Abelmoschus moschatus (musk mallow)
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
- Biology and Ecology
- Climate
- Latitude/Altitude Ranges
- Air Temperature
- Rainfall
- Rainfall Regime
- Soil Tolerances
- Natural enemies
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Impact
- Economic Impact
- Risk and Impact Factors
- Uses
- Uses List
- References
- Contributors
- Distribution Maps
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Top of pageIdentity
Top of pagePreferred Scientific Name
- Abelmoschus moschatus Medik.
Preferred Common Name
- musk mallow
Other Scientific Names
- Abelmoschus betulifolia Wall.
- Abelmoschus chinensis Wall.
- Abelmoschus ciliaris Walp.
- Abelmoschus cryptocarpus Walp.
- Abelmoschus cubensis Walp.
- Abelmoschus cucurbitaceus Walp.
- Abelmoschus haenkeanus C.Presl
- Abelmoschus marianus C.Presl
- Abelmoschus palustris Walp.
- Abelmoschus pseudoabelmoschus (Blume) Walp.
- Abelmoschus roseus Walp.
- Abelmoschus sublobatus C.Presl
- Hibiscus abelmoschus L.
- Hibiscus collinsianus Nutt. ex Torr. & A. Gray
- Hibiscus moschatus (Medik.) Salisb.
International Common Names
- English: annual hibiscus; musk okra; musky-seeded hibiscus; native rosella; ornamental okra; tropical jewel hibiscus
- Spanish: abelmosco; algalia; almisclillo; almisquillo; almizcle; ambarcillo
- French: ambrette; gombo musqué; graine de musc; guimauve veloutée; ketmie des marais; ketmie musquée
- Chinese: huang kui
Local Common Names
- Cuba: ambarina
- Dominican Republic: albalia; albangalia; algalia; medic
- Germany: Bisamstrauch; Eibisch, Bisam-; Eibisch, Moschus-
- Haiti: gombo marron; gumbo
- India: jangli bhindi; kaattu kasturi; kalkasturi; kasturi-dana; latakasturi; mushakdan; mushkdana
- Indonesia: gandapura; kakapasan; kasturi
- Italy: ambretta
- Lesser Antilles: gombo maudi; gombo modi
- Malaysia: kapas hantu; kapas hutan
- Myanmar: balu-wah; kon-kado; taw-wah
- Netherlands: abelmos; amberbloem; muskuszaad
- Philippines: dalupang; kastiokastiokan; kastuli
- Puerto Rico: almizcle vegetal; caballo asi; malva almizclera
- Thailand: chamot-ton; mahakadaeng; som-chaba
- Vietnam: búp vàng; cây bông vàng
EPPO code
- ABMMO (Abelmoschus moschatus)
Summary of Invasiveness
Top of pageAbelmoschus moschatus is an aromatic and medicinal plant that has been widely introduced across tropical, subtropical and temperate regions of the world. This species is regarded as a weed outside its natural habitats. It has repeatedly escaped from cultivation to become naturalized, primarily in cultivated, ruderal and semi-natural areas. Once established, it often behaves as a weed, outcompeting and displacing native plant species. A. moschatus is spread by seeds, small tubers and stem fragments and is also adapted to grow in a wide range of climates and soils types. It is native to South East Asia and Northern Australia. It is listed as invasive in many areas across the Asia-Pacific region, where it is threatening the growth and survival of native flora and fauna. It is also listed as “widespread” and “potentially invasive” on many islands in the Caribbean and has been introduced to countries in South America.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Malvales
- Family: Malvaceae
- Genus: Abelmoschus
- Species: Abelmoschus moschatus
Notes on Taxonomy and Nomenclature
Top of pageMalvaceae is a large family of flowering plants containing 243 genera and approximately 4,225 species of herbs, shrubs, and trees distributed primarily across the tropics, but with some species also occurring in subtropical and temperate regions of the world (Stevens, 2017).
Abelmoschus is a small genus comprising approximately 10-14 species native to South Asia, Australia and the Southwest Pacific (The Plant List, 2018). Several subspecies have been described in India, regions of Asia, Australia and the Pacific Islands, but the delimitation of species and other infraspecific taxa is still problematic within this genus. The species A. moschatus, A. manihot, and A. esculentus comprise wild and cultivated forms, while the remaining species are truly wild (Patil et al., 2015).
Abelmoschus moschatus is a very variable species with sub-classifications. At least three subspecies are recognized: A. moschatus ssp. moschatus, ssp. biakensis and ssp. tuberosus (Ravindran, 2017).
Description
Top of pageMuskmallow is an annual or biennial erect shrub, 1–2 m tall that has a taproot or tuberous root. The whole plant is hairy and the stem is usually solid, sometimes hollow; the shoot tip and petioles have many sharp bristles, rarely sparsely hairy or glabrous. The leaves are simple, alternate, hairy, very variable in size and shape, 6–22 cm × 8–24 cm; the lower leaves are orbicular to elliptical, with a cordate base and are palmately lobed or parted; higher leaves are usually narrower, hastate or sagitate with oblong– lanceolate lobes. The petiole is 6–30 cm long; stipules are linear–filiform and with simple hairs. Flowers are large, showy, axillary and solitary; the pedicel is 2–19 cm long. The epicalyx segments are 4–10 and may go up to 16, free, persistent, linear– lanceolate or oblong, not enveloping the entire fruit, usually acute and hairy. The calyx is spathaceous, apex five-toothed, splitting on one side during expansion of the corolla, adnate to and falling with the corolla; outside is stellate–tomentose and inside sericeous. Petals are five, obovate, yellow or rarely white to red with a crimson centre. They are scattered with gland-hairs or glabrous, apex rounded, base fleshy and ciliate with simple hairs. The staminal column is much shorter than the petals, glabrous, covered with anthers throughout, usually yellow with a dark purple base. The ovary is superior, ovoid, five-celled and hirsute, with a single style, which branches out and ends in discoid stigmas. The fruit is a dry, dehiscent capsule, many seeded, ovoid or globose, with stiff hairs, black or dark brown when dry. Seeds are reniform, 3–4.5 mm long, mostly glabrous, concentrically ribbed and somewhat warty. They are black–brown and often smell of musk (Ravindran, 2017).
Distribution
Top of pageA. moschatus is native to South East Asia and Northern Australia. It has been introduced, and can be found naturalized, across tropical Asia, Central and South America, the Caribbean, Madagascar, Europe, and on many islands in the Pacific region (Orwa et al., 2009; Sankaran and Suresh, 2013; PROSEA, 2016; GRIIS, 2018; PIER, 2018; USDA-ARS, 2018). It is cultivated in Java, India, Madagascar and in parts of South America. In India the area under cultivation is increasing and seeds are exported to France, Germany, Japan, Singapore and Spain for oil extraction, which is highly valued in perfumery and in aromatherapy (Ravindran, 2017).
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 |
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Madagascar | Present | Introduced | |||||
Seychelles | Present | Introduced | |||||
Asia |
|||||||
Bangladesh | Present | Native | |||||
Bhutan | Present | Introduced | 2011 | ||||
Cambodia | Present | Native | |||||
China | Present | Native | |||||
-Guangdong | Present | Native | |||||
-Guangxi | Present | Native | |||||
-Guizhou | Present | Native | |||||
-Hunan | Present | Native | |||||
-Jiangxi | Present | Native | |||||
-Yunnan | Present | Native | |||||
Hong Kong | Present | Native | |||||
India | Present | Native and Introduced | Has been listed as both native and introduced/invasive | ||||
-Andaman and Nicobar Islands | Present | Native | |||||
-Karnataka | Present | Original citation: India Biodiversity (2018) | |||||
-Kerala | Present | Original citation: India Biodiversity (2018) | |||||
-Tamil Nadu | Present | ||||||
Indonesia | Present | Native | |||||
-Java | Present | Introduced | |||||
Japan | Present | Introduced | Invasive | ||||
-Bonin Islands | Present | Introduced | |||||
-Ryukyu Islands | Present | Introduced | |||||
Laos | Present | Native | |||||
Malaysia | Present | Native | |||||
Maldives | Present | Introduced | |||||
Myanmar | Present | ||||||
Philippines | Present | Native and Introduced | Has been listed as both native and introduced/invasive | ||||
Singapore | Present | Introduced | Invasive | ||||
Sri Lanka | Present | Native | |||||
Taiwan | Present | Native and Introduced | Has been listed as both native and introduced/invasive | ||||
Thailand | Present | Native | |||||
Vietnam | Present | Native | |||||
Europe |
|||||||
Denmark | Present | Introduced | |||||
France | Present | Introduced | |||||
Germany | Present | Introduced | |||||
Italy | Present | Introduced | |||||
Netherlands | Present | Introduced | |||||
Russia | Present | Introduced | |||||
Spain | Present | Introduced | Naturalized | Naturalized | |||
North America |
|||||||
Barbados | Present, Widespread | Introduced | |||||
Belize | Present | Introduced | |||||
Costa Rica | Present | Introduced | Naturalized | Naturalized, cultivated | |||
Cuba | Present | Introduced | |||||
Dominica | Present, Widespread | Introduced | Widespread | ||||
Dominican Republic | Present | Introduced | |||||
Guadeloupe | Present, Widespread | Introduced | Naturalized | Naturalized. Potentially invasive; Original citation: Fournet (2002) | |||
Guatemala | Present | Introduced | Original citation: Flora Mesoamerica (2019) | ||||
Haiti | Present | Introduced | |||||
Honduras | Present | Introduced | Naturalized | Naturalized, cultivated; Original citation: Flora Mesoamerica (2019) | |||
Jamaica | Present | Introduced | |||||
Martinique | Present, Widespread | Introduced | Naturalized | Naturalized. Potentially invasive; Original citation: Fournet (2002) | |||
Mexico | Present | Introduced | Naturalized | Naturalized/ cultivated | |||
Netherlands Antilles | Present, Widespread | Introduced | Widespread | ||||
Panama | Present | Introduced | Naturalized | Naturalized, cultivated; Original citation: Flora Mesoamerica (2019) | |||
Puerto Rico | Present | Introduced | |||||
Saint Lucia | Present, Widespread | Introduced | |||||
Saint Vincent and the Grenadines | Present, Widespread | Introduced | |||||
United States | Present | Introduced | Present based on regional distribution | ||||
-Hawaii | Present | Introduced | Invasive | ||||
Oceania |
|||||||
American Samoa | Present | Introduced | Invasive | ||||
Australia | Present | Native | A. moschatus subsp. moschatus introduced in New South Wales and A. moschatus subsp. moschatus native to New South Wales, Northern Territory and Queensland | ||||
-New South Wales | Present | Introduced | A. moschatus subsp. moschatus | ||||
-Northern Territory | Present | Native | A. moschatus subsp. tuberosus | ||||
-Queensland | Present | Native | A. moschatus subsp. tuberosus | ||||
-Western Australia | Present | Native | A. moschatus subsp. tuberosus | ||||
Cook Islands | Present | Introduced | Invasive | ||||
Federated States of Micronesia | Present | Introduced | Invasive | ||||
Fiji | Present | Introduced | Invasive | ||||
French Polynesia | Present | Introduced | Invasive | ||||
Guam | Present | Introduced | Invasive | ||||
Marshall Islands | Present | Introduced | Invasive | ||||
New Caledonia | Present | Introduced | Invasive | ||||
Niue | Present | Introduced | Invasive | ||||
Northern Mariana Islands | Present | Introduced | Invasive | ||||
Palau | Present | Introduced | Invasive | ||||
Papua New Guinea | Present | Introduced | |||||
Samoa | Present | Introduced | Invasive | ||||
Solomon Islands | Present | Introduced | |||||
Tonga | Present | Introduced | Invasive | ||||
Wallis and Futuna | Present | Introduced | Invasive | ||||
South America |
|||||||
Bolivia | Present | Introduced | Naturalized | Naturalized | |||
Colombia | Present | Introduced | |||||
Ecuador | Present | Introduced | Original citation: Jørgensen and León-Yánez (1999) | ||||
French Guiana | Present | Introduced | |||||
Guyana | Present | Introduced | |||||
Peru | Present | Introduced | |||||
Suriname | Present | Introduced | |||||
Venezuela | Present | Introduced |
History of Introduction and Spread
Top of pageA. moschatus has been extensively introduced across tropical, subtropical and temperate regions of the world mostly as an ornamental and medicinal herb. It is also cultivated for the musk-like oil contained in its seeds, which is valued for perfume and for use in the cosmetic industry (PROSEA, 2016; GRIIS, 2018; USDA-ARS, 2018).
In the Caribbean, A. moschatus was first reported as "naturalized” in Jamaica in 1864 (Grisebach, 1864). On the islands of Martinique and Guadeloupe, this species has been listed as naturalized and cultivated since 1897 (Duss, 1972; Grenand et al., 2012).
Risk of Introduction
Top of pageThe risk of A. moschatus being introduced into new regions is very high. Worldwide, this species has been intentionally introduced as an ornamental plant, a medicinal herb and for the extraction of ambrette oil from its seeds. It has repeatedly escaped from cultivation and has the potential to become naturalized in many different habitats. Currently, the international demand of essential oils, including ambrette oil, is increasing due to the growing market for natural and organic products and advances in the use of essential oils in medical therapies (OECD-FAO, 2017). It is therefore likely that further introductions, and the expansion of areas of cultivation, will occur. For example, in India, where A. moschatus has been cultivated for centuries on a small scale as a medicinal herb, the increasing demand of ambrette oil has led to farmers expanding the cultivated area of this important medicinal crop (Oudhia, 2015; Lokesh and Prajapati, 2017).
Habitat
Top of pageA. moschatus prefers open forests in moist and wet habitats and seasonal rainforests, behaving as a weed in open and disturbed areas. It is common in agricultural areas, paddy fields, open and disturbed sites, roadsides, open forests, and urban areas and gardens, but also in monsoon forest, woodlands, grasslands, scrublands on slopes, valleys, riversides, swamps and wetlands. It often grows on rocky hillsides and occasionally on flat lands at elevations from sea level to around 1650 m (Smith, 1981; FAO, 2007; ANPSA, 2010; Florabank, 2018; Sankaran and Suresh, 2013, PROSEA, 2016; Flora of China Editorial Committee, 2018; PIER, 2018).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Natural |
Terrestrial | Managed | Cultivated / agricultural land | Present, no further details | Productive/non-natural |
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 | Natural grasslands | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Natural grasslands | Present, no further details | Productive/non-natural |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Riverbanks | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Riverbanks | 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 |
Terrestrial | Natural / Semi-natural | Scrub / shrublands | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Scrub / shrublands | Present, no further details | Natural |
Terrestrial | Natural / Semi-natural | Scrub / shrublands | 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 |
Biology and Ecology
Top of pageGenetics
The chromosome number of A. moschatus is 2n=72 (Cheng and Tsai, 1999; PROSEA, 2016). The main centre of diversity for Abelmoschus is India where A. esculentus, A. manihot, A. moschatus and several other related wild species occur (Patil et al., 2015; PROSEA, 2016).
Reproductive biology
A. moschatus is an autogamous species with bisexual flowers. Flowering is prolific with flowers opening in the morning and lasting for only one day. Flowers are scented and are visited and pollinated by insects (Orwa et al., 2009; ANPSA, 2010; PROSEA, 2016).
Physiology and phenology
Under favourable conditions, germination starts 4-15 days after sowing and is complete after 15-30 days. The optimum temperature for germination is approximately 30°C. The germination rate of commercial seeds is approximately 85% (PROSEA, 2016; PROTA, 2018). In India, plants start producing flower buds 25-39 days after germination. Flower buds take 22-25 days to reach full bloom and flowering continues for 45-80 days. Anthesis occurs in the morning and the stigma is receptive on the day of anthesis. The fruit takes approximately 25 days from setting to maturity (PROSEA, 2016).
In Australia, A. moschatus flowers between October and April. It seems that the length and timing of the wet season is important in regulating the flowering activity of this species within Australian forests (ANPSA, 2010; Florabank, 2018). In China, it has been recorded flowering from June to October (Flora of China Editorial Committee, 2018). Across tropical Asia, it flowers from July to September and the seeds ripen from August to October. In India it has been recorded flowering and fruiting from August to December (Orwa et al., 2009; India Biodiversity, 2018).
Longevity
A. moschatus is an annual to perennial herb. Life span is approximately 15 years or less. It dies back to an underground tuber in the dry season, usually resprouting when the rains return during the wet season (ANPSA, 2010; Florabank, 2018).
Associations
A. moschatus is the host of Dysdercus cingulatus (Heteroptera: Pyrrhocoridae), an important pest of cotton plantations (Kohno and Ngan, 2004; Sankaran and Suresh, 2013).
Environmental requirements
A. moschatus is a plant species of the tropical and subtropical regions, but can also grow in temperate sites. It prefers a mean temperature in the range of 20-30°C, but can tolerate temperatures ranging from 7-35°C. It cannot withstand temperatures of greater than 45°C or frost conditions. It is well adapted to areas with a mean annual rainfall in the range of 1000-1400 mm (but tolerates 700-2750 mm). It thrives in well-drained loamy and sandy soils with a pH ranging from 5.5-7.8, but can also grow on heavy clays. It cannot grow in heavily shaded areas but it is moderately drought tolerant and can regenerate foliage after damage by fire (FAO, 2007; Orwa et al., 2009; Sankaran and Suresh, 2013; PROSEA, 2016; Florabank, 2018).
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) |
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
55 | 30 | 0 | 1650 |
Air Temperature
Top of pageParameter | Lower limit | Upper limit |
---|---|---|
Mean annual temperature (ºC) | 10 | 35 |
Mean maximum temperature of hottest month (ºC) | 27 | 45 |
Mean minimum temperature of coldest month (ºC) | 7 | 18 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Dry season duration | 700 | 2750 | number of consecutive months with <40 mm rainfall |
Mean annual rainfall | 900 | 1500 | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
Soil reaction
- acid
- alkaline
- neutral
Soil texture
- light
- medium
Special soil tolerances
- saline
Natural enemies
Top of pageNatural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Alternaria alternata | Pathogen | Other|All Stages | not specific | |||
Anomis flava | Herbivore | Other|All Stages | not specific | |||
Colletotrichum hibisci | Pathogen | Other|All Stages | not specific | |||
Fusarium chlamydosporum | Pathogen | Other|All Stages | not specific | Khare et al. (2015) | ||
Hibiscus yellow vein mosaic disease | Pathogen | Other|All Stages | not specific | |||
Pectinophora gossypiella | Herbivore | Plants|Seeds | not specific |
Notes on Natural Enemies
Top of pageA. moschatus is affected by several diseases, the most important of which are Hibiscus mosaic virus (HMV) [Hibiscus yellow vein mosaic virus], anthracnose and Hibiscus leaf spot. Anthracnose, caused by Colletotrichum hibisci, affects all plant parts and may start in the seedling stage. Alternaria leaf spot and Phytophthora leaf blight can also cause damage, especially under humid conditions. In India, Earias insulana (spotted bollworm) attacks the crop during vegetative growth and the fruiting stage. Pectinophora gossypiella (pink bollworm) causes some damage to pods and seeds, and the caterpillars of Anomis flava feed on A. moschatus during the rainy season (PROSEA, 2016). Stem canker caused by Fusarium chlamydosporum was identified in A. moschatus during the rainy season in India (Khare et al., 2015). Many infected seedling girdled at the site of infection which led to their subsequent death; the fungus was found to be highly pathogenic to members of the Malvaceae family (Khare et al., 2015).
Means of Movement and Dispersal
Top of pageA. moschatus spreads by seeds and vegetatively by small tubers and stem fragments or cuttings (ANPSA, 2010; Florabank, 2018). Fruits are capsules containing numerous small seeds (less than 4 mm) that are easily dispersed when dried and split open. Seeds can also be dispersed by waterways, animals and by humans (India Biodiversity, 2018; PROSEA, 2016).
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Crop production | Cultivated for its seeds (oil extraction) | Yes | Yes | PROSEA (2016) |
Disturbance | Often naturalized in ruderal areas, roadsides, fallow lands | Yes | Yes | Orwa et al. (2009) |
Escape from confinement or garden escape | Frequent escape from cultivation | Yes | Yes | PROSEA (2016) |
Garden waste disposal | Seeds | Yes | Yes | PROSEA (2016) |
Horticulture | Cultivated as ornamental for its attractive flowers | Yes | Yes | GISD (2018) |
Industrial purposes | Extraction of ambrette oil from the seeds | Yes | Yes | PROSEA (2016) |
Intentional release | Cultivated for its seeds (oil extraction) and as ornamental | Yes | Yes | PROSEA (2016) |
Internet sales | Seeds available online | Yes | Yes | Amazon.com search (2018) |
Medicinal use | Used in traditional Asian medicine | Yes | Yes | Orwa et al. (2009) |
Ornamental purposes | Cultivated as ornamental for its attractive flowers | Yes | Yes | GISD (2018) |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Debris and waste associated with human activities | Seeds, stem fragments, and tubers | Yes | Yes | GISD (2018) |
Seeds available online | Yes | Yes | Amazon.com search (2018) | |
Water | Seeds | Yes | Yes | India Biodiversity (2018) |
Impact Summary
Top of pageCategory | Impact |
---|---|
Cultural/amenity | Positive |
Economic/livelihood | Positive and negative |
Environment (generally) | Positive and negative |
Human health | Positive |
Impact
Top of pageA. moschatus is regarded as weedy outside its natural habitats. It has repeatedly escaped from cultivation and has the potential to become naturalized and to colonize different habitats in cultivated, ruderal and semi-natural areas (ANPSA, 2010; PROSEA, 2016; Florabank, 2018). Once established, this species may behave as a weed exhibiting competitive and aggressive behaviour resulting in competition with, and displacement of, native plant species. It has become invasive in many areas across the Asia-Pacific region where it is threatening the growth and survival of native flora and fauna (ISGG, 2006; ANPSA, 2010; Sankaran and Suresh, 2013; GISD, 2018; GRIIS, 2018; PIER, 2018).
A. moschatus is also harmful because of its role as a host for the insect Dysdercus cingulatus, which is a severe pest of cotton crops (Kohno and Ngan, 2004; ISSG, 2006; Sankaran and Suresh, 2013).
Economic Impact
Top of pageA. moschatus is sometimes commercialized as an ornamental for its colourful and attractive flowers. Ambrette oil is used in luxury perfumery, cosmetics and as an additive in the preparation of some kinds of chewing tobacco, baked products, sweets, alcoholic (e.g. vermouth and bitters) and non-alcoholic drinks (Orwa et al., 2009; PROSEA, 2016). Worldwide, India, Colombia, Ecuador and Martinique are the main producers of ambrette oil. In India, the area cultivated with A. moschatus is rapidly increasing (Oudhia, 2015).
Risk and Impact Factors
Top of page- Proved invasive outside its native range
- Has a broad 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
- Pioneering in disturbed areas
- Highly mobile locally
- Benefits from human association (i.e. it is a human commensal)
- Long lived
- Fast growing
- Has high reproductive potential
- Gregarious
- Has propagules that can remain viable for more than one year
- Reproduces asexually
- Ecosystem change/ habitat alteration
- Modification of successional patterns
- Reduced native biodiversity
- Threat to/ loss of native species
- Competition - monopolizing resources
- Rapid growth
- Rooting
- Highly likely to be transported internationally deliberately
Uses
Top of pageProductive Uses and Management
A. moschatus is a multipurpose plant, valued especially for its essential oil, but also as a source of food, medicines and a range of commodities. It is often planted as an ornamental, aromatic and medicinal herb. The oil extracted from the seeds, known as ambrette oil, has a strong musky odor and is used in both the perfume industry and in aromatherapy. Seeds are used to flavour coffee, burned as incense and used in making incense sticks (agarbattis). Extracts of the fruit and upper parts of the plant have insecticidal qualities, and in India and Malaysia seeds are placed between clothes to deter insects (Orwa et al., 2009; Sankaran and Suresh, 2013; Fern, 2014; PROSEA, 2016; USDA-ARS, 2018).
Social benefit
As a spice A. moschatus is not widely used, although there are still many dishes where seed powder and oil are incorporated. Its most widespread use is in flavouring coffee and tea, mainly in Islamic countries of the Middle East and adjoining regions. In Saudi Arabia, seeds are also used to flavour soups. Young leaves and shoots are used as a vegetable in soups; unripe pods are used just like okra (Abelmoschus esculentus). Seeds are fried and roasted and used to flavour various dishes. Essential oil is used in baked goods, ice cream, sweets, soft drinks and alcoholic drinks. A. moschatus is used in many western dishes such as: caramel musk muffins, musky honey wings, musk-vanilla ice cream, musk waffles, ginger cinnamon and musk tea, golden cinnamon and musk brioche loaves, iced cinnamon and musk rolls, orange musk French toast, red musk candy, cinnamon syrup, musk apple cake, muscadine comfits and alcoholic drinks like hippocras with musk.
A. moschatus plants and seeds are regarded as medicinal in South Asia, China and in other countries where it is grown. A. moschatus is used in traditional and Ayurveda herbal medicine. Its uses range from being used as an antidote for snakebites to a decoction of the roots and leaves being taken as a remedy for gonorrhea and rheumatism. Seeds (known commonly as musk daana in India) are described as diuretic, anti-spasmodic, stomachic, nervine (curative for nervous disorders) and are used externally for skin diseases and itching. Root and leaf paste and mucilage are indicated in venereal diseases, urinary discharges and painful micturition. Seeds steeped in water are used against colds, flu and asthma. It is used as antiseptic, anti-spasmodic, anti-anxiety drug, aphrodisiac, appetite stimulant, cardiotonic, carminative, deodorant, anti-depressant, anti-diabetic, antidiarrhoea, digestive, diuretic, anti-dyspepsia, hyperglycaemic, ophthalmic (Orwa et al., 2009; Grenand et al., 2012; Oudhia, 2015; PROSEA, 2016; Ravindran, 2017). It is also used in the treatment of respiratory and skin disorders; however, most of these actions have not been confirmed through rigorous experimentation.
Seed oil is widely employed in aromatherapy. Seed-oil massage is used for relieving stress, fatigue and anxiety. It is also used for cramps, muscle aches, depression and nervous complaints (Ravindran, 2017).
Uses List
Top of pageEnvironmental
- Amenity
Human food and beverage
- Food additive
- Oil/fat
- Seeds
- Spices and culinary herbs
- Vegetable
Materials
- Beads
- Essential oils
- Fibre
Medicinal, pharmaceutical
- Source of medicine/pharmaceutical
- Traditional/folklore
Ornamental
- garden plant
- Propagation material
References
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Fryxell PA, 2007. Malvaceae. In: Manual de Plantas de Costa Rica, 111(6) [ed. by Hammel BE, Grayum MH, Herrera Mora C, Zamora N]. St. Louis, Missouri, USA: Missouri Botanical Garden. 313-373.
GISD, 2018. Species profile: Abelmoschus moschatus. In: Global Invasive Species Database . http://www.iucngisd.org/gisd/species
Grenand P, Prévost MF, Fleury M, 2012. The discret journey of plants: Abelmoschus moschatus (Malvaceae) and Zingiber zerumbet (Zingiberaceae) in the Neotropics. (Le voyage discret des plantes Abelmoschus moschatus (Malvaceae) et Zingiber zerumbet (Zingiberaceae) en Amérique tropicale). Revue d’ethnoécologie, 1. http://journals.openedition.org/ethnoecologie/733 ; DOI : 10.4000/ethnoecologie.733
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ISSG, 2006. IUCN/SSC Invasive Species Specialist Group. http://issg.org/database/species/ecology.asp?si=15&fr=1&sts=&lang=EN
Jørgensen PM, Nee MH, Beck SG, 2014. Catalogue of the Vascular Plants of Bolivia. (Catálogo de las Plantas Vasculares de Bolivia). Monogr. Syst. Bot. Missouri Bot. Gard, 127 (1-2)(i–viii), 1741.
Kato H, 2007. Herbarium records of Makino Herbarium. Tokyo Metropolitan University
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Kress WJ, DeFilipps RA, Farr E, Yin Yin Kyi D, 2003. A checklist of the trees, shrubs, herbs, and climbers of Myanmar. Contributions from the United States National Herbarium, 45, 1-590.
Lokesh C, Prajapati RK, 2017. Impact of Intercropping on Growth and Productivity of Muskdana (Abelmoschus Moschatus Medic.) Under Acacia Mangium Based Multitier Agro Forestry system. International Journal of Environmental Sciences & Natural Resources, 6(1), 555677. https://juniperpublishers.com/ijesnr/IJESNR.MS.ID.555677.php
Miles J, 2015. Report to Kayangel State: 2015 Survey of Invasive Plant Species, Palau Bureau of Agriculture , 6. http://www.hear.org/pier/reports/kayangel_2015_survey_report.htm
OECD-FAO, 2017. Agricultural Outlook 2007-2016. https://www.oecd.org/tad/agricultural-trade/38893266.pdf
Orwa C, Mutua A, Kindt R, Jamnadass R, Anthony S, 2009. Agroforestree Database: a tree reference and selection guide version 4.0. http://www.worldagroforestry.org/sites/treedbs/treedatabases.asp
Oudhia P, 2015. Muskdana or Ambrette (Abelmoschus moschatus): Aromatic and Medicinal. In: The New Crop Resource Online Program : Purdue University.https://www.hort.purdue.edu/newcrop/CropFactSheets/muskdana.html
Patil P, Sutar S, Joseph JK, Malik S, Rao S, Yadav S, Bhat KV, 2015. A systematic review of the genus Abelmoschus (Malvaceae). Rheedea, 25(1), 14-30.
PIER, 2018. Pacific Islands Ecosystems at Risk. Honolulu, USA: HEAR, University of Hawaii.http://www.hear.org/pier/index.html
PROSEA, 2016. Plant Resources of South-East Asia. http://proseanet.org/prosea/eprosea.php
PROTA, 2018. PROTA4U web database. In: Plant Resources of Tropical Africa Wageningen, Netherlands: http://www.prota4u.org/search.asp
Smith AC, 1981. Flora Vitiensis nova: a new flora of Fiji, Lawai, Kauai, Hawaii, USA: National Tropical Botanical Garden
Space JC, Flynn T, 2000. Report to the Government of Niue on invasive plant species of environmental concern. USDA Forest Service, Honolulu
Space JC, Flynn T, 2002. Report to the Government of Samoa on invasive plant species of environmental concern. USDA Forest Service, Honolulu
Stevens PF, 2017. Angiosperm Phylogeny Website. http://www.mobot.org/MOBOT/research/APweb/
The Plant List, 2018. 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, 2018. 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
Wu T, 2001. Check List of Hong Kong Plants. Agriculture, Fisheries and Conservation Department Bulletin 1 (revised), Hong Kong Herbarium and the South China Institute of Botany.384.
Distribution References
ANPSA, 2010. Australian Native Plant Society., http://anpsa.org.au/a-mos.html
Argüelles LC, García ÁI, Orueta JF, Zilleti B, 2006. (Especies Exóticas Invasoras: Diagnóstico y bases para la prevención y el manejo)., Madrid, Spain: Ministerio de Agricultura y Pesca. 288. https://www.aragon.es/documents/20127/674325/capdevilla.pdf/5947bd6b-f619-23d1-54a7-2d36104b5127
CABI, Undated. Compendium record. Wallingford, UK: CABI
CABI, Undated a. CABI Compendium: Status inferred from regional distribution. Wallingford, UK: CABI
CABI, Undated b. CABI Compendium: Status as determined by CABI editor. Wallingford, UK: CABI
Fryxell PA, 1988. Malvaceae of Mexico. In: Systematic Botany Monographs, 25 1-522.
Fryxell PA, 2007. Malvaceae. In: Manual de Plantas de Costa Rica, 111 (6) [ed. by Hammel BE, Grayum MH, Herrera Mora C, Zamora N]. St. Louis, Missouri, USA: Missouri Botanical Garden. 313-373.
GISD, 2018. Species profile: Abelmoschus moschatus. In: Global Invasive Species Database, http://www.iucngisd.org/gisd/species
GRIIS, 2018. Global Register of Introduced and Invasive Species., http://www.griis.org/
Jørgensen PM, Nee MH, Beck SG, 2014. Catalogue of the vascular plants of Bolivia. (Catálogo de las plantas vasculares de Bolivia). In: Monographs in systematic botany from the Missouri Botanical Garden, 127 1-1744.
Kato H, 2007. Herbarium records of Makino Herbarium., Tokyo Metropolitan University.
Kress WJ, DeFilipps RA, Farr E, Yin Yin Kyi D, 2003. A checklist of the trees, shrubs, herbs, and climbers of Myanmar. In: Contributions from the United States National Herbarium, 45 1-590.
Miles J, 2015. Report to Kayangel State: 2015 Survey of Invasive Plant Species., Palau Bureau of Agriculture. 6. http://www.hear.org/pier/reports/kayangel_2015_survey_report.htm
Smith AC, 1981. Flora Vitiensis nova: a new flora of Fiji., Lawai, Kauai, Hawaii, USA: National Tropical Botanical Garden.
Space JC, Flynn T, 2000. Report to the Government of Niue on invasive plant species of environmental concern., Honolulu, USDA Forest Service. 34.
Space JC, Flynn T, 2002. Report to the Government of Samoa on invasive plant species of environmental concern., Hawaii, USA: USDA Forest Service, Institute of Pacific Islands Forestry. 80 pp.
Contributors
Top of page29/05/18 Original text by:
Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH, Washington DC, USA
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