilia. In: Lista de Espécies da Flora do Brasil, Rio de Janeiro, Brazil: Jardim Botânico do Rio de Janeiro. http://floradobrasil.jbrj.gov.br/jabot/floradobrasil/FB16105
CABI, Undated. Compendium record. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
CABI, Undated b. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Chacón E, Saborío G, 2003. (Lista De Especies De Plantas Introducidas En Costa Rica)., San Jose, Costa Rica: Asociación para la Conservación y el Estudio de la Biodiversidad (ACEBIO).
Gonzales GB, Webb ME, 1989. (Manual Para la Identificacion y Control de Malezas en el Area Integrada de Santa Cruz)., Santa Cruz, Bolivia: Centro Internacional de Agricultura Tropical.
GRIIS, 2018. Global Register of Introduced and Invasive Species., http://www.griis.org/
Haselwood EL, Motter GG, 1966. Handbook of Hawaiian weeds., Hawaii, USA: Hawaiian Sugar Planters' Association. 479 pp.
Holm L, Doll J, Holm E, Pancho J, Herberger J, 1997. World Weeds. Natural Histories and Distribution., New York, USA: John Wiley and Sons, Inc.
IRRI, 1989. Weeds Reported in Rice in South and South East Asia., Manila, Philippines: International Rice Research Institute.
Kleinschmidt HE, Johnson RW, 1977. Weeds of Queensland., Brisbane, Australia: Department of Primary Industries.
Labrada R, 2003. Important Weed Species in Crops and Countries, Caribbean, Cuba. Data stored from 59 developing countries., Rome, Italy: FAO.
Lorenzi H, 2000. Weeds of Brazil, terrestrial and aquatic, parasitic, poisonous and medicinal. (Plantas daninhas de Brasil, terrestres, aquaticas, parasitas, toxicas e medicinais)., Nova Odessa, Brazil: Plantarum Institute.
Pancho JV, Vega MR, Plucknett DL, 1969. Some Common Weeds of the Philippines., Laguna, Philippines: Weed Science Society of the Philippines, University of the Philippines at Los Baños.
Parham J, 1958. The Weeds of Fiji. In: Bulletin 35, Suva, Fiji: Department of Agriculture.
Remaudiere G, van Harten A, Ilharco FA, 1977. Some Aphidiodea of French Polynesia. In: Bulletin de la Societe Entomologique de France, 82 (5-6) 150-155.
Robertson SA, 1989. Flowering Plants of Seychelles., Kew, UK: Royal Botanic Gardens.
Trinidad and Tobago Biodiversity, 2016. Lists of Invasive species in Trinidad and Tobago., Port of Spain, Trinidad & Tobago: Trinidad & Tobago Biodiversity. http://www.biodiversity.gov.tt/home/trinidad-a-tobago-biodiversity/invasive-alien-species.html
UPHOF J C T, 1968. Dictionary of economic plants. Dictionary of economic plants. 591 pp.
USDA-ARS, 2018. Germplasm Resources Information Network (GRIN). Online Database. In: Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysimple.aspx
Wang Z R, 1990. Farmland Weeds in China. Beijing, China: Agricultural Publishing House.
Links to Websites
Top of pageWebsite | URL | Comment |
---|---|---|
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gateway | https://doi.org/10.5061/dryad.m93f6 | Data source for updated system data added to species habitat list. |
Contributors
Top of page27/02/18 Updated by:
Dr. Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH (Rojas-SandovalJ@si.edu)
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