Cyrtomium falcatum (Japanese holly fern)
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
- Air Temperature
- Soil Tolerances
- Natural enemies
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Impact Summary
- Environmental Impact
- Threatened Species
- Risk and Impact Factors
- Uses
- Uses List
- Similarities to Other Species/Conditions
- Prevention and Control
- References
- Contributors
- Distribution Maps
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Top of pagePreferred Scientific Name
- Cyrtomium falcatum (L. f.) C. Presl
Preferred Common Name
- Japanese holly fern
Other Scientific Names
- Aspidium falcatum (L. f.) Sw.
- Cyrtomium acutidens H. Christ
- Cyrtomium yiangshanense Ching & Y. C. Lan
- Dryopteris falcata (L. f.) O. Kuntze
- Phanerophlebia falcata (L. f.) Copel.
- Polypodium falcatum L. f.
- Polypodium japonicum Houttuyn
- Polystichum falcatum (L. f.) Diels
International Common Names
- English: Asian net-veined holly fern; house holly fern; Japanese netvein holly fern
- Chinese: quan yuan guan zhong
Local Common Names
- Korea, Republic of: Do-kkae-bi-go-bi; Do-kkae-bi-soe-go-bi
- USA/Hawaii: ka'ape'ape
EPPO code
- CWUFA (Cyrtomium falcatum)
Summary of Invasiveness
Top of pageCyrtomium falcatum, commonly known as Japanese holly fern, is native to Asia (including China and Japan). It has been introduced across the world as an ornamental plant and has spread throughout tropical and subtropical areas, and in temperate regions with milder climates, and has spread rapidly across the USA. Colonization of new areas is facilitated by its ability to reproduce apogamously. It can be found in a broad range of habitats, typically on rock or masonry substrates, including coastal areas, waterfalls, karst, boulders, streams, as well as man-made structures. Where it occurs in natural habitats it can displace native species, including rare bryophytes and ferns. In the USA it has been recognized by the US National Park Service as invasive in much of its naturalized range.
Taxonomic Tree
Top of page- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Pteridophyta
- Class: Filicopsida
- Family: Dryopteridaceae
- Genus: Cyrtomium
- Species: Cyrtomium falcatum
Notes on Taxonomy and Nomenclature
Top of pageC. falcatum is a fern in the family Dryopteridaceae. The species was originally described as Polypodium falcatum by Linnaeus the Younger, based on a specimen from Japan. In 1836 Presl described the new genus Cyrtomium and transferred the species (Presl, 1836). The circumscription of Cyrtomium and the similar genus Polystichum has been controversial (Christensen, 1930), and the species has sometimes been treated as a member of that genus (Engler and Prantl, 1899). Genetic studies by Little and Barrington (2003), Li et al. (2004), and Lu et al. (2005) have shown that Cyrtomium is nested within a polyphyletic Polystichum. This required that Cyrtomium be included in a more broadly defined Polystichum, or, as recommended by Lu et al. (2005), separation of the Polystichum clade Balansana into a new genus, and retention of Cyrtomium. The genus Cyrtomium is currently recognized to contain about 35 species (Flora of China Editorial Committee, 2015).
Several subspecies have sometimes been recognized based on cytotypes and geographic distribution (Matsumoto, 2003b). This subdivision has not been followed by recent works (Flora of China Editorial Committee, 2015; Flora of North America Editorial Committee, 2015).
Description
Top of pageC. falcatum is a fern with an erect rhizome covered with brown lanceolate scales, 30-60 cm or rarely longer, stipe stramineous, base with brown scales, leaves pinnate, stiff and glossy, pinnae alternate, 4-15 pairs, falcate, medial pinnae 6-10 cm long, to 3 cm wide, margins undulate, entire to coarsely dentate, apex long acuminate to caudate, sori throughout abaxial side of pinnae, indusial brown.
Distribution
Top of pageC. falcatum is native to coastal provinces of China and Japan (Ohwi et al., 1965; Flora of China Editorial Committee, 2015). Reports in older literature from other regions in Asia, such as Hong Kong (Bentham, 1861) and India (Blatter and D’Almeida, 1922) refer to other Cyrtomium species.
C. falcatum has become naturalized in North America, Africa, Europe and Oceania and a few occurrences have been recorded in South America and the Caribbean. Some reports represent short-lived colonies, particularly those in colder climates. These have been difficult to identify because of a lack of published follow-up data.
In North America, the species has become established primarily in southern states but other populations have been reported in colder climates including Oregon, Virginia, Ohio, New York, New Jersey and Connecticut (Flora of North America Editorial Committee, 2015; USDA-NRCS, 2015; Weakley, 2015). In Texas, it has been reported as showing little or no increase of abundance or range (Nesom, 2009).
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: 10 Feb 2022Continent/Country/Region | Distribution | Last Reported | Origin | First Reported | Invasive | Reference | Notes |
---|---|---|---|---|---|---|---|
Africa |
|||||||
Madagascar | Present | Introduced | 2005 | Invasive | |||
Réunion | Present | Introduced | |||||
South Africa | Present | Introduced | Invasive | First reported: 1909-1911 | |||
Asia |
|||||||
China | Present | Native | |||||
-Fujian | Present | Native | |||||
-Guangdong | Present | Native | |||||
-Hubei | Present | Native | |||||
-Jiangsu | Present | Native | |||||
-Liaoning | Present | Native | |||||
-Shandong | Present | Native | |||||
-Zhejiang | Present | Native | |||||
Hong Kong | Absent, Invalid presence record(s) | ||||||
India | Absent, Invalid presence record(s) | ||||||
Japan | Present | Native | |||||
-Honshu | Present | Native | |||||
-Kyushu | Present | Native | |||||
-Ryukyu Islands | Present | Native | |||||
-Shikoku | Present | Native | |||||
North Korea | Present | Native | |||||
South Korea | Present | Native | Dokdo | ||||
Taiwan | Present | Native | |||||
Vietnam | Present | Native | |||||
Europe |
|||||||
Austria | Present | Introduced | 1951 | As: Polystichum falcatum | |||
Belgium | Present | Introduced | 2002 | ||||
Croatia | Present | Introduced | 1994 | ||||
Czechia | Present | ||||||
Ireland | Present | Introduced | 1983 | West Cork | |||
Italy | Present | Introduced | 1987 | Emilia-Romagna | |||
-Sicily | Present | ||||||
Netherlands | Present | Introduced | 1915 | ||||
Portugal | Present | Introduced | 1987 | ||||
-Azores | Present | Introduced | 1932 | ||||
-Madeira | Present | Introduced | 1986 | ||||
Romania | Present | Introduced | 1969 | ||||
Spain | Present | Introduced | 1986 | ||||
-Canary Islands | Present | 1985 | Salvage Islands, Canaries, Madeira | ||||
Switzerland | Present | Introduced | 2014 | Canton Ticino | |||
United Kingdom | Present | Introduced | 1976 | ||||
North America |
|||||||
Bermuda | Present | Introduced | Invasive | ||||
United States | Present | Present based on regional distribution. | |||||
-Alabama | Present | Introduced | 1915 | ||||
-Arkansas | Present | Introduced | 2002 | ||||
-California | Present | Introduced | 1940 | ||||
-Connecticut | Present | ||||||
-Florida | Present | Introduced | 1923 | St. Augustine, Duval | |||
-Georgia | Present | Introduced | |||||
-Hawaii | Present | Introduced | 1928 | Maui, Oahu, Molokai, Kauai, Hawaii | |||
-Louisiana | Present | Introduced | |||||
-Mississippi | Present | Introduced | |||||
-New Jersey | Present | Introduced | 1907 | ||||
-New York | Present | Introduced | |||||
-North Carolina | Present | Introduced | |||||
-Ohio | Present | Introduced | 1956 | ||||
-Oregon | Present | Introduced | |||||
-South Carolina | Present | Introduced | |||||
-Texas | Present | Introduced | 1998 | ||||
-Virginia | Present | Introduced | |||||
Oceania |
|||||||
Australia | Present | Introduced | 1959 | ||||
-Lord Howe Island | Present | Introduced | 1981 | ||||
-New South Wales | Present | Introduced | 1981 | ||||
-Queensland | Present | Introduced | Invasive | ||||
-South Australia | Present | Introduced | Adelaide | ||||
-Tasmania | Present | Introduced | |||||
-Victoria | Present | Introduced | |||||
-Western Australia | Present | Introduced | |||||
French Polynesia | Present | Native | |||||
New Zealand | Present | Introduced | 1988 | ||||
Norfolk Island | Present | Introduced | 1989 | On walls in garden | |||
South America |
|||||||
Argentina | Present | Introduced | 1996 |
History of Introduction and Spread
Top of pageThe earliest report of naturalization was from New Jersey, USA, in 1907, when C. falcatum was found to be establishing in a well near a greenhouse where it was being cultivated (Benedict, 1907). It was then found in Alabama around 1915 (Graves, 1919), and in Florida in 1923 (Christensen, 1930). It has since spread and is found in at least 17 US states, including Hawaii.
It was first reported in South Africa between 1909 and 1911, but it may not have become permanently established there until recent years (Roux, 2011). It was recorded in the Netherlands (Europe) in 1915 (Denters, 2003), New South Wales (Australia) in 1981 (Pickard, 1984), and Argentina (South America) in 1996 (Missouri Botanical Garden, 2015). The species continues to be recorded in new countries, such as Switzerland in 2014 (Schoenenberger et al., 2014).
Risk of Introduction
Top of pageNew introductions will continue because C. falcatum is a popular ornamental plant.
Climate change will influence the spread of this species into cooler climates. Denters (2003) reports range expansion due to warmer winters in Belgium and the Netherlands.
Habitat
Top of pageDespite its thick leaves suggesting a preference for xeric habitats, C. falcatum favours mesophytic or coastal habitats (Meyer, 1927; Katsuyama et al., 2011; Flora of China Editorial Committee, 2015). In China, the species grows in lowland forests and coastal areas, to 500 m (Flora of China Editorial Committee, 2015). In Taiwan, it similarly grows in rocky coastal areas (Turner et al., 2001). In Japan, it is primarily a coastal species, growing in rocky areas (Ohwi et al., 1965; Katsuyama et al., 2011) but is occasionally found inland (Ohwi et al., 1965).
In its introduced range, C. falcatum can be found in a variety of habitats, usually associated with rocks or masonry, both in coastal and inland areas. Throughout the introduced range it occurs on man-made structures including walls, well interiors, stairways and other masonry or brick structures where there is shade and protection from excessive cold (Diddell, 1941; Degener and Hawkes, 1951; Esler, 1988; Mele et al., 2006; Roux, 2011).
In the eastern USA it is associated with stream banks, limestone outcrops, bluffs, drainage ditches, wooded ravines and waterfalls (Faircloth, 1975; Hill, 1992; Woods and Diamond, 2008; Peck, 2011; Weakley, 2015). Unlike its native range and some parts of its naturalized range, it has not been reported for coastal habitats in this region. In California, USA, it has been found associated with a waterfall in a canyon (Tracy, 1940). In Hawaii it has been found in “bare, windswept precipice and in the wooded gullies” (Degener and Hawkes, 1951).
In Italy, C. falcatum occupies streams, cliffs, walls, wells and brackish areas (Marchetti, 2014) and humid cliffs (Mele et al., 2006). In the Azores, it colonizes coastal areas, rock crevices, walls, slopes, and shady ravines (Schafer, 2001). In South Africa, it is known from watercourses, moist cliffs, rocky outcrops, stone walls and sometimes inland forests (Roux, 2011).
Habitat List
Top of pageCategory | Sub-Category | Habitat | Presence | Status |
---|---|---|---|---|
Terrestrial | Managed | Disturbed areas | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Disturbed areas | Present, no further details | 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 | Buildings | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Managed | Buildings | Present, no further details | 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 |
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 | Rocky areas / lava flows | Present, no further details | Harmful (pest or invasive) |
Terrestrial | Natural / Semi-natural | Rocky areas / lava flows | Present, no further details | Natural |
Littoral | Coastal areas | Present, no further details | Harmful (pest or invasive) | |
Littoral | Coastal areas | Present, no further details | Natural |
Biology and Ecology
Top of pageGenetics
C. falcatum has a chromosome number of 2n=82 (Lu et al., 2006), although naturalizing populations are reported to be apogamous triploids with a chromosome number of 2n=123 (Flora of North America Editorial Committee, 2015; Weakley, 2015). Three cytotypes have been identified in the species, including sexual diploid, apogamous triploid and sexual tetraploid (Matsumoto, 2003a; Lu et al., 2006; Flora of China Editorial Committee, 2015).
Reproductive Biology
C. falcatum is a homosporous fern (Chung and Chung, 2013). Populations that have naturalized are apogamous triploids. Being apogamous means that these plants can avoid the sexual process in the gametophyte stage so sporophytes arise more efficiently, allowing for easier colonization of new sites (Robinson, 2009).
Physiology and Phenology
C. falcatum produces spores from spring to autumn (Diggs and George, 2006).
It is moderately tolerant of arsenic (Sridokchan et al., 2005).
Associations
In Korea, the roots of C. falcatum were reported to be colonized by a mycorrhizal fungus with constricted hyphae, similar to those of Rhizoctonia spp. that colonize orchid roots (Lee et al., 2001).
Environmental Requirements
C. falcatum generally requires moist or shaded conditions for establishment, such as stream banks, shaded walls, waterfalls and ravines, and is sensitive to colder temperatures. In studies of phenology and wintering capacity, Toshiyuki (1982) found gametophytes resistant to temperatures of -30°C, and sporophytes to -15°C. Gametophytes survived well in a region where temperatures of -30°C can occur. They also found that gametophytes could survive independently of sporophytes under some conditions.
Climate
Top of pageClimate | Status | Description | Remark |
---|---|---|---|
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 | |
Cs - Warm temperate climate with dry summer | Preferred | Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers | |
Cw - Warm temperate climate with dry winter | Preferred | Warm temperate climate with dry winter (Warm average temp. > 10°C, Cold average temp. > 0°C, dry winters) | |
Df - Continental climate, wet all year | Preferred | Continental climate, wet all year (Warm average temp. > 10°C, coldest month < 0°C, wet all year) | |
Dw - Continental climate with dry winter | Preferred | Continental climate with dry winter (Warm average temp. > 10°C, coldest month < 0°C, dry winters) |
Soil Tolerances
Top of pageSoil drainage
- free
Soil reaction
- alkaline
- neutral
Soil texture
- light
- medium
Special soil tolerances
- infertile
Natural enemies
Top of pageNatural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Aphelenchoides | Herbivore | not specific | ||||
Coccus hesperidum | Herbivore | not specific | ||||
Colletotrichum acutatum | Pathogen | not specific | ||||
Heliothrips haemorrhoidalis | Herbivore | not specific | ||||
Idiopterus nephrelepidis | Herbivore | not specific | ||||
Macromyzus woodwardiae | Herbivore | not specific | ||||
Pseudococcus longispinus | Herbivore | not specific | ||||
Pseudomonas | Pathogen | not specific | ||||
Pseudomonas asplenii | Pathogen | |||||
Pythium | Pathogen | not specific | ||||
Rhizoctonia | Pathogen | not specific |
Notes on Natural Enemies
Top of pageLittle published data exists on natural enemies of C. falcatum. In its native range in Korea, an aphid, Macromyzus woodwardiae (Sternorrhyncha, Aphididae), has been documented from the undersides of new leaves (Lee, 2002).
Several pests have been identified in its introduced range, primarily associated with threats to cultivated plants. Greenhouse thrips (Heliothrips haemorrhoidalis) have been found on cultivated C. falcatum in Bermuda (Nakahara and Hilburn, 1989). Fern anthracnose (Colletotrichum acutatum) has severely damaged C. falcatum in central Florida, USA, and has caused economic losses (Strandberg et al., 1997).
Means of Movement and Dispersal
Top of pageNatural Dispersal
C. falcatum, like all ferns, produces spores which are small and dispersed by wind (Chung and Chung, 2013).
Accidental Introduction
C. falcatum is grown outdoors and indoors as an ornamental plant. Where grown outside, windborne spores may be dispersed from mature plants.
Intentional Introduction
C. falcatum is valued as an ornamental fern and may be introduced to new areas for this purpose.
Pathway Causes
Top of pageCause | Notes | Long Distance | Local | References |
---|---|---|---|---|
Cut flower trade | Yes | Yes | ||
Escape from confinement or garden escape | Yes | Yes | ||
Garden waste disposal | Yes | |||
Horticulture | Yes | Yes | ||
Landscape improvement | Yes | Yes | ||
Nursery trade | Yes | Yes | ||
Ornamental purposes | Yes | Yes |
Pathway Vectors
Top of pageVector | Notes | Long Distance | Local | References |
---|---|---|---|---|
Clothing, footwear and possessions | Yes | |||
Debris and waste associated with human activities | Yes | |||
Mulch, straw, baskets and sod | Yes | |||
Plants or parts of plants | Yes | Yes | ||
Wind | Yes |
Impact Summary
Top of pageCategory | Impact |
---|---|
Economic/livelihood | Positive |
Environment (generally) | Negative |
Environmental Impact
Top of pageImpact on Biodiversity
C. falcatum can colonize sparsely vegetated rocks, often in moist and humid conditions. It therefore has the potential to displace co-occurring rare ferns and bryophytes that often grow in such habitats at low population sizes. In Hawaii, USA, it has been reported to displace the endangered Stenogyne bifida, a herbaceous vine in the mint family (Lamiaceae) (US Fish and Wildlife Service, 2010). In Bermuda, it is reported to compete with the endangered Bermuda shield fern (Thelypteris bermudiana) (Copeland and Malcolm, 2014) and the endangered epiphyte, wild Bermuda pepper (Peperomia septentrionalis) (Bárrios et al., 2015).
In Macaronesia, C. falcatum is displacing the fern, sea spleenwort (Asplenium marinum) (Robinson, 2009). It has the potential in Florida to displace rare, native fern species such as Trichomanes punctatum subsp. floridanum, but it has not been observed to displace rare native ferns in the southeastern USA (Alan Cressler, Atlanta, GA, USA, personal communication, 2015; Jennifer Possley, Fairchild Tropical Botanic Garden, Florida, USA, personal communication, 2015).
Threatened Species
Top of pageThreatened Species | Conservation Status | Where Threatened | Mechanism | References | Notes |
---|---|---|---|---|---|
Peperomia septentrionalis (wild Bermuda pepper) | EN (IUCN red list: Endangered) | Bermuda | Barrios et al. (2015) | ||
Stenogyne bifida (twocleft stenogyne) | CR (IUCN red list: Critically endangered); USA ESA listing as endangered species | Hawaii | Competition - shading; Competition - smothering | US Fish and Wildlife Service (2010) | |
Thelypteris bermudiana (Bermuda shield fern) | EN (IUCN red list: Endangered) | Bermuda | Competition - smothering | Copeland and Malcolm (2014) |
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
- Pioneering in disturbed areas
- Tolerant of shade
- Benefits from human association (i.e. it is a human commensal)
- Long lived
- Fast growing
- Has high reproductive potential
- Reproduces asexually
- Ecosystem change/ habitat alteration
- Infrastructure damage
- Modification of successional patterns
- Reduced native biodiversity
- Threat to/ loss of endangered species
- Threat to/ loss of native species
- Causes allergic responses
- Competition - monopolizing resources
- Competition - shading
- Competition - smothering
- Highly likely to be transported internationally deliberately
- Difficult to identify/detect as a commodity contaminant
Uses
Top of pageEconomic Value
C. falcatum is cultivated globally as an ornamental plant (Degener and Hawkes, 1951). The fronds are also used in cut flower arrangements (Will and Burch, 1985).
Similarities to Other Species/Conditions
Top of pageC. falcatum can be confused with some larger forms of Cyrtomium fortunei in herbaria, although they are not likely to be confused when alive because of the glossy pinna surface of C. falcatum (Christensen, 1930).
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.
Control
New colonies are often the result of spread from cultivated plants so efforts should be made to eliminate plants from adjacent areas and may require the cooperation of landowners nearby.
Physical/Mechanical Control
Control of C. falcatum is primarily accomplished by hand pulling. Pulled plants should be removed from the site to prevent the spread of spores.
Chemical Control
Where there are denser populations of C. falcatum, or where plants occur on sensitive substrates such as historical masonry structures, control can be achieved with foliar glyphosate application.
References
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Barrios S, Copeland A, Malcolm P, 2015. Peperomia septentrionalis. The IUCN Red List of Threatened Species. Version 2015.2. http://www.iucnredlist.org/details/68982125/0
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Jermy AC, British PP, 1978. Atlas of ferns of the British Isles. London, UK: Botanical Society of the British Isles, British Pteridological Society.
Jung S, Byun J, Park S, Oh S, Yang J, Jang J, Chang K, Lee Y, 2014. The study of distribution characteristics of vascular and naturalized plants in Dokdo, South Korea. Journal of Asia-Pacific Biodiversity, 7(2):e197-e205.
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Schafer H, 2001. Distribution and status of the pteridophytes of Faial island, Azores (Portugal). Fern Gazette, 16(5):213-237.
Schoenenberger N, Rothlisberger J, Carraro G, 2014. The exotic flora of the Canton Ticino (Switzerland). (La flora esotica del Cantone Ticino (Svizzera). Bolletino della Societa ticinese di scienze naturali, 102:13-30.
Segarra-Moragues JG, 2001. Data on pteridoflora subspontaneous Iberica - Cyrtomium falcatum (Dryopteridaceae) and Nephrolepis cordifolia (Nephrolepidaceae). (Datos sobre la pteridoflora subespontanea Iberica - Cyrtomium falcatum (Dryopteridaceae) y Nephrolepis cordifolia (Nephrolepidaceae)). Acta Botanica Malacitana, 26:247-249.
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Distribution References
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Hutchinson G, Thomas BA, 1992. Distribution of Pteridophyta in Wales. In: Watsonia, 19 (1) 1-19.
Jermy AC, British PP, 1978. Atlas of ferns of the British Isles., London, UK: Botanical Society of the British Isles, British Pteridological Society.
Jung S, Byun J, Park S, Oh S, Yang J, Jang J, Chang K, Lee Y, 2014. The study of distribution characteristics of vascular and naturalized plants in Dokdo, South Korea. In: Journal of Asia-Pacific Biodiversity, 7 (2) e197-e205.
Li J, Chiou W, 2006. Changes in the flora on islet Pengchiayu across 100 years. In: Taiwania, 51 (3) 195-209.
Lubin D, 2015. Ferns of Bermuda., Massachussetts, USA: Street Allston. http://nefern.info/SiteList/bermudalist.htm
Marchetti D, 2004. Pteridophytes of Italy. (Le Pteridofite D'Italia). In: Annals of the Museum of Civilisation Rovereto, 19 71-231.
Missouri Botanical Garden, 2015. Tropicos database., St. Louis, Missouri, USA: Missouri Botanical Garden. http://www.tropicos.org/
Mountier CF, 2014. Rarity and commonness in New Zealand ferns. In: Bachelor of Science Dissertation, Christchurch, New Zealand: Lincoln University.
Negrean G, 2011. Addenda to flora Romaniae, volumes 1-12 - Newly published plants, nomenclature, taxonomy, chorology and commentaries (Part 1). In: Kanitzia, 8 89-194.
Peck JH, 2003. Arkansas flora - additions, reinstatements, exclusions, and re-exclusions. In: Sida, 20 (4) 1737-1757.
Peck JH, 2011. New and noteworthy additions to the Arkansas fern flora. In: Phytoneuron, 30 1-33.
PlantNET, 2015. New South Wales flora online., Sydney, New South Wales, Australia: National Herbarium of New South Wales. http://plantnet.rbgsyd.nsw.gov.au/floraonline.htm
Press JR, Biscoito M, Zino FJ, 1986. New plant records from the Salvage Islands. In: Bocagiana, 90 1-4.
Roux JP, 2011. The genus Cyrtomium (Pteridophyta, Dryopteridaceae) in Africa and Madagascar. In: Botanical Journal of the Linnean Society, 167 (4) 449-465.
Schafer H, 2001. Distribution and status of the pteridophytes of Faial island, Azores (Portugal). In: Fern Gazette, 16 (5) 213-237.
Schoenenberger N, Rothlisberger J, Carraro G, 2014. The exotic flora of the Canton Ticino (Switzerland). (La flora esotica del Cantone Ticino (Svizzera)). In: Bolletino della Societa ticinese di scienze naturali, 102 13-30.
Segarra-Moragues JG, 2001. Data on pteridoflora subspontaneous Iberica - Cyrtomium falcatum (Dryopteridaceae) and Nephrolepis cordifolia (Nephrolepidaceae). (Datos sobre la pteridoflora subespontanea Iberica - Cyrtomium falcatum (Dryopteridaceae) y Nephrolepis cordifolia (Nephrolepidaceae)). In: Acta Botanica Malacitana, 26 247-249.
SIBIS, 2015. South African Biodiversity Information Facility., South Africa: South African National Biodiversity Institute. http://sibis.sanbi.org/faces/Home.jsp?1=1
Tracy HH, 1940. Cyrtomium in southern California. In: American Fern Journal, 30 (2) 52-56.
Trinajstic I, Panjol Z, 1994. Cyrtomium falcatum (L. fil.) C Presl. (Polystichaceae) a newcomer in the Croatian flora. In: Natura Croatica, 3 (1) 87-90.
USDA-NRCS, 2015. The PLANTS Database. Greensboro, North Carolina, USA: National Plant Data Team. https://plants.sc.egov.usda.gov
Verloove F, Lambinon J, 2014. The sixth edition of the Nouvelle Flore de la Belgique - nomenclatural and taxonomic remarks. In: Dumortiera, 104 7-40.
Weakley AS, 2015. Flora of the southern and mid-Atlantic States - Working draft of 2015., Chapel Hill, North Carolina, USA: University of North Carolina Herbarium (NCU).
Wilson K A, 1996. Alien ferns in Hawai'i. Pacific Science. 50 (2), 127-141.
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