Triumfetta semitriloba (burweed)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Description
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat
- Habitat List
- Biology and Ecology
- Climate
- Latitude/Altitude Ranges
- Air Temperature
- Rainfall
- Rainfall Regime
- Soil Tolerances
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Economic Impact
- Environmental Impact
- Social Impact
- Risk and Impact Factors
- Uses
- Similarities to Other Species/Conditions
- Prevention and Control
- References
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Triumfetta semitriloba Jacq.
Preferred Common Name
- burweed
Other Scientific Names
- Heliocarpus hirtus (Vahl) R.O.Williams & Sandwith
- Triumfetta abutiloides A.St.-Hil
- Triumfetta hirta Vahl
- Triumfetta obscura A.St.-Hil.
- Triumfetta oxyphylla DC.
- Triumfetta rubricaulis Kunth
- Triumfetta tricuspis A.St.-Hil.
International Common Names
- English: black bush; sacramento bur; sacramento burbark; triumfetta
- Spanish: cadillo de perro; cadillo de perro; escobilla amarilla; escobilla amarilla; gúizapol de Borrego; guizazo de caballo (Cuba); huizapolillo; mozote colorado; mozote colorado; pegadillo
- French: cousin-petit; mahot-cousinrouge; petit mahot-cousin; tête à nègre
Local Common Names
- Brazil: carrapicho; carrapicho-de-calçada; carrapicho-miúdo; juta-nacional; juta-nacional
- China: fei dao ci shuo ma
- Cuba: guizazo de caballo
- Ecuador/Galapagos Islands: pegadillo
- Guam: dadangsi; masiksik lahe
- USA: black bush; Sacramento bur; Sacramento burbark; triumfetta
EPPO code
- TIUSE (Triumfetta semitriloba)
Summary of Invasiveness
Top of pageTriumfetta semitriloba (burweed) is a weedy perennial shrub species, native to large parts of tropical and subtropical America, from northern Argentina and Chile to Mexico and Florida. It has been introduced and has become invasive in a number of Pacific islands. It is a declared noxious weed in Hawaii and is noted as invasive in the Galapagos islands, Micronesia, Tonga, Guam and Taiwan, generally found in wasteland, farmland and forest areas. It is, however, less widespread that the widely naturalized and invasive T. rhomboidea. Although reasons for international introduction are unknown, the hooked barbs on the burs attach themselves to animals, and are the main reason for its spread. Control is difficult, and further accidental introduction is likely, therefore efforts should be made to reduce such risks.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Malvales
- Family: Tiliaceae
- Genus: Triumfetta
- Species: Triumfetta semitriloba
Notes on Taxonomy and Nomenclature
Top of pageThere appears to be some confusion regarding taxonomic placement of the genus Triumfetta. It is generally regarded as a member of the Malvaceae family, though placed by some in the Tiliaceae. Nonetheless, it is a clearly demarcated genus, containing several to many species, depending on the classification used. Triumfetta semitriloba has cleary defined taxonomic limits, but given its very broad native range, from Florida to Argentina and Chile, it is not surprising that several varieties are reported, including var. berlandieri, var. brasiliensis, var. martiana and var. surinamensis, and a form, f. althaeoides.
Description
Top of pageAdapted from: Long and Lakela (1976); Howard (1989); Liogier (1994); Flora of China (2015); PIER, (2015).
T. semitriloba is a commonly single-stemmed, perennial but short-lived shrub, generally 1 m tall or more, up to 3 m, or occasionally a herb or subshrub 0.5 m tall. Stems erect, with a woody main stem to 3 cm diameter, with smooth, grey bark. Branchlets pubescent and densely stellate especially when young, hairs simple and stellate, becoming glabrate with age. Leaves variable in shape, usually broadly ovate or rhombic-ovate to lanceolate especially in the upper parts of the plant, sometimes obscurely 3-lobed and 3-nerved from base, 3-8 cm long, 3-6 cm wide, stellate pubescent, more so on lower surface, margins irregularly serrate-dentate, apex acuminate, base very broadly cuneate to truncate, rarely subcordate, Petioles 0.5-(1.5-6)-9.5 cm long growing progressively shorter toward the plant apex. Flowers are 5 mm long, in leaf axils, with 5 yellow petals. Flower buds are cylindrical, ca. 4 mm, pubescent, pedicel 2-3 mm, sepals linear, 4-7 mm long, abaxially stellate pubescent, appendage subapical, ca. 0.5 mm, pubescent. Petals narrowly elliptic-obovate or oblanceolate, 3.5-6.5 mm long, about as long as the sepals, stamens 15-20, filaments glabrous. Ovary 3-loculed, spiny; style 3-5 mm; stigma ± 3-lobed. The fruits, with scattered reflexed hairs on the hooked spines, are round burs 6-8 mm in diameter, borne in groups of two or three. Each fruit has three compartments containing 1-3 brown seeds, 2 mm long and broadly oval. Capsule globose, body 3-5 mm in diameter, 3-loculed, indehiscent, glabrescent; spines 1.5-2 mm, retrorsely pilosulose at base, conical at base, tip hooked.
Distribution
Top of pageT. semitriloba has a very broad native range in the Americas, from Mexico and central Florida, down through the Caribbean and Central America, to northern and central South America as far as northern Argentina and Chile (USDA-ARS, 2015). Isolated records from the very south-east of Georgia, USA, are recorded as introduced (USDA-NRCS, 2015).
T. semitriloba is recorded as introduced throughout much of the Pacific region, as far as the Philippines and Taiwan (PIER, 2015). However, there are no records from mainland New Zealand or Australia, nor from any part of Africa or mainland Asia. Noting its morphological similarity to the much more widespread and naturalized weed T. rhomboidea, it is possible that it is present elsewhere but remains as yet unidentified. Unconfirmed herbarium records in GBIF (2015) in Cameroon, Papua New Guinea and West Papua, Indonesia, are examples where further work may yield additional records or clarify uncertainty.
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: 10 Jan 2020Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Asia |
|||||||
Philippines | Present | Introduced | |||||
Taiwan | Present | Introduced | Invasive | ||||
North America |
|||||||
Antigua and Barbuda | Present | Native | |||||
Bahamas | Present | Native | |||||
Barbados | Present | Native | |||||
Belize | Present | Native | |||||
Bermuda | Present | Native | |||||
British Virgin Islands | Present | Native | |||||
Cayman Islands | Present | Native | |||||
Costa Rica | Present | Native | |||||
Cuba | Present | Native | |||||
Dominica | Present | Native | |||||
Dominican Republic | Present | Native | |||||
El Salvador | Present | Native | |||||
Grenada | Present | Native | |||||
Guadeloupe | Present | Native | |||||
Guatemala | Present | Native | |||||
Haiti | Present | Native | |||||
Honduras | Present | Native | |||||
Jamaica | Present | Native | |||||
Martinique | Present | Native | |||||
Mexico | Present | Native | |||||
Montserrat | Present | Native | |||||
Nicaragua | Present | Native | |||||
Panama | Present | Native | |||||
Puerto Rico | Present | Native | |||||
Saint Lucia | Present | Native | |||||
Saint Vincent and the Grenadines | Present | Native | |||||
U.S. Virgin Islands | Present | Native | |||||
United States | Present | Present based on regional distribution. | |||||
-District of Columbia | Present | Native | |||||
-Florida | Present | Native | |||||
-Georgia | Present | Introduced | |||||
-Hawaii | Present | Introduced | Invasive | ||||
Oceania |
|||||||
Cook Islands | Present | Introduced | |||||
Federated States of Micronesia | Present | Introduced | Invasive | ||||
Guam | Present | Introduced | Invasive | ||||
Nauru | Present | Introduced | |||||
New Caledonia | Present | Introduced | |||||
Northern Mariana Islands | Present | Introduced | Invasive | ||||
Samoa | Present | Introduced | |||||
Tonga | Present | Introduced | Invasive | ||||
South America |
|||||||
Argentina | Present | Native | |||||
Bolivia | Present | Native | |||||
Brazil | Present | Native | |||||
-Bahia | Present | Native | |||||
-Goias | Present | Native | |||||
-Mato Grosso do Sul | Present | Native | |||||
-Minas Gerais | Present | Native | |||||
-Parana | Present | Native | |||||
-Rio de Janeiro | Present | Native | |||||
-Sao Paulo | Present | Native | |||||
Chile | Present | Native | |||||
-Easter Island | Present | Possible introduction | |||||
Colombia | Present | Native | |||||
Ecuador | Present | Native | |||||
-Galapagos Islands | Present | Native | |||||
Guyana | Present | Native | |||||
Paraguay | Present | Native | |||||
Peru | Present | Native | |||||
Venezuela | Present | Native |
History of Introduction and Spread
Top of pageIt is assumed that the introduction of T. semitriloba throughout the Pacific occurred in the early twentieth century, if not before. The first record of its presence in the Pacific islands was on Maui, Hawaii, in 1910 (Motooka et al., 2003), and it was also noted as a noxious weed in Hawaii by the middle of the 1900s (Hosaka and Thistle, 1954).
Risk of Introduction
Top of pageThe invasiveness of the closely related T. rhomboidea, and the lack of information on means of introduction and spread, indicate that T. semitriloba has a high risk of further introduction and invasion. In order to minimize the risk, this species should be included on prohibited species lists for countries with suitable tropical and subtropical climates.
Habitat
Top of pagePIER (2015) collate reports of T. semitriloba being naturalized and often common in dry, disturbed sites up to 1000 m altitude in Hawaii, and arid lowlands and moist uplands in the Galápagos Islands. In Florida it is found in pinelands and hammocks (Long and Lakela, 1976), while in Puerto Rico it is found growing in roadsides, neglected pastures, and wastelands up to around 700 m. Where naturalized in Taiwan and the Philippines, it is found in agricultural fields and wastelands (Flora of China, 2015).
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 | Managed grasslands (grazing systems) | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Harmful (pest or invasive) |
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 | Scrub / shrublands | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Scrub / shrublands | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Arid regions | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Arid regions | Present, no further details | Natural |
Littoral | Coastal areas | Present, no further details | Harmful (pest or invasive) | |
Littoral | Coastal areas | Present, no further details | Natural |
Biology and Ecology
Top of pageGenetics
T. semitriloba has a chromosome count of 2n = 32 (Long and Lakela, 1976).
Reproductive Biology
T. semitriloba begins flowering and fruiting at about 6 months and produces fruit in abundant quantities (Long and Lakela 1976). Seed production is guaranteed by self-pollination, but cross-pollination increases seed set and probably seed quality, aided by solitary and social bees in Brazil (Collevatti et al., 1997). There are approximately 250,000 seeds per kg, and on filter paper, epigeal germination begins after 10 days, with 40% germination after 4 months.
Physiology and Phenology
T. semitriloba flowers and fruits continuously from six months of age until it dies (Long and Lakela, 1976), but in Florida, flowering tends to concentrate in the period from October to January. In seasonally dry habitats it behaves as an annual, but may live up to three years. Structural features of the floral nectaries and glands, located at the margins of the leaves of T. semitriloba, are typical of other taxa of the Malvales (Leitao et al., 2005). They secrete sucrose, glucose, and fructose and are of a specialized type, with a secretory epidermis comprising pluricellular and multiserial nectariferous trichomes, covering a nectariferous parenchyma, vascularized by phloem and xylem. Foliar and bract nectaries contain phenolic compounds, absent in floral nectaries, and also differ in their length and diameter.
Environmental Requirements
T. semitriloba is predominantly a neotropical species, but has a native range that also extends into the subtropics, where it will also tolerate dry and even temperate climates at the extremes of its range. In the native range in Puerto Rico, the diverse habitats populated by T. semitriloba are in areas with an annual rainfall within the range of 900-2200 mm. Where introduced in Hawaii, it grows from sea level to 1067 m and in areas with mean annual rainfall of 760-1500 mm (Haselwood and Motter 1966). T. semitriloba grows in a variety of soils from sands to clays, with pH values from approximately 5.5 to 8.0.
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]) | |
BS - Steppe climate | Tolerated | > 430mm and < 860mm annual precipitation | |
BW - Desert climate | Tolerated | < 430mm annual precipitation | |
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) |
---|---|---|---|
28 | 28 |
Air Temperature
Top of pageParameter | Lower limit | Upper limit |
---|---|---|
Mean annual temperature (ºC) | 10 | 30 |
Mean maximum temperature of hottest month (ºC) | 15 | 35 |
Mean minimum temperature of coldest month (ºC) | 5 | 25 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Dry season duration | 0 | 4 | number of consecutive months with <40 mm rainfall |
Mean annual rainfall | 750 | 2200 | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
- impeded
Soil reaction
- acid
- alkaline
- neutral
Soil texture
- heavy
- light
- medium
Special soil tolerances
- infertile
- shallow
Means of Movement and Dispersal
Top of pageT. semitriloba appears to require disturbance for successful establishment. Given an equal start, it competes well with other herbs, grasses and shrubs in full sun or partial shade (Motooka et al., 2003).
The fruit are burs with specially adapted hooks or barbs that cling to clothing and fur, and seeds are dispersed when the burs attach themselves to passing animals. The weed is also commonly known simply as ‘burweed’ which reflects this.
There is no information available on the reasons for international introduction, though having no real use, intentional introduction is considered unlikely. It is possible that T. semitriloba burs were introduced accidentally, hitchhiking on clothing and fur, either via people or livestock and their products.
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Animal production | Yes | |||
Disturbance | Yes |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Clothing, footwear and possessions | Yes | |||
Livestock | Yes |
Economic Impact
Top of pageT. semitriloba is an alternative host of the leafhopper Empoasca formosana, which is a vector of cadang-cadang disease on coconuts. However, the plant was found not to be a reservoir for the actual virus responsible for cadang-cadang (Bigornia, 1963).
Environmental Impact
Top of pageT. semitriloba is generally found growing in small patches and as single, dispersed plants, but can be numerous in disturbed forest sites. In these situations, it can prevent the establishment of native species, such as in the Haleakala National Park in Hawaii (Motooka et al., 2003).
Social Impact
Top of pageThe hooked burs are a nuisance to people and especially to livestock and other animals, in both pastures and forests, where the plant is present (Motooka et al., 2003).
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
- Tolerant of shade
- Has high reproductive potential
- Has high genetic variability
- Threat to/ loss of native species
- Competition - monopolizing resources
- Produces spines, thorns or burrs
- Highly likely to be transported internationally accidentally
- Difficult to identify/detect as a commodity contaminant
- Difficult to identify/detect in the field
- Difficult/costly to control
Uses
Top of pageT. semitriloba has no real use or value. Foliage is reported to have no forage value, and the stem is too small to be a meaningful source of fuelwood (Haselwood and Motter, 1966). Fibres extracted from the bark of larger stems are reported to have been used by the inhabitants of Rapa Nui (Easter Island) to make fishing lines, and related species are reported to have medicinal value.
Similarities to Other Species/Conditions
Top of pageT. semitriloba very easily confused with the more widespread T. rhomboidea, but is distinguished by having longer pedicels (2-3 mm compared to 1 mm in T. rhomboidea)and 15 stamens or more (10 in T. rhomboidea) (Flora of China, 2015). The former also tends to be larger (Motooka et al., 2003) and have longer, hairy spines (PIER, 2015).
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.
Control
Because the burs stick to clothing and fur, sanitation measures and control before seed set is critical to prevent its spread (Motooka et al., 2003).
Where introduced and invasive in parts of the Pacific, control is often needed in cropland and pastures. Treatments follow normal practice for coarse broadleaved weeds, such as manual digging, mechanical cultivation and spraying with herbicides such as 2,4-D and foliar drizzle applications of triclopyr and of glyphosate (Motooka et al., 2003).
References
Top of pageFlora of China Editorial Committee, 2014. Flora of China. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.efloras.org/flora_page.aspx?flora_id=2
GBIF, 2015. Global Biodiversity Information Facility. http://www.gbif.org/species
Haselwood EL; Motter GG, 1966. Handbook of Hawaiian weeds. Hawaii, USA: Hawaiian Sugar Planters' Association, 479pp.
Hosaka EY; Thistle A, 1954. Noxious plants of the Hawaiian ranges. Hawaii Agricultural Experimental Station Bulletin 62. Honolulu, Hawaii, USA: University of Hawaii, College of Agriculture, 39 pp.
Liogier HA, 1994. Descriptive flora of Puerto Rico and adjacent islands: Spermatophyta, 3. Río Piedras, Puerto Rico: Editorial de la Universidad de Puerto Rico, 461 pp.
Lorenzi H, 1982. Plantas Daninhas do Brasil. Sao Paulo, Brazil: H. Lorenzi, 425 pp.
Missouri Botanical Garden, 2015. Tropicos database. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/
PIER, 2015. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
The Plant List, 2013. The Plant List: a working list of all plant species. Version 1.1. London, UK: Royal Botanic Gardens, Kew. http://www.theplantlist.org
USDA-ARS, 2015. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx
USDA-NRCS, 2015. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/
Distribution References
CABI, Undated. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Missouri Botanical Garden, 2015. Tropicos database., St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/
PIER, 2015. Pacific Islands Ecosystems at Risk., Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
USDA-ARS, 2015. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysimple.aspx
USDA-NRCS, 2015. The PLANTS Database. Greensboro, North Carolina, USA: National Plant Data Team. https://plants.sc.egov.usda.gov
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