Adiantum hispidulum (rosy maidenhair fern)
Index
- Pictures
- Identity
- Summary of Invasiveness
- Taxonomic Tree
- Description
- Plant Type
- Distribution
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat
- Habitat List
- Biology and Ecology
- Climate
- Latitude/Altitude Ranges
- Rainfall
- Soil Tolerances
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Environmental Impact
- Threatened Species
- Risk and Impact Factors
- Uses List
- Detection and Inspection
- Similarities to Other Species/Conditions
- Prevention and Control
- References
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Adiantum hispidulum Sw.
Preferred Common Name
- rosy maidenhair fern
International Common Names
- English: rough maidenhair fern
Local Common Names
- Australia: five-fingered Jack
- New Zealand: rosy maidenhair
EPPO code
- ADIHI (Adiantum hispidulum)
Summary of Invasiveness
Top of pageA. hispidulum, the rosy maidenhair fern, is known to be invasive and weedy in the main Hawaiian Islands where it has escaped from cultivation. In Hawaii it is a serious weed generally of mesic slopes and gulch bottoms and is often abundant along intermittent and perennial streams. It is capable of invading intact plant communities and pristine areas. A. hispidulum usually begins to colonize in areas where there is some type of natural disturbance such as landslides, tree falls, disturbance by feral ungulates, or even a single dislodged rock. The dense clumps and rhizome mats of this fern prevent establishment of many native taxa including rare species. A. hispidulum can also overrun other ferns and herbs (Wilson, 1996; Palmer, 2003; H. Oppenheimer, Hawaii Plant Extinction Prevention Program (PEP), USA, personal communication, 2013). It is naturalized locally in a few other parts of the world including the southeastern USA and parts of its native range including eastern and southern Africa, Malaya, and Singapore.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Pteridophyta
- Class: Filicopsida
- Order: Polypodiales
- Family: Pteridaceae
- Genus: Adiantum
- Species: Adiantum hispidulum
Description
Top of pageTerrestrial ferns, plants stiff, erect. Rhizomes erect to decumbent, short-creeping, with dark brown scales. Fronds clustered at apex of rhizome, erect, (6-)15–60 cm tall, young fronds rosy pink; stipes dark brown, rough, up to 30 cm long, clothed with short dark fibrils and hairs; blades ± fan-shaped, deltate to ovate, dichotomously branched at 45º angle into 7–15 branches; pinnules asymmetrically oblong-rectangular to diamond shaped, 0.5–1.7 cm long, 3–8 mm wide, the upper and outer margins gently rounded, finely toothed, the lower straight and entire, softly pubescent to ± glabrate, veins mostly ending in marginal teeth; pinnule stalks 0.5–1 mm long. Sori 6–14 per segment, small, closely placed on upper and outer edges in notches between the lobes; indusium flaps 3–4(–5) mm wide, circular to broadly oblong or kidney-shaped, covered with numerous small, pointed brown hairs (Verdcourt, 2002; Palmer, 2003).
Distribution
Top of pageA. hispidulum is widespread and presumed to be native from Australia and Africa to Asia, Malesia and various Pacific Islands (Palau, Fiji, New Caledonia, Vanuatu), and eastward to Polynesia (Austral Islands (Rapa), Society Islands (Tahiti), Cook Islands (Raratonga), and New Zealand. However, it is sporadic throughout its native range, and in addition to native plant communities it often occurs in disturbed habitats. For example around villages, along trails, on roadside banks, rock walls, or in the understory of forestry plantings, suggesting a potential for invasiveness. Australia is the type locality and presumably the centre of diversity for A. hispidulum, as it occurs in all States and Territories. Bostock et al. (1998) recognize four taxonomic varieties in Australia. The widespread var. hispidulum is terrestrial or lithophytic in a variety of habitats, including open forest and as relictual populations in gorges in arid areas. The other three varieties are said to be more localized and endemic to Australia. In this treatment, however, a single variable species is recognized without infraspecific taxa (subspecies, varieties, or forms), following International Plant Names Index (IPNI) (2013) and Tropicos (2013).
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: 14 Dec 2020Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Comoros | Present | Native | Mayotte, Anjouan, Grand Comore | ||||
Ethiopia | Present | Native | |||||
Kenya | Present | Native | |||||
Madagascar | Present, Few occurrences | Native | West Madagascar: Haut Bemarivo; Analamomby | ||||
Malawi | Present, Localized | Native | |||||
Mauritius | Present, Widespread | Native | Saxicolous, sometimes in soil, often in shade on talus, rocky walls, waterfalls, roadside banks, dry thickets and dry forest; widespread, to 1000 m | ||||
-Rodrigues | Present, Widespread | Native | Saxicolous: sometimes in soil, often in shade on talus or rocky walls, waterfalls, roadside banks, dry thickets and dry forest; widespread to 1000 m | ||||
Mayotte | Present | Native | Mayotte, Anjouan, Grande Comore | ||||
Mozambique | Present, Localized | Native | |||||
Réunion | Present, Widespread | Native | Saxicolous: sometimes in soil, often in shade on talus or rocky walls, waterfalls, roadside banks, dry thickets and dry forest; widespread to 1000 m; Original citation: Badre and Lorence (2008) | ||||
South Africa | Present, Localized | Native | Naturalized | In Natal at 830 m where it may have escaped from cultivation. Also naturalised in a few localities on the Cape Peninsula | |||
Tanzania | Present, Localized | Native | |||||
Asia |
|||||||
Indonesia | Present | Present based on regional distribution. | |||||
-Java | Present, Widespread | Native | On steep earth banks in shady places | ||||
Malaysia | Present | Present based on regional distribution. | |||||
-Peninsular Malaysia | Present, Localized | Native | Malaya, uncommon and never seen in the wild | ||||
Philippines | Present | Native | Luzon | ||||
Singapore | Present, Localized | Native | On bare shaded earth banks around suburbs, uncommon, presumably native | ||||
Sri Lanka | Present, Widespread | Native | Shady roadside banks, steep earth banks, 'jungle', tea plantations, 160-1675 m | ||||
Taiwan | Present | Native | |||||
North America |
|||||||
United States | Present | Present based on regional distribution. | |||||
-Connecticut | Present, Localized | Introduced | Naturalized | Introduced, sporadic escapes from cultivation, possibly naturalised locally. Banks and old walls; 0-100 m | |||
-Florida | Present, Localized | Introduced | Naturalized | Introduced, sporadic escapes from cultivation, possibly naturalised locally. Banks and old walls; 0-100 m | |||
-Georgia | Present, Localized | Introduced | Naturalized | Introduced, sporadic escapes from cultivation, possibly naturalised locally. Banks and old walls; 0 - 100 m | |||
-Hawaii | Present, Widespread | Introduced | Invasive | Widely naturalised on all main islands (not recorded from Niihau). First collected in wild on Oahu in 1923. Naturalised in native mesic forest on Kauai, forming dense mats | |||
-Louisiana | Present, Localized | Introduced | Naturalized | Introduced, sporadic escapes from cultivation, possibly naturalised locally. Banks and old walls; 0 - 100 m | |||
Oceania |
|||||||
Australia | Present, Widespread | Native | All states and Territories of mainland Australia. Four varieties recognised. Var. hipsidulum is terrestrial or lithophytic in a variety of habitats, including open forest and relictual populations in gorges, arid areas. The other three endemic varieties are more localised | ||||
Cook Islands | Present, Few occurrences | Native | Raratonga: locally common on shaded road cuts | ||||
Fiji | Present, Widespread | Native | Indigenous, common in forests of the dry and intermediate zones, also in very well-drained light forest of higher rainfall areas | ||||
French Polynesia | Present, Few occurrences | Native | Rapa, lithophytic on basalt cliffs. Tahiti, on cliff faces | ||||
New Caledonia | Present, Widespread | Native | Abundant, especially on dry talus slopes and open sunny areas | ||||
Palau | Present, Few occurrences | Native | |||||
Solomon Islands | Present | Native | Bougainville | ||||
Vanuatu | Present, Few occurrences | Native |
History of Introduction and Spread
Top of pageA. hispidulum has become widely naturalized and weedy in Hawaii, where it grows in dry to mesic, sunny and rocky slopes, woods or trails on all of the main islands (not recorded from Niihau). Its date of introduction is unknown, but it was not recorded by Hillebrand (1888). It was first collected in the wild on Oahu in 1923 (Wilson, 1996).
In continental North America (USA) it is introduced and represented in the flora by sporadic escapes from cultivation and possibly naturalized locally (Paris, 1993) in Connecticut and Georgia. It is also reported from Florida and Louisiana, where it usually occurs on banks and old walls, 0-100 m elevation.
This species is sporadic throughout east tropical and temperate Africa. In East Africa it is confined to moist shaded habitats in South Africa (Cape Province, Natal, and Transvaal), Mozambique, Malawi, Kenya, Tanzania, and Ethiopia (Schelpe and Anthony, 1986). In Natal, it has been recorded at 830 m altitude where it may have escaped from cultivation, and it has also been found naturalized in a few localities on the Cape Peninsula.
It is uncommon in Malaya and not seen in the wild, or in primary forests, but only near villages (Holttum, 1954). In Java it is found throughout, usually in the lower hilly regions, on steep earth banks in shady places. In Singapore it is presumably native and occurs on bare but shaded earth banks around the suburbs of the city but it is not common (Holttum, 1954).
Risk of Introduction
Top of pageA. hispidulum is sporadic throughout its native range, but is known to escape from cultivation via spores. A. hispidulum may colonize native plant communities as well as disturbed habitats such as around villages, along trails, on roadside banks, rock walls, or in the understory of forestry plantings. This species is potentially invasive in tropical and subtropical moist to wet environments and most likely spreads from cultivated plants by spore dispersal.
Habitat
Top of pageA. hispidulum occurs in dry to mesic, sunny to shady, usually moist rocky slopes, cliffs, woods, gulch bottoms, trails, roadside banks, rock walls, and understory of forestry plantings and native forest.
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | ||||
Terrestrial | Managed | Managed forests, plantations and orchards | Present, no further details | |
Terrestrial | Managed | Rail / roadsides | Present, no further details | |
Terrestrial | Natural / Semi-natural | Natural forests | Present, no further details | |
Terrestrial | Natural / Semi-natural | Rocky areas / lava flows | Present, no further details |
Biology and Ecology
Top of pageGenetics
Based on chromosome counts of material from Australia and Ceylon, A. hispidulum is an apogamous hexaploid (has six sets of chromosomes), with a chromosome number of n = ca. 170-180 (Manton and Sledge, 1954). The base chromosome number in A. hispidulum appears to be 29 rather than 30, the usual base number for the genus (Brownlie, 1977).
Reproductive Biology
The apogamous (asexual) life cycle of certain ferns means that they produce 32, larger than normal diploid spores per sporangium, instead of the normal 64 haploid spores (Moran, 2004). Other apogamous taxa with higher polyploid chromosome numbers (triploid, tetraploid, hexaploid, etc.) cannot reproduce sexually either. When their spores germinate the resulting prothallus (gametophyte or gamete producing phase in a fern’s life cycle) does not produce sex organs but proliferates vegetatively without fertilization. The resulting sporophyte (spore producing) plantlet grows to maturity and in turn produces fronds with apogamous spores. Apogamous reproduction is advantageous in ferns that grow in dry habitats for two reasons: firstly apogamous ferns lack swimming sperm and there is no need for water in reproduction; and secondly their prothallus matures faster than those of sexually reproducing ferns (Moran, 2004). Apogamous ferns generally have wider geographic distributions than their sexually reproducing relatives. This appears to be the case for A. hispidulum, thus explaining its wide distribution, success in colonizing dry to mesic, disturbed habitats, and invasive tendencies.
Physiology and Phenology
Apogamy may explain the wide distribution, success in colonizing dry to mesic, disturbed habitats, and invasive tendencies of A. hispidulum. In addition to this the growth rate of all life stages of A. hispidulum is much greater than those of native fern species on Hawaiian islands.
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]) | |
Cf - Warm temperate climate, wet all year | Preferred | Warm average temp. > 10°C, Cold average temp. > 0°C, wet all year |
Latitude/Altitude Ranges
Top of pageLatitude North (°N) | Latitude South (°S) | Altitude Lower (m) | Altitude Upper (m) |
---|---|---|---|
22 | 30 |
Rainfall
Top of pageParameter | Lower limit | Upper limit | Description |
---|---|---|---|
Mean annual rainfall | 1800 | mm; lower/upper limits |
Means of Movement and Dispersal
Top of pageSpores of A. hispidulum and other fern species are transported and dispersed primarily by air currents and wind. Spores may be transported in the soil on shoes or stuck to fur of animals but this method of spore dispersal is unlikely. The spores require a moist, shady, stable environment to germinate and grow into gameophytes and eventually into sporophytes or the spore producing phase. Many species of Adiantum, including A. hispidulum, are grown horticulturally and may spread unintentionally from cultivated plants.
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Disturbance | In Singapore, A. hispidulum occurs on bare but shaded earth banks around the suburbs of towns. | Yes | Holttum, 1954 | |
Escape from confinement or garden escape | Escaped from cultivation and/or naturalized in south eastern USA, Hawaii, Natal and Singapore | Yes | Schelpe and Anthony, 1986 |
Environmental Impact
Top of pageImpact on Habitats
This species can cause habitat degradation by forming dense mats that outcompete or prevent the establishment and growth of native plants (Weller et al., 2010).
Impact on Biodiversity
The dense mats formed by this fern species can smother, exclude, or prevent establishment of native plant species, including at least five federally listed endangered species; Asplenium dielpallidum, Delissea kauaiensis, Euphorbia haeleeleana, Isodendrion laurifolium and Psychotria hobdyi (Weller et al., 2010). Other thretened and federally listed endangered species affected by A. hispidulum in Hawaii include Diellia erecta, Diellia mannii, Ctenitis squamigera and Remya mauiensis (R. Aguraiuja, Tallin Botanical Garden, Estonia, personal communication, 2015).
Threatened Species
Top of pageThreatened Species | Conservation Status | Where Threatened | Mechanism | References | Notes |
---|---|---|---|---|---|
Asplenium dielpallidum | No Details | Hawaii | Competition - monopolizing resources; Competition - shading; Competition - smothering; Rapid growth | Weller et al., 2010 | |
Delissea kauaiensis | USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Competition - shading; Competition - smothering; Rapid growth | Weller et al., 2010 | |
Euphorbia haeleeleana | USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Competition - shading; Competition - smothering; Rapid growth | Weller et al., 2010 | |
Isodendrion laurifolium | USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Competition - shading; Competition - smothering; Rapid growth | Weller et al., 2010 | |
Psychotria hobdyi (Hobdy's wild-coffee) | USA ESA listing as endangered species; USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Competition - shading; Competition - smothering; Rapid growth | Weller et al., 2010 | |
Poa mannii (Mann's bluegrass) | CR (IUCN red list: Critically endangered); USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources | US Fish and Wildlife Service, 2010a | |
Pritchardia munroi (Kamalo pritchardia) | No Details | Hawaii | Competition - smothering | US Fish and Wildlife Service, 2011a | |
Remya mauiensis (Maui remya) | USA ESA listing as endangered species | Hawaii | Competition | US Fish and Wildlife Service, 2009 | |
Schiedea apokremnos (Kauai schiedea) | CR (IUCN red list: Critically endangered); USA ESA listing as endangered species | Hawaii | Competition | US Fish and Wildlife Service, 2010b | |
Schiedea hookeri (sprawling schiedea) | CR (IUCN red list: Critically endangered); USA ESA listing as endangered species | Hawaii | Competition - monopolizing resources; Ecosystem change / habitat alteration | US Fish and Wildlife Service, 2011b |
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
- Tolerant of shade
- Highly mobile locally
- Benefits from human association (i.e. it is a human commensal)
- Fast growing
- Has high reproductive potential
- Gregarious
- Reproduces asexually
- Damaged ecosystem services
- Ecosystem change/ habitat alteration
- Modification of successional patterns
- Monoculture formation
- Negatively impacts cultural/traditional practices
- Reduced native biodiversity
- Threat to/ loss of endangered species
- Threat to/ loss of native species
- Negatively impacts animal/plant collections
- Competition - monopolizing resources
- Competition - shading
- Competition - smothering
- Competition (unspecified)
- Interaction with other invasive species
- Rapid growth
- Rooting
- Highly likely to be transported internationally accidentally
- Highly likely to be transported internationally deliberately
- Difficult to identify/detect as a commodity contaminant
- Difficult/costly to control
Detection and Inspection
Top of pageThis species can be detected by visual identification, facilitated by using a reference book (Heath and Chinnock, 1974) or key (Palmer, 2003).
Similarities to Other Species/Conditions
Top of pageA. hispidulum may be distinguished from related maidenhair species (e.g. A. capillus-veneris, A. aethiopicum, A. raddianum) by it fronds that repeatedly fork at 45º angles, stipes clothed with short, dark fibrils and hairs, and pinnules with short, light brown hairs.
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.
References
Top of pageBadré F, Lorence D, 2008. Adiantum. In: Flore des Mascareignes, Adiantacées [ed. by Bosser, J. \Badré, F. \Guého, J.]. Paris, France: Institut du recherche pour le dévelopment, Mauritius Sugar Industry Research Institute and Royal Botanic Gardens (Kew), 102-110.
Bostock PD, Farrant PA, Parris BS, 1998. Adiantum. In: Flora of Australia, Ferns, Gymnosperms and Allied Groups, 48 [ed. by McCarthy, P. M. \Orchard, A. E.]. Collingwood, Victoria, Australia: Australian Biological Resources Study/CISRO, 253-263.
Brownlie G, 1969. Adiantum. In: Flore de la Nouvelle-Calédonie et Dépendances. 3. Ptéridophytes, 3. Paris, France: Museum National D'Histoire Naturelle, 177-183.
Brownlie G, 1977. The pteridophyte flora of Fiji. Vaduz, Liechtenstein: J. Cramer, 189-193.
Copeland EB, 1958. Fern flora of the Philippines. Manila, Philippines: Bureau of Printing, 161.
Fraser-Jenkins CR, Verdcourt B, Walker TG, 2006. Pteridaceae. In: A Revised Handbook of the Flora of Ceylon XV, part B [ed. by Shaffer-Fehre, \M.]. Enfield, New Hampshire, USA: Science Publishers, 349-352.
Heath E, Chinnock RJ, 1974. Ferns and fern allies of New Zealand. Wellington, NZ: Reed AH and Reed, AW, 12-13.
Hillebrand W, 1888. Flora of the Hawaiian Islands. London, UK: Williams & Norgate, 633-634.
Hillman Kitalong AE, DeMeo R, Holm T, 2008. Native trees of Palau: a field guide. Koror, Palau: The Environment Inc, 220.
Holttum RE, 1954. A revised flora of Malaya, Singapore: Government Printing Office, 603-604.
International Plant Names Index (IPNI), 2013. International Plant Names Index. http://www.ipni.org/
JSTOR, 2013. Global Plants. https://plants.jstor
Kato M, Takehisa N, Matsumoto S, Ebihara A, 2008. Illustrated flora of ferns and fern-allies of South Pacific Islands. Tsukuba, Japan: National Museum of Nature and Science, 110 pp.
Knapp R, 2011. Ferns and fern allies of Taiwan, 352. Taipei, Taiwan: KBCC Press & Yuan-Liou Publishing, 433.
Lorence DH, 1976. The pteridophytes of Rodrigues Island. Botanical Journal of the Linnean Society, 72:269-283.
Lorence DH, 1978. The pteridophytes of Mauritius (Indian Ocean): ecology and distribution. Botanical Journal of the Linnean Society, 76:207-247.
Manton I, Sledge WA, 1954. Observations on the cytology and taxonomy of the pteridophyte flora of Ceylon. Philosophical Transactions of the Royal Society of London Series B, Biological Sciences, 238:16-180.
Moran RC, 2004. A natural history of ferns. Portland, USA: Timber Press, 38-42.
National Tropical Botanical Garden, 2013. Herbarium Database. http://ntbg.org/herbarium/
Palmer DD, 2003. Hawai`i's ferns and fern allies. Honolulu, Hawaii: University of Hawai`i Press, 42-45.
Paris CA, 1993. Adiantum. In: Flora of North America, 2. New York, USA: Oxford University Press, 125-130.
PIER, 2013. Pacific Islands Ecosystems at Risk. Honolulu, Hawaii, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Schelpe EACLE, 1970. Pteridophyta. In: Flora Zambesiaca [ed. by Exell, A. W. \ Launert, E.]. London, UK: Crown Agents for Oversea Governments and Administrations, 108-112.
Schelpe EACLE, Anthony NC, 1986. Pteridophyta. In: Flora of Southern Africa [ed. by Leistner, O. A.]. Pretoria, South Africa: Botanical Research Institute, Department of Agriculture and Water Supply, 100-101.
Tardieu-Blot ML, 1958. Flore de Madagascar et des Comores [ed. by Humbert, H.]. Paris, France: Museum National d'Histoire Naturelle, 131-132.
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
Tropicos, 2012. Tropicos. Missouri, USA: Missouri Botanical Garden. http://www.tropicos.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
Verdcourt B, 2002. Flora of tropical East Africa. Rotterdam, The Netherlands: A.A. Balkema Publishers.
Weller SG, Cabin RJ, Lorence DH, Perlman S, Wood K, Flynn T, Sakai AK, 2010. Alien plant invasions, introduced ungulates, and alternative states in a mesic forest in Hawaii. Restoration Ecology, 19:671-680.
Wilson KA, 1996. Alien ferns in Hawaii. Pacific Science, 50(2):127-141.
Distribution References
Bostock PD, Farrant PA, Parris BS, 1998. Adiantum. In: Flora of Australia, Ferns, Gymnosperms and Allied Groups, 48 [ed. by McCarthy PM, Orchard AE]. Collingwood, Victoria, Australia: Australian Biological Resources Study/CISRO. 253-263.
Brownlie G, 1969. Adiantum. In: Flore de la Nouvelle-Calédonie et Dépendances. 3. Ptéridophytes, 3, Paris, France: Museum National D'Histoire Naturelle. 177-183.
Brownlie G, 1977. The pteridophyte flora of Fiji., Vaduz, Liechtenstein: J. Cramer. 189-193.
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
Copeland EB, 1958. Fern flora of the Philippines., Manila, Philippines: Bureau of Printing. 161.
Fraser-Jenkins CR, Verdcourt B, Walker TG, 2006. Pteridaceae. In: A Revised Handbook of the Flora of Ceylon XV, [ed. by Shaffer-Fehre M]. Enfield, New Hampshire, USA: Science Publishers. 349-352.
Hillman Kitalong AE, DeMeo R, Holm T, 2008. Native trees of Palau: a field guide., Koror, Palau, The Environment Inc. 220.
Holttum RE, 1954. A revised flora of Malaya., Singapore, Government Printing Office. 603-604.
JSTOR, 2013. Global Plants., https://plants.jstor
Kato M, Takehisa N, Matsumoto S, Ebihara A, 2008. Illustrated flora of ferns and fern-allies of South Pacific Islands., Tsukuba, Japan: National Museum of Nature and Science. 110 pp.
Knapp R, 2011. Ferns and fern allies of Taiwan., 352 Taipei, Taiwan: KBCC Press & Yuan-Liou Publishing. 433.
Lorence DH, 1976. The pteridophytes of Rodrigues Island. In: Botanical Journal of the Linnean Society, 72 269-283.
National Tropical Botanical Garden, 2013. Herbarium Database., http://ntbg.org/herbarium/
Palmer DD, 2003. Hawai`i's ferns and fern allies., Honolulu, Hawaii, University of Hawai`i Press. 42-45.
Paris CA, 1993. Adiantum. In: Flora of North America, 2 New York, USA: Oxford University Press. 125-130.
PIER, 2013. Pacific Islands Ecosystems at Risk., Honolulu, Hawaii, USA: HEAR, University of Hawaii. http://www.hear.org/pier/index.html
Schelpe EACLE, 1970. Pteridophyta. In: Flora Zambesiaca, [ed. by Exell AW, Launert E]. London, UK: Crown Agents for Oversea Governments and Administrations. 108-112.
Schelpe EACLE, Anthony NC, 1986. Pteridophyta. In: Flora of Southern Africa, [ed. by Leistner OA]. Pretoria, South Africa: Botanical Research Institute, Department of Agriculture and Water Supply. 100-101.
Tardieu-Blot ML, 1958. (Flore de Madagascar et des Comores)., [ed. by Humbert H]. Paris, France: Museum National d'Histoire Naturelle. 131-132.
Weller SG, Cabin RJ, Lorence DH, Perlman S, Wood K, Flynn T, Sakai AK, 2010. Alien plant invasions, introduced ungulates, and alternative states in a mesic forest in Hawaii. In: Restoration Ecology, 19 671-680.
Wilson K A, 1996. Alien ferns in Hawai'i. Pacific Science. 50 (2), 127-141.
Contributors
Top of page21/12/2013 Original text by:
David H. Lorence, National Tropical Botanical Garden, Hawaii, USA
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