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Invasive Species Compendium
Datasheet report for Terminalia catappa (Singapore almond)
Pictures
Picture Title Caption Copyright
Mature treeTerminalia catappa (Singapore almond); habit. In exposed coastal situations, the stem may become crooked and/orlean. In sheltered situations the stem is more or less cylindrical and straight.
©CSIRO/AustralianTree Seed Centre
Bole Terminalia catappa (Singapore almond); base of mature coastline tree, showing bark and exposed root system©CSIRO/AustralianTree Seed Centre
Bark Terminalia catappa (Singapore almond); bark.©CSIRO/AustralianTree Seed Centre
Foliage Terminalia catappa (Singapore almond); foliage.©CSIRO/AustralianTree Seed Centre
Inflorescence Terminalia catappa (Singapore almond); inflorescence. ©A.R. Pittaway
Fruits andfoliage
Terminalia catappa (Singapore almond); foliage and maturing fruits.©CSIRO/AustralianTree Seed Centre
Identity
Preferred Scientific NameTerminalia catappa L.
Preferred Common NameSingapore almond
Other Scientific NamesBadamia commersonii Gaertn.Buceras catappa (L.) Hitchc.Juglans catappa (L.) Lour.Myrobalanus catappa (L.) KuntzePhytolacca javanica OsbeckTerminalia badamia DC.Terminalia intermedia Bertero ex Spreng.Terminalia latifolia BlancoTerminalia mauritiana BlancoTerminalia moluccana Lam.Terminalia myrobalana RothTerminalia ovatifolia NoronhaTerminalia paraensis Mart.Terminalia procera Roxb.Terminalia rubrigemmis Tul.Terminalia subcordata Humb. & Bonpl. ex Willd.
International Common NamesEnglish: beach almond; country almond; Indian almond; Malabar almond; sea almond; tropical almondSpanish: almendra; almendrillo; almendro; almendro de playaFrench: amandier de la Martinique; amandier des Indes; badamier; myrobolanChinese: lan ren shuPortuguese: amendoeira; amendoeira da India
Local Common NamesAustralia: kotambaBrazil: amendoeira-da-India; amendoeira-da-praia; castanha da praia; castanhola; chapéu-de-sol; guarda-sol; sombreiroBrunei Darussalam: telisai; terminaliaCambodia: barang; châmbak barang; kapang; pareang prangColombia: kotambaCuba: almendro de la IndiaFiji: tavali; tiviGermany: etangen baum; indischer Mandelbaum; KatappenbaumHaiti: amadier tropical; amandier des Indes; badannier; zamanne; zammandeIndia: adamaram; badam; badambo; badami; badan; bangla-badam; deshi-bandam; hindi-badam; jangli-badam; patti-badam; vathakottai natavadom; white bombweIndia/Andaman and Nicobar Islands: white Bombay; white bombwayIndonesia: ketapangIndonesia/Java: katapangIndonesia/Nusa Tenggara: ai calesse catapoKiribati: te kunikun; te ntarineLaos: hou kouang; hu kwang; huu kwaang; sômz moox dôngLesser Antilles: Barbados almond; Z’amande; zanmannMalaysia: jelawai ketapang; ketapangMalaysia/Peninsular Malaysia: lingkakMalaysia/Sabah: telisaiMyanmar: badanNetherlands: amandel boom; wilde amandelPapua New Guinea: jara almond; reddish-brown Terminalia; talisPeru: castanaPhilippines: dalinsi; kalumpit; logo; talisaiSamoa: talieSolomon Islands: saoriSri Lanka: kottambaThailand: dat mue; hukwang; khon; taa-pangTonga: telieTuvalu: talieUSA/Hawaii: false kamani; haole; kamani-haoleVanuatu: natapoaVietnam: b[af]ng; b[af]ng nh[os]c; bang bien; bang nu'o'c; mo c[uws]a
EPPO codeTEMCA (Terminalia catappa)
Trade nameAndaman badamIndian almond
Summary of Invasiveness
T. catappa is a perennial tree species that has been extensively introduced into littoral habitats, coastal forests, gardens and parks to be used as an ornamental, shade tree, and sand-dune stabilizer (Orwa et al., 2009; ISSG, 2017). This species has become of the most common trees in littoral habitats and beaches across tropical and subtropical regions of America,India, southeastern Asia, and the Pacific Ocean, due in part to human-mediated introductions, the adaptation of its fruits to be dispersed over long-distances by sea currents and itstolerance to salt-spray, coastal-winds and drought conditions (Thomson and Evans, 2006; Brown and Cooprider, 2013). T. catappa is a prolific seed producer and fruits may remainviable for a long time, even after floating in salt water for considerable time periods.
This species naturalizes readily in littoral habitats and has been listed as invasive in the United States (Florida and Hawaii), Brazil, the Bahamas, Cuba, Dominican Republic, Trinidadand Tobago, Puerto Rico and Virgin Islands where it is displacing native vegetation and altering coastal dynamics (Smith, 2010; Oviedo Prieto et al., 2012; Mir, 2012; Rojas-Sandovaland Acevedo-Rodríguez, 2015; FLEPPC, 2017; I3N-Brazil, 2017; ISSG, 2017).
Taxonomic Tree
Domain: Eukaryota Kingdom: Plantae Phylum: Spermatophyta Subphylum: Angiospermae Class: Dicotyledonae Order: Myrtales Family: Combretaceae Genus: Terminalia Species: Terminalia catappa
Notes on Taxonomy and Nomenclature
Combretaceae is a family of flowering plants comprising 14 genera and about 500 species distributed largely across tropical and subtropical regions of the world. The genus Terminaliaincludes 190 species some of them with economic importance as ornamentals and timber yielding plants (Orwa et al., 2009). The generic name is derived from the characteristicclustered spirals of leaves at the twig tips. Terminalia and other tree species within the Combretaceae often look rather pagoda-like, the branches are often arranged in whorls andconsisting of flattened sprays of leaf rosettes (Stevens, 2012). Key references to the genus include Exell (1954), Coode (1969, 1973, 1978) and Smith (1971, 1985).
Terminalia catappa is the type species for the genus and the specific epithet 'catappa' is taken from its name in Malaysia, viz. ketapang (Wheatley, 1992). Closely related species in theSouth Pacific include T. glabrata Forst. f., T. litoralis Seem. and T. samoensis Rechinger (Fosberg and Sachet, 1981). The species has a vast number of common names, but is mostwidely known as beach, Indian or sea almond.
T. procera is considered by some to be a synonym of T. catappa (see, for example, Sosef et al., 1995). However, other authors consider T. procera (which has a limited distribution inthe Andaman Islands and Myanmar) to be a separate species (Mabberley, 1997; Troup and Joshi, 1984).
Description
Trees to 20 m tall; trunk to 2 m dbh. Bark brownish black, longitudinally peeling. Branches spreading, forming tiers. Branchlets densely brownish yellow tomentose near apex, denselycovered with conspicuous leaf scars. Leaves alternate, crowded into pseudo-whorls at apices of branchlets; petiole 0.5–2 cm, stout, tomentose; leaf blade obovate to oblanceolate,narrowed in proximal half, 12–30 × 8–15 cm, both surfaces glabrous or abaxially sparsely softly hairy when young, base narrow, cordate or truncate, apex obtuse or mucronate; lateralveins in 10–12 pairs. Inflorescences axillary, simple, long, slender spikes, 15–20 cm, numerous flowered; axis shortly white tomentose. Flowers fragrant. Calyx tube distally cupular, 7–8mm, abaxially white tomentose, densely so on ovary, sparsely so on cupular part, adaxially glabrous; lobes 5. Stamens 10, exserted, 2–3 mm. Fruit not stipitate, red or blackish greenwhen ripe, ellipsoid, slightly to strongly compressed, strongly 2-ridged to narrowly 2-winged (wings to 3 mm wide), 3–5.5 × 2–3.5 cm, glabrous; pericarp woody, rigid (Flora of ChinaEditorial Committee, 2017).
Plant Type
Broadleaved Perennial Seed propagated Tree Woody
Distribution
T. catappa is native to the Malaysian Peninsula, Southeast Asia and the Andaman Islands. This species together with Casuarina trees and coconut palms is one of the most commontrees across tropical and subtropical coastal habitats (Brown and Cooprider, 2013). It can be found naturalized across tropical and subtropical America, the West Indies, tropical andtemperate Asia, and East and West Africa (Valkenburg and Waluyo, 1991; Orwa et al., 2009; PROTA, 2017; USDA-ARS, 2017).
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 detailsmay be available for individual references in the Distribution Table Details section which can be selected by going to Generate Report.
Last updated: 17 Feb 2021
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
Africa
Botswana Present Introduced Invasive Haysom and Murphy (2003)
Burundi Present Planted CABI (Undated b)
Cabo Verde Present Planted CABI (Undated b)
Cameroon Present Introduced PROTA (2017)
Congo, DemocraticRepublic of the
Present Planted CABI (Undated b)
Congo, Republic of the Present Planted CABI (Undated b)
Gabon Present Introduced PROTA (2017)
Gambia Present Planted CABI (Undated b)
Ghana Present IntroducedPROTA (2017); Badii et al. (2015);CABI (Undated)
Kenya Present Introduced PROTA (2017); CABI (Undated)
Liberia Present Introduced PROTA (2017)
Madagascar Present IntroducedValkenburg and Waluyo (1991);CABI (Undated) Cultivated
Malawi Present Planted CABI (Undated b)
Nigeria Present Introduced PROTA (2017); CABI (Undated)
Réunion Present Planted CABI (Undated b)
Rwanda Present Planted CABI (Undated b)
Senegal Present Introduced PROTA (2017); CABI (Undated)
Seychelles Present NativeThomson and Evans (2006); CABI(Undated) Native and cultivated
Somalia Present Introduced PROTA (2017); CABI (Undated)
Sudan Present Introduced PROTA (2017)
Tanzania Present IntroducedPROTA (2017); Mwatawala et al.(2009); CABI (Undated)
-Zanzibar Island Present Introduced PROTA (2017); CABI (Undated)
Uganda Present Introduced PROTA (2017); CABI (Undated)
Zimbabwe Present Planted CABI (Undated b)
Asia
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
Afghanistan Present Introduced Orwa et al. (2009) Cultivated
Bangladesh Present Orwa et al. (2009); CABI (Undated)
Brunei Present CABI (Undated b)
Cambodia Present Native USDA-ARS (2017); CABI (Undated)
China Present IntroducedFlora of China Editorial Committee(2017); CABI (Undated)
-Guangdong Present IntroducedFlora of China Editorial Committee(2017); CABI (Undated)
-Hainan Present IntroducedFlora of China Editorial Committee(2017)
-Yunnan Present IntroducedFlora of China Editorial Committee(2017); CABI (Undated)
India Present Native
USDA-ARS (2017); Sakthivel et al.(2012); Selvaraj et al. (2017); CABI(Undated)
-Andaman and NicobarIslands
Present NativeThomson and Evans (2006); CABI(Undated) Native and cultivated
-Karnataka Present Planted Selvaraj et al. (2017)
-Kerala Present Planted CABI (Undated b)
-Maharashtra Present Planted CABI (Undated b)
-Odisha Present Planted CABI (Undated b)
-Punjab Present Planted CABI (Undated b)
-Tamil Nadu Present Planted Sakthivel et al. (2012)
-Uttar Pradesh Present Planted CABI (Undated b)
-West Bengal Present Planted CABI (Undated b)
Indonesia Present Native USDA-ARS (2017); CABI (Undated)
-Irian Jaya Present CABI (Undated b)
-Java Present CABI (Undated b)
-Maluku Islands Present Planted CABI (Undated b)
-Sulawesi Present Planted CABI (Undated b)
-Sumatra Present NativeValkenburg and Waluyo (1991);CABI (Undated)
Japan PresentCABI (Undated a); Sahashi et al.(2015)
Present based onregional distribution.
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
-Ryukyu Islands Present CABI (Undated b)
Laos Present Native Orwa et al. (2009); CABI (Undated)
Malaysia Present Native USDA-ARS (2017); CABI (Undated)
-Peninsular Malaysia Present Planted CABI (Undated b)
-Sabah Present Planted CABI (Undated b)
-Sarawak Present Planted CABI (Undated b)
Myanmar Present Native USDA-ARS (2017); CABI (Undated)
Nepal Present Planted CABI (Undated b)
Pakistan Present IntroducedValkenburg and Waluyo (1991);Tariq et al. (2007); CABI (Undated) Cultivated
Philippines Present Native USDA-ARS (2017); CABI (Undated)
Singapore Present Orwa et al. (2009); CABI (Undated)
Sri Lanka Present Orwa et al. (2009); CABI (Undated)
Taiwan Present IntroducedFlora of China Editorial Committee(2017); CABI (Undated)
Thailand Present NativeThomson and Evans (2006); CABI(Undated) Native and cultivated
Vietnam Present Native USDA-ARS (2017); CABI (Undated)
North America
Anguilla Present Introduced Naturalized Broome et al. (2007) Naturalized
Antigua and Barbuda Present Introduced Naturalized Broome et al. (2007) Naturalized
Bahamas Present Introduced Invasive Smith (2010)
Barbados Present Introduced InvasiveHaysom and Murphy (2003);Broome et al. (2007)
Belize Present Introduced Davidse et al. (2009)
Bermuda Present Introduced Orwa et al. (2009)
Bonaire, Saint Eustatiusand Saba
-Saba Present Introduced Naturalized Broome et al. (2007) Naturalized
-Sint Eustatius Present Introduced Naturalized Broome et al. (2007) Naturalized
British Virgin Islands Present Introduced InvasiveRojas-Sandoval and Acevedo-Rodríguez (2015)
Guana, Tortola, VirginGorda
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
Cayman Islands Present IntroducedAcevedo-Rodríguez and Strong(2012)
Costa Rica Present Introduced Orwa et al. (2009); CABI (Undated)
Cuba Present Introduced InvasiveOviedo Prieto et al. (2012); CABI(Undated)
Curaçao Present Planted CABI (Undated b)
Dominica Present Introduced Naturalized Broome et al. (2007) Naturalized
Dominican Republic Present Introduced Invasive Mir (2012); CABI (Undated)
El Salvador Present Introduced Orwa et al. (2009)
Grenada Present Introduced Naturalized Broome et al. (2007) Naturalized
Guadeloupe Present Introduced Naturalized Broome et al. (2007) Naturalized
Guatemala Present IntroducedDavidse et al. (2009); CABI(Undated)
Haiti Present IntroducedAcevedo-Rodríguez and Strong(2012); CABI (Undated)
Honduras Present Introduced Davidse et al. (2009)
Jamaica Present Introduced InvasiveTownsend and Newell (2006); CABI(Undated)
Martinique Present Introduced Naturalized Broome et al. (2007) Naturalized
Mexico Present IntroducedDavidse et al. (2009); CABI(Undated)
Montserrat Present Introduced Naturalized Broome et al. (2007) Naturalized
Nicaragua Present Introduced Davidse et al. (2009)
Panama Present IntroducedDavidse et al. (2009); CABI(Undated)
Puerto Rico Present Introduced Invasive Planted
Haysom and Murphy (2003); Rojas-Sandoval and Acevedo-Rodríguez(2015)
Saint Lucia Present Introduced Naturalized Broome et al. (2007) Naturalized
Saint Vincent and theGrenadines
Present Introduced Naturalized Broome et al. (2007) Naturalized
Sint Maarten Present Introduced Naturalized Broome et al. (2007) Naturalized
Trinidad and Tobago Present Introduced Invasive CABI (Undated)Original citation: Trinidadand Tobago Biodiversity(2016)
U.S. Virgin Islands Present Introduced InvasiveRojas-Sandoval and Acevedo-Rodríguez (2015)
St Croix, St Thomas, StJohn
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
United StatesPresent,Localized
Introduced USDA-ARS (2017); CABI (Undated)
-California Present Planted CABI (Undated b)
-Florida Present Introduced Invasive PlantedHaysom and Murphy (2003);FLEPPC (2017)
-Hawaii Present Introduced USDA-ARS (2017); CABI (Undated)
Oceania
American Samoa Present Planted CABI (Undated b)
Australia Present NativeThomson and Evans (2006); CABI(Undated)
-Northern Territory Present Native USDA-ARS (2017); CABI (Undated)
-Queensland Present Native USDA-ARS (2017); CABI (Undated)
Cook Islands Present Planted CABI (Undated b)
Federated States ofMicronesia
PresentThomson and Evans (2006); CABI(Undated)
Probably aboriginalintroduction
Fiji Present NativeThomson and Evans (2006); CABI(Undated)
French Polynesia PresentThomson and Evans (2006); CABI(Undated)
Probably aboriginalintroduction
Guam Present Planted CABI (Undated b)
Kiribati Present Planted CABI (Undated b)
Marshall Islands Present Planted CABI (Undated b)
New Caledonia Present Native USDA-ARS (2017); CABI (Undated)
Niue Present Planted CABI (Undated b)
Northern Mariana Islands Present Planted CABI (Undated b)
Papua New Guinea Present NativeThomson and Evans (2006); CABI(Undated)
Samoa PresentThomson and Evans (2006); CABI(Undated)
Probably aboriginalintroduction
Solomon Islands Present NativeThomson and Evans (2006); CABI(Undated)
Tokelau Present Planted CABI (Undated b)
Tonga PresentThomson and Evans (2006); CABI(Undated)
Probably aboriginalintroduction
Tuvalu Present Planted CABI (Undated b)
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
Vanuatu Present NativeThomson and Evans (2006); CABI(Undated)
Wallis and Futuna Present Planted CABI (Undated b)
South America
Argentina Present Introduced Davidse et al. (2009)
Bolivia Present Introduced Davidse et al. (2009)
Brazil Present Introduced Invasive CABI (Undated b)
-Acre Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Amazonas Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Bahia Present Introduced Invasive I3N-Brasil (2017)
-Ceara Present Introduced Invasive I3N-Brasil (2017)
-Distrito Federal Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Espirito Santo Present Introduced Invasive I3N-Brasil (2017)
-Mato Grosso Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Mato Grosso do Sul Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Minas Gerais Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Para Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Paraiba Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Parana Present Introduced Invasive I3N-Brasil (2017)
-Pernambuco Present Introduced Invasive I3N-Brasil (2017)
-Piaui Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Rio de Janeiro Present Introduced Invasive I3N-Brasil (2017)
-Rio Grande do Norte Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Roraima Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
-Santa Catarina Present Introduced Invasive I3N-Brasil (2017)
-Sao Paulo Present Introduced Invasive I3N-Brasil (2017); CABI (Undated)
-Sergipe Present Introduced Invasive I3N-Brasil (2017)
-Tocantins Present Introduced Naturalized Marquete and Loiola (2015) Naturalized
Colombia Present Introduced Orwa et al. (2009)
Continent/Country/Region Distribution LastReported Origin First
Reported Invasive Planted Reference Notes
Ecuador Present Introduced Jørgensen and León-Yánez (1999)
-Galapagos Islands Present Introduced Jørgensen and León-Yánez (1999)
French Guiana Present Introduced Funk et al. (2007)
Guyana Present Introduced Funk et al. (2007)
Paraguay Present Introduced Davidse et al. (2009)
Peru Present Introduced Davidse et al. (2009)
Suriname Present Introduced Funk et al. (2007); CABI (Undated)
Venezuela Present Introduced CABI (Undated) Original citation: Hokcheet al. (2010)
History of Introduction and Spread
The rind of the fruit, comprising light, pithy/corky tissue, enables the fruits to float and be naturally dispersed long distances by sea currents (Kadambi, 1954; Nakanishi, 1989; Troupand Joshi, 1984). The extent to which its range has also been extended through movement by humans is difficult to determine.
In Hawaii, T. catappa was introduced probably before 1800. Now it can be found naturalized at low altitudes, mainly near beach shores. Similarly, across the archipelagos of Polynesiaand Micronesia it is considered an aboriginal introduction to the eastern parts of its current range, widely naturalized across coastal areas (Thomson and Evans, 2006).
In the West Indies, T. catappa appears in herbarium collections made as early as 1871 in the Dominican Republic, 1880 in Martinique, and 1881 in Puerto Rico and the Virgin Islands(US National Herbarium).
Introductions
Introduced to Introducedfrom Year Reason Introduced
by
Established in wild through
References NotesNaturalreproduction
Continuousrestocking
Hawaii 1800Horticulture (pathwaycause)
Yes NoThomson and Evans(2006)
DominicanRepublic
1871Horticulture (pathwaycause)
Yes No
Martinique 1880Horticulture (pathwaycause)
Yes No
Puerto Rico 1881Horticulture (pathwaycause)
Yes No
Risk of Introduction
The likelihood of new introductions of T. catappa is very high. This species is extensively commercialized and planted across tropical and subtropical coastal habitats. Additionally, it isa prolific seed producer and seeds float and can be carried considerable distances by sea currents and still remain viable (Thomson and Evans, 2006; Orwa et al., 2009). A riskassessment carried out for PIER (2017), however, gave the species a low risk score of 4.
Habitat
T. catappa grows in coastal thickets, beaches, rocky shores, sand dunes, parks, gardens, and edges of mangrove swamps. It is a pioneer species in disturbed sites across littoralhabitats and in sandy areas just above the level of high tides (Valkenburg and Waluyo, 1991; Thomson and Evans, 2006; Orwa et al., 2009).
Habitat List
Category Sub-Category Habitat Presence Status
Brackish Inland saline areas Present, no further details Harmful (pest or invasive)
Brackish Inland saline areas Present, no further details Natural
Brackish Inland saline areas Present, no further details Productive/non-natural
Terrestrial
Terrestrial Managed Disturbed areas Present, no further details Harmful (pest or invasive)
Terrestrial Managed Disturbed areas Present, no further details Natural
Terrestrial Managed Disturbed areas Present, no further details Productive/non-natural
Terrestrial Managed Rail / roadsides Present, no further details Harmful (pest or invasive)
Terrestrial Managed Rail / roadsides Present, no further details Natural
Terrestrial Managed Rail / roadsides Present, no further details Productive/non-natural
Terrestrial Managed Urban / peri-urban areas Present, no further details Harmful (pest or invasive)
Terrestrial Managed Urban / peri-urban areas Present, no further details Natural
Terrestrial Managed Urban / peri-urban areas Present, no further details Productive/non-natural
Terrestrial Natural / Semi-natural Wetlands Present, no further details Harmful (pest or invasive)
Terrestrial Natural / Semi-natural Wetlands Present, no further details Natural
Terrestrial Natural / Semi-natural Wetlands Present, no further details Productive/non-natural
Littoral Coastal areas Present, no further details Harmful (pest or invasive)
Littoral Coastal areas Present, no further details Natural
Littoral Coastal areas Present, no further details Productive/non-natural
Littoral Coastal dunes Present, no further details Harmful (pest or invasive)
Littoral Coastal dunes Present, no further details Natural
Littoral Coastal dunes Present, no further details Productive/non-natural
Littoral Mangroves Present, no further details Harmful (pest or invasive)
Littoral Mangroves Present, no further details Natural
Littoral Mangroves Present, no further details Productive/non-natural
Biology and Ecology
Genetics The chromosome number reported for T. catappa is 2n = 24 (Valkenburg and Waluyo, 1991).
Reproductive Biology T. catappa is an andromonoecious species, with male and perfect flowers occurring on the same tree. Usually perfect flowers occur at the base of the raceme and male flowers directlyabove. Flowers of both types are greenish-white or light brown. This species yields fruits by autogamy and geitonogamy, but it is also facultatively apomictic. Flowers produce traces ofnectar and large quantities of pollen and are visited and pollinated by insects including bees, flies, wasps and ants.
In India the bee genera Trigona and Apis and the fly genera Chrysomya and Sarcophaga are the most important pollinators. Trees growing isolated or in urban areas tend to be totallyapomictic (Atluri et al., 2003; Orwa et al., 2009).
Typically 1–5 fruits are formed on the basal part of the flower spike. Fruits are sessile, laterally compressed, ovoid to ovate, smooth-skinned drupes. During maturation, fruits changecolour from green, through yellow to bright red or dark purplish-red at full maturity (Coode, 1978; Whistler, 1992a, 1992b; Jensen, 1995). Fruit size varies considerably, e.g. 3.5–7 cm x2–5.5 cm (Exell, 1954), with Walter and Sam (1993) reporting an exceptional range in length from 2.5 to 10 cm. The kernel consists of two delicate and intricately entwined cotyledonsenclosed in an inconspicuous cream-coloured (sometimes red) testa (Evans, 1991).
Physiology and Phenology T. catappa sheds its leaves all at once, after they have turned yellow/red. In Southeast Asia and Peninsular Malaysia, this process occurs usually twice a year (January–February andJuly–August). Across tropical America, trees lose their leaves during the dry season (Valkenburg and Waluyo, 1991; Brown and Cooprider, 2013).
Flowers normally appear in early summer and fruits follow quite late in the year in India. In China, T. catappa has been recorded flowering from March to June and in October andfruiting in May and from July to September (Orwa et al., 2009; Flora of China Editorial Committee, 2017). Apparently trees never flower when defoliated (Valkenburg and Waluyo, 1991).
Flowering and fruiting occur sporadically throughout much of the year in Hawaii (Little and Skolmen, 1989), Fiji (Smith, 1985) and Vanuatu (Walter and Sam, 1993), but flowering andfruiting of cultivated trees seem to be more synchronous in Vanuatu. Flowering peaks around October to January and is followed by fruiting around March to June. In the South Pacific,T. catappa produces fruit sporadically throughout the year at lower latitudes, and has heavier crops towards the end of the year at higher latitudes (Evans, 1996). In Samoa, fruitingoccurs in June-July and February-March (Foliga and Blaffart, 1995), while in New Guinea the productive period is between November and March, especially December-February(Bourke, 1996).
Longevity T. catappa is a perennial (deciduous or semi-deciduous) tree (Thomson and Evans, 2006).
Activity patterns T. catappa is a fast growing tree at juvenile stages, moderating the speed of growth as it ages (Brown and Cooprider, 2013). In cultivation, plants usually start flowering and fruitingwithin 2 to 3 years after planting. Seeds may remain viable for a long time. They germinate readily, even after floating in salt water for considerable time periods. Germination typicallyoccurs 3–8 weeks after sowing with germination rates >50% (Valkenburg and Waluyo, 1991; Thomson and Evans, 2006).
Associations T. catappa is a food plant for the larval stages of the brown awl butterfly Badamia exclamationis. The foliage is also used for feeding tasar or katkura silk worms (Thomson and Evans,2006).
Within its native distribution rage, T. catappa often grows associated with species such as Acacia simplex, Tournefortia argentea, Barringtonia asiatica, Calophyllum inophyllum,Casuarina equisetifolia, Cocos nucifera, Cordia subcordata, Excoecaria agallocha, Hernandia nymphaeifolia, Hibiscus tiliaceus, Morinda citrifolia, Scaevola taccada, Schleinitziainsularum, Terminalia littoralis, Thespesia populnea, and Vitex trifoliata (Thomson and Evans, 2006).
Environmental Requirements T. catappa is well-adapted to grow in littoral areas across subtropical and tropical climates with mean annual rainfall ranging from 1000 mm to 3500 mm and mean annual temperaturesaround 13–36°C. It has the capability to grow in a wide range of soil types, including saline and alkaline sand, sandy loams, loams, and heavy clays with pH ranging from 4.0 to 8.5.Seedlings and saplings tolerate moderate shade levels but require high light levels to grow. Mature trees prefer full sunlight. The species tolerates strong and steady coastal winds,drought, and coastal salt spray (Thomson and Evans, 2006; Brown and Cooprider, 2013).
Climate
Climate Status Description Remark
Af - Tropical rainforest climate Preferred > 60mm precipitation per month
Am - Tropical monsoon climate PreferredTropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annualprecipitation(mm}/25]))
As - Tropical savanna climate with drysummer
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])
Latitude/Altitude Ranges
Latitude North (°N) Latitude South (°S) Altitude Lower (m) Altitude Upper (m)
25 -30 0 800
Air Temperature
Parameter Lower limit Upper limit
Absolute minimum temperature (ºC) 7
Mean annual temperature (ºC) 20 26
Mean maximum temperature of hottest month (ºC) 32 35
Mean minimum temperature of coldest month (ºC) 15 17
Rainfall
Parameter Lower limit Upper limit Description
Dry season duration 0 6 number of consecutive months with <40 mm rainfall
Mean annual rainfall 1000 3500 mm; lower/upper limits
Rainfall Regime
Bimodal Summer Uniform
Soil Tolerances
Soil drainagefreeseasonally waterlogged
Soil reactionacidalkalineneutral
Soil textureheavylightmedium
Special soil tolerancessaline
Natural enemies
Natural enemy Type Life stages Specificity References Biological controlin
Biological controlon
Anastrephasuspensa
Fruits|pods not specific
Bactrocera correcta Plants|Whole plant not specific
Bactrocera dorsalis Plants|Whole plant not specific
Badamiaexclamationis
Herbivore Plants|Whole plant not specific
Ceratitis capitata Fruits|pods not specific
Cryptotermes brevis Antagonist Plants|Whole plant not specific
Ophiusa coronata Fruits|pods not specific
Paecilomycesvariotii
Pathogen Plants|Seedlings not specific
Selenothripsrubrocinctus
Herbivore Plants|Whole plant not specific
Notes on Natural Enemies
T. catappa is susceptible to defoliating insects, especially when young. Seedlings are often defoliated by grasshoppers and beetles in Thailand and Malaysia. In Papua New Guinea,there is a record of trees being killed after attack by beetles of the genus Agrilus which are cambial feeders (Valkenburg and Waluyo, 1991). In Puerto Rico, the thrip speciesSelenothrips rubrocintus causes leaf discoloration and premature defoliation of adult trees. Trees are also susceptible to termites (i.e., Cryptotermes brevis). The sapwood issusceptible to attack by Lyctus species. In Asia, the fungus species Paecilomyces variotii causes dieback of seedlings (Orwa et al., 2009).
Means of Movement and Dispersal
T. catappa spreads by seeds. Each tree has the potential to produce large numbers of fruits. The rind of the fruit is a light, pithy, or corky tissue that enables the fruit to float and bedispersed by sea currents. Trees are also found away from coastal areas due to fruits being carried inland and dropped by frugivorous birds and bats, and as a result of deliberateplanting by humans (Valkenburg and Waluyo, 1991; Thomson and Evans, 2006).
Natural Dispersal (Non-Biotic)
Sea currents can disperse fruits of T. catappa over long distances (Valkenburg and Waluyo, 1991; Thomson and Evans, 2006).
Intentional Introduction
T. catappa has been widely planted as an ornamental and shade tree in many coastal habitats across tropical and subtropical regions (Valkenburg and Waluyo, 1991; Thomson andEvans, 2006).
Pathway Causes
Cause Notes Long Distance Local References
Botanical gardens and zoos Ornamental and shade tree Yes Yes Orwa et al. (2009)
Disturbance Often naturalized along roadsides, disturbed littoral habitats Yes Yes Thomson and Evans (2006)
Escape from confinement or garden escape Yes Yes Thomson and Evans (2006)
Food Fruits edible – consumed by humans Yes Yes Orwa et al. (2009)
Forestry Timber species Yes Yes Orwa et al. (2009)
Habitat restoration and improvement Trees planted for sand-dune stabilization Yes Yes Orwa et al. (2009)
Horticulture Widely commercialized as ornamental and shade tree Yes Yes Orwa et al. (2009)
Medicinal use Fruits and leaves Yes Yes Orwa et al. (2009)
Ornamental purposes Widely commercialized as ornamental and shade tree Yes Yes Orwa et al. (2009)
Timber trade Yes Yes Orwa et al. (2009)
Pathway Vectors
Vector Notes Long Distance Local References
Floating vegetation and debris Fruits float- dispersed by sea-currents Yes Yes Thomson and Evans (2006)
Water Fruits float- dispersed by sea-currents Yes Yes Thomson and Evans (2006)
Environmental Impact
T. cattapa is a fast-growing species that produces many new seedlings with the potential of invading large areas along the littoral and outcompeting and displacing native vegetation(Gilman and Watson, 1994; ISSG, 2017).
T. cattapa has a deep-rooting system that may alter the dynamics of coastal areas by inhibiting the natural movement of sand dunes and changing soil chemistry. Sand dunes providehabitat for highly specialized plants and animals, which are affected by the presence of this alien species (Smith, 2010; ISSG, 2017).
Threatened Species
Threatened Species Conservation Status WhereThreatened Mechanism References Notes
Panicum fauriei (Carter'spanicgrass)
NatureServe; USA ESA listing as endangeredspecies
HawaiiCompetition(unspecified)
US Fish and Wildlife Service(2011)
Social Impact
The fruits of T. catappa contain tannic acid that stains cars and other commodities. Trees produce a significant amount of litter, leaves and fruits, which require constant removal fromparks and gardens (Brown and Cooprider, 2013). The tree is difficult to manage because of multiple trunks, requiring regular pruning because of its fast growth. Exposed surface rootsystem can also be hazardous to humans, sidewalks and buildings (Gilman and Watson, 1994).
Risk and Impact Factors
InvasivenessProved invasive outside its native rangeHas a broad native rangeAbundant in its native rangeHighly adaptable to different environmentsIs a habitat generalistTolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etcPioneering in disturbed areasHighly mobile locallyBenefits from human association (i.e. it is a human commensal)Long livedFast growingHas high reproductive potentialGregariousHas propagules that can remain viable for more than one yearReproduces asexuallyHas high genetic variability
Impact outcomesDamaged ecosystem servicesEcosystem change/ habitat alterationInfrastructure damageModification of nutrient regimeModification of successional patternsReduced native biodiversitySoil accretionThreat to/ loss of native speciesTransportation disruption
Impact mechanismsCompetition - monopolizing resourcesCompetition - shadingCompetition (unspecified)Pest and disease transmissionHerbivory/grazing/browsingRapid growth
Likelihood of entry/controlHighly likely to be transported internationally deliberately
Uses
In the horticultural trade, T. catappa is promoted as an excellent ornamental for coastal areas and valued for its shade, edible fruits and ability to stabilize soils (Brown and Cooprider,2013). This species has been used medicinally in India, the Philippines, Indonesia and New Caledonia and the leaves are regarded as a contraceptive. The leaves have a sudorificaction and are applied to rheumatic joints. The tannin from bark and leaves is used as an astringent in dysentery and thrush. It is also regarded as diuretic and cardiotonic and isapplied externally on skin eruptions. In the Philippines a decoction of the leaves is employed as a vermifuge.
The fibrous fruit has a pleasant smell and is edible though not very tasty. Fruit quality can range from sweet to bitter. The kernel is eaten raw or roasted and has an almond-like tastedue to the high oil content (Janick and Paull, 2008). The seed is considered delicious and the pale odourless oil it contains is similar to almond oil. The oil is employed in cooking andmedicinally as a substitute for true almond oil to relieve abdominal inflammations, and, cooked with the leaves, in treating leprosy, scabies and other skin diseases. The foliage is usedas feed for silkworms and other animals (Valkenburg and Waluyo, 1991; Orwa et al., 2009).
T. catappa is often planted for erosion control, land reclamation and soil improvement. This species has a vast root system that binds together both sands and poor soils and it is also agood provider of mulch for the protection of soil and young crops (Thomson and Evans, 2006; Orwa et al., 2009; ISSG, 2017; PROTA, 2017). The tree is often planted in avenues andgardens as a shade tree. It is very well suited for this purpose because of its pagoda-like habit, with long, horizontal branches and large leaves.
The bark and leaves and sometimes roots and green fruits are locally used for tanning leather and provide a black dye, used for dyeing cottons and rattan and as ink. Fruit yield a reddye.
Economic Value Trees of T. catappa provide a red, good-quality, elastic, cross-grained timber often used for the construction of buildings, boats, bridges, floors, boxes, crates, planks, carts, barrels,wheelbarrows and furniture (Thomson and Evans, 2006; Orwa et al., 2009). The distinctive pagoda-like shape of the tree and the red leaves along with its fast growth make it valuableas an ornamental species (Janick and Paull, 2008).
Uses List
Animal feed, fodder, forageFodder/animal feedInvertebrate food for silkworms
EnvironmentalAgroforestryAmenityErosion control or dune stabilizationLand reclamationRevegetationShade and shelter
FuelsFuelwood
Human food and beverageBeverage baseFruitsNutsSeeds
MaterialsDye/tanningEssential oilsGum/resinLipidsMiscellaneous materialsResinsWood/timber
Medicinal, pharmaceuticalSource of medicine/pharmaceuticalTraditional/folklore
OrnamentalChristmas treeCut flowergarden plantPotted plantPropagation materialSeed trade
Wood Products
Boats
ContainersBoxesCrates
Furniture
RoundwoodBuilding polesPosts
Sawn or hewn building timbersBeamsBridgesCarpentry/joinery (exterior/interior)Engineering structuresFlooringFor heavy constructionFor light constructionHydraulic works
Wood-based materialsPlywood
WoodwareIndustrial and domestic woodware
Prevention and Control
Biological Control
The ISSG website suggests that bio-control agents could potentially be used in the control and management of T. catappa, but this website does not provide specific information.Beetles, grasshoppers, leaf rollers, leaf miners, fruit flies have been observed to affecting plants at different stages in India, Malaysia, Puerto Rico and Costa Rica and could potentiallybe used for its bio-control. However, further investigation is needed to establish the effectiveness of such vectors, as well as their possibility of becoming invasive species themselves(ISSG, 2017).
Chemical Control
In Florida (USA) areas invaded by T. catappa are treated with basal applications of herbicides such as triclopyr (Hadden et al., 2005). In Santa Catarina, Brazil, cutting the tree andapplying 4% triclopyr to the stump was the most effective treatment for T. catappa (Dechoum and Ziller, 2013).
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Links to Websites
Website URL Comment
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE EuropeanInvasive Alien Species Gateway
https://doi.org/10.5061/dryad.m93f6Data source for updated system dataadded to species habitat list.
Contributors
13/04/17 Updated by:
Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH, Washington DC, USA
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - World
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - Africa
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - Asia
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - Europe
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - Pacific
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - North America
CABI, 2021. Terminalia catappa. In: Invasive Species Compendium. Wallingford, UK: CAB International. https://www.cabi.org/isc
CABI Summary Data
Map Legends - Central America