Melilotus albus (honey clover)
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Plant Type
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat List
- Biology and Ecology
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Economic Impact
- Environmental Impact
- Social Impact
- Risk and Impact Factors
- Uses List
- Similarities to Other Species/Conditions
- Prevention and Control
- Links to Websites
- Distribution Maps
Don't need the entire report?
Generate a print friendly version containing only the sections you need.Generate report
PicturesTop of page
IdentityTop of page
Preferred Scientific Name
- Melilotus albus Medik.
Preferred Common Name
- honey clover
International Common Names
- English: bokhara clover (Australia); sweet clover; white melilot; white melilot (UK); white sweet clover (USA)
- Spanish: alfa-rusa (Argentina); meliloto blanco; trebol blanco; trebol de olor blanco (Bolivia); trebol de Santa Maria (Nicaragua)
- French: melilot blanc; trèfle de Bokhara
- Portuguese: meliloto-branco
Local Common Names
- : handaquq; nafal
- Armenia: isharvuit spitak
- Azerbaijan: ag kheshenbul
- Brazil: trevo-doce-branco
- China: bai hua cao mu xi
- Estonia: valge mesikas
- Finland: valkomesikka
- Germany: Bokharaklee; Bokharaklee; Bucharaklee; Honigklee; Steinklee, Weisser; weisser Steinklee
- Italy: meliloto bianco; meliloto bianco; meliloto bianco; trifoglio di Bokhara; trilobo bianco; vetturina bianca
- Japan: shirobana-shinagawa-hagi
- Korea, Republic of: huinje ondongs sari
- Latvia: baltais amolins
- Lithuania: baltaziedis barkunas
- Moldova: sulchine albe
- Mongolia: gavir tzetzeg; zagaan khoshoon
- Netherlands: witte honingklaver
- Norway: hvitsteinklover
- Poland: nostrzyk bialy
- Portugal: meliloto branco; meliloto-branco
- Russian Federation: donnik belyi; sulfina alba; urun donnik (Yakut)
- Spain: meliloto blanco; meliloto-blanco
- Sweden: vit sotvappling; vit sotvappling; vitmelot
- Turkmenistan: eshekyorunzha
- Ukraine: burkun bilyi
- MEUAL (Melilotus alba)
Summary of InvasivenessTop of page
M. albus is a legume native from south-western Europe to China, the Middle East and north-eastern Africa. It has been introduced to northern Europe, North and South America, Australasia and southern Africa, often as a potential fodder crop. M. albus has typical weedy attributes such as prolific seed production, persistence and presence along roadsides and railways (Turkington et al., 1978), and as a result can negatively impact ecosystem services, wildlife habitats, and agriculture (Gucker, 2009). Although M. albus can be a problematic invasive species it is also important in many places as a fodder crop, a honey producer, soil stabiliser and a useful species for land reclamation.
Taxonomic TreeTop of page
- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Fabales
- Family: Fabaceae
- Subfamily: Papilionoideae
- Genus: Melilotus
- Species: Melilotus albus
Notes on Taxonomy and NomenclatureTop of page
M. albus can either be annual or biennial. The annual form has been named M. albus var. annuus, but this is not accepted (ITIS, 2013).
DescriptionTop of page
Plants have a strong tap root, a crown which produces 1 to 10 upright stems, and trifoliate leaves with the terminal leaflet stalked.
Stem 0.3-2.6 m high, upright, coarse or fine, grooved or channelled, usually pubescent or pilose near the tip. Leaflets of the trifoliate lower leaves broadly ovate, obovate or rhomboidal, rounded or truncate at the tip, irregularly dentate, 1.5-5 cm long; those of the upper leaves oblong-lanceolate, usually rounded or truncate at the tip, dentate or almost entire. Stipules 7-10 mm long, entire, narrowly cuneate, those of the lower leaves with one or two teeth near the broadened base. Each raceme 40-80, rarely 120 flowered, elongated at maturity, 8-15 cm long or occasionally up to 28 cm in some annual varieties. Pedicels 1.5-2 mm long. Flowers-white, 4-6 mm long, single, 10 stamens, 2 ovules in ovary, style and stigma hidden inside a pair of keel petals which are more or less fused along the outer margin to form the keel. Calyx 2-2.5 mm long, teeth as long as the tube, rarely shorter, triangular-lanceolate. Wings and standard more or less equal and longer than the keel. Pod 3-4 mm long, 2-2.5 mm broad, 1.5-2 mm thick, obliquely ovate, reticulately nerved, black, dark grey or tawny, tip obtuse, base of style persisting. Pods usually have 1 seed, rarely 2 or 3. Seeds oval 2-2.5 mm long, 1.5 mm broad, yellow or rarely greenish-yellow; endosperm present, two-layered and completely enclosing the embryo.
Weaver (1920, cited in Gucker, 2009) observed first year taproots over 1.2 m deep and second year ones up to 1.7 m deep.
Plant TypeTop of page Annual
DistributionTop of page
M. albus is native to much of Asia and southern Europe, from France and Spain to Kazakhstan and Myanmar, and also north-east Africa (USDA-ARS, 2014). It has been introduced to many parts of Europe outside its native range, as well as to North and South America, Australasia and southern Africa, often as a crop or potential crop (Turkington et al., 1978). In the USA, the species is considered most common in the upper Midwest and Great Plains regions, including Kentucky, Nebraska, Tennessee and Wisconsin (Gucker, 2009; USDA-NRCS, 2013).
Distribution TableTop of page
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: 10 Jan 2020
|Continent/Country/Region||Distribution||Last Reported||Origin||First Reported||Invasive||Reference||Notes|
|Mozambique||Present, Only in captivity/cultivation||Introduced||Hyde et al. (2013)|
|South Africa||Present||Introduced||USDA-ARS (2013)|
|Tanzania||Present||Introduced||CABI (Undated b)|
|-Beijing||Present||Native||Wang HuaFeng et al. (2011)||Present in all the districts and counties of Beijing|
|-Jammu and Kashmir||Present||CABI Data Mining (Undated); Kaul (1986)|
|-Madhya Pradesh||Present||CABI (Undated b)|
|-Odisha||Present||CABI (Undated b)|
|-Punjab||Present||CABI Data Mining (Undated)|
|-Uttar Pradesh||Present||CABI Data Mining (Undated); Khanna (2009)|
|Kuwait||Present||Mathew et al. (2012)|
|Saudi Arabia||Present||Native||USDA-ARS (2013)|
|South Korea||Present||Native||Kil et al. (2004)|
|United Arab Emirates||Present||Native||USDA-ARS (2013)|
|Belarus||Present||Native||CABI (Undated b)|
|Belgium||Present||Introduced||CABI (Undated b)||Near cities, still increasing|
|Bulgaria||Present||Introduced||CABI (Undated b)|
|Hungary||Present||Native||CABI (Undated b)|
|Iceland||Present||Introduced||Flora Islands (2013)|
|Ireland||Present||Native||Milbau and Stout (2006)|
|Italy||Present||CABI Data Mining (Undated); USDA-ARS (2013)|
|Norway||Present||Introduced||CABI (Undated)||Original citation: Gederaas L Salvesen I Viken A (2007)|
|Portugal||Present||CABI (Undated a)||Present based on regional distribution.|
|Russia||Present||CABI (Undated a)||Present based on regional distribution.|
|-Central Russia||Present||Native||USDA-ARS (2013)|
|-Northern Russia||Present||Native||USDA-ARS (2013)|
|-Southern Russia||Present||Native||USDA-ARS (2013)|
|-Western Siberia||Present||Native||USDA-ARS (2013)|
|Serbia||Present||Native||Nestorovic and Konstantinovic (2011)|
|-Canary Islands||Present||Introduced||CABI (Undated b)|
|United Kingdom||Present||CABI Data Mining (Undated); DAISIE (2008)|
|Canada||Present||CABI (Undated b)|
|-Alberta||Present||CABI Data Mining (Undated); CABI (Undated)|
|-British Columbia||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-New Brunswick||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-Newfoundland and Labrador||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-Northwest Territories||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-Nova Scotia||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-Prince Edward Island||Present||Introduced||Invasive||USDA-NRCS (2013)|
|Dominican Republic||Present||Introduced||ILDIS (2013)|
|Mexico||Present||Introduced||Invasive||Weeds of Mexico (2013)|
|Puerto Rico||Present||Introduced||ILDIS (2013)|
|Saint Pierre and Miquelon||Present||Introduced||Invasive||USDA-NRCS (2013)|
|United States||Present||CABI Data Mining (Undated)|
|-District of Columbia||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-New Hampshire||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-New Jersey||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-New Mexico||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-New York||Present||CABI Data Mining (Undated); USDA-NRCS (2013)|
|-North Carolina||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-North Dakota||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-Rhode Island||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-South Carolina||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-South Dakota||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-Washington||Present||CABI Data Mining (Undated); USDA-NRCS (2013)|
|-West Virginia||Present||Introduced||Invasive||USDA-NRCS (2013)|
|-New South Wales||Present||Introduced||PlantNet (2008)||Weed of cultivation and waste places, rarely common|
|-Queensland||Present||Introduced||Richardson et al. (2006)|
|-South Australia||Present||Introduced||Richardson et al. (2006)|
|-Tasmania||Present||Introduced||Richardson et al. (2006)|
|-Victoria||Present, Only in captivity/cultivation||Introduced||Evans (2001)|
|-Western Australia||Present||Introduced||Florabase (2013)|
|New Zealand||Present||Introduced||Webb et al. (1988)|
|Argentina||Present, Only in captivity/cultivation||Introduced||Evans (2001)|
|-Rio Grande do Sul||Present||Introduced||Schneider (2007)|
|Colombia||Present||Introduced||CABI (Undated)||Original citation: Cardenas and Coulston (1967)|
|Ecuador||Present||Introduced||Jørgensen and León-Yànez (1999)|
|Venezuela||Present||Introduced||CABI (Undated)||Original citation: Cardenas and Coulston (1967)|
History of Introduction and SpreadTop of page
Plants of Melilotus (species unknown) were reported present in North America in 1664 by Boucher (Stevenson, 1969). Its early spread was probably facilitated by beekeepers and agriculturalists, as it can be an important fodder crop and food source for honey bees (Heitlinger, 1975, cited in Turkington et al., 1978).
Risk of IntroductionTop of page
The risk of deliberate introduction to further countries is high as M. albus is sometimes seen as a potentially high value fodder crop. Seeds of M. albus are also sometimes introduced as impurities in seeds of other crops such as lucerne (Medicago sativa) (Gucker, 2009).
HabitatTop of page
M. albus is common in sand dune, prairie, bunchgrass and meadow habitats. It is common in desert shrub, sagebrush (Artemisia spp.), pinyon-juniper (Pinus-Juniperinus) and ponderosa pine (P. ponderosa) communities, but in arid areas it may be most common in riparian areas (Gucker, 2009).
M. albus is an early to mid-seral species common on open, disturbed sites. It rarely persists in dense shade and often appears early in the succession of recently disturbed or bare sites (Gucker, 2009).
In Canada, M. albus is found along roadside edges, railway rights-of-way, pastures and disturbed areas (Turkington et al., 1978). Despite its apparent preference for calcareous soils and its unsuitability for acid soils, it is found on a wide range of soil types, including soils with very low nutrient levels, and both fine and coarse-textured soils (Stoa, 1933). It prefers to grow on recently disturbed sites.
In California, Nevada and Florida, USA, M. albus is primarily restricted to recently disturbed sites. Across almost all the USA it is common in riparian areas (Gucker, 2009).
In Alaska, USA, M. albus occupies habitats with extreme weather (Gucker, 2009), with rainfall being below 170 mm in some places and almost 4000 mm in others, with the average annual temperature in inland Alaska as low as -3.3oC (Conn et al., 2008).
In Hawaii, it is 'apparently uncommon in disturbed sites' (Wagner et al., 1999).
M. albus cannot withstand prolonged flooding, but is occasionally found on gravelly open banks beside rivers in Southern Ontario, Canada. It can apparently tolerate moderate salinity, even occurring on soils where salt crystals were visible on the surface (in Alberta, Saskatchewan and Manitoba, Canada; Braidek et al., 1984). It has been promoted in Australia for use on dryland soils affected by salinity (Evans, 2001; Evans and Kearney, 2003).
Habitat ListTop of page
|Terrestrial – Managed||Cultivated / agricultural land||Present, no further details|
Biology and EcologyTop of page
Plants flower in June-July. In Ontario, Canada, M. albus flowers by the last week of June and continues flowering until frosts in the autumn. Flowers remain fresh for about 2 days, and the first seeds ripen by early August (in Ontario). Seeds continue to ripen until late autumn and many remain on the plant over winter (Turkington et al., 1978).
When pistils and stigmas are the same length, self-pollination takes please readily, but when the pistil is longer than the stamens there is little pollination (Clarke, 1935). Barcikowska (1966, cited in Turkington et al., 1978) found that M. albus is cross-fertile but sometimes exhibits high self-fertility in both its annual and biennial forms. Gorz and Haskins (1971) estimated that cross-pollination was 72% in a biennial population and 67% in an annual population. The authors mentioned that inbreeding is widely used in sweetclover (Melilotus) breeding programmes, resulting in a loss of vigour. However, they stress that vigour would be rapidly recovered when inbred lines are used in producing a variety.
Honey bees (Apis mellifera) are the most important pollinators but Coe and Martin (1920, cited in Turkington et al., 1978) listed a wide variety of insects pollinating sweetclover.
Various estimates have been made of the number of seeds produced per plant, ranging from fewer than 100 seeds (for damaged plants, those on infertile ground or suffering from intense competition) to 350,000 seeds (Turkington et al., 1978).
Physiology and phenology
M. albus has a symbiotic relationship with Rhizobium bacteria in its nodules. The highest nitrogen content is in the vegetative parts in late autumn (Dunham, 1933). The compound coumarin, characteristic of Melilotus plants, is concentrated in flower buds and fresh leaves from the tips of the branches (Linton et al., 1963). Roots, stems and mature leaves have very low levels of coumarin.
Day length affects induction of flowering. When grown in a greenhouse at 25.5oC in the day and 20oC at night, biennial plants of M. albus needed at least a 17 hour photoperiod to initiate flowering (Wiggans, 1953, cited in Turkington et al., 1978). However, annual plants flowered during photoperiods of 12-20 hours.
M. albus produces both ‘soft’ seeds, which germinate readily, and a variable proportion of ‘hard seeds’ that are inherently dormant because of the seed coat’s impermeability to water (Gucker, 2009). Although published reports present very variable results, hard seeds appear to be able to survive in the soil for periods estimated at up to 81 years. Germination of hard seeds can be encouraged by heat treatment (including burning), and also by fluctuating temperatures, with the lower temperatures around freezing (Martin, 1945, cited in Gucker, 2009; Van Assche et al., 2003).
Surprisingly, in a species that seems to establish best in open spaces with little surrounding vegetation, Tobe and Gao (2007) claimed that light is not required for germination. There seems to be some evidence that neighbouring vegetation may to some extent act as a nurse crop by moderating seedling establishment conditions (Smith et al., 2004).
Moisture is needed for germination, but, once established, plants are tolerant of extremely dry conditions.
In southern Ontario, Canada, seedlings appear at any time of the year, although there are pronounced peaks of emergence in March-April and September-October (Turkington et al., 1978).
Smith and Graber (1948, cited in Turkington et al., 1978) described early development of plants of the biennial M. albus. The primary stem becomes branched and a prominent primary root develops. During the first year the crown develops and top growth reaches a maximum in late summer when the roots grow rapidly in size. As root size increases crown buds develop and in the spring of the second year these buds produce rapidly growing stems.
Annual and biennial seedlings are initially similar but by midsummer the top growth of the biennial is more decumbent than that of the annual and buds begin to appear on the crown. Later growth is mainly in the tops in the annual and there is rapid development of the root and crown rhizomes in the biennial (Smith and Gorz, 1965, reported in Turkington et al., 1978).
Although the plants of M. albus last only for one or two years, many seeds are the ‘hard’, impermeable type, which can last in the soil for 20 years or more (Stoa, 1933, cited in Turkington et al., 1978; Munn, 1954, cited in Smith and Gorz, 1965).
Population size and structure
Seedlings in fertile loam or clay often arise in clumps, but most die, presumably from competition for light from faster growing neighbours. In gravelly, sandy or stony ground flowering plants are often large and widely spaced, with seldom more than 1 or 2 m-2 (Turkington et al., 1978). Seedling mortality is always high, with less than 25% of emergent seedlings surviving for more than 5 months. Late summer counts at sandy or gravelly locations showed densities of 50-125 plants m-2 of non-flowering plants, the vast majority of which died before the following spring. Widely-spaced plants are often large with many flowering racemes.
At seedling or early vegetative stages M. albus is not a good competitor with vigorous plants of other species, so that plants tend to be restricted to disturbed, ploughed or eroded ground. However, second year plants quickly grow tall in spring and are effective competitors with newly arising weeds (Turkington et al., 1978).
Mowing of roadsides or waste areas usually favours populations (Turkington et al., 1978).
Populations of M. albus can vary in size from year to year, with ‘boom’ populations in some years (Van Riper and Larson, 2009). In South Dakota ‘sweetclover years’ occur when populations are very high (Johnson and Nicholls, 1970, cited in Gucker, 2009).
As with other legume species, M. albus growth is restricted at low levels of sulphur, and application of nitrogen depresses nitrogen fixation and nodulation (Ashford and Bolton, 1961). The species appears to be able to grow on coal ash dumps (Seraya and Komov, 1971, cited in Turkington et al., 1978) and is also salt tolerant to a degree (Evans, 2001). The species has strong deep taproots and can make good growth on soils of moderately low fertility (Smith and Gorz, 1965, cited in Turkington et al., 1978).
In North America, M. albus grows in a wide range of communities and so is associated with different species (Turkingon et al., 1978). It is associated with herbs and grasses in prairies, with wheat, barley (as a weed in both) or oats (as a companion crop) in crop fields, and with a range of grasses, clover and weedy species in a well-drained abandoned field in Ontario.
In the United States, Gucker (2009) mentions that less common habitats of M. albus include moderately saline marshes, disturbed subalpine fir/grouse whortleberry (Abies lasiocarpa/Vaccinium scoparium) forests in the Northern Rocky Mountains, dry mixed oak and oak-hickory woodlands on the Cumberland Plateau in Tennessee, USA, and hardwood hammocks in Pinellas County, Florida, USA.
M. albus is adapted to a wide range of climatic conditions and is drought tolerant. It only requires adequate moisture for germination and is then capable of development under extremely dry conditions (Turkington et al., 1978). The species is also winter hardy and its range extends as far north as the Yukon and North West Territories in Canada and Alaska in the United States.
M. albus cannot withstand prolonged flooding, but is occasionally found on gravelly open banks beside rivers in Southern Ontario, Canada. Less than 10% of plants survived a 5-day immersion in water at 20oC in Ontario (Turkington et al., 1978).
Notes on Natural EnemiesTop of page
Turkington et al. (1978) listed a number of insects common on M. albus or M. officinalis in London, Ontario, Canada. Frame (2013) named sweetclover weevil (Sitona cylindricollis) as a major pest at establishment that can also damage established stands. Other pests mentioned include the root borer (Walshia miscecoloella), blister beetles (Epicauta spp.) and aphids (Therioaphis riehmi). Frame (2013) also named a number of diseases that affect M. albus: mainly clover rot (Sclerotinia trifoliorum), spring black stem (Ascochyta meliloti), summer black stem (Cercospora davisii), stem canker (Ascochyta caulicola) and root rot (Phytophthora cactorum).
Means of Movement and DispersalTop of page
Natural dispersal (non-biotic)
The large seeds can be blown a few metres by strong winds, but rain and streams are probably much more important for dispersal (Turkington et al., 1978). The authors found that more than two-thirds of M. albus seeds still floated after 15 minutes in violently agitated water.
Vector transmission (biotic)
M. albus seeds can pass in a germinable state through the digestive system of the moose (Alces alces), at the rate of about 16% of seeds ingested (3,595 of 22,000), most being defecated 2 to 3 days after feeding, but with small numbers sometimes still being defacated 11 days after feeding (Seefeldt et al., 2010). Seeds have also been found to survive passage through white-tailed deer, calves, horses, sheep and pigs (Harmon and Keim, 1934; Myers et al., 2004).
Propagules with the outer fruit layers attached can become attached to wet and dry clothing and can be transported in this way (Turkington et al., 1978).
Conn (2010) found seeds of Melilotus (species not determined) in samples of crop, grass and bird seed imported into Alaska, USA. M. albus seeds have been reported as being introduced in imported bird seed (Hanson and Mason, 1985).
M. albus was intentionally introduced to North and South America, Australasian and southern Africa, but its escape and naturalisation as an invasive species were probably neither expected nor considered.
Pathway CausesTop of page
Economic ImpactTop of page
M. albus is regarded as a weed of wheat and barley in Canada (Turkington et al., 2013). As a weed of wheat, M. albus can cause melilot or sweet-clover taint of wheat, caused when still-green sweetclover is harvested with wheat, allowing wheat can absorb the odour of sweet clover (Greenshields, 1957).
Royer and Dickinson (1999, cited in Gucker, 2009) noted the association of M. albus with 28 viral plant diseases including beety curly tip, cucumber mosaic and tobacco streak virus.
Sweet clover disease is a haemorrhagic disease of cattle, occurring mostly in the USA and Canada when mouldy or spoiled sweet clover hay is fed to cattle (Connor, 1997). Large obvious swellings representing subcutaneous haemorrhages are the first clinical signs, usually accompanied by internal haemorrhaging. Sweet clover disease can also occur in sheep, but they are less sensitive. The mycotoxin is dicoumarol, an anti-coagulant, produced from coumaric and melilotic acids in plant tissue by action of the fungi in the hay.
Environmental ImpactTop of page
In the USA, many studies have shown that M. albus adversely affects native grass and forb recruitment and growth, as well as restricting the establishment and growth of woody plant species (Gucker, 2009). M. albus is typically more problematic or invasive in northern rather than southern temperate US grasslands, notably in the upper Midwest and Great Plains regions (Gucker, 2009).
Spellman and Wurtz (2011) studied the effects of M. albus on river floodplains in interior Alaska, USA, and found that its invasion had created a novel shade environment in early seral floodplain plant communities. They recommended that the species should be actively managed to prevent its spread into more glacial rivers in Alaska.
M. albus is a particular threat to prairies because it easily invades open areas and may compete for resources with native species, besides fixing nitrogen and thus affecting edaphic conditions. It is also undesirable on prairie reserves because it is a highly visible exotic when in flower.
As a nitrogen fixer, M. albus also has the potential to alter the soil nutrient status and modify the environment in nitrogen-poor ecosystems, often making them more attractive to other invasive species. It has been suggested that the use of Melilotus species for roadside vegetation and rangeland improvement should be discontinued until its effects on ecosystems has been better determined (Lesica and DeLuca, 2000).
Social ImpactTop of page
The tall and vigorous growth of M. albus can hide guide rails and sign posts, creating a hazard for motorists, especially in Northern Ontario, Canada (Turkington et al., 1978).
Risk and Impact FactorsTop of page Invasiveness
- 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
- Pioneering in disturbed areas
- Fast growing
- Has high reproductive potential
- Has propagules that can remain viable for more than one year
- Has high genetic variability
- Altered trophic level
- Negatively impacts animal health
- Highly likely to be transported internationally accidentally
- Highly likely to be transported internationally deliberately
UsesTop of page
M. albus has long been valued for its potential as a fodder crop, for soil and land reclamation, for stabilising soil and roadside cuttings and for honey production. These features led to its adoption in the early 1900s in many parts of the USA. In Illinois, for example, there were 19,000 ha of sweetclover (Melilotus) grown in 1910 and by 1929 this had increased to 310, 000 ha. Similarly, in Nebraska, 12,000 ha were grown in 1920 and 450,000 ha by 1930 (Smith and Gorz, 1965). However, Turkington et al. (1978) pointed out its use in agriculture has been restricted because of the coarseness of its stems, which detracts from its value as a hay crop, and its impermeable seed coat, which means that the seed has to be scarified before it is sown.
Species of Melilotus have been seeded onto burned areas to help in rapid restoration of vegetation cover, but these efforts have not always been successful (Gucker, 2009).
M. albus has several medicinal uses, such as an anticoagulant and as an eye lotion. Its pleasantly-scented dried leaves have been used to scent linens and sleeping quarters (Gucker, 2009).
M. albus can provide food and nectar for native species. For example, Haack (1993) mentioned it as a nectar source for the endangered Karner blue butterfly (Lycaeids melissa samuelis) in Indiana and Wisconsin, USA. Tepedino et al. (2008) suggested that, since M. albus provided nectar and pollen when floral diversity was low and flowers few at Capitol Reef National Park, Utah, USA, many species of native bees may have benefited from the extended flowering season it provides. In parts of Canada, Turkingon et al. (1978) mentioned that pheasants (Phasianus colchicus) nest in sweetclover (Melilotus) stands.
Uses ListTop of page
Animal feed, fodder, forage
- Fodder/animal feed
- Erosion control or dune stabilization
- Soil conservation
- Soil improvement
Human food and beverage
- Honey/honey flora
Similarities to Other Species/ConditionsTop of page
M. officinalis (yellow sweetclover) is almost indistinguishable from M. albus except that the latter species has white flowers. M. officinalis is also rather smaller, flowers earlier and is found in drier habitats. The seed pods of M. albus are reticularly veined as opposed to the transversely ridged pods of M. officinalis (Webb et al., 1988).
M. indicus is similar in general appearance to M. officinalis and M. albus but is shorter, its corolla shorter (and yellow, becoming white with age), its inflorescence denser, and its pods similar to those of M. albus, but less distinctly veined (Webb et al., 1988). M. altissima also has yellow flowers, but is a very tall biennial of annual with pubescent ovaries and pods (Turkington et al., 1978).
Prevention and ControlTop of page
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.
As with many weedy invasive species that can invade native or improved grasslands, the best method of prevention is to maintain healthy natural communities or pastures/grasslands whose vegetation is disturbed as little as possible (Sheley et al., 2009).
Cultural control and sanitary measures
Because M. albus invades disturbed areas, the establishment and maintenance of a uniform, tall and vigorous perennial community can help resist the advance of species like M. albus. DiTomaso and Healy (2003) effectively eliminated M. albus within two years of establishing perennial species cover.
Gucker (2009) described at length the effects of burning on M. albus. The plant is well adapted to survive fire, especially in its second year. In addition, even if the plants themselves are killed by fire, the seeds can survive for long periods in the soil and their germination is stimulated by heat. Furthermore, the new seedlings take advantage of the lack of competition after fire has passed through an area.
For these reasons, fire can have very mixed effects on M. albus. It can be used to control the species if dormant-season fires used to promote germination of its seed are followed by growing-season fires to kill second-year plants and prevent seed production (Kline, 1986, cited in Gucker, 2009). However, this control method will also reduce native forbs.
Conn and Seefeldt (2009) tested burning M. albus (although their paper described the species as M. officinalis, S. Seefeldt now says it was M. albus; S. Seefeldt, pers. comm., 23 July 2013) with a propane weed burner, combined with cutting plants at 2.5 or 10 cm. Flamed first-year plants wilted immediately after flaming and never recovered, whereas cut first-year plants sent out new branches from meristems at leaf axils below the cut, although still produced fewer seeds than untouched control plants. Second-year plants were damaged but not killed by flaming, and still produced some seeds, as did some of the plants cut at 2.5 cm and most of those cut at 10 cm.
Hand pulling can be used for control, but is usually only effective on very small, isolated populations, and is most effective when the ground is soft enough that the root can be removed (Gucker, 2009).
Cutting or mowing infestations has given mixed results (Gucker, 2009), sometimes reducing population size and seed production but sometimes dispersing the seed even more widely.
Seefeldt et al. (2010) observed that moose ingest and spread viable seeds of M. albus and suggested that control of new infestations might be best carried out by following moose trails and monitoring for new patches of the weed.
No biocontrol agents have been used for its control, although White et al. (1999) suggested that the American native sweetclover weevil (Sitona cylindricollis) may provide some control when present in large numbers.
Turkington et al. (1978) reported that Melilotus spp. are extremely sensitive to damage from widely used herbicides such as 2,4-D, MCPA, MCPB, 2,4-DB and dicamba, although it becomes harder to kill by its second year.
In Alaska, where M. officinalis is proving invasive, Conn and Seefeldt (2009) tested different herbicides in both glasshouse and field for their effectiveness. In the field they found that chlorsulfuron both reduced plant biomass and prevented seed production. Although clopyralid, 2,4-D and triclopyr reduced biomass, results using these chemicals varied from year to year.
The abundance of M. albus can be reduced most effectively by integrated management that encourages native or grassland species and limits growth and reproduction of invasive species (Gucker, 2009).
Conn and Seefeldt (2009) suggested that a combination of a range of herbicides (to reduce the chances of development of herbicide resistance or tolerance) and non-chemical methods of control may be most effective in the long term.
Control by utilization
M. albus is eaten by many herbivores, both domestic and feral, including deer, antelope and elk. However, herbivores consuming seed-bearing plants are more likely to spread the species than control it (Gucker, 2009; Seefeldt et al., 2010). M. albus seeds and insect visitors attract waterfowl, game birds and song birds although, again, these may be more important in spreading the seed than controlling the plant (Gucker, 2009).
ReferencesTop of page
Armstrong JF, 1871. On the naturalized plants of the Province of Canterbury. Transactions and Proceedings of the Royal Society of New Zealand, 1868-1961, 4:284-290. http://rsnz.natlib.govt.nz/volume/rsnz_04/rsnz_04_00_002170.pdf
Ashford R; Bolton JL, 1961. Effects of sulphur and nitrogen fertilization, and inoculation with Rhizobium meliloti on the growth of sweet clover (Melilotus alba Desr.). Canadian Journal of Plant Science, 41:81-90.
Barcikowska B, 1966. Self fertility and inbreeding depressions in white and yellow sweet clover (Melilotus albus Desr. and M. officinalis (L.) Desr. Genetica Polonica, 7:1-11.
BERDS, 2006. Introduced (alien) species checklist. Biodiversity and environmental resource data system of Belize. Accessed 31 July 2013
Braidek JT; Fedec P; Jones D, 1984. Field survey of halophytic plants of disturbed sites on the Canadian prairies. Canadian Journal of Plant Science, 64:745-751.
Cal-IPC (California Invasive Plant Council), 2013. California Invasive Plants Council. Berkeley, California, USA: California Invasive Plant Council. http://www.cal-ipc.org/
Coe; HS; Martin JN, 1920. Sweet-clover seed. US Department of Agriculture Bulletin 844.
Conn JS, 2010. Quantifying and identifying weed seed contaminants in crop seed, grass seed, wildflower mixes, and bird seed. In: Proceedings of 11th Annual Invasive Species Conference. Fairbanks, Alaska, USA: USDA-ARS. http://uaf.edu/files/ces/cnipm/otherresources/11th-annual-proceedings/Conn.pdf
Conn JS; Beattie KL; Shephard MA; Carlson ML; Lapina I; Hebert M; Gronquist R; Densmore R; Rasy M, 2008. Alaska Melilotus invasions: distribution, origin, and susceptibility of plant communities. Arctic, Antarctic, and Alpine Research, 40(2):298-308. http://instaar.colorado.edu/AAAR/index.html
DiTomaso JM; Healy EA, 2003. Aquatic and riparian weeds of the West [ed. by DiTomaso, J. M.\Healy, E. A.]. Oakland, USA: University of California, Agriculture and Natural Resources Communications Services - Publications, vi + 442 pp.
Eckardt N, 1987. Melilotus alba; Melilotus officinalis: sweetclover or white sweetclover; yellow sweetclover. Element Stewardship Abstracts, Nature Conservancy. http://sbsc.wr.usgs.gov/research/projects/swepic/factsheets/MELIL_SPP_APRS.pdf
Evans PM, 2001. Melilotus alba: the preferred forage legume for autumn and spring-summer production on saline soils in SW Victoria. In: Proceedings of 10th Agronomy Conference, Hobart, January 2001., Australia: Australian Society of Agronomy.
Evans PM; Kearney GA, 2003. Melilotus albus (Medik.) is productive and regenerates well on saline soils of neutral to alkaline reaction in the high rainfall zone of south-western Victoria. Australian Journal of Experimental Agriculture, 43(4):349-355.
FAO, 2013. Grassland Species Profiles. Detailed decription of more than 600 grassland species. http://www.fao.org/ag/AGP/AGPC/doc/GBASE/Default.htm
Flora Islands, 2013. Flora of Iceland. Plöntutal - Checklist of vascular plants. http://www.floraislands.is/PDF-skjol/plontutal.pdf
Florabase, 2013. Flora of Western Australia. Perth, Western Australia: Department of Environment and Conservation. http://florabase.dec.wa.gov.au/
Global Compendium of Weeds, 2012. Department of Agriculture and Food, Government of Western Australi, Perth, Australia, and HEAR (online). http://www.hear.org/gcw/
Gucker CL, 2009. Melilotus alba, M. officinalis. Fire Effects Information System (online). Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. http://www.fs.fed.us/database/feis/plants/forb/melspp/all.html
Haack RA, 1993. The endangered Karner blue butterfly (Lepidoptera: Lycaenidae): biology, management considerations, and data gaps. In: Proceedings, 9th central hardwood forest conference; 1993 March 8-10; West Lafayette, IN. Gen. Tech. Rep. NC-161 [ed. by Gillespie, A. R. \Parker, G. R. \Pope, P. E.]. Department of Agriculture, Forest Service, North Central Forest Experiment Station, 83-100.
Harmon GW; Keim FD, 1934. The percentage and viability of weed seeds recovered in the feces of farm animals and their longevity when buried in manure. Journal of the American Society of Agronomy, 26:762-767.
Heitlinger ME, 1975. Burning a protected tallgrass prairie to suppress sweetclover, Melilotus alba Desr. Prairie: a multiple view [ed. by Wali, M. K.]. Grand Forks, North Dakota, USA: University of North Dakota Press., 123-132.
Higgins KF; Barker WT, 1982. Changes in vegetation structure in seeded nesting cover in the prairie pothole region. Special Scientific Report - Wildlife, 242. Washington, DC, USA: US Department of the Interior, Fish and Wildlife Service, 27 pp.
Hsu PS, 2010. The Exotic Flora of Shanghai: A comparison with Hong Kong and Singapore, 2(4):1-24.
Hyde MA; Wursten BT; Ballings P; Dondeyne S, 2013. Flora of Mozambique. http://www.mozambiqueflora.com
IABIN, 2008. Paraguay. Red interamericana de Informacion sobre Biodiversidad. Red de Informacion sobre Especies Invasoras (I3N) ([English title not available]).
ILDIS, 2013. International Legume Database & Information Service. Reading, UK: School of Plant Sciences, Unversity of Reading. http://www.ildis.org/
ILDIS, 2014. International Legume Database and Information Service. Reading, UK: School of Plant Sciences, University of Reading. http://www.ildis.org/
ITIS, 2013. Integrated Taxonomic Information System (ITIS). Washington, DC, USA: Smithsonian Institution/NMNH. http://www.itis.gov/
Johnson JR; Nichols JT, 1970. Plants of South Dakota grasslands: A photographic study. Bulletin, Bulletin 566:163 pp.
Kil JH; Shim KC; Park SH; Koh KS; Suh MH; Ku YB; Suh SU; Oh HK; Kong HY, 2004. Distributions of naturalized alien plants in South Korea. Weed Technology [Invasive plants in natural and managed systems (IPINAMS) conference, Fort Lauderdale, Florida, USA, November 2003.], 18(Suppl.):1493-1495.
Kline VM, 1986. Response of sweet clover (Melilotus alba Desr.) and associated prairie vegetation to seven experimental burning and mowing treatments. In: The prairie: past, present and future: Proceedings of the 9th North American Prairie conference; 1984 July 29 - August 1 [ed. by Clambey, G. K. \Pemble, R. H.]. Tri-College University Center for Environmental Studies, 149-152. http://images.library.wisc.edu/EcoNatRes/EFacs/NAPC/NAPC09/reference/econatres.napc09.vkline.pdf
Lesica PL; DeLuca TH, 2000. Melilotus : a potential problem for the northern Great Plains. Journal of Soil and Water Conservation, 55:259-261.
Linton; JH; Goplen BP; Bell JM; Jacques LB, 1963. Dicoumaril studies. The prothrombin time response of sheep to various levels of contamination in low coumarin sweetclover varieties. Canadian Journal of Animal Science, 43:353-360.
Martin JN, 1945. Germination studies of sweet clover seed. Iowa State College Journal of Science, 19:289-300.
Milbau A; Stout JC, 2006. Database of alien plants in Ireland. Dublin, Ireland: School of Natural Sciences, Trinity College Dublin.
Mulligan GA, 1957. Chromosome numbers of Canadian weeds. Canadian Journal of Botany, 35:779-789.
Myers JA; Vellend M; Gardescu S; Marks PL, 2004. Seed dispersal by white-tailed deer: implications for long-distance dispersal, invasion, and migration of plants in eastern North America. Oecologia, 139(1):35-44.
Nestorovic MLJ; Konstantinovic B, 2011. Overview of the Weed Flora in the Serbia. Contemporary Agriculture,The Serbian Journal of Agricultural Sciences, 60:215-230.
PIER, 2013. Pacific Islands Ecosystems at Risk. Honolulu, Hawaii, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
PlantNet, 2008. Flora of New South Wales. Flora of New South Wales. http://plantnet.rbgsyd.nsw.gov.au/floraonline.htm
Randall RP, 2012. A Global Compendium of Weeds. Perth, Australia: Department of Agriculture and Food Western Australia, 1124 pp. http://www.cabi.org/isc/FullTextPDF/2013/20133109119.pdf
Richardson FJ; Richardson RG; Shepherd RCH, 2006. Weeds of the South-East. Meredith, Victoria, Australia: R.G. and F.J. Richardson, 438 pp.
Royal Botanic Gardens Sydney, 2013. Australia’s Virtual Herbarium. Sydney, Australia: Royal Botanic Gardens. http://avh.chah.org.au/
Royer F; Dickinson R, 1999. Weeds of the northern US and Canada: a guide for identification. Edmonton, AB; Renton, WA, Canada; USA: The University of Alberta Press; Lone Pine Publishing, 434 pp.
Schneider AA, 2007. The naturalized flora of Rio Grande do Sul State, Brazil: subspontaneous herbaceous plants. (Flora naturalizada no estado do Rio Grande do Sul, Brasil: herbáceas subespontâneas.) Biociências, 15(2):257-268. http://revistaseletronicas.pucrs.br/ojs/index.php/fabio/article/viewFile/254/3005
Seefeldt SS; Collins WB; Kuhl JC; Clauss M, 2010. White sweetclover (Melilotus albus) and narrowleaf hawksbeard (Crepis tectorum) seed germination after passing through moose. Invasive Plant Science and Management, 3(1):26-31. http://www.wssa.net
Seraya GP; Komov SV, 1971. Seed growth and shoot formation in flowering plants on coal ash. Ekologiya, 2:91-93.
Sheley RL; Manoukian M; Marks G, 1999. Preventing noxious weed invasion. In: Sheley RL, Petroff JK, eds. Biology and Management of Noxious Rangeland Weeds. Corvallis, USA: Oregon State University Press, 69-72.
Smith WK; Gorz HJ, 1965. Sweet clover improvement. Advances in Agronomy, 17:163-231.
Spellman BT; Wurtz TL, 2011. Invasive sweetclover (Melilotus alba) impacts native seedling recruitment along floodplains of interior Alaska. Biological Invasions, 13(8):1779-1790. http://www.springerlink.com/content/d027n5434l8vl02q/
Stevenson GA, 1969. An agronomic and taxonomic review of the genus Melilotus Mill. Canadian Journal of Plant Science, 49:1-20.
Tepedino VJ; Bradley BA; Griswold TL, 2008. Might flowers of invasive plants increase native bee carrying capacity? Intimations from Capitol Reef National Park, Utah. Natural Areas Journal, 28(1):44-50. http://www.naturalarea.org
USDA-ARS, 2013. 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, 2013. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/
Wagner WI; Herbst DR; Sohmer SH, 1999. Manual of the Flowering Plants of Hawaii, revised edition. Honolulu, Hawaii, USA: University of Hawaii Press.
Wang HuaFeng; López-Pujol J; Meyerson LA; Qiu JiangXiao; Wang XiaoKe; Ouyang ZhiYun, 2011. Biological invasions in rapidly urbanizing areas: a case study of Beijing, China. Biodiversity and Conservation, 20(11):2483-2509. http://www.springerlink.com/content/vq847t82k48u28j6/
Weaver JE, 1920. Root development in the grassland formation: A correlation of the root systems of native vegetation and crop plants. Washington, DC, USA: Carnegie Institution of Washington, 151 pp.
Weeds of Mexico, 2013. Weeds of Mexico (Malezas de Mexico). http://www.conabio.gob.mx/malezasdemexico/fabaceae/melilotus-alba/fichas/ficha.htm
White D J; Haber E; Keddy C, 1993. Invasive Plants of Neutral Habitats in Canada. Ottawa, Canada: Canadian Wildlife Service.
Wunderlin RP; Hansen BF, 2003. Atlas of Florida Vascular Plants. Institute for Systematic Biology, University of South Florida, Tampa, USA. http://www.plantatlas.usf.edu/.
BERDS, 2006. Introduced (alien) species checklist. In: Biodiversity and environmental resource data system of Belize,
CABI Data Mining, Undated. CAB Abstracts Data Mining.,
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
Evans P M, 2001. Melilotus alba: the preferred forage legume for autumn and spring-summer production on saline soils in SW Victoria. In: Science and technology: delivering results for agriculture? Proceedings of the 10th Australian Agronomy Conference, 29 January - 1 February 2001, Hobart, Tasmania, Australia. [ed. by Rowe B, Donaghy D, Mendham N]. Warragul, Australia: Australian Society of Agronomy Inc. unpaginated. http://www.agronomyaustraliaproceedings.org/images/sampledata/2001/3/b/evans.pdf
Flora Islands, 2013. Flora of Iceland. In: Plöntutal - Checklist of vascular plants, http://www.floraislands.is/PDF-skjol/plontutal.pdf
Florabase, 2013. Flora of Western Australia., Perth, Western, Australia: Department of Environment and Conservation. http://florabase.dec.wa.gov.au/
Hsu PS, 2010. The Exotic Flora of Shanghai: A comparison with Hong Kong and Singapore., 2 (4) 1-24.
Hyde MA, Wursten BT, Ballings P, Dondeyne S, 2013. Flora of Mozambique., http://www.mozambiqueflora.com
IABIN, 2008. [English title not available]. (Paraguay. Red interamericana de Informacion sobre Biodiversidad Red de Informacion sobre Especies Invasoras (I3N)).,
ILDIS, 2013. International Legume Database & Information Service., Reading, UK: School of Plant Sciences, Unversity of Reading. http://www.ildis.org/
Kil J H, Shim K C, Park S H, Koh K S, Suh M H, Ku Y B, Suh S U, Oh H K, Kong H Y, 2004. Distributions of naturalized alien plants in South Korea. Weed Technology. 18 (Suppl.), 1493-1495. DOI:10.1614/0890-037X(2004)018[1493:DONAPI]2.0.CO;2
Milbau A, Stout JC, 2006. Database of alien plants in Ireland., Dublin, Ireland: School of Natural Sciences, Trinity College Dublin.
Nestorovic MLJ, Konstantinovic B, 2011. Overview of the Weed Flora in the Serbia. In: Contemporary Agriculture,The Serbian Journal of Agricultural Sciences, 60 215-230.
PIER, 2013. Pacific Islands Ecosystems at Risk., Honolulu, Hawaii, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
PlantNet, 2008. Flora of New South Wales., http://plantnet.rbgsyd.nsw.gov.au/floraonline.htm
Randall RP, 2012. A Global Compendium of Weeds., Perth, Australia: Department of Agriculture and Food Western Australia. 1124 pp. http://www.cabi.org/isc/FullTextPDF/2013/20133109119.pdf
Richardson FJ, Richardson RG, Shepherd RCH, 2006. Weeds of the South-East., Meredith, Victoria, Australia: R.G. and F.J. Richardson. 438 pp.
Schneider A A, 2007. The naturalized flora of Rio Grande do Sul State, Brazil: subspontaneous herbaceous plants. (Flora naturalizada no estado do Rio Grande do Sul, Brasil: herbáceas subespontâneas.). Biociências. 15 (2), 257-268. http://revistaseletronicas.pucrs.br/ojs/index.php/fabio/article/viewFile/254/3005
USDA-ARS, 2013. 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, 2013. The PLANTS Database. Greensboro, North Carolina, USA: National Plant Data Team. https://plants.sc.egov.usda.gov
Wang HuaFeng, López-Pujol J, Meyerson L A, Qiu JiangXiao, Wang XiaoKe, Ouyang ZhiYun, 2011. Biological invasions in rapidly urbanizing areas: a case study of Beijing, China. Biodiversity and Conservation. 20 (11), 2483-2509. http://www.springerlink.com/content/vq847t82k48u28j6/ DOI:10.1007/s10531-011-9999-x
Webb C J, Sykes W R, Garnock-Jones P J, 1988. Flora of New Zealand, Volume IV: Naturalised pteridophytes, gymnosperms, dicotyledons. Christchurch, New Zealand: Botany Division, DSIR. 1365 pp. http://floraseries.landcareresearch.co.nz/pages/Book.aspx?fileName=Flora%204.xml
Weeds of Mexico, 2013. Weeds of Mexico. (Malezas de Mexico)., http://www.conabio.gob.mx/malezasdemexico/fabaceae/melilotus-alba/fichas/ficha.htm
ContributorsTop of page
: Original text by:
Ian Popay, consultant, New Zealand, with the support of Landcare Research.
Distribution MapsTop of page
Unsupported Web Browser:
One or more of the features that are needed to show you the maps functionality are not available in the web browser that you are using.
Please consider upgrading your browser to the latest version or installing a new browser.
More information about modern web browsers can be found at http://browsehappy.com/