Chamaecrista nictitans (sensitive partridge pea)
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
- Climate
- Latitude/Altitude Ranges
- Soil Tolerances
- Natural enemies
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Impact Summary
- Economic Impact
- Environmental Impact
- Threatened Species
- Social Impact
- Risk and Impact Factors
- Uses
- Uses List
- Detection and Inspection
- Similarities to Other Species/Conditions
- Prevention and Control
- Gaps in Knowledge/Research Needs
- References
- Links to Websites
- Organizations
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Chamaecrista nictitans (L.) Moench
Preferred Common Name
- sensitive partridge pea
Other Scientific Names
- Cassia aeschinomene Collad.
- Cassia aspera var. mohrii Pollard
- Cassia brachypoda Benth.
- Cassia chamaecrista var. nictitans Kuntze
- Cassia diffusa DC.
- Cassia lechenaultiana DC.
- Cassia mimosoides subsp. leschenaultiana (DC.) H. Ohashi
- Cassia multipinnata Pollard
- Cassia nictidans L.
- Cassia nictitans L.
- Cassia patellaria DC. ex Collad.
- Cassia pennelliana Amshoff
- Cassia procumbens L.
- Cassia riparia Kunth
- Chamaecrista aeschinomene (Collad.) Greene
- Chamaecrista aspera var. mohrii (Pollard) Pollard ex A. Heller
- Chamaecrista mohrii (Pollard) Britton & Rose
- Chamaecrista molinae G. Flores & M. Sousa
- Chamaecrista multipinnata Pennell
- Chamaecrista procumbens (L.) Greene
- Nictitella amena Raf.
International Common Names
- English: Japanese tea senna; partridge pea; sensitive cassia; sensitive pea; sensitive plant; wild sensitive plant; wild sensitive senna
Local Common Names
- Japan: kobo-cha; Nemu-cha
- Tonga: Mateloi vava'u
- USA/Hawaii: Lauki
Summary of Invasiveness
Top of pageChamaecrista nictitans is an annual leguminous herb which is widespread in the Neotropics as well as the southern and eastern USA. It has been introduced to a number of Asian countries and a number of island nations, and is listed as invasive or potentially invasive in Tonga (Space & Flynn, 2001), and as an invasive species of environmental concern in Samoa (Space & Flynn, 2002), Palau (Space et al., 2009), and Niue. It was first recorded as invasive in Niue in 1970 (Space et al., 2004). It does however receive a low risk assessment score for introduced species for Palau (score = 0 -- Space et al., 2009), and in general is low risk (score = 0) (PIER, 2013).
C. nictitans has characteristics that indicate invasiveness such as its ability to naturalize, its broad climate suitability (environmental versatility), a history of repeated introductions outside its native range, weedy growth, production of viable long-lived seed, self-compatibility, reproduction with short generation time, and good seed dispersal (PIER, 2013). On Niue, these characteristics may well have allowed it to colonise new areas of the island after cyclone disturbance, increasing its distribution (Space et al., 2004).
However, there is little evidence that it has a significant adverse impact in its introduced range – the literature refers to potential impacts (such as nitrogen enrichment or the outcompetition of native plants) rather than serious actual impacts.
It has several potential uses, for example to stabilize soils or fix nitrogen, or as forage – see the ‘Uses’ section for more information.
The species is listed as endangered in New Hampshire, USA, near the northern edge of its native range (New England Wild Flower Society, 2013).
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Fabales
- Family: Fabaceae
- Subfamily: Caesalpinioideae
- Genus: Chamaecrista
- Species: Chamaecrista nictitans
Notes on Taxonomy and Nomenclature
Top of pageCassia nictitans is the accepted basionym - the original name from which the current name is derived - and was assigned by Linnaeus in 1753; it was superseded by the current name Chamaecrista nictitans (Moench) in 1794 (Missouri Botanical Garden, 2013). There are over 30 synonyms, varieties, and subspecies of C. nictitans (Missouri Botanical Garden, 2013; The Plant List, 2013; GBIF, 2013).
Description
Top of page(Description from Gargiullo et al. (2008) except where indicated otherwise). C. nictitans is a herbaceous or woody (C. Parker, consultant, UK, personal communication, 2014) annual, 10-80 cm tall. It has a branching form with hairy green stems, often with a reddish upper surface; stipules are narrow and paired on either side of the stem base (13mm long, 3mm wide). Leaves are alternate, evenly pinnate, 10cm long and 3cm wide (Miller and Miller (2005) state that they are 2-5 cm long). Leaves have a hairy midrib, with a 7mm long stalk. Leaflets are in 7-26 pairs, oblong, and 6-20mm long and 2mm wide; they are hairy below and fold slowly when touched. Flowers are yellow, 10mm wide, and bilaterally symmetrical. They have five petals which are unequal, the largest being 8mm long and the others much smaller. Flowers have five stamens, and five short and unequal sepals. Flowers bloom a few at a time in leaf axils along the underside of stems. Individual plants can produce up to 30 inflorescences with 1-5 flowers per inflorescence (Lee, 1989). Fruits are dry pods, 20-40mm long, 3-6mm wide. They are flat and oblong, splitting open to release seeds (1-12 seeds per pod – Lee, 1989).
There is one extrafloral nectary per petiole, which is close to the flowers and fruit. Nectar is produced in the extrafloral nectaries from when the leaf attached to the petiole begins to expand until it dies (Ruhren and Handel, 1999; Ruhren, 2003).
Little information is available on how to distinguish between different varieties and subspecies.
Distribution
Top of pageC. nictitans is native to the Neotropics and the southern and eastern USA (USDA-ARS, 2013), and is now widely naturalized elsewhere in tropical and sub-tropical climates (PIER, 2013). It has been introduced to several island nations including Mauritius and Reunion (ILDIS, 2013), and several Pacific islands (e.g. PIER, 2013).
There is some discrepancy over its distribution in the Hawaiian Islands: Space et al. (2000b) state that C. nictitans is not present on Hawaii, yet several other sources (Wagner et al., 1999; USDA-NRCS, 2013; PIER, 2013; Carino & Daehler, 2002) contradict this, and list it as an introduced and invasive species. Similarly, Space et al. (2000a) state that C. nictitans is not present on Chuuk (Federated States of Micronesia), which is again contradicted by PIER (2013).
According to ILDIS (2013) it is present in a number of Asian countries and is native to some of them, but its native status there is not supported by other sources such as PIER (2013) (citing Wagner, 1999) and USDA-ARS (2013), which indicate that the Neotropics and parts of North America are its native range.
It has been planted experimentally in China (Hacker et al., 2001; Zhan et al., 2005), but is not known to be more widely present there.
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 |
|||||||
Mauritius | Present | Introduced | |||||
Réunion | Present | Introduced | |||||
Asia |
|||||||
Bangladesh | Present | ||||||
Bhutan | Present | ||||||
China | Present | Present based on regional distribution. | |||||
-Fujian | Present, Only in captivity/cultivation | ||||||
-Hunan | Present, Only in captivity/cultivation | ||||||
Georgia | Present | Introduced | |||||
India | Present | ||||||
-Bihar | Present | ||||||
-Delhi | Present | ||||||
-Uttar Pradesh | Present | ||||||
-West Bengal | Present | ||||||
Indonesia | Present | Introduced | |||||
-Irian Jaya | Present | ||||||
-Java | Present | ||||||
Japan | Present | Introduced | Bonin (Ogasawara) Islands | ||||
Malaysia | Present | Introduced | |||||
-Peninsular Malaysia | Present | ||||||
Singapore | Present | Introduced | |||||
Sri Lanka | Present | ||||||
Taiwan | Present | Introduced | 1910 | ||||
Europe |
|||||||
Norway | Present | Introduced | 1999 | ||||
North America |
|||||||
Antigua and Barbuda | Present | Native | |||||
Bahamas | Present | Native | |||||
Belize | Present | Native | |||||
British Virgin Islands | Present | Native | |||||
Cayman Islands | Present | ||||||
Costa Rica | Present | Native | |||||
Cuba | Present | Native | |||||
Dominican Republic | Present | ||||||
El Salvador | Present | Native | |||||
Grenada | Present | Native | |||||
Guadeloupe | Present | Native | |||||
Guatemala | Present | Native | |||||
Haiti | Present | ||||||
Honduras | Present | Native | |||||
Jamaica | Present | Native | |||||
Martinique | Present | Native | |||||
Mexico | Present | Native | |||||
Netherlands Antilles | Present | Native | |||||
Nicaragua | Present | Native | |||||
Panama | Present | Native | |||||
Puerto Rico | Present | Native | |||||
Saint Kitts and Nevis | Present | Native | |||||
Saint Vincent and the Grenadines | Present | Native | |||||
Trinidad and Tobago | Present | Native | Trinidad | ||||
U.S. Virgin Islands | Present | Native | |||||
United States | Present | Present based on regional distribution. | |||||
-Alabama | Present | Native | |||||
-Arizona | Present | Native | |||||
-Arkansas | Present | Native | |||||
-Connecticut | Present | Native | |||||
-Delaware | Present | Native | |||||
-District of Columbia | Present | Native | |||||
-Florida | Present | Native | |||||
-Georgia | Present | Native | |||||
-Hawaii | Present | 1999 | Introduced | Invasive | Hawai'i (Big) Island, Kaho' olawe Island, Lana'i Island, Maui Island, Ni'ihau Island, O'ahu Island | ||
-Illinois | Present | Native | |||||
-Indiana | Present | Native | |||||
-Kansas | Present | Native | |||||
-Kentucky | Present | Native | |||||
-Louisiana | Present | Native | |||||
-Maine | Absent, Invalid presence record(s) | ||||||
-Maryland | Present | Native | |||||
-Massachusetts | Present | Native | |||||
-Michigan | Present | Native | |||||
-Mississippi | Present | Native | |||||
-Missouri | Present | Native | |||||
-New Hampshire | Present, Few occurrences | Native | Endangered | ||||
-New Jersey | Present | Native | |||||
-New Mexico | Present | Native | |||||
-New York | Present | Native | |||||
-North Carolina | Present | Native | |||||
-Ohio | Present | Native | |||||
-Oklahoma | Present | Native | |||||
-Pennsylvania | Present | Native | |||||
-Rhode Island | Present | Native | |||||
-South Carolina | Present | Native | |||||
-Tennessee | Present | Native | |||||
-Texas | Present | Native | |||||
-Vermont | Present, Few occurrences | Native | Rare | ||||
-Virginia | Present | Native | |||||
-West Virginia | Present | Native | |||||
Oceania |
|||||||
Federated States of Micronesia | Present | Introduced | Invasive | Cultivated and invasive on Pohnpei Island; also present on Weno (Moen) and Yap (Waqab) islands | |||
Fiji | Present | 1985 | Introduced | Invasive | Vanua Levu and Viti Levu Islands | ||
Guam | Present | 1970 | Introduced | Invasive | Guam Island | ||
Kiribati | Absent, Unconfirmed presence record(s) | 1997 | Tarawa Atoll | ||||
New Caledonia | Present | 1994 | Introduced | Île Grande Terre | |||
Niue | Present | 2004 | Introduced | Invasive | |||
Northern Mariana Islands | Present | 1979 | Introduced | Invasive | Pagan and Rosa Islands; invasive on Pagan | ||
Palau | Present | Introduced | Invasive | Babeldaob, Koror & Malakal Islands | |||
Papua New Guinea | Present | ||||||
Samoa | Present | 2002 | Introduced | Invasive | Upola Island | ||
Solomon Islands | Present | Introduced | |||||
Tonga | Present | 2001 | Introduced | Invasive | Ha-ano Island, Lifuka and Foa Islands, 'Uiha Island, 'Eua Island, Tongatapu Island, Vava'u Island | ||
Wallis and Futuna | Present | 2007 | Introduced | Invasive | Wallis ('Uvea) Island | ||
South America |
|||||||
Argentina | Present | Native | Charo, Corrientes, Formosa, Jujuy, Misiones, Salta | ||||
Bolivia | Present | Native | |||||
Brazil | Present | Native | |||||
-Amapa | Present | Native | |||||
-Amazonas | Present | Native | |||||
-Bahia | Present | Native | |||||
-Ceara | Present | Native | |||||
-Espirito Santo | Present | Native | |||||
-Maranhao | Present | Native | |||||
-Mato Grosso | Present | Native | |||||
-Mato Grosso do Sul | Present | Native | |||||
-Minas Gerais | Present | Native | |||||
-Para | Present | Native | |||||
-Parana | Present | Native | |||||
-Pernambuco | Present | Native | |||||
-Rio de Janeiro | Present | Native | |||||
-Rio Grande do Sul | Present | Native | |||||
-Rondonia | Present | Native | |||||
-Santa Catarina | Present | Native | |||||
-Sao Paulo | Present | Native | |||||
Colombia | Present | Native | |||||
Ecuador | Present | Native | Cotopaxi, Guyas, Loja | ||||
French Guiana | Present | Native | |||||
Guyana | Present | Native | |||||
Paraguay | Present | Native | |||||
Peru | Present | Native | |||||
Suriname | Present | Native | |||||
Venezuela | Present | Native |
History of Introduction and Spread
Top of pageThere is no detailed information regarding the history of spread of C. nictitans. On Niue, its distribution increased following disturbance from Cyclone Heta in 2003/4, with the development of several extensive stands of which some were almost monocultures (Space et al., 2004). It is known to have been planted experimentally in China as a potentially useful plant (Hacker et al., 2001; Zhan et al., 2005).
Risk of Introduction
Top of pageThere is risk of introduction between islands within the same region; for example C. nictitans is listed as a species of concern in Palau and is present on Koror and Malakal, but not present on Angaur, Kayangel, Pelelie, Ngercheu, the Rock Islands, Sonsoral State and Hatohobei State. It does however receive a risk assessment score = 0 for Palau (Space et al., 2009). There is also potential for introduction between Samoan islands: C. nictitans is present on Samoa and Upolu, but not Savai’i (Space & Flynn, 2002).
There is no information on the pathways of spread, however some productive uses such as soil stabilization, cut-and-carry forage (Hacker et al., 2001) or integrated pest management (Zhan et al., 2005) may provide reasons for the species to be spread deliberately (it is known to have been planted experimentally in China for these purposes).
Habitat
Top of pageThere is currently no information on major regional or country variations in the habitats containing C. nictitans.
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | Productive/non-natural |
Terrestrial | Managed | Disturbed areas | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Natural forests | Principal habitat | Natural |
Terrestrial | Natural / Semi-natural | Natural grasslands | Principal habitat | Natural |
Terrestrial | Natural / Semi-natural | Rocky areas / lava flows | Principal habitat | Natural |
Hosts/Species Affected
Top of pageThere is currently no evidence that C. nictitans negatively affects crops or other plants.
Biology and Ecology
Top of pageGenetics
C. nictitans has a chromosome number of 2n = 48, with evidence for some differences in chromosome size between different populations (Souza & Benko-Iseppon, 2004). There is currently no literature on hybridization between species of Chamaecrista.
Reproductive Biology
C. nictitans reproduces via seed and is both self-compatible and self-pollinating. Plants produce up to 30 inflorescences with 1-5 flowers each, and 1-12 seeds per fruit, but there is evidence of fruit abortion when resources are limited (Lee, 1989). Flowers are produced during summer months in temperate climates, so it would be logical to suggest that either temperature or rainfall cues determine flowering and fruiting times, but there is no literature examining this.
In Vermont, USA, seeds were found to germinate in spring, and plants begin flowering in mid-summer; axillary inflorescences each produce 1-5 flowers during late July and August, with individual plants producing up to 30 inflorescences. Flowers are open for one day. Fruits require several weeks to mature in late September/early October, and each contain 1-12 mature seeds (Lee, 1989). In Costa Rica, flowers bloom between August and January, and in May (Gargiullo et al., 2008)
Physiology and Phenology
There is little literature detailing survival strategies, adaptability and phenological variation of C. nictitans. However, it is known to be a weedy species which takes advantage of disturbance events for colonisation (Space et al., 2004). There is no evidence of differences in populations between native and exotic ranges. See above under ‘Reproductive Biology’ for information on the timing of flowering and fruiting.
Associations
C. nictitans produces nectar in extra-floral nectaries which act as a food source for ants, parasitoid wasps, laictid bees and jumping spiders. The most common ant associated with C. nictitans is Crematogaster lineolata Say (Ruhren, 2003). Plants with resident jumping spiders (Eris sp. and Metaphidippus sp.) - which feed on herbivores, ants, bees and other spiders - have been shown to set more seed than plants with no spiders, indicating that they are beneficial to plant fecundity (Ruhren & Handel, 1999).
Environmental requirements
There is no information on any specific environmental requirements of C. nictitans. Hacker et al. (2001) found that some accessions from Argentina and Paraguay survived the winter when planted in Fujian and Hunan provinces of southern China, but those from lower latitudes did not. A number of sources suggest that the species prefers light sandy soils and open sunny situations (C. Parker, consultant, UK, personal communication, 2014).
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
A - Tropical/Megathermal climate | Preferred | Average temp. of coolest month > 18°C, > 1500mm precipitation annually | |
Af - Tropical rainforest climate | Preferred | > 60mm precipitation per month | |
Am - Tropical monsoon climate | Preferred | Tropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25])) | |
As - Tropical savanna climate with dry summer | Tolerated | < 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]) | |
C - Temperate/Mesothermal climate | Preferred | Average temp. of coldest month > 0°C and < 18°C, mean warmest month > 10°C | |
Cs - Warm temperate climate with dry summer | Preferred | Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers |
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
45 | 45 |
Natural enemies
Top of pageNatural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Sennius cruentatus | Herbivore | Plants|Seeds | to species |
Notes on Natural Enemies
Top of pageThere is little information detailing natural enemies of C. nictitans; however Ruhren & Handel (1999) do state that Sennius cruentatus (Bruchidae) is a specialist seed predator of C. nictitans, and it has a range covering the eastern USA and Mexico, part of the native range of C. nictitans (Kingsolver, 2004).
Means of Movement and Dispersal
Top of pageNatural Dispersal (Non-Biotic)
Seeds are likely to be dispersed through force and gravity when seed pods open (PIER, 2013); they are not adapted for wind or water dispersal.
Vector Transmission
Seeds are not adapted for attachment, and fruits are not eaten by animals (PIER, 2013).
Accidental Introduction
There is potential for C. nictitans to be introduced as a contaminant of soil, debris, or garden waste (Space et al., 2004).
Intentional Introduction
C. nictitans could be introduced to new areas as a soil-stabilising plant, and for cut-and-carry forage (Hacker et al., 2001). It has also been shown to enhance pest management in longan (Dimocarpus longan) orchards, by maintaining natural enemies of pest species (Zhan et al., 2005), and might possibly be introduced for that reason. It is known to have been planted experimentally in China for these purposes.
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Positive |
Environment (generally) | Negative |
Economic Impact
Top of pageThere is no evidence suggesting that C. nictitans has a negative economic impact.
Environmental Impact
Top of pageImpact on Habitats
There is potential for C. nictitans to colonize new areas following disturbance, and form large stands which could become a monoculture (Space et al., 2004). There is also potential for C. nictitans to alter nutrient cycling and productivity of ecosystems through its ability to fix nitrogen in root nodules: after senescence of plants, soil nitrogen levels can increase which can alter nutrient cycling (Carino and Daehler, 2002).
Impact on Biodiversity
C. nictitans may indirectly facilitate the invasion of other alien species through increasing soil nitrogen levels (Carino & Daehler, 2002). These other alien species may be more harmful to native species. There is little evidence to suggest that C. nictitans directly negatively affects native species, although where it has formed dense stands native plants could become outcompeted (Space et al., 2004).
Threatened Species
Top of pageThreatened Species | Conservation Status | Where Threatened | Mechanism | References | Notes |
---|---|---|---|---|---|
Sesbania tomentosa | National list(s); USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Ecosystem change / habitat alteration | US Fish and Wildlife Service (2010a) | |
Spermolepis hawaiiensis (Hawaii scaleseed) | USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Ecosystem change / habitat alteration | US Fish and Wildlife Service (2010b) |
Social Impact
Top of pageThere is no evidence suggesting that C. nictitans has a negative social impact.
Risk and Impact Factors
Top of page- Proved invasive outside its native range
- Has a broad native range
- Abundant in its native range
- Pioneering in disturbed areas
- Fast growing
- Has high reproductive potential
- Has propagules that can remain viable for more than one year
- Increases vulnerability to invasions
- Modification of nutrient regime
- Modification of successional patterns
- Monoculture formation
- Reduced native biodiversity
- Competition - monopolizing resources
- Interaction with other invasive species
Uses
Top of pageEconomic Value
There is potential for C. nictitans to be used in the improvement of food production: for example, Lu et al. (2009) found that using growth substrates containing C. nictitans improved the yield of edible fungi such as Coprinus comatus. C. nictitans has also been shown to improve pest management in longan orchards through provision of nectar to arthropods (Zhan et al., 2005). It could also be used as cut-and-carry forage (Hacker et al., 2001).
Social Benefit
There may be potential for using C. nictitans in the treatment of herpes simplex infection (Herrero Uribe et al., 2004). In Brazil it is used in folk medicine to treat kidney diseases, although a study by Carvalho Osorio et al. (1996) found no significant effect on renal calculi in rats.
Environmental Services
C. nictitans could function as a soil stabilizer (Hacker et al., 2001), and more generally for its nitrogen fixing properties (Morris, 1997).
Detection and Inspection
Top of pageDetection of the presence of C. nictitans could come from dedicated surveys and identification in the field.
Similarities to Other Species/Conditions
Top of pageAccording to Miller and Miller (2005), C. nictitans is similar to C. fasciculata (which is found in most US states where C. nictitans is found – USDA-NRCS, 2013), but C. nictitans has smaller leaves. (Note that Miller and Miller (2005) give a smaller size for the leaves of C. nictitans than that given by Gargiullo et al. (2005)).
Prevention and Control
Top of pageDue to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.
There is no information currently available detailing prevention and control methods for this species. As it is known to be weedy in habit, colonising disturbed ground, it is logical that monitoring such sites for colonisation and subsequent removal of plants would help prevent invasion.
Gaps in Knowledge/Research Needs
Top of pageDetails of this species in general are lacking. There is very little literature dealing with its impact on natural systems: research should focus on any negative impact that it might have on native flora and fauna, so that mitigation of impacts can be undertaken. There is also little information on how and why the species has been transported outside its native range by humans historically.
References
Top of pageGargiullo MB, Magnuson BL, Kimball LD, 2008. A field guide to plants of Costa Rica. Oxford, UK: Oxford University Press, 544 pp.
GBIF, 2013. Global Biodiversity Information Facility. Global Biodiversity Information Facility (GBIF). http://data.gbif.org/species/
Herrera K, Lorence D, Flynn T, Balick MJ, 2010. Checklist of the vascular plants of Pohnpei with local names and uses. Lawai, Hawaii, USA: National Tropical Botanical Garden, 146 pp.
ILDIS, 2013. International Legume Database & Information Service. Reading, UK: School of Plant Sciences, Unversity of Reading. http://www.ildis.org/
Kingsolver JM, 2004. Handbook of the Bruchidae of the United States and Canada. Washington, DC, USA: United States Department of Agriculture, Agricultural Research Service, 536 pp. [USDA Technical Bulletin 1912.] http://www.ars.usda.gov/is/np/Bruchidae/BruchidaeIntro.htm
Lee TD, 1989. Patterns of Fruit and Seed Production in a Vermont Polulation of Cassia nictitans L. (Caesalpiniaceae). Bulletin of the Torrey Botanical Club, 116(1):15-21.
Missouri Botanical Garden, 2013. Tropicos database. St Louis, USA: Missouri Botanical Garden. http://www.tropicos.org/
New England Wild Flower Society, 2013. Go Botany. Framingham, Massachusetts, USA: New England Wild Flower Society. https://gobotany.newenglandwild.org/
PIER, 2013. Pacific Islands Ecosystems at Risk. Honolulu, Hawaii, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Raulerson L, Rinehart AF, Falanruw MC, 1996. A botanical reconnaissance of the proposed Compact-impact road alignment on Babeldaob Island, Republic of Palau. Mangilao, Guam: University of Guam, 78 pp. [University of Guam Herbarium Contribution no. 32.]
Souza MGC, Benko-Iseppon AM, 2004. Cytogenics and chromosome banding pattern in Caesalpinioideae and Papilionioideae species of Para, Amazonas, Brazil. Botanical Journal of the Linnean Society, 144:181-191.
Space JC, Flynn T, 2000. Report to the Government of Niue on Invasive Plant Species of Environmental Concern. Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry, 34 pp. http://www.hear.org/pier/pdf/niue_report.pdf
Space JC, Flynn T, 2001. Report to the Kingdom of Tonga on Invasive Plant Species of Environmental Concern. Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry, 78 pp. http://www.hear.org/pier/pdf/tonga_report.pdf
Space JC, Flynn T, 2002. Report to the Government of Samoa on Invasive Plant Species of Environmental Concern. Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry, 78 pp. http://www.hear.org/pier/pdf/samoa_report.pdf
Space JC, Lorence DH, LaRosa AM, 2009. Report to the Republic of Palau: 2008 update on invasive plant species. Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry, 227 pp. http://www.hear.org/pier/pdf/Palau_report_2008.pdf
Space JC, Waterhouse B, Denslow JS, Nelson D, Waguk E, 2000. Invasive plant species on Kosrae, Federated States of Micronesia. Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry, 43 pp. http://www.hear.org/pier/pdf/kosrae_report.pdf
Space JC, Waterhouse BM, Miles JE, Tiobech J, Rengulbai K, 2003. Report to the Republic of Palau on Invasive Species of Environmental Concern. Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry, 174 pp. http://www.hear.org/pier/pdf/palau_report.pdf
Space JC, Waterhouse BM, Newfield M, Bull C, 2004. Report to the Government of Niue and the United Nations Development Programme: Invasive Plant Species on Niue following Cyclone Heta. 76 pp. http://www.hear.org/pier/pdf/niue_report_20041217.pdf
Stone BC, 1970. The flora of Guam. Micronesia, 6:1-659.
The Plant List, 2013. The Plant List: a working list of all plant species. Version 1.1. London, UK: Royal Botanic Gardens, Kew. http://www.theplantlist.org
USDA-ARS, 2013. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx
USDA-NRCS, 2013. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/
Wu TL, Hu QM, Xia NH, Lai PCC, Yip KL, 2001. Check List of Hong Kong Plants:384 pp. [Agriculture, Fisheries and Conservation Department Bulletin 1 (revised).] http://www.hkflora.com/v2/flora/plant_check_list.php
Distribution References
CABI, Undated. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Gargiullo MB, Magnuson BL, Kimball LD, 2008. A field guide to plants of Costa Rica., Oxford, UK: Oxford University Press. 544 pp.
ILDIS, 2013. International Legume Database & Information Service., Reading, UK: School of Plant Sciences, Unversity of Reading. http://www.ildis.org/
Missouri Botanical Garden, 2013. Tropicos database., St Louis, USA: Missouri Botanical Garden. http://www.tropicos.org/
New England Wild Flower Society, 2013. GoBotany., 180 Hemenway Road, Framingham, Massachusetts, USA: New England Wild Flower Society. https://gobotany.newenglandwild.org/
PIER, 2013. Pacific Islands Ecosystems at Risk., Honolulu, Hawaii, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Raulerson L, Rinehart AF, Falanruw MC, 1996. A botanical reconnaissance of the proposed Compact-impact road alignment on Babeldaob Island, Republic of Palau. In: University of Guam Herbarium Contribution no. 32, Mangilao, Guam: University of Guam. 78 pp.
Space JC, Flynn T, 2000. Report to the Government of Niue on Invasive Plant Species of Environmental Concern., Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry. 34 pp. http://www.hear.org/pier/pdf/niue_report.pdf
Space JC, Flynn T, 2001. Report to the Kingdom of Tonga on Invasive Plant Species of Environmental Concern., Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry. 78 pp. http://www.hear.org/pier/pdf/tonga_report.pdf
Space JC, Flynn T, 2002. Report to the Government of Samoa on Invasive Plant Species of Environmental Concern., Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry. 78 pp. http://www.hear.org/pier/pdf/samoa_report.pdf
Space JC, Waterhouse BM, Miles JE, Tiobech J, Rengulbai K, 2003. Report to the Republic of Palau on Invasive Species of Environmental Concern., Honolulu, Hawaii, USA: USDA Forest Service, Pacific Southwest Research Station, Institute of Pacific Islands Forestry. 174 pp. http://www.hear.org/pier/pdf/palau_report.pdf
Space JC, Waterhouse BM, Newfield M, Bull C, 2004. Report to the Government of Niue and the United Nations Development Programme: Invasive Plant Species on Niue following Cyclone Heta., 76 pp. http://www.hear.org/pier/pdf/niue_report_20041217.pdf
USDA-ARS, 2013. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysimple.aspx
USDA-NRCS, 2013. The PLANTS Database. Greensboro, North Carolina, USA: National Plant Data Team. https://plants.sc.egov.usda.gov
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 Biodiversity Information Facility | http://www.gbif.org | |
PIER | http://www.hear.org/pier/index.html | |
The Plant List | http://www.theplantlist.org | |
Tropicos | http://www.tropicos.org/ |
Organizations
Top of pageUSA: PIER (Pacific Island Ecosystems at Risk), University of Hawaii, Honolulu, http://www.hear.org/pier/index.html
Distribution Maps
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