Odontonema cuspidatum (Cardinal’s guard)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat
- Habitat List
- Biology and Ecology
- Climate
- Air Temperature
- Soil Tolerances
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Environmental Impact
- Risk and Impact Factors
- Uses
- Uses List
- References
- Links to Websites
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Odontonema cuspidatum (Nees) Kuntze
Preferred Common Name
- Cardinal’s guard
Other Scientific Names
- Odontonema strictum Sensu West Indian authors, non (Nees) Kuntze
- Thyrsacanthus cuspidatus Nees
International Common Names
- English: cardinal flower; cardinal’s crest; fire spike; mottled toothedthread; odontonema; red justicia; scarlet firespike
Local Common Names
- Ecuador: lava botellas
- Mexico: coral de jardín; flor de chupa miel; flor de chuparrosa
- Paraguay: clavo de fuego
- Saint Lucia: firespike
Summary of Invasiveness
Top of pageO. cuspidatum is a shrub commonly planted as an ornamental for its attractive red tubular flowers. It has escaped from cultivation and can be found naturalized in disturbed areas as well as in relatively unaltered forests (Lorence et al., 1995; Space and Flynn, 2002; Meyer and Lavergne, 2004). O. cuspidatum represents a serious problem due to its ability to invade the understory of native forests. O. cuspidatum is included in the Global Compendium of Weeds (Randall , 2012), and it is also listed as invasive in Hawaii, French Polynesia, Samoa, the Galápagos Islands, and Cuba (Lorence et al., 1995; Meyer and Lavergne, 2004; Oviedo Prieto et al., 2012; PIER, 2014). It is considered as potentially invasive in Puerto Rico (Rojas-Sandoval and Acevedo-Rodríguez, unpublished data).
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Scrophulariales
- Family: Acanthaceae
- Genus: Odontonema
- Species: Odontonema cuspidatum
Notes on Taxonomy and Nomenclature
Top of page
The family Acanthaceae includes about 221 genera and 4000 species widespread in both New and Old World Tropics (Scotland and Vollesen, 2000; Stevens, 2012). Species within this family are herbs or woody shrubs, lianas and trees. Member of the Acanthaceae may be recognized by their fruit: a few-seeded, explosively dehiscent capsule within which seeds are borne on hook-like structures called retinacula (the lignified derivatives of the funiculus) (McDade et al., 2008).
The genus Odontonema is native to the New World and includes about 20-30 species distributed in Mexico, Central and South America and the Caribbean (Daniel, 1995). Several Odontonema species are commonly cultivated as ornamentals in nurseries, greenhouses, and gardens in tropical and subtropical regions (Daniel, 1995; Francis, 2005).
Francis (2005) lists Odontonema tubiforme (Bertol.) Kuntze as a synonym of O. cuspidatum, and states that some authors propose separating O. cuspidatum and O. tubiforme into individual species or using only the name O. tubiforme. The ITIS database, however, says that I. tubiforme is an orthographic variant (misspelling) of the accepted species Odontonema tubaeforme (Bertol.) Kuntze. Odontonema strictum has been listed by various authorities as a synonym of both O. cuspidatum and O. tubaeforme.
Distribution
Top of pageO. cuspidatum is native to Mexico (Daniel, 1995; USDA-ARS, 2014). It has been widely cultivated as an ornamental and can now be found naturalized in the southern United States (Florida), Central and South America, West Indies and several islands in the Pacific Ocean (see distribution table for details, Daniel 1995, 2001, 2005; PIER, 2014; USDA-ARS, 2014).
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 |
|||||||
Tanzania | Present | Introduced | Cultivated as ornamental | ||||
Asia |
|||||||
India | Present | Present based on regional distribution. | |||||
-Maharashtra | Present | Introduced | |||||
Singapore | Present | Introduced | Cultivated | ||||
North America |
|||||||
Costa Rica | Present | Introduced | Cultivated/escaped | ||||
Cuba | Present | Introduced | Invasive | Reported for this island as Odontonema strictum | |||
Dominican Republic | Present | Introduced | |||||
El Salvador | Present | Introduced | |||||
Haiti | Present | Introduced | |||||
Honduras | Present | Introduced | Naturalized | Cultivated/naturalized | |||
Martinique | Present | Introduced | |||||
Mexico | Present | Native | |||||
Panama | Present | Introduced | |||||
Puerto Rico | Present | Introduced | Potentially invasive | ||||
Saint Lucia | Present | Introduced | Naturalized | Escaped/naturalized | |||
United States | Present | Present based on regional distribution. | |||||
-Florida | Present | Introduced | Escaped from cultivation | ||||
-Hawaii | Present | Introduced | Invasive | ||||
Oceania |
|||||||
American Samoa | Present | Introduced | Invasive | ||||
French Polynesia | Present | Introduced | Invasive | ||||
Marshall Islands | Present | Introduced | Cultivated | ||||
Samoa | Present | Introduced | Invasive | Original citation: Space and Flynn (2002) | |||
South America |
|||||||
Ecuador | Present | Introduced | |||||
-Galapagos Islands | Present | Introduced | Invasive | ||||
Paraguay | Present | Introduced |
History of Introduction and Spread
Top of pageAccording to Meyer and Lavergne (2004), O. cuspidatum (under the name O. strictum) was first collected in 1927 in Tahiti (French Polynesia) and in 1937 in Hawaii. Wagner et al. (1990) reported this species for Hawaii (under the name O. strictum) as “sometimes observed in disturbed areas” and concluded that the species “does not appear to be naturalized”. In the website treatment for the flora of Hawaii, Wagner et al. (2005) correct the name of the Hawaiian plants to O. cuspidatum and report the species as naturalized. In the West Indies, the occurrence of O. cuspidatum was reported as early as 1900 for Cuba (Urban, 1901). In 1925, Britton and Wilson reported O. cuspidatum as a strictly garden plant. By 1997, O. cuspidatum was reported as escaped (Liogier, 1997) in Puerto Rico, and in 1999 Acevedo-Rodríguez and Axelrod reported it as an “aggressive exotic, very common in the understory of secondary forests and plantations” for areas of the Rio Abajo Forest Reserve. Currently, O. cuspidatum is widespread along roadsides and understory of secondary forest in numerous localities across Puerto Rico and in areas of the El Yunque National Forest (Acevedo- Rodríguez unpublished data). In the Dominican Republic O. cuspidatum is known to occur since 1921 as a roadside plant (US Herbarium Collection). The species is considered as escaped in the most recent flora of Hispaniola (Liogier, 1995). In summary, these sources indicate that O. cuspidatum has the capacity of becoming naturalized and abundant in a relatively short period of time after being introduced as a garden plant.
Risk of Introduction
Top of pageThe risk of introduction of O cuspidatum is high. It has been widely cultivated as an ornamental in tropical and subtropical regions of the world where it has escaped and become naturalized in natural habitats (Daniel, 1995; Lorence et al., 1995; Meyer and Lavergne 2004; Liogier, 1995, 1997). The ability of this species to tolerate shaded conditions and spread vegetatively by root-suckers means that it has a high potential to colonize new areas and spread much further than it has to date (Meyer and Lavergne, 2004).
Habitat
Top of pageO. cuspidatum can be found naturalized in wet open areas, secondary forests, forest edges, along roadsides, lowland rainforests, montane forests, pine-oak forests, and cloud forests from sea level to 1950 m (Lorence et al., 1995; Space and Flynn, 2002; Meyer and Lavergne, 2004; PIER, 2014). Because it is shade tolerant, it is able to colonize the understory of both disturbed and mature forests (Space and Flynn, 2002; Meyer and Lavergne, 2004).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
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 | Natural |
Terrestrial | Managed | Rail / roadsides | Present, no further details | Productive/non-natural |
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 | Natural forests | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | Natural |
Biology and Ecology
Top of pageGenetics
The chromosome number for the species O. cuspidatum is unknown. However, for the genus Odontonema the chromosome number reported is n=21 (Daniel, 1995).
Reproductive Biology
Flowers in O. cuspidatum are heterostylous and require specialized pollinators to set fruits. Within its native distribution range, it is visited and possibly pollinated by hummingbirds (Daniel, 1995).
Physiology and Phenology
In warm and moist climates, O. cuspidatum has been reported flowering and fruiting throughout the year (Daniel, 1995), but in temperate climates it flowers in the autumn (Watkins, 1975; Francis, 2005).
Environmental Requirements
O. cuspidatum grows best on fertile and moderately fertile soils, with neutral pH, that are continually moist. It is shade tolerant but does not tolerate salty soils or freezing conditions and plants generally die if the ground is frozen (Watkins, 1975; Francis, 2005). O. cuspidatum grows in wet, montane, rain, and cloud forests from sea level to 1950 m in elevation (Daniel, 1995).
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
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 | 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]) | |
Cs - Warm temperate climate with dry summer | Tolerated | Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers | |
Cw - Warm temperate climate with dry winter | Tolerated | Warm temperate climate with dry winter (Warm average temp. > 10°C, Cold average temp. > 0°C, dry winters) |
Air Temperature
Top of pageParameter | Lower limit | Upper limit |
---|---|---|
Absolute minimum temperature (ºC) | -1 | |
Mean annual temperature (ºC) | 10 | 35 |
Notes on Natural Enemies
Top of pageThe cucumber mosaic virus (CMV) has been recorded on leaves of O. cuspidatum plants (Baker et al., 2012). Plants can also be attacked by mealy bugs belonging to the genus Pseudococcidae (Francis, 2005).
Means of Movement and Dispersal
Top of pageO. cuspidatum spreads by seeds and vegetatively by stem segments or root-suckers. Seeds are produced in capsules that fall off before drying, liberating the seeds (Francis, 2005). In Puerto Rico, although O. cuspidatum is common, plants produce few viable seeds and most of the stands of this species have originated from abandoned gardens or stem segments and/or roots that have been transported by streams or dumped in the woods with garden disposals. Once established, O. cuspidatum spreads mostly by root suckers. The stems also layer (root) easily when they become prostrate (Francis, 2005).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Escape from confinement or garden escape | Commonly cultivated as ornamental | Yes | Yes | Daniel (1995) |
Garden waste disposal | Stems and roots | Yes | Yes | Francis (2005) |
Horticulture | Commonly cultivated as ornamental | Yes | Yes | Daniel (1995) |
Nursery trade | Yes | Daniel (1995) | ||
Ornamental purposes | Yes | Yes | Daniel (1995) |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Debris and waste associated with human activities | Pieces of stems and roots from gardens | Yes | Yes | Francis (2005) |
Land vehicles | Pieces of stems and roots from gardens | Yes | Yes | Francis (2005) |
Machinery and equipment | Pieces of stems and roots from gardens | Yes | Yes | Francis (2005) |
Soil, sand and gravel | Pieces of stems and roots from gardens | Yes | Yes | Francis (2005) |
Water | Stems and roots may be transported by steams | Yes | Yes | Francis (2005) |
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Positive and negative |
Environment (generally) | Positive and negative |
Environmental Impact
Top of pageO. cuspidatum is an aggressive species that can grow forming dense thickets in the understory of secondary and relatively unaltered forests. For example, Meyer and Lavergne (2004) reported dense monospecific stands of this species (between 100 m2 and 500 m2) in the understory of secondary low- and mid-elevation wet forest in Hawaii, Tahiti, and Samoa; a similar pattern has been reported for Puerto Rico (Acevedo-Rodríguez and Axelrod, 1999). O. cuspidatum is also invading native montane rainforest in Tahiti (Meyer and Lavergne, 2004). In Cuba, O. cuspidatum is listed as one of the 100 most noxious plants invading natural habitats (Oviedo Prieto et al., 2012).
Risk and Impact Factors
Top of page- Proved invasive outside its native range
- Abundant in its native range
- Highly adaptable to different environments
- Is a habitat generalist
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
- Tolerant of shade
- Highly mobile locally
- Benefits from human association (i.e. it is a human commensal)
- Long lived
- Fast growing
- Reproduces asexually
- Ecosystem change/ habitat alteration
- Monoculture formation
- Reduced native biodiversity
- Threat to/ loss of native species
- Competition - monopolizing resources
- Competition - smothering
- Pest and disease transmission
- Rapid growth
- Rooting
- Highly likely to be transported internationally deliberately
- Difficult to identify/detect in the field
Uses
Top of pageO. cuspidatum is an economically important species in the horticultural and nursery trade. It is widely cultivated as an ornamental in tropical and subtropical areas for its conspicuous red flowers (Watkins, 1975; Daniel, 1995; Francis, 2005). It is also popular in gardens because it attracts butterflies and hummingbirds that feed on the nectar (Watkins, 1975).
Uses List
Top of pageAnimal feed, fodder, forage
- Invertebrate food
Ornamental
- Potted plant
- Propagation material
- Seed trade
References
Top of pageAcevedo-Rodríguez P; Strong MT, 2012. Catalogue of the Seed Plants of the West Indies. Smithsonian Contributions to Botany, 98:1192 pp. Washington DC, USA: Smithsonian Institution. http://botany.si.edu/Antilles/WestIndies/catalog.htm
Britton NL; Wilson P, 1925. Botany of Porto Rico and the Virgin Islands. Scientific Survey of Porto Rico & Virgin Islands, Volume 6
Brunken U; Schmidt M; Dressler S; Janssen T; Thiombiano A; Zizka G, 2008. West African plants - A Photo Guide. Frankfurt/Main, Germany: Forschungsinstitut Senckenberg. www.westafricanplants.senckenberg.de
Chong KY; Tan HTW; Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species., Singapore: Raffles Museum of Biodiversity Research, National University of Singapore, 273 pp.
Daniel TF, 1995. Revision of Odontonema (Acanthaceae) in Mexico. Contributions of the University of Michigan Herbarium, 20:147-171.
Daniel TF, 2001. Catalog of Acanthaceae in El Salvador. Contributions from the University of Michigan Herbarium, 23:115-137.
Daniel TF, 2010. Catalog of Guatemalan Acanthaceae: taxonomy, ecology, and conservation. Proceedings of the California Academy of Science, 61:289-377.
Daniel TF; McDade LA, 1995. Additions to the Acanthaceae of Panama. Annals of the Missouri Botanical Garden, 82:542-548.
Florence J; Chevillotte H; Ollier C; Meyer J-Y, 2013. Base de données botaniques Nadeaud de l'Herbier de la Polynésie Française (PAP) (Botanical database of the Nadeaud Herbarium of French Polynesia). http://www.herbier-tahiti.pf
Francis JK, 2005. Odontonema cuspidatum (Nees) Kuntze. Wildland Shrubs of the United States and its Territories: Thamnic Descriptions. General Technical Report IITF-WB-1. U.S. Department of Agriculture, Forest Service International Institute of Tropical Forestry and Shrub Sciences Laboratory. http://www.fs.fed.us/global/iitf/pdf/shrubs/Odontonema%20cuspidatum.pdf
Graveson R, 2012. The Plants of Saint Lucia (in the Lesser Antilles of the Caribbean). The Plants of Saint Lucia (in the Lesser Antilles of the Caribbean). http://www.saintlucianplants.com
Guézou A; Trueman M; Buddenhagen E; Chamorro S; Guerrero AM; Pozo P; Atkinson R, 2010. An extensive Alien Plan Inventory from the Inhabited Areas of Galapagos. Plos One, 5(4):e10276.
INBio, 2014. PLANTAE Database., Costa Rica: Instituto Nacional de Biodiversidad de Costa Rica. http://www.inbio.ac.cr/bims/PLANTAE.html
Jogdand VR; Dhabe AS, 2013. Odontonema cuspidatum (Nees) Kuntze (Acanthaceae): Addition to exotic record for Maharashtra. BIOINFOLET-A Quarterly Journal of Life Sciences, 10:1098-1099.
Liogier AH, 1995. La Flora de La Española. VII ([English title not available]). San Pedro de Macoris, Dominican Republic: Ediciones de la UCE, 491 pp.
Liogier HA, 1997. Descriptive flora of Puerto Rico and adjacent Islands: Spermatophyta-Dicotyledoneae Vol. 5: Acanthaceae to Compositae. Puerto Rico: Editorial de la Universidad de Puerto Rico.
Oviedo Prieto R; Herrera Oliver P; Caluff MG, et al. , 2012. National list of invasive and potentially invasive plants in the Republic of Cuba - 2011. (Lista nacional de especies de plantas invasoras y pontencialmente invasoras en la República de Cuba - 2011.) Bissea: Boletín sobre Conservación de Plantad del Jardín Botánico Nacional de Cuba, 6(Special Issue 1):24-96.
PIER, 2014. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
PROTA, 2014. PROTA4U web database. Grubben GJH, Denton OA, eds. Wageningen, Netherlands: Plant Resources of Tropical Africa. http://www.prota4u.org/search.asp
Randall RP, 2012. A Global Compendium of Weeds. Perth, Australia: Department of Agriculture and Food Western Australia, 1124 pp. http://www.cabi.org/isc/FullTextPDF/2013/20133109119.pdf
Scotland RW; Vollesen K, 2000. Classification of Acanthaceae. Kew Bulletin, 55:513-589.
Space JC; Flynn T, 2000. Observations on invasive plant species in American Samoa. USDA Forest Service, Honolulu, 51.
Space JC; Flynn T, 2002a. Report to the Government of Samoa on invasive plant species of environmental concern. Honolulu, USA: USDA Forest Service, 83 pp.
Stevens PF, 2012. Angiosperm Phylogeny Website. http://www.mobot.org/MOBOT/research/APweb/
Urban I, 1901. Symbolae Antillanae. Volumen II. Lipsiae, Germany: Fratres Borntraeger, 860 pp.
USDA-ARS, 2014. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx
Vander VN, 2003. The vascular plants of Majuro Atoll, Republic of the Marshall Islands. Atoll Research Bulletin, 503:1-141.
Wagner WL; Herbst DR; Sohmer SH, 1990. Manual of Flowering Plants of Hawaii. Bernice Pauahi Bishop Museum Special Publication 83. Honolulu, Hawaii, USA: University of Hawaii.
Watkins JV, 1975. Florida landscape plants, native and exotic. Gainesville, FL., USA: The University Presses of Florida, 420 pp.
Wunderlin RP; Hansen BF, 2008. Atlas of Florida Vascular Plants. Florida, USA: University of South Florida. http://www.plantatlas.usf.edu/
Zuloaga FO; Morrone O; Belgrano MJ, 2008. Catálogo de las Plantas Vasculares del Cono Sur: (Argentina, Sur de Brasil, Chile, Paraguay y Uruguay) ([English title not available])., USA: Missouri Botanical Garden Press, 3348 pp.
Distribution References
Brunken U, Schmidt M, Dressler S, Janssen T, Thiombiano A, Zizka G, 2008. West African plants - A Photo Guide., Frankfurt/Main, Germany: Forschungsinstitut Senckenberg. http://www.westafricanplants.senckenberg.de
CABI, Undated. Compendium record. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
Chong KY, Tan HTW, Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species., Singapore, Raffles Museum of Biodiversity Research, National University of Singapore. 273 pp.
Daniel TF, McDade LA, 1995. Additions to the Acanthaceae of Panama. In: Annals of the Missouri Botanical Garden, 82 542-548.
Florence J, Chevillotte H, Ollier C, Meyer J-Y, 2013. Nadeaud botanical database of the Herbarium of French Polynesia. (Base de données botaniques Nadeaud de l'Herbier de la Polynésie Française (PAP))., https://nadeaud.ilm.pf/
Graveson R, 2012. The Plants of Saint Lucia (in the Lesser Antilles of the Caribbean)., http://www.saintlucianplants.com
INBio, 2014. PLANTAE Database., Costa Rica: Instituto Nacional de Biodiversidad de Costa Rica. http://www.inbio.ac.cr/bims/PLANTAE.html
Jogdand VR, Dhabe AS, 2013. Odontonema cuspidatum (Nees) Kuntze (Acanthaceae): Addition to exotic record for Maharashtra. In: BIOINFOLET-A Quarterly Journal of Life Sciences, 10 1098-1099.
PIER, 2014. Pacific Islands Ecosystems at Risk., Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Space JC, Flynn T, 2000. Observations on invasive plant species in American Samoa. In: USDA Forest Service, Honolulu, USDA Forest Service. 51.
USDA-ARS, 2014. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysimple.aspx
Vander VN, 2003. The vascular plants of Majuro Atoll, Republic of the Marshall Islands. In: Atoll Research Bulletin, 503 1-141.
Wunderlin RP, Hansen BF, 2008. Atlas of Florida Vascular Plants., Florida, USA: University of South Florida. http://www.plantatlas.usf.edu/
Zuloaga FO, Morrone O, Belgrano MJ, 2008. [English title not available]. (Catálogo de las Plantas Vasculares del Cono Sur: (Argentina, Sur de Brasil, Chile, Paraguay y Uruguay))., USA: Missouri Botanical Garden Press. 3348 pp.
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. |
Wildland shrubs of the United States and its territories | http://www.fs.fed.us/global/iitf/wildland_shrubs.htm |
Contributors
Top of page05/03/14 Original text by:
Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH, Washington DC, USA
Pedro Acevedo-Rodríguez, Department of Botany-Smithsonian NMNH, Washington DC, USA
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