Tragus racemosus (stalker bur grass)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Description
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Introductions
- Risk of Introduction
- Habitat
- Habitat List
- Hosts/Species Affected
- Biology and Ecology
- Climate
- Latitude/Altitude Ranges
- Air Temperature
- Rainfall
- Rainfall Regime
- Soil Tolerances
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Economic Impact
- Impact: Biodiversity
- Risk and Impact Factors
- Uses
- Uses List
- Similarities to Other Species/Conditions
- References
- Links to Websites
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Tragus racemosus (L.) All.
Preferred Common Name
- stalker bur grass
Other Scientific Names
- Cenchrus racemosus L.
- Lappago decipiens Fig. & De Not.
- Lappago racemosa (L.) Honck.
- Nazia racemosa (L.) Kuntze
- Tragus adriaticus Gand.
- Tragus arenarius Bremek. & Oberm.
- Tragus brevicaulis Boiss.
- Tragus decipiens (Fig. & De Not) Boiss.
- Tragus echinatus Cav.
- Tragus pallens Gand.
- Tragus paucispinus Hack.
International Common Names
- English: carrot seed grass; European bur grass; large carrot-seed grass; spike bur grass
Local Common Names
- Cuba: rabo de gato
- France: tragus à grappes
- Germany: Klettengras
- Italy: lappola
- South Africa: wortelsaadgras
- Spain: cerretes; escanyyagats; grama enmarañada
- Sweden: piprensargräs
Summary of Invasiveness
Top of pageTragus racemosus is an annual grass native to Europe, Asia and Africa. It is listed as an invasive species in Cuba, being naturalized from the central part of the country to the eastern provinces. Although this species is reported as not affecting crops it is very competitive in dry and nutrient-poor soils. T. racemosus is also listed as invasive in Belgium and Serbia but without further details given. Although considered as a rare and ephemeral alien species in Belgium, it is recognized that this species is spreading fast from southern Europe and becoming abundant at some disturbed areas. T. racemosus is also described as a prostrate weed of warm semiarid areas.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Monocotyledonae
- Order: Cyperales
- Family: Poaceae
- Genus: Tragus
- Species: Tragus racemosus
Notes on Taxonomy and Nomenclature
Top of pageTragus is a genus in the Poaceae family with seven to eight accepted species, mostly tropical and subtropical (Anton, 1981; World Flora Online, 2020). The genus is characterized by having a disarticulating inflorescence, a rudimentary first glume and an awnless second glume with distinctive prickles or spines on its nerves (Anton, 1981).
The genus name Tragus comes from the Greek word ‘tragos’ meaning he-goat and the specific epithet ‘racemosus’ refers to the racemose inflorescence (SEINet, 2020). Of the synonyms reported for T. racemosus, Aira malatrina, Cenchrus linearis, Lappago biflora, Phalaris muricata, T. biflorus and T. muricatus are invalid names; T. halleri and T. orientalis are illegitimate names (World Flora Online, 2020).
Description
Top of pageThe following description is from PROTA (2020):
Annual up to 25 cm tall, erect or geniculately ascending; leaf laminas 2-6 cm × 1.5-4.5 mm, flat or plicate, glaucous, the margins thickened, whitish, pectinate with bulbous-based hairs or barbellate. Inflorescence 2.5-6 cm long, compactly cylindrical, congested; racemelets comprising (1)2-4 fertile and (1)2 sterile spikelets borne on a short peduncle. Spikelets 3.2-4 mm long; superior glume prominently 7-nerved, the nerves bearing hooked, bulbous-based prickles, glabrous between the nerves; anthers 0.5-0.7 mm long.
Distribution
Top of pageTragus racemosus is a small ephemeral grass native to arid areas, deserts, semi-desert and semiarid continental areas of Africa, Asia and Europe (Kalapos et al., 1996; Shabana et al., 2018; Native Plant Trust, 2020; PROTA, 2020; SEINet, 2020; USDA-ARS, 2020). Its native distribution in Europe is restricted to the semiarid continental climate of Europe where it grows only during the hot and dry months (Kalapos et al., 1996). It has been introduced to the New World accidentally as a contaminant of wool products (Native Plant Trust, 2020).
Tragus racemosus is reported in Asia, Africa, Europe, North America, the Caribbean and South America (Fasseaux, 1949; Harsh and Sen, 1975; Proctor, 1982; Sulekic and Zapater, 2001; E-Flora of South Africa, 2020; Euro+Med, 2020; India Biodiversity Portal, 2020; Missouri Botanical Garden, 2020; PROTA, 2020; SEINet, 2020; USDA-ARS, 2020).
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: 17 Dec 2021Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Algeria | Present | Native | |||||
Angola | Present | Native | |||||
Botswana | Present | Native | |||||
Cabo Verde | Present | Native | |||||
Central African Republic | Present | Native | |||||
Egypt | Present | Native | |||||
Ethiopia | Present | Native | |||||
Lesotho | Present | Native | |||||
Libya | Present | Introduced | 1984 | Sources differ as to whether it is native or introduced | |||
Mali | Present | Native | |||||
Mauritania | Present | Native | |||||
Morocco | Present | Native | |||||
Namibia | Present | Native | |||||
Senegal | Present | Native | |||||
Somalia | Present | Native | |||||
South Africa | Present | Native | |||||
Sudan | Present | Native | |||||
Tunisia | Present | Native | |||||
Zimbabwe | Present | Native | |||||
Asia |
|||||||
Afghanistan | Present | Native | |||||
Armenia | Present | Native | |||||
Azerbaijan | Present | Native | |||||
China | Absent, Invalid presence record(s) | Misidentified record | |||||
Georgia | Present | Native | |||||
India | Present | Native | |||||
-Rajasthan | Present | Native | Ephemeral. Appears with the start of the rainy season and disappears in late August | ||||
-Uttar Pradesh | Present | Native | |||||
Iran | Present | Native | |||||
Kazakhstan | Present | Native | |||||
Kyrgyzstan | Present | Introduced | |||||
Lebanon | Present | Native | |||||
Oman | Present | Native | |||||
Pakistan | Present | Occurrence rare, available during monsoon season for grazing by camels in Cholistan desert | |||||
Saudi Arabia | Present | Native | |||||
Syria | Present | Native | |||||
Thailand | Present | Native | |||||
Turkey | Present | Native | |||||
United Arab Emirates | Present | Native | |||||
Yemen | Present | Native | |||||
Europe |
|||||||
Albania | Present | Native | |||||
Austria | Present | Introduced | 1872 | Urban areas, agricultural areas, disturbed areas, grass and heathlands | |||
Belgium | Present | Introduced | Invasive | ||||
Bulgaria | Present | Native | |||||
Croatia | Present | Native | |||||
Czechia | Present | Native | |||||
France | Present | Native | |||||
-Corsica | Present | Native | |||||
Germany | Present | Introduced | |||||
Greece | Present | Native | |||||
Hungary | Present | Native | |||||
Italy | Present | Native | |||||
Malta | Present | Native | |||||
Moldova | Present | ||||||
Netherlands | Present | Introduced | Casual | ||||
Poland | Present | Introduced | Casual | ||||
Romania | Present | Native | |||||
Russia | Present | Native | |||||
Serbia | Present | Invasive | |||||
Slovakia | Present | Native | |||||
Slovenia | Present | Native | |||||
Spain | Present | Native | |||||
-Balearic Islands | Present | Native | |||||
-Canary Islands | Present | Native | |||||
Switzerland | Present | Native | |||||
Ukraine | Present | Introduced | |||||
United Kingdom | Absent, Formerly present | Recorded from the wild by 1908. Does not appear to have been recorded recently | |||||
North America |
|||||||
Cuba | Present | Introduced | Invasive | ||||
Jamaica | Present | Introduced | 1954 | ||||
United States | Present | Introduced | |||||
-Arizona | Present | Introduced | Primarily in Cochise and Pima counties | ||||
-Delaware | Present | Introduced | |||||
-Maine | Absent, Formerly present | ||||||
-Maryland | Present | Introduced | 1953 | ||||
-Massachusetts | Present | Introduced | 1882 | Boston flats. As a fugitive plant | |||
-New Jersey | Present | Introduced | |||||
-New Mexico | Absent, Formerly present | ||||||
-New York | Absent, Formerly present | ||||||
-North Carolina | Absent, Invalid presence record(s) | Confused with T. berteronianus | |||||
-Pennsylvania | Absent, Formerly present | ||||||
-Texas | Absent, Formerly present | ||||||
-Virginia | Present | Introduced | |||||
Oceania |
|||||||
Australia | Absent, Invalid presence record(s) | A misidentification of T. australiensis | |||||
South America |
|||||||
Argentina | Present | Introduced | Occasional | ||||
Bolivia | Present | Introduced | |||||
Peru | Present | Introduced |
History of Introduction and Spread
Top of pageTragus racemosus is reported as present in Belgium prior to 1850, as a common wool alien from 1887 to 1947. In recent times, it has been found in disturbed sites near railways (Alien plants of Belgium, 2020) and reported to be spreading rapidly in southern Europe, with stable populations found in northern France. Diaspores of T. racemosus were introduced into the Czech Republic with wool into local woollen mills, and spread to the surrounding areas via wool waste (Kaplan et al., 2015). Although T. racemosus is reported as native to Africa, it is listed in Libya as both native and introduced (El-Gadi et al., 1987).
In the USA, T. racemosus has been reported since the late 1800s in the northeast as a ballast waif and as growing in dumps of wool carding factories (Knowlton et al., 1913; Pohl, 1947; Native Plant Trust, 2020). It has spread to the western USA from Arizona to Texas and in the eastern USA from Maine to North Carolina, but without details given (Reed, 1954). According to SEINet (2020), the species was collected in Maine, Pennsylvania, New York and North Carolina in the late 19th century, but is no longer present in those states. It is considered as an occasional anthropogenic weed in eastern USA (Native Plant Trust, 2020). From its distribution in the western USA, some of the reports for New Mexico and Texas appear to be misidentifications of T. berteronianus (SEINet, 2020). In the New World, it is also known to occur in South America since the mid-1800s and in the Caribbean in the 1950s (Proctor, 1982; Missouri Botanical Garden, 2020).
Introductions
Top of pageIntroduced to | Introduced from | Year | Reason | Introduced by | Established in wild through | References | Notes | |
---|---|---|---|---|---|---|---|---|
Natural reproduction | Continuous restocking | |||||||
Libya | 1984 | Yes | No | El-Gadi et al. (1987) | ||||
USA | 1879 | Hitchhiker (pathway cause) | Yes | No | Pohl (1947) | |||
Jamaica | 1954 | Yes | No | Proctor (1982) | ||||
Bolivia | 1848-1861 | No | No | Missouri Botanical Garden (2020) | ||||
Belgium | Prior to 1850 | Hitchhiker (pathway cause) | Yes | No | Alien plants of Belgium (2020) | |||
Germany | 1900 | No | No | Missouri Botanical Garden (2020) | Seeds? |
Risk of Introduction
Top of pageThere is not enough information on the biology of the species and its environmental requirements to fully assess the risk of introduction of T. racemosus. This species is not actively used for forage due to its low stature, low yield and ephemeral nature (PROTA, 2020). It is also unlikely to be introduced to any country as an ornamental, or for any economic or social benefits. At present, T. racemosus has a medium risk of introduction due to the potential for accidental introductions through wool products (Alien plants of Belgium, 2020; PROTA, 2020; SEINet, 2020).
Habitat
Top of pageTragus racemosus is an annual prostrate grass reported from wooded grasslands, dwarf shrublands, river margins. roadsides, railroads, waste and disturbed areas, savannahs, sand steppes, coastal sandy areas away from the littoral zone, ruderal areas and dry creek beds, from near sea level to 1800 m elevation (Weare and Yalala, 1971; Gibbs Russell and Biegel, 1973; Lawesson, 1990; Palmer, 1991; Jabbour et al., 1996; Moore et al., 2016; García-Lahera and Morgado, 2018; E-Flora of South Africa, 2020; PROTA, 2020).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Disturbed areas | Present, no further details | Natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Natural |
Terrestrial | Managed | Urban / peri-urban areas | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Rocky areas / lava flows | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Scrub / shrublands | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Deserts | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Arid regions | Present, no further details | Natural |
Littoral | Coastal areas | Present, no further details | Natural |
Hosts/Species Affected
Top of pageCatasús Guerra (2015) reports T. racemosus as not affecting crops in Cuba.
Biology and Ecology
Top of pageGenetics
Germplasm collections of T. racemosus are available at USDA facilities and at the Millennium Seed Bank (Kew Royal Botanic Gardens, 2020; USDA-ARS, 2020). The chromosome number reported for the species is 2n = 40 (PROTA, 2020).
Reproductive Biology
Tragus racemosus is an ephemeral grass that reproduces by seed (PROTA, 2020). A 75% germination rate and 100% seed viability are reported for the species at the Millennium Seed Bank (Kew Royal Botanic Gardens, 2020). T. racemosus is also reported as having a low seed yield (PROTA, 2020).
Physiology and Phenology
Tragus racemosus is a small annual prostrate C4 grass (Kalapos, 1991). This species has a short life cycle, with seeds germinating in June, and plants flowering and fruiting from July to September and dying in the first frosts (Jabbour et al., 1996; Catasús Guerra, 2015; E-Flora of South Africa, 2020). Seeds are reported to have a short-lived persistence in soil (Johannsmeier, 2009).
Longevity
Tragus racemosus is an annual prostrate grass with a short growth cycle (PROTA, 2020).
Activity Patterns
Tragus racemosus is reported as being an early successional species (Kalapos et al., 1996).
Environmental Requirements
There is very little information available on the environmental requirements of T. racemosus. The species is reported as growing in all soil types, especially dry sandy soils with low nutrients and low humus (Obeid and Mahmoud, 1969; Leistner and Werger, 1973; Jabbour et al., 1996; Kalapos et al., 1996; E-Flora of South Africa, 2020; PROTA, 2020). It has high temperature requirements and will not survive frosts (Jabbour et al., 1996). T. racemosus is reported as growing in arid hot deserts, semi-deserts and semiarid continental climates (Kalapos et al., 1996; Shabana et al., 2018).
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
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 | Preferred | > 430mm and < 860mm annual precipitation | |
BW - Desert climate | Preferred | < 430mm annual precipitation | |
Cs - Warm temperate climate with dry summer | Preferred | Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers | |
Cf - Warm temperate climate, wet all year | Preferred | Warm average temp. > 10°C, Cold average temp. > 0°C, wet all year |
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
50 | 37 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Mean annual rainfall | 125 | 975 | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
Soil texture
- heavy
- light
- medium
Special soil tolerances
- infertile
Notes on Natural Enemies
Top of pageUstilago tragana and Striga densiflora have been reported on T. racemosus (Srinivasan, 1947; Ramakrishnan and Srinivasan, 1950).
Means of Movement and Dispersal
Top of pageNatural Dispersal
Although the seeds of T. racemosus have hooked spines adapted for animal dispersal, Catasús Guerra (2015) also reports the species as being wind dispersed.
Vector Transmission (Biotic)
Tragus racemosus seeds have hooked spines adapted for animal dispersal (Freund et al., 2014; Catasús Guerra, 2015; Shabana et al., 2018; PROTA, 2020).
Accidental Introduction
Tragus racemosus has been accidentally introduced to various countries as a contaminant of wool products and waste (Parlin, 1904; Alien plants of Belgium, 2020; SEINet, 2020). It is also reported as introduced in ship ballast (Angelo and Boufford, 1998; Native Plant Trust, 2020).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Disturbance | Found growing in open disturbed areas | Yes | PROTA (2020) | |
Forage | Occasionally foraged by animals | Yes | PROTA (2020) | |
Harvesting fur, wool or hair | Accidentally introduced to various countries as a contaminant of wool products | Yes | Yes | Alien plants of Belgium (2020); SEINet (2020) |
Hitchhiker | Accidentally introduced to various countries as a contaminant of wool products | Yes | Yes | Alien plants of Belgium (2020); SEINet (2020) |
Off-site preservation | Germplasm collections are available at USDA facilities and at the Millennium Seed Bank | Yes | Yes | Kew Royal Botanic Gardens (2020); USDA-ARS (2020) |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Clothing, footwear and possessions | No information available but possible as the seeds have hooked spines that could attach easily to clothes and footwear | Yes | PROTA (2020) | |
Debris and waste associated with human activities | Found growing at dump sites near wool factories and ballast dump sites | Yes | Yes | Native Plant Trust (2020) |
Germplasm | Germplasm collections are available at USDA facilities and at the Millennium Seed Bank | Yes | Yes | Kew Royal Botanic Gardens (2020); USDA-ARS (2020) |
Ship ballast water and sediment | Found growing at ballast dump sites | Yes | Yes | Native Plant Trust (2020) |
Soil, sand and gravel | Possible. No information available but as it is an ephemeral species, the seeds that germinate in the summer are at least from the previous season | Yes | ||
Wind | Although adapted for animal dispersal, there is a report of the species being wind dispersed | Yes | Catasús Guerra (2015) |
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Negative |
Environment (generally) | Positive and negative |
Economic Impact
Top of pageTragus racemosus is reported as causing severe 'seedy wool' problems on sheep farms in Africa and as a potential seed contaminant, but without further details given (PROTA, 2020). In France, in the Haute Provence region, this species is regarded as a weed, and reported as aggressively carpeting lavender fields during summer after they have been cleared of weeds in early summer (Bogaard et al., 2020). Although predicted to have low competitive ability and not an important weed in the organic arable fields of Provence, T. racemosus is considered an effective, and increasing, summer-annual colonist of fallow sites where existing annual vegetation has been removed in spring or early summer (Bogaard et al., 2020).
Impact: Biodiversity
Top of pageThere are no details about the impact of T. racemosus on other species; according to Catasús Guerra (2015) it can outcompete other species in dry and nutrient-poor habitats.
Risk and Impact Factors
Top of page- Proved invasive outside its native range
- Has a broad native range
- Pioneering in disturbed areas
- Fast growing
- Has propagules that can remain viable for more than one year
- Damages animal/plant products
- Competition - monopolizing resources
- Rapid growth
- Produces spines, thorns or burrs
- Highly likely to be transported internationally accidentally
Uses
Top of pageSocial Benefit
Tragus racemosus is occasionally grazed by sheep, cattle and camels (Ali et al., 2009; PROTA, 2020); due to its short cycle and low seed yield, it is not actively used for forage. The seeds are listed as used in porridges but without further details (PROTA, 2020).
Environmental Services
The presence of T. racemosus is generally indicative of a denuded field in an early successional stage (PROTA, 2020). It may be used as a cover crop to prevent soil erosion (Bogaard et al., 2020).
Uses List
Top of pageAnimal feed, fodder, forage
- Fodder/animal feed
Environmental
- Erosion control or dune stabilization
Human food and beverage
- Seeds
Similarities to Other Species/Conditions
Top of pageAccording to Anton (1981), nearly all the species of Tragus at one time or another have been confused with T. racemosus although the species is well delimited by the 7-nerved second glume and the clustered arrangement of the spikelets. Sometimes only (3-)5 nerves in the second glume are strongly developed, producing spines that are almost contiguous to one another, with 2-4 intermedial nerves being less evident and diminishing towards the apex.
Tragus racemosus is distinguished from T. berteronianus by its looser inflorescence, especially towards the bottom, with larger spikelets (3-4 mm). T. berteronianus has a tight, cylindrical inflorescence with smaller (2-3 mm) spikelets (SEINet, 2020).
References
Top of pageAnton, A. M., 1981. The genus Tragus (Gramineae). Kew Bulletin, 36(1), 55-61. doi: 10.2307/4119004
Bogaard, A., Hodgson, J., Whitlam, J., Aumeeruddy-Thomas, Y., Delauge, J., Huc, S., Vanderpert, H., Saatkamp, A., Pavon, D., 2020. Field weeds of organic cereals in the Sault region, Haute Provence: their identification and ecology, Oxford, UK: University of Oxford.98 pp.
Catasús Guerra, L, 2015. Considerations about the invasive grasses in Cuba. (Consideraciones sobre las gramíneas invasoras en Cuba). In: Revista del Jardín Botánico Nacional , 36. 115-150.
E-Flora of South Africa, 2020. E-Flora of South Africa. Pretoria, South Africa: South African National Biodiversity Institute (SANBI).https://www.sanbi.org/biodiversity/foundations/biosystematics-collections/e-flora/
El-Gadi, A , Sherif, AS , El-Taife, Labani, RM, 1987. New plant records for Libya - II. Willdenowia, 16(2), 409-413.
Fasseaux, W, 1949. (Les Tragus adventices en Belgique). Bulletin de la Société Royale de Botanique de Belgique/Bulletin van de Koninklijke Belgische Botanische Vereniging, 82(1), 67-70.
Gibbs Russell, G. E., Biegel, H. M., 1973. Report on botanical collecting trips to Maun and the Northern Okavango Delta. Botswana Notes and Records, 5, 154-169 .
Jabbour, A. A., Kalapos, T. , Hahn, I., Kovács-Láng, E., 1996. Field water relations of three sand steppe grass species. Abstracta Botanica, 20(1), 37-46 .
Johannsmeier, A. E., 2009. Seedbank strategies in a Kalahari ecosystem in relation to grazing and habitats. Master of Science thesis. Pretoria, South Africa: Université de Pretoria. viii + 118 pp. https://repository.up.ac.za/handle/2263/28892
Kalapos, T., 1991. C3 and C4 grasses of Hungary: environmental requirements, phenology and role in the vegetation. Abstracta Botanica, 15(2), 83-88.
Knowlton, CH, Blake, SF, Cushman, JA, Deane, W, 1913. Reports on the flora of the Boston district, - XVI. Rhodora, 15(171), 54-59.
Lawesson, JE, 1990. Sahelian woody vegetation in Sénégal. Vegetatio, 86(2), 161-174.
Leistner, O. A., Werger, M. J. A. , 1973. Southern Kalahari phytosociology. Vegetatio, 28(5), 353-399.
Moore, G., Brecht, R., Schweitzer, D., 2016. Additions and corrections to the checklist of vascular plants of Cumberland County, New Jersey. Bartonia, 68, 1-59.
Native Plant Trust, 2020. Native Plant Trust – Go Botany. Framingham, Massachusetts, USA: Native Plant Trust.https://gobotany.nativeplanttrust.org/
Obeid, M., Mahmoud, A., 1969. The vegetation of Khartoum Province. Sudan Notes and Records, 50, 134-159.
Palmer, A. R., 1991. Vegetation/environment relationships in the central area of the Cape midlands, South Africa. Coenoses, 6, 29-38.
Parlin, JC, 1904. Some casual elements in the flora of western Maine. Rhodora, 6(65), 81-84.
Pohl, RW, 1947. A taxonomic study on the grasses of Pennsylvania. The American Midland Naturalist, 38(3), 513-604.
Proctor, GR, 1982. More Additions to the Flora of Jamaica. In: Journal of the Arnold Arboretum , 63(3) . 199-316.
Ramakrishnan, T. S. , Srinivasan, K. V. , 1950. Two grass smuts. Current Science, 19(7), 216-217 pp.
Reed, CF, 1954. New or additional records of grasses in Maryland and Delaware. In: Rhodora , 56(668) . 178-181.
SEINet, 2020. Southwest Environmental Information Network SEINet - Arizona - New Mexico Chapter. USA: Southwest Environmental Information Network (SEINet).https://swbiodiversity.org/seinet/index.php
Srinivasan, A. R., 1947. Some new hosts for Striga. Current Science, 16, 320-1.
Sulekic, A, Zapater, MA, 2001. (El género Tragus (Poaceae, Zoisieae) en la Argentina). Darwiniana, 39(3-4), 247-254.
Weare, P. R., Yalala, A., 1971. Provisional vegetation map of Botswana. Botswana Notes and Records, 3, 131-147.
Distribution References
Catasús Guerra L, 2015. Considerations about the invasive grasses in Cuba. (Consideraciones sobre las gramíneas invasoras en Cuba). In: Revista del Jardín Botánico Nacional, 36 115-150.
El-Gadi A , Sherif AS , El-Taife, Labani RM, 1987. New plant records for Libya - II. Willdenowia. 16 (2), 409-413.
Fasseaux W, 1949. (Les Tragus adventices en Belgique). Bulletin de la Société Royale de Botanique de Belgique/Bulletin van de Koninklijke Belgische Botanische Vereniging. 82 (1), 67-70.
Knowlton CH, Blake SF, Cushman JA, Deane W, 1913. Reports on the flora of the Boston district, - XVI. Rhodora. 15 (171), 54-59.
Lawesson JE, 1990. Sahelian woody vegetation in Sénégal. Vegetatio. 86 (2), 161-174.
Lazkov G, Sennikov A, 2014. New records in vascular plants alien to Kyrgyzstan. Biodiversity Data Journal. e1018.
Parlin JC, 1904. Some casual elements in the flora of western Maine. Rhodora. 6 (65), 81-84.
Pohl RW, 1947. A taxonomic study on the grasses of Pennsylvania. The American Midland Naturalist. 38 (3), 513-604.
Proctor GR, 1982. More Additions to the Flora of Jamaica. In: Journal of the Arnold Arboretum, 63 (3) 199-316.
Rat M, Simonović P, Glavendekić M, Paunovic M, Stojanović V, Karaman M, Radišić D, Anačkov G, 2016. Country reports. Overview of the invasive alien species in Serbia. In: ESENIAS Scientific Reports 1. State of the art of alien species in south-eastern Europe. [ed. by Rat M, Trichkova T, Scalera R, Tomov R, Uludag A]. Novi Sad, Serbia: University of Novi Sad, IBER-BAS, ESENIAS. 91-114.
Reed CF, 1954. New or additional records of grasses in Maryland and Delaware. In: Rhodora, 56 (668) 178-181.
SEINet, 2020. Southwest Environmental Information Network SEINet - Arizona - New Mexico Chapter., USA: Southwest Environmental Information Network (SEINet). https://swbiodiversity.org/seinet/index.php
Sulekic A, Zapater MA, 2001. (El género Tragus (Poaceae, Zoisieae) en la Argentina). Darwiniana. 39 (3-4), 247-254.
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Links to Websites
Top of pageWebsite | URL | Comment |
---|---|---|
E-Flora of South Africa | https://www.sanbi.org/biodiversity/foundations/biosystematics-collections/e-flora/ | |
Euro+Med PlantBase | http://ww2.bgbm.org/EuroPlusMed | |
Flora of Pakistan | http://www.tropicos.org/Project/Pakistan | |
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. |
Global register of Introduced and Invasive species (GRIIS) | http://griis.org/ | Data source for updated system data added to species habitat list. |
India Biodiversity Portal | http://indiabiodiversity.org/species/list | |
Millennium Seed Bank - Seed List | http://apps.kew.org/seedlist/SeedlistServlet | |
Native Plant Trust | https://gobotany.nativeplanttrust.org | |
PROTA4U web database | https://www.prota4u.org/database/ | |
SEINet data portal | https://swbiodiversity.org/seinet/index.php |
Contributors
Top of page30/04/2020 Original text by:
Jeanine Vélez Gavilán, University of Puerto Rico at Mayagüez, Puerto Rico
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