Sesbania punicea (red sesbania)
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
- Hosts/Species Affected
- Biology and Ecology
- Latitude/Altitude Ranges
- Air Temperature
- Rainfall
- Rainfall Regime
- Soil Tolerances
- Natural enemies
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Vectors
- Plant Trade
- Impact Summary
- Impact
- Environmental Impact
- Impact: Biodiversity
- Social Impact
- Risk and Impact Factors
- Uses
- Uses List
- Similarities to Other Species/Conditions
- Prevention and Control
- References
- Links to Websites
- Distribution Maps
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Top of pagePreferred Scientific Name
- Sesbania punicea (Cav.) Benth.
Preferred Common Name
- red sesbania
Other Scientific Names
- Daubentonia punicea (Cav.) DC.
- Daubentonia tripetii Poit.
- Emerus puniceus (Cav.) Kuntze
- Ormocarpum elegans G. Don
- Piscidia ovalifolia D.A. Larranaga
- Piscidia ovalis D.A. Larranaga
- Piscidia punicea Cav.
- Sesbania tripetii Hubb.
International Common Names
- English: black acacia; Brazil rattlebox; Brazilian glory pea; coffee of the coast; coffee weed; false poinciana; purple sesbane; purple sesbania; rattle box; rattlebush; red seine bean; tame acacia
- Spanish: acacia de bañado; acacia mansa; rama negra
Local Common Names
- USA: Chinese wisteria; rattle pod
EPPO code
- SEBPU (Sesbania punicea)
Summary of Invasiveness
Top of pageTaxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Fabales
- Family: Fabaceae
- Subfamily: Faboideae
- Genus: Sesbania
- Species: Sesbania punicea
Notes on Taxonomy and Nomenclature
Top of pageDescription
Top of pageThe plants are generally more shrubby in the native range, where pod and viable seed production is moderated by phytophagous natural enemies (Erb, 1980). In South Africa, historically, S. punicea grew into large trees up to 6 m tall, with basal stem diameters reaching 180 mm (occasionally somewhat more) and producing copious numbers of pods and viable seeds each season (Hoffmann and Moran, 1988).
Distribution
Top of pageDistribution 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: 12 May 2022Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Congo, Democratic Republic of the | Present | Introduced | |||||
Eswatini | Present | Introduced | Invasive | ||||
Lesotho | Present | Introduced | |||||
Malawi | Present | Introduced | |||||
Mauritius | Present | Introduced | Invasive | First reported: 1980s | |||
Namibia | Present | Introduced | |||||
South Africa | Present, Widespread | Introduced | 1858 | Invasive | |||
Zambia | Present | Introduced | |||||
Zimbabwe | Present | Introduced | 1978 | ||||
Europe |
|||||||
France | Present, Few occurrences | ||||||
-Corsica | Present | Introduced | 1990 | ||||
Italy | Present | ||||||
-Sardinia | Present | ||||||
-Sicily | Present | ||||||
Portugal | Present | Introduced | 2003 | ||||
North America |
|||||||
United States | Present | ||||||
-Alabama | Present | Introduced | Invasive | ||||
-Arkansas | Present | Introduced | Invasive | ||||
-California | Present, Widespread | Introduced | Invasive | ||||
-Florida | Present, Widespread | Introduced | Invasive | ||||
-Georgia | Present, Widespread | Introduced | Invasive | ||||
-Louisiana | Present | Introduced | Invasive | ||||
-Mississippi | Present | Introduced | Invasive | ||||
-North Carolina | Present | Introduced | Invasive | ||||
-South Carolina | Present | Introduced | Invasive | ||||
-Texas | Present | Introduced | Invasive | ||||
Oceania |
|||||||
Australia | Present | Introduced | 1888 | ||||
South America |
|||||||
Argentina | Present | Native | |||||
Brazil | Present | ||||||
-Rio Grande do Sul | Present | Native | |||||
-Sao Paulo | Present | ||||||
Paraguay | Present | ||||||
Uruguay | Present | Native | |||||
Venezuela | Present |
History of Introduction and Spread
Top of pageIn the USA, S. punicea has raised concerns in recent years as an invasive species (Cuda et al., 1996).
Unpublished records show that S. punicea has recently become naturalised and is spreading on the Indian Ocean island of Mauritius. No doubt additional records will arise about invasions of this species in other countries because of its popularity as a garden ornamental and the ease with which it spreads from cultivation.
Risk of Introduction
Top of pageHabitat
Top of pageIn its natural range in South America, S. punicea is most frequently encountered as isolated plants or small clumps of plants on river banks, drainage ditches and depressions, where moisture accumulates (Erb, 1980). In the southwestern regions of South Africa, which experience a Mediterranean climate (i.e. dry summers and wet winters), S. punicea is largely confined to river banks and wetlands. In the summer rainfall regions it is predominantly associated with moist habitats but it also occurs in dryland habitats (especially grasslands and disturbed areas), presumably establishing itself in these areas during periods of unusually prolonged and above average rainfall (Hoffmann and Moran, 1988). In the USA, S. punicea is "a weed of humid pastures and natural areas" (Cuda et al., 1996).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | |
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | |
Terrestrial | Managed | Managed grasslands (grazing systems) | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Disturbed areas | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Urban / peri-urban areas | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Wetlands | Present, no further details | Harmful (pest or invasive) |
Hosts/Species Affected
Top of pageBiology and Ecology
Top of pageIn its natural range S. punicea breeds true and there are no closely related species to give it the opportunity to hybridize. In North America it reportedly hybridizes readily with S. drummondii, a close congeneric from that region (Cuda et al., 1996). As with 15 of the 26 species of Sesbania where the ploidy level is known (Gill and Husaini, 1985; Evans and Rotar, 1987), S. punicea is diploid. It has a chromosome number 2n=12 (Evans and Rotar, 1987).
Physiology and Phenology
Sesbania punicea is a deciduous shrub or small tree up to 5 m high with many slender, thornless branches. The first leaf is simple, with subsequent leaves being pinnate. The plants are deciduous but some leaves are retained in regions with mild winters. Maximum growth of shoots, leaves and flowers occurs in spring and early summer.
Reproductive Biology
Seeds of S. punicea are hard-coated but they have no inherent dormancy and germinate as soon as imbibition occurs when moisture is available (Graaff and van Staden, 1984). As a result, there is no substantial accumulation of seeds in the soil, and seedlings sprout in large numbers soon after seed fall. Some seedlings fail to emerge from seeds buried at depths >70 mm and no seeds produced seedlings from below 120 mm (Graaff and van Staden, 1984). Reproduction is entirely sexual although rootstocks can be transplanted manually with some success.
The flowers are pollinated by generalist insect pollinators (usually bees) (Evans and Rotar, 1987) and give rise to clusters of three or four (rarely ten) seed pods on the original stalks of the inflorescences. The characteristically winged pods ripen in mid to late summer so that by autumn, in the absence of natural enemies, the branches of the trees appear mottled brown due to the mantle of pods. Some pods dehisce while still hanging on the trees and expel their seeds but most of the pods dislodge from the plants while still intact and containing seeds. Long-range dispersal of seeds occurs through the buoyant water-borne pods being carried downstream and seeds are released as the pods become weathered and disintegrate.
Environmental Requirements
S. punicea has high moisture requirements, especially for seed germination and seedling survival, so the plants only become naturalised in areas where soils remain moist for relatively long periods. In regions with predominantly summer rainfall, S. punicea plants are sometimes found in open areas away from water but most occur in the vicinity of rivers and streams (Henderson and Wells, 1986). In dry regions, and in winter-rainfall regions, S. punicea plants are almost always confined to banks and islands of perennial rivers (Brown and Gubb, 1986), streams, depressions, roadsides or other mesic sites. Periodic high-rainfall seasons allow S. punicea to form thickets away from water courses in low-rainfall areas, but the extent to which this happens is limited.
The plants grow over a wide range of altitudes from sea level upwards and are tolerant of periodic sub-zero temperature conditions. Seeds fail to germinate when incubated at 40°C (Graaff and van Staden, 1984).
Associations
In common with most leguminous plants, S. punicea has nitrogen-fixing bacteria, Rhizobium sp., associated with its roots (Evans and Rotar, 1987).
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
0 | 0 | 0 | 0 |
Air Temperature
Top of pageParameter | Lower limit | Upper limit |
---|---|---|
Absolute minimum temperature (ºC) | -10 | |
Mean annual temperature (ºC) | 8 | 30 |
Mean maximum temperature of hottest month (ºC) | 27 | 33 |
Mean minimum temperature of coldest month (ºC) | -2 | 12 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Dry season duration | 6 | number of consecutive months with <40 mm rainfall | |
Mean annual rainfall | 414 | 1228 | mm; lower/upper limits |
Natural enemies
Top of pageNatural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Apion decipiens | Herbivore | Plants|Leaves; Plants|Seeds | ||||
Astraptes fulgerator | Herbivore | Plants|Leaves | ||||
Diplogrammus quadrivittatus | Herbivore | |||||
Eudiagogus episcopalis | Herbivore | Plants|Leaves; Plants|Roots | ||||
Neodiplogrammus quadrivittatus | Herbivore | Plants|Leaves; Plants|Roots; Plants|Stems | South Africa | |||
Rhyssomatus marginatus | Herbivore | Plants|Leaves; Plants|Seeds | South Africa | |||
Trichapion lativentre | Herbivore | Plants|Inflorescence; Plants|Leaves | South Africa | |||
Urodera fallax | Herbivore | Plants|Leaves |
Notes on Natural Enemies
Top of pageMeans of Movement and Dispersal
Top of pageSesbania punicea relies almost exclusively on flowing water for dispersal. The seeds are retained in the pods which fall from the trees and float downstream, dispersing the seeds which sink as the pods disintegrate with time.
Vector Transmission (Biotic)
The propagules have no specific adaptations for biotic dispersal. The seeds are toxic and not attractive to birds or animals.
Agricultural Practices
There is no evidence that S. punicea is dispersed to any great extent by agricultural practices. S. punicea seldom encroaches on crops so there is no source of seeds to contaminate and be transported with harvest. Irrigation channels may serve to some extent as conduits for moving seeds from river systems to adjacent areas.
Accidental Introduction
Accidental introductions of seeds between sites at a national level occur through deliberate movement of soils, especially collection of builder's sand from river beds, and, inadvertently, on soil adhering to vehicles and implements. Accidental introductions internationally are probably not common but could happen when related Sesbania species are promoted for useful purposes including nitrogen fixation, fodder, green manure and gum production (Evans and Rotar, 1987).
Intentional Introduction
The abundance of showy flowers, and pleasing size and shape, have made S. punicea a very popular ornamental garden species which has been moved extensively within and between countries by horticulturalists. Seeds are readily available from distributors in many parts of the world and this process will undoubtedly foster invasions of S. punicea in regions where the plants are not yet naturalised.
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Clothing, footwear and possessions | Yes | |||
Land vehicles | Yes | |||
Yes | ||||
Soil, sand and gravel | Yes |
Plant Trade
Top of pagePlant parts liable to carry the pest in trade/transport | Pest stages | Borne internally | Borne externally | Visibility of pest or symptoms |
---|---|---|---|---|
Fruits (inc. pods) | weeds/seeds | |||
True seeds (inc. grain) |
Impact Summary
Top of pageCategory | Impact |
---|---|
Animal/plant collections | None |
Animal/plant products | None |
Biodiversity (generally) | Negative |
Crop production | Negative |
Environment (generally) | Negative |
Fisheries / aquaculture | None |
Forestry production | None |
Human health | None |
Livestock production | Negative |
Native fauna | Negative |
Native flora | Negative |
Rare/protected species | Negative |
Tourism | Negative |
Trade/international relations | None |
Transport/travel | Negative |
Impact
Top of pageEnvironmental Impact
Top of pageImpact: Biodiversity
Top of pageSocial Impact
Top of pageRisk and Impact Factors
Top of page- Proved invasive outside its native range
- Highly adaptable to different environments
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
- Highly mobile locally
- Has high reproductive potential
- Has propagules that can remain viable for more than one year
- Damaged ecosystem services
- Ecosystem change/ habitat alteration
- Negatively impacts agriculture
- Negatively impacts animal health
- Negatively impacts tourism
- Reduced amenity values
- Reduced native biodiversity
- Competition - monopolizing resources
- Highly likely to be transported internationally deliberately
- Difficult to identify/detect as a commodity contaminant
- Difficult/costly to control
Uses
Top of pageSimilarities to Other Species/Conditions
Top of pagePrevention 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.
Cultural ControlIn general, S. punicea is not amenable to cultural control methods. The plants occur predominantly in habitats that are moist and do not ignite easily or burn intensely enough to kill the plants. Prescribed burning can be used to regulate S. punicea in grasslands when conditions are dry, but only seedlings and small plants are killed outright. Large plants are mostly only scorched and usually re-sprout. The weed has no real agroforestry value, although the wood is used opportunistically in South Africa on a small scale for firewood. Browsing on the foliage is rare because of the toxicity of the plants (Terblanche et al., 1966).
Mechanical Control
This is the predominant manual method of control for S. punicea. Seedlings and small plants can be pulled, by hand or with implements (Pienaar, 1980). Large plants must be felled and the stumps treated with triclopyr to prevent coppicing. Mechanical control operations in well-established infestations usually disturb the soil and promote seed germination, so frequent follow-up operations are required to ensure sustained control of the weed.
Chemical Control
In South Africa, herbicides are applied as a foliar spray with either triclopyr or glyphosate, or as a cut stump treatment with triclopyr, or as soil treatment with clopyralid and tebuthiuron (Wyat, 1997). The use of herbicides as foliar sprays and soil treatment against S. punicea is not common because other control methods (mechanical and biological) are preferred.
Biological Control
A very successful biological control programme has kept S. punicea under control in many parts of South Africa since the 1980s (Hoffmann and Moran, 1991a; Hoffmann and Moran, 1999). The programme relies on three introduced agent species: Trichapion lativentre, a bud-feeding weevil which feeds on the leaflets as adults and develops within the flower buds as larvae; Rhyssomatus marginatus, a weevil whose larvae destroy the ripening seeds within the pods and whose adults feed on the leaves, flowers and meristems of the plants; and Neodiplogrammus quadrivittatus, a large stem-boring weevil whose larvae tunnel in the stems and branches causing structural damage, especially to vascular tissues, which eventually kills the plants. A root-feeding weevil, Eudiagogus episcopalis, was also considered for introduction into South Africa, but was not pursued because of difficulties with handling the beetles in quarantine and because the effectiveness of the other three species rendered it superfluous.
All three beetles act in combination to effect control (Hoffmann, 1990; Hoffmann and Moran, 1991b, 1998). The bud feeder destroys almost all (>98%) of the flowers and reduces seed production dramatically (Hoffmann, 1988; Moran and Hoffmann, 1989; Hoffmann et al., 1990; Hoffmann and Moran, 1992a). The seed feeder destroys 84% of the seeds that are produced in spite of damage caused by the bud feeder (Hoffmann and Moran, 1992b). Together these two species reduce seed production by >99.8%, rendering the plants almost sterile. The invasive potential of S. punicea is much reduced by these two weevils and populations of the weed are unable to recover as readily as happened before the introduction of the weevils. The bud feeder and seed feeder together have reduced the density of the weed in some situations (Hoffmann and Moran, 1998). The stem borer on its own is seemingly unable to bring S. punicea under biological control because recruitment from seedlings outstrips mortality due to the borer and the net loss is insufficient to cause a decline in the weed populations (Hoffmann, 1990). It is the combined action of all three weevils acting simultaneously which ensures that the reproductive capacity and survival of the weed are curtailed sufficiently to reduce its density and keep it in check.
Integrated Control
Although no deliberate integrated control programme has been mounted against S. punicea in South Africa, mechanical control operations have proved much more effective since the introduction of Trichapion lativentre and Rhyssomatus marginatus and the drastic reduction in seed production of the weed. The lack of seeds due to damage caused by these two beetles ensures that recruitment of seedlings is minimal following mechanical or chemical clearing operations. Follow-up treatments to combat the weed successfully need not be as rigorous or frequent as was necessary before these agents were introduced.
Under some circumstances mechanical control may negate the effectiveness of biological control because the insect agents are unable to persist in areas where the S. punicea is removed entirely. The weed may then re-invade such areas and flourish until the agents are re-introduced or re-colonize naturally. There are also documented examples of insecticide drift from adjacent citrus orchards detrimentally affecting the biological control agents of S. punicea (Hoffmann and Moran, 1995).
References
Top of pageBrown CJ; Gubb AA, 1986. Invasive alien organisms in the Namib desert, upper Karoo and the arid and semi-arid savannas of western southern Africa. In: The ecology and management of biological invasions in southern Africa, Macdonald IAW, Kruger FJ, Ferrar AA, eds. Cape Town, South Africa: Oxford University Press, 93-108.
EPPO, 2014. PQR database. Paris, France: European and Mediterranean Plant Protection Organization. http://www.eppo.int/DATABASES/pqr/pqr.htm
Gill LS; Husaini WH, 1985. Cyto-geographical studies of the genus Sesbania Scop. (Leguminosae) from Nigeria. Bulletin du Museum National d'Histoire Naturelle, 4e Serie 7, Section B, Adansonia, No. 3:331-336.
Graaff JL; van Staden J, 1984. The germination characteristics of two Sesbania species. South African Journal of Botany, 3: 59-62.
Henderson L, 2001. Alien Weeds and Invasive Plants. Plant Protection Research Institute Handbook No. 12. Cape Town, South Africa: Paarl Printers.
Henderson L; Wells MJ, 1986. Alien plant invasions in grassland and savanna biomes. In: Macdonald IAW, Kruger FJ, Ferrar AA, eds. The ecology and management of biological invasions in southern Africa. Cape Town, South Africa: Oxford University Press, 109-117.
Lock JM, 1989. Legumes of Africa, a check list. Kew, UK: Royal Botanic Gardens, 619 pp.
Macdonald IAW; Richardson DM, 1986. Alien species in terrestrial ecosystems of the fynbos biome. In: Macdonald IAW, Kruger FJ, Ferrar AA, eds. The ecology and management of biological invasions in southern Africa. Cape Town, South Africa: Oxford University Press, 77-91.
McGibbon J, 1858. Catalogue of problem plants in the botanic garden, Cape Town, Cape of Good Hope. Cape Town, South Africa: Solomon.
Pienaar KV, 1977. Sesbania punicea (Cav.) Benth. the handsome plant terrorist. Veld and Flora, 63: 17-18.
Pienaar KV, 1980. Sesbania. In: Stirton CH ed. Plant invaders, beautiful but dangerous. Department of Nature and Environmental Conservation of the Cape Provincial Administration, Cape Town, 2nd edition, 136-139.
Polhill RM, 1990. Legumineuses. In: Bosser J, Cadet TH, Gueho J, Marais W, eds, Flore des Mascareignes- La Reunion, Maurice, Rodrigues, 235 pp.
Terblanche M; de Klerk WA; Smit JD; Adelaar TF, 1966. A toxicological study of the plant Sesbania punicea Benth. Journal of the South African Veterinary Medical Association, 37: 109-111.
USDA; NRCS, 2002. The PLANTS Database, Version 3.5. National Plant Data Center, Baton Rouge, USA. http://plants.usda.gov.
Wells MJ; Balsinhas AA; Joffe H; Engelbrecht VM; Harding G; Stirton CH, 1986. A catalogue of problem plants in South Africa. Memoirs of the botanical survey of South Africa No 53. Pretoria, South Africa: Botanical Research Institute.
Wells MJ; Poynton RJ; Balsinhas AA; Musil KJ; Joffe H; van Hoepen E; Abbott SK, 1986. The history of introduction of invasive alien plants to southern Africa. In: Macdonald IAW, Kruger FJ, Ferrar AA, eds. The ecology and management of biological invasions in southern Africa. Cape Town, South Africa: Oxford University Press, 21-35.
Wyat J, 1997. Alien plant control guide. Rennies Wetlands Project, Part. 6, http//:psybergate.com/wetfix/WetlandFix/WetlandFix6/wfPart6.htm.
Distribution References
CABI, Undated. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Lock JM, 1989. Legumes of Africa, a check list., Kew, UK: Royal Botanic Gardens. 619 pp.
Wells MJ, Poynton RJ, Balsinhas AA, Musil KJ, Joffe H, van Hoepen E, Abbott SK, 1986. The history of introduction of invasive alien plants to southern Africa. In: The ecology and management of biological invasions in southern Africa, [ed. by Macdonald IAW, Kruger FJ, Ferrar AA]. Cape Town, South Africa: Oxford University Press. 21-35.
Links to Websites
Top of pageWebsite | URL | Comment |
---|---|---|
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gateway | https://doi.org/10.5061/dryad.m93f6 | Data source for updated system data added to species habitat list. |
Global register of Introduced and Invasive species (GRIIS) | http://griis.org/ | Data source for updated system data added to species habitat list. |
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