Skip the header
Open access
Datasheet
Enhanced
11 January 2017

Hemigraphis alternata (red ivy)

Datasheet Type: Invasive species

Abstract

This datasheet on Hemigraphis alternata covers Identity, Overview, Distribution, Dispersal, Diagnosis, Biology & Ecology, Environmental Requirements, Natural Enemies, Impacts, Uses, Prevention/Control, Further Information.

Identity

Preferred Scientific Name
Hemigraphis alternata (Burm.f.) T. Anderson
Preferred Common Name
red ivy
Other Scientific Names
Blechum cordatum Leonard
Goldfussia colorata (Blume) Moritzi
Hemigraphis colorata (Blume) Hallier f.
Ruellia alternata Burm.f.
Ruellia colorata Blume
International Common Names
English
cemetery plant
metal leaf
red flame ivy
redivy
Spanish
cucaracha
Local Common Names
Australia
purple waffle plant
India
murian pacha
murikootti
Puerto Rico
Asia negra
USA
red-flame ivy

Summary of Invasiveness

Hemigraphis alternata is a creeping herb native to Indonesia and Malaysia that has been widely commercialized as an ornamental, mainly due to its metallic green and purple foliage. It is often planted as a carpet plant or ground cover in gardens, and is regularly dumped in garden waste, from which it spreads into wild areas. Once established, the species grows forming large dense carpets that totally cover the understorey of natural forests, displacing native vegetation. In areas outside its native range, it seems to reproduce only by vegetative means (cuttings or clump division). It is currently listed as invasive in the Dominican Republic, Hawaii, Fiji, Chagos, Reunion, Cook Islands, Samoa, French Polynesia, Niue, Palau and Tonga.

Taxonomic Tree

This content is currently unavailable.

Notes on Taxonomy and Nomenclature

Acanthaceae is a family of flowering plants comprising 220 genera and at least 4000 species of herbs, shrubs and trees (rarely vines, except Thunbergia and Mendoncia, which are almost entirely climbing plants) distributed mostly across the tropics (McDade et al., 2009; Stevens, 2012). The genus Hemigraphis (20-60 species) is classified within the subfamily Acanthoideae. Species in this subfamily are usually herbs and can be recognized by their often swollen nodes, the stem immediately above them collapsing on drying, and the opposite leaves (Stevens, 2012).

Plant Type

Broadleaved
Herbaceous
Perennial
Seed propagated
Vegetatively propagated

Description

Ascending or creeping herb, the stems pilosulous, rooting at the lower nodes. Leaves on petioles 1-5 cm long, the blades mostly 3-6 cm long, 2-5 cm wide, broadly ovate to ovate-oblong, acute or obtuse, cordate at base, densely puberulent, sparingly pilosulous or glabrate, the margins crenate. Inflorescences are axillary spikes on a peduncle to 1.5 cm long and 1 cm wide. Flowers generally two per bract, the calyx segments slightly unequal, linear subulate, up to 9 mm long, peeled, ciliate; corolla white, about 1.5 cm long; capsule slender; seeds 4-20 (Standley et al., 1974; Flora of Panama, 2016; PIER, 2016).

Distribution

H. alternata is native to Indonesia and Malaysia (Meyer and Lavergne, 2004; USDA-ARS, 2016). It has been widely commercialized and introduced as an ornamental plant into tropical and subtropical countries across Asia, America, the Caribbean and into many islands in the Indian and Pacific Ocean (Daniel, 2001; 2005; Meyer and Lavergne, 2004Acevedo-Rodríguez and Strong, 2012; PIER, 2016). After escaping from cultivation, the species has become naturalized and invasive in many areas, primarily on islands in the Indian and Pacific region (PIER, 2016). 
H. alternata was first introduced to Reunion in 1862 and to Fiji in 1928 (Meyer and Lavergne, 2004). The species is also spreading in Hawaii, where a herbarium collection states that it was introduced in 1927 (Wagner et al., 1999). Large dense carpets that totally cover the ground in the understorey of low- and mid-elevation secondary wet forests, have been reported on the islands of Niue, Samoa and Tahiti (Meyer and Lavergne, 2004).
In Honduras, El Salvador, Panama and Nicaragua, H. alternata is also reported as an ornamental species that has escaped from cultivation and is now becoming naturalized and spreading across natural areas, disturbed sites and along trails and roads (Daniel 2001, 2005; Correa et al., 2004).

Distribution Map

This content is currently unavailable.

Distribution Table

This content is currently unavailable.

Risk of Introduction

The risk of introduction of H. alternata is high, mainly because the species is widely commercialized as an ornamental plant due to its metallic green and purple foliage. Stems and plant fragments are regularly dumped in garden waste, from where it can spread into new areas (University of Queensland, 2016).

Means of Movement and Dispersal

In areas outside its native range, H. alternata rarely produces fruits, mainly spreading vegetatively by cuttings or clump division (Rauch and Hensley, 1997; Meyer and Lavergne, 2004; PIER, 2016).

Pathway Causes

Pathway causeNotesLong distanceLocalReferences
Disturbance (pathway cause)Naturalized along roads and trailsYesYes
Escape from confinement or garden escape (pathway cause)Garden waste dumpingYesYes
Horticulture (pathway cause)Widely commercialized as ornamentalYesYes
Intentional release (pathway cause)Widely commercialized as ornamentalYesYes
Ornamental purposes (pathway cause)Often planted as ornamental and as ground cover in gardensYesYes

Pathway Vectors

Pathway vectorNotesLong distanceLocalReferences
Debris and waste associated with human activities (pathway vector)Stem fragments dumped in garden wasteYesYes

Similarities to Other Species/Conditions

H. alternata looks similar to H. reptans, but they can be distinguished by the following traits:
H. alternata is a creeping herb with purple, narrow, cordate leaves 3.5-15 cm long, 1.6-6 cm wide, and white flowers in terminal spikes;
H. reptans has green leaves with blades elliptic to narrowly ovate, 4-15 cm long, 1.6-4.3 cm wide, and yellowish or white flowers (Wagner et al., 1999).

Habitat

In Saint Lucia, the species is a naturalized herb of wet roadsides and wet open areas (Graveson, 2012). In other countries, it spreads across natural areas, disturbed sites and along trails and roads (Daniel 2001; 2005; Correa et al., 2004). 

Biology and Ecology

Physiology and Phenology

H. alternata is a perennial fast-growing herb (Daniel, 2005). The species roots readily from stem cuttings in 7-10 days (Rauch and Hensley, 1997).

Environmental Requirements

H. alternata grows best in light or medium shade. It prefers slightly acid and moist soils, with pH ranging from 6.1 to 7.5. It does not tolerate drought or salty conditions (Rauch and Hensley, 1997).

Climate

Climate typeDescriptionPreferred or toleratedRemarks
Af - Tropical rainforest climate> 60mm precipitation per monthPreferred 
Am - Tropical monsoon climateTropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25]))Preferred 
As - Tropical savanna climate with dry summer< 60mm precipitation driest month (in summer) and < (100 - [total annual precipitation{mm}/25])Preferred 
Aw - Tropical wet and dry savanna climate< 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25])Preferred 

Latitude/Altitude Ranges

Latitude North (°N)Latitude South (°S)Altitude lower (m)Altitude upper (m)
3015  

Air Temperature

ParameterLower limit (°C)Upper limit (°C)
Mean annual temperature1730

Rainfall

ParameterLower limitUpper limitDescription
Dry season duration  number of consecutive months with <40 mm rainfall
Mean annual rainfall1500 mm3000 mmmm; lower/upper limits

Soil Tolerances

Soil texture > light
Soil texture > medium
Soil reaction > neutral
Soil drainage > free

Notes on Natural Enemies

Mealybugs can attack H. alternata. The following fungi have also been found associated with this species: Alternaria spp., Colletotrichum spp., Curvularia spp., Pythium spp., Rhizoctonia solani [Thanatephorus cucumeris], Sclerotinia sclerotiorum and Sclerotium rolfsii [Athelia rolfsii] (Rauch and Hensley, 1997; Cool Garden, 2016; PIER, 2016). 

Natural enemies

Natural enemyTypeLife stagesSpecificityReferencesBiological control inBiological control on
ColletotrichumPathogen
Whole plant
not specific   
Curvularia (black kernel)Pathogen
Whole plant
not specific   
PythiumPathogen
Whole plant
not specific   
Thanatephorus cucumeris (many names, depending on host)Pathogen
Whole plant
not specific   
Sclerotinia sclerotiorum (cottony soft rot)Pathogen
Whole plant
not specific   
Athelia rolfsii (sclerotium rot)Pathogen
Whole plant
not specific   

Impact Summary

CategoryImpact
 Positive and negative
 Positive

Impact: Environmental

H. alternata grows by forming large dense mats in the understorey of native forests, inhibiting the establishment of seedlings and young plants of native species, completely outcompeting them (Meyer and Lavergne, 2004; Mir, 2012; PIER, 2016). 
In northern Queensland, Australia, H. alternata is regarded as an emerging environmental weed, capable of invading the understorey of wet forests in warm climates (University of Queensland, 2016).
On several islands in the Pacific, H. alternata has been reported forming large mats of vegetation in disturbed sites and in areas close to forests. For example, in Niue and Fiji, it spreads along trails, roads and in secondary forests. In American Samoa, it has become naturalized at several locations, including conservation areas and national parks, where it forms dense low stands that outcompete native species (Meyer and Lavergne, 2004; PIER, 2016).

Risk and Impact Factors

Invasiveness

Proved invasive outside its native range
Highly adaptable to different environments
Is a habitat generalist
Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
Pioneering in disturbed areas
Tolerant of shade
Highly mobile locally
Benefits from human association (i.e. it is a human commensal)
Long lived
Fast growing
Gregarious
Reproduces asexually

Impact outcomes

Ecosystem change/ habitat alteration
Modification of successional patterns
Monoculture formation
Reduced native biodiversity
Threat to/ loss of native species

Impact mechanisms

Competition - monopolizing resources
Competition - smothering
Rapid growth
Rooting

Likelihood of entry/control

Highly likely to be transported internationally deliberately

Uses

Economic Value

 H. alternata is widely commercialized as an ornamental indoor and outdoor plant. It is often planted in gardens, hanging baskets and used as ground cover in gardens (Rauch and Hensley, 1997; Priya, 2013; USDA-ARS, 2016).

Social Benefit

H. alternata is used in traditional Asian medicine to cure anaemia, treat bloody dysentery and haemorrhoids, and to mend gallstones. It is also used as a contraceptive and a means of inducing sterility (Priya, 2013).

Uses List

Environmental > Amenity
Medicinal, pharmaceutical > Traditional/folklore
Ornamental > Propagation material
Ornamental > Potted plant
Ornamental > garden plant

Prevention and Control

Due 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.
Control
Chemical control

An ornamental herbicide with the active constituents oxyfluorfen and oryzalin has been tested to control H. alternata, but the species appears to be tolerant to different concentrations of this herbicide. Only slight injury symptoms of irregular necrotic spots, not enough to cause death, were reported (PIER, 2016). 

Links to Websites

NameURLComment
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gatewayhttps://doi.org/10.5061/dryad.m93f6Data source for updated system data added to species habitat list.

References

Acevedo-Rodríguez P, Strong MT, 2012. Catalogue of seed plants of the West Indies. Smithsonian Contributions to Botany, 98: 1-1192. Washington DC, USA: Smithsonian Institution.
Balick MJ, Nee MH, Atha DE, 2000. Checklist of the vascular plants of Belize. Memoirs of The New York Botanical Garden, 85: 1-246.
Brundu, G., Camarda, I., 2004. The exotic flora of Chad: a first contribution.Weed Technology, 18Suppl.1226-1231.
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.
Cool Garden, 2016. Growing Hemigraphis. http://www.coolgarden.me/growing-hemigraphis-2555/
Correa AMD, Galdames C, Stapf M, 2004. Catalogue of the vascular plants of Panama. (Catalogo de las plantas vasculares de Panamá). Panama: Smithsonian Tropical Research Institute, 599 pp.
Daniel, T. F., 2001. Catalog of Acanthaceae in El Salvador.Contributions from the University of Michigan Herbarium, 23115-137.
Daniel, T. F., 2005. Catalog of Honduran Acanthaceae with taxonomic and phytogeographic notes.Contributions from the University of Michigan Herbarium, 2451-108.
Flora Mesoamericana, 2015. Flora Mesoamericana. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/Project/fm
Flora of Panama, 2016. Flora of Panama (WFO), Tropicos website. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.tropicos.org/Project/FOPWFO
Graveson R, 2012. Plants of Saint Lucia: a pictorial flora of wild and cultivated vascular plants. http://www.saintlucianplants.com
Hokche O, Berry PE, Huber O, 2008. New catalogue of vascular flora of Venezuela. (Nuevo catalogo de flora vascular de Venezuela.) Caracas, Venezuela: Fundación Instituto Botánico de Venezuela, 859 pp.
Idárraga-Piedrahita A, Ortiz RDC, Callejas Posada R, Merello M, 2011. Flora of Antioquia. Catalogue of the vascular plants, Volume 2. List of the vascular plants of the Department of Antioquia. (Flora de Antioquia. Catálogo de las plantas vasculares, Volume 2. Listado de las plantas vasculares del Departamento de Antioquia). Medellín, Colombia: Universidad de Antioquia, 939 pp.
India Biodiversity Portal, 2016. Online Portal of India Biodiversity. http://indiabiodiversity.org/species/
Jørgensen PM, Nee MH, Beck SG, 2014. Catalogue of the vascular plants of Bolivia. (Catálogo de las plantas vasculares de Bolivia). Monographs in systematic botany from the Missouri Botanical Garden, 127: 1-1744.
McDade LA, Kiel C, Tripp E, 2009. Acanthaceae. The Tree of Life Web Project. http://tolweb.org/Acanthaceae/20878/2009.11.15
Meyer, J. Y., Lavergne, C., 2004. Beautés fatales: Acanthaceae species as invasive alien plants on tropical Indo-Pacific islands.Diversity and Distributions, 10(5/6) 333-347.
Mir C, 2012. [English title not available]. (Estrategia Nacional de especies exóticas invasoras realizado en el marco del Proyecto “Mitigando las amenazas de las especies exóticas invasoras en el Caribe Insular”). Dominican Republic: Ministerio de Medio Ambiente y Recursos Naturales Santo Domingo.
PIER, 2016. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Priya, M. D., 2013. Review on pharmacological activity of Hemigraphis colorata (Blume) H. G. Hallier.International Journal of Herbal Medicine, 1(3) 120-121. http://florajournal.com/vol1issue3/aug2013/1.1.pdf
Rauch FD, Hensley D, 1997. Hemigraphis. Cooperative Extension Service. Manoa, Hawaii, USA: College of Tropical Agriculture and Human Resources, University of Hawaii at Manoa. http://www.ctahr.hawaii.edu/oc/freepubs/pdf/of-7.pdf
Smith, A. C., 1991. Flora Vitiensis nova: a new flora of Fiji (Spermatophytes only). Volume 5: Angiospermae: Dicotyledones, families 170-186, Moncotyledones, Family 32, addenda et corrigenda, index. In: Flora Vitiensis nova: a new flora of Fiji (Spermatophytes only). Volume 5: Angiospermae: Dicotyledones, families 170-186, Moncotyledones, Family 32, addenda et corrigenda, index.Pacific Tropical Botanical Garden. iii + 626 pp.
Space JC, Flynn T, 2000. Observations on invasive plant species in American Samoa. Honolulu, Hawaii, USA: USDA Forest Service, 51 pp.
Space JC, Flynn T, 2001. Report to the Kingdom of Tonga on invasive plant species of environmental concern. Honolulu, Hawaii, USA: USDA Forest Service, 78 pp.
Space JC, Flynn T, 2002. Report to the Government of the Cook Islands on invasive plant species of environmental concern. Honolulu, Hawaii, USA: USDA Forest Service, 146 pp.
Space JC, Waterhouse B, Miles JE, Tiobech J, Rengulbai K, 2003. Report to the Republic of Palau on invasive plant species of environmental concern. Honolulu, Hawaii, USA: USDA Forest Service, 174 pp.
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. UNDP NIU/98/G31 - Niue Enabling Activity, 80 pp.
Standley, P. C., Williams, L. O., Gibson, D. N., 1974. Flora of Guatemala.Fieldiana: Botany, 24Part X, No. 3/4153-466.
Stevens PF, 2012. Angiosperm Phylogeny Website. St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.mobot.org/MOBOT/research/APweb/
Swarbrick JT, 1997. Environmental weeds and exotic plants on Christmas Island, Indian Ocean: a report to Parks Australia. Australia: Weed Science Consultancy, 131 pp.
Thaman RR, Fosberg FR, Manner HI, Hassall DC, 1994. The flora of Nauru. Atoll Research Bulletin, 392:1-223.
USDA-ARS, 2016. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, USA: National Germplasm Resources Laboratory. http://www.ars-grin.gov/cgi-bin/npgs/html/tax_search.pl
USDA-NRCS, 2016. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. https://plants.usda.gov/java/
University of Queensland, 2016. Weeds of Australia. Biosecurity Queensland Edition. Australia: University of Queensland. http://keyserver.lucidcentral.org/weeds/data/media/Html/index.htm
Wagner, W. L., Herbst, D. R., Sohmer, S. H., 1999. Manual of the flowering plants of Hawai'i, Vols. 1 & 2, Revised editionUniversity of Hawai'i Press/Bishop Museum Press. 1918 + [1] pp.
Whistler WA, 1996. Botanical survey of Diego Garcia, Chagos Archipelago, British Indian Ocean Territory. Isle Botanica, 49 pp. http://www.zianet.com/tedmorris/dg/2005NRMP-Appendixe-botanicalsurvey.pdf

Information & Authors

Information

Published In

History

Published online: 11 January 2017

Language

English

Authors

Affiliations

Metrics & Citations

Metrics

VIEW ALL METRICS

SCITE_

Citations

Export citation

Select the format you want to export the citations of this publication.

EXPORT CITATIONS

View Options

View options

Login Options

Restore your content access

Enter your email address to restore your content access:

Note: This functionality works only for purchases done as a guest. If you already have an account, log in to access the content to which you are entitled.

Media

Figures

Other

Tables

Share

Share

Copy the content Link

Share on social media

Related Articles

Skip the navigation