Arthurdendyus triangulatus (New Zealand flatworm)
- Summary of Invasiveness
- Taxonomic Tree
- Notes on Taxonomy and Nomenclature
- Distribution Table
- History of Introduction and Spread
- Risk of Introduction
- Habitat List
- Hosts/Species Affected
- List of Symptoms/Signs
- Biology and Ecology
- Rainfall Regime
- Notes on Natural Enemies
- Means of Movement and Dispersal
- Pathway Causes
- Pathway Vectors
- Plant Trade
- Impact Summary
- Economic Impact
- Environmental Impact
- Threatened Species
- Social Impact
- Risk and Impact Factors
- Detection and Inspection
- Similarities to Other Species/Conditions
- Prevention and Control
- Gaps in Knowledge/Research Needs
- Links to Websites
- Distribution Maps
Don't need the entire report?
Generate a print friendly version containing only the sections you need.Generate report
PicturesTop of page
IdentityTop of page
Preferred Scientific Name
- Arthurdendyus triangulatus (Dendy, 1894) Jones and Gerard (1999)
Preferred Common Name
- New Zealand flatworm
Other Scientific Names
- Artioposthia triangulata (Dendy, 1894)
- Geoplana triangulata Dendy, 1894
Local Common Names
- Denmark: Newzealandsk fladorm
- Faroe Islands: selendski flatmaðkurin
- Germany: Neuseelandplattwurm
- Iceland: Nýsjálenski flatorm
- Norway: New Zealandsk flatorm
- Sweden: Nyazeeländska plattmasken
Summary of InvasivenessTop of page
A. triangulatus is a free-living terrestrial flatworm. Native to New Zealand, it was found outside its natural habitat in Belfast, Northern Ireland in 1963 (Ministry of Agriculture, Northern Ireland, 1963, 1964). The species is harmful because it is a predator of earthworms and a decline in earthworms could reduce soil fertility and earthworm-feeding wildlife. The flatworm is found in Ireland, Great Britain and the Faroe Islands. Although capable of active movement the flatworm has been spread mainly by the trade in containerised plants. Its tendency to shelter under debris on the soil surface and its sticky body, have facilitated inadvertent carriage on plant containers, agricultural equipment and soil. There have been several scientific reviews of the biology of A. triangulatus published (Blackshaw and Stewart, 1992; Cannon et al., 1999; Boag and Yeates, 2001). A. triangulatus is considered an indirect plant pest by the European and Mediterranean Plant Protection Organisation (EPPO) (IPPC-Secretariat, 2005).
Taxonomic TreeTop of page
- Domain: Eukaryota
- Kingdom: Metazoa
- Phylum: Platyhelminthes
- Class: Turbellaria
- Order: Tricladida
- Family: Geoplanidae
- Genus: Arthurdendyus
- Species: Arthurdendyus triangulatus
Notes on Taxonomy and NomenclatureTop of page
Arthurdendyus triangulatus was originally described as Geoplana triangulata by Dendy (1894). Fyfe (1937) transferred it to the genus Artioposthia due to the presence of muscular gland organs (adenodactyli) in the genital atrium. Jones and Gerard (1999) subsequently erected the genus Arthurdendyus for planarians with elongate ovaries lateral to the male copulatory apparatus and a bell-shaped pharynx.
DescriptionTop of page
A. triangulatus is a large terrestrial flatworm measuring up to 10 mm wide and 200 mm in length when fully extended. However, the length is highly variable depending on the state of extension. The body is that of a flattened strap, narrowing towards the anterior. The colour is liver brown with a pale marginal fringe that extends from the underside. This fringe and the underside are beige and flecked with grey. The anterior head has a pink tinge with a row of minute black eye spots present on each side of the tip. The flatworm is covered in mucus and sticky to the touch. Non-specialist descriptions are given by Willis and Edwards (1977), Boag et al. (1994a) and Jones (2005). Egg capsules are shiny black and ovoid, typically measuring 4-8 mm in diameter.
DistributionTop of page
A. triangulatus is widespread but relatively rare in its native range, which is restricted to the South Island in New Zealand. It has established itself in Ireland, Great Britain and the Faroe Islands but not so far in continental Europe. This is something of a puzzle as much of the horticultural plant trade to the British Isles and the Faroe Islands, the presumed method of transfer of these flatworms, passes through other countries, in particular the Netherlands. It was possibly introduced into Great Britain on plants collected by the Edinburgh Botanic Gardens since it was discovered there in 1965 (Boag et al., 1998b). Analyses of genetic variation in A. triangulatus using PCR-RFLP, suggests multiple introductions of A. triangulatus into the UK (Dynes et al., 2001). This contention is supported by the presence of several other non-indigenous flatworms in the UK and Ireland, e.g. Australoplana sanguinea, Kontikia andersoni and A. albidus. Therefore, the fact that this species has not established on continental Europe may be due to other factors such as climate. However, it would seem likely that at least some areas of continental Europe may be at risk from invasion by this species (Boag et al., 1995a).
Distribution TableTop of page
The 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 2021
|Continent/Country/Region||Distribution||Last Reported||Origin||First Reported||Invasive||Reference||Notes|
|Faroe Islands||Present, Widespread||Introduced||1982||Invasive||First record from the downpipes of the parliament building in Tórshavn|
|Iceland||Present, Only in captivity/cultivation||Introduced||Reported from a glasshouse in Iceland. Either an isolated or unconfirmed report|
|Ireland||Present, Widespread||Introduced||Invasive||Summary of records in Ireland (both North and South)|
|United Kingdom||Present, Widespread||Introduced||Invasive||Distribution in Scotland – mainly in the populated central belt from Glasgow to Edinburgh but also records from the islands|
|-Northern Ireland||Present, Widespread||Introduced||1963||Invasive||Northern Ireland -first record outside New Zealand|
|New Zealand||Present, Widespread||Native||Specimens collected from Christchurch, Rapaki and Ashburton on the South Island|
History of Introduction and SpreadTop of page
A. triangulatus was first found outside of New Zealand in Belfast, Northern Ireland, in 1963. Exactly how this species came to be in Belfast is unknown but it is thought to have been carried inadvertently with ornamental plants such as daffodils, roses or rhododendrons (Willis and Edwards, 1977; Blackshaw and Stewart, 1992). A similar situation is likely to have happened in Scotland. The first record was from the Royal Botanic Gardens in Edinburgh, and many flatworm records have been associated with botanic gardens, garden centres and nurseries (Boag and Yeates, 2001). As an example, 22 live flatworms (though not A. triangulatus) were found within a Dicksonia antarctica (tree fern) from Australia (Parker et al., 2005). The spread of A. triangulatus to the relatively isolated Faroe Islands, was thought to have occurred via goods from Scotland, although direct transmission from New Zealand cannot be excluded (Mather and Christensen, 1992).
IntroductionsTop of page
|Introduced to||Introduced from||Year||Reason||Introduced by||Established in wild through||References||Notes|
|Natural reproduction||Continuous restocking|
|Faroe Islands||1982||Yes||Bloch (1992); Mather and Christensen (1992)||May have been introduced accidentally from Scotland or New Zealand|
|Northern Ireland||New Zealand||1963||Horticulture (pathway cause)||Yes||Ministry and Northern (1964)||Accidental introduction (Blackshaw and Stewart, 1992). First confirmed record of this species outside of its native range in New Zealand|
|UK||1965||Horticulture (pathway cause)||Yes||Boag et al. (1994a); Boag et al. (1994b); Willis and Edwards (1977)||To Scotland and England, associated with botanic gardens and nurseries|
Risk of IntroductionTop of page
A. triangulatus has been present in Ireland and Great Britain since the early 1960s. It has become almost ubiquitous within the populated areas of Northern Ireland (Moore et al., 1998) and has a cosmopolitan distribution in Scotland (Jones and Boag, 1996; Boag et al., 2006a). The colonisation of the Scottish and Faroe Islands demonstrates how this species can be easily spread from infected areas to relatively isolated regions. The risk of introduction of A. triangulatus is most severe in local regions of Ireland, Scotland, England and Wales. Unless steps are taken to limit local movement of this species, it is likely to continue to spread in Ireland and Great Britain.
A. triangulatus has not established on continental Europe, despite being present in Ireland and GB since the 1960s. Climate matching would suggest that A. triangulatus could establish in large areas of north-western continental Europe such as Denmark, Germany, the Netherlands and Belgium (Boag et al., 1995a; Boag and Yeates, 2001). The fact that A. triangulatus has not already been found on continental Europe is a puzzle and may suggest more stringent environmental conditions necessary for establishment. Outside of Europe, there are regions in the United States, Canada, Japan, Argentina and Australia, which are theoretically at risk from invasion by this species (Boag et al., 1995b). Perhaps of particular risk is Tasmania, which would be climatically similar to the South Island of New Zealand. A. vegrandis, another New Zealand species, has been found on the Australian subantarctic Macquarie Island (Greenslade et al., 2007).
HabitatTop of page
Typically found under debris on the soil surface, mostly in gardens or on the margins of agricultural land. Increasingly found in pasture in Northern Ireland (Murchie et al., 2003) and in potato fields in the Faroe Islands (Christensen and Mather, 1998). A. triangulatus may be active on the soil surface at night.
Habitat ListTop of page
|Terrestrial||Managed||Cultivated / agricultural land||Principal habitat||Harmful (pest or invasive)|
|Terrestrial||Managed||Managed forests, plantations and orchards||Secondary/tolerated habitat||Harmful (pest or invasive)|
|Terrestrial||Managed||Managed grasslands (grazing systems)||Principal habitat||Harmful (pest or invasive)|
Hosts/Species AffectedTop of page
A. triangulatus is a predator of earthworms and therefore an indirect plant pest. That is, the flatworm does not attack plants directly but by reducing earthworm numbers, soil fertility and hence plant productivity are also reduced. The concept of an indirect plant pest has been accepted by the European and Mediterranean Plant Protection Organisation (EPPO) (Schrader and Unger, 2003; IPPC-Secretariat, 2005; Murchie, 2008).
List of Symptoms/SignsTop of page
|Roots / reduced root system|
|Whole plant / dwarfing|
Biology and EcologyTop of page
The main factors limiting A. triangulatus dispersal are soil temperature, soil moisture and the availability of prey (Boag et al., 1998a). Soil temperatures greater than 20°C are detrimental to A. triangulatus, with 100% mortality after 3 weeks (Blackshaw and Stewart, 1992). Similarly, consistent low temperatures of -2°C caused 100% mortality after 3 days, whereas at -1°C mortality had only reached c. 50% after 21 days (Scottish Executive Rural Affairs Department, 2000). There has been little quantitative work on the effects of soil moisture on A. triangulatus, although it is clearly important (Boag et al., 2005). Part of the reason for this, is that in the UK and Ireland, soil moisture and temperature are often correlated, with high temperatures corresponding to low soil moisture.
ClimateTop of page
|Cs - Warm temperate climate with dry summer||Preferred||Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers|
Rainfall RegimeTop of page
Notes on Natural EnemiesTop of page
Predatory ground beetles of the families Carabidae and Staphylinidae will prey on A. triangulatus (Blackshaw, 1996; Gibson et al., 1997) but it is unlikely that they will do so in sufficient numbers to limit flatworm spread. There are also consistent reports of birds and other generalist worm predators such as shrews feeding on flatworms (Cannon et al., 1999). However, it would seem that flatworms are not choice prey and are distasteful to most predators (Cannon et al., 1999). Arthur Dendy, who described A. triangulatus and in whose honour the genus is named, describes tasting two specimens of land planarian. He found it to be “an exceedingly unpleasant sensation” (Dendy, 1891). Ducks, geese and even ferrets are known to feed on them without ill effects (B Boag, The James Hutton Institute, UK, personal communication, 2013).
Little is known about the natural enemies of A. triangulatus in New Zealand, although they are presumed to be ground beetles and other flatworms. Planarivora insignis (Diptera: Keroplatidae) is a parasitoid of terrestrial flatworms in Tasmania (Hickman, 1965). It is possible that a similar species may exist in the native habitat of A. triangulatus.
Means of Movement and DispersalTop of page
Natural Dispersal (Non-Biotic)
There have been anecdotal stories about greenkeepers releasing flatworms in order to reduce earthworm casting on golf and bowling greens, but these are unsubstantiated.
Pathway CausesTop of page
|Crop production||Possibly from Scotland to the Faroe Islands with potatoes, also via manure, silage & machinery||Yes||Yes||Boag et al. (1999); Mather and Christensen (1992); Moore et al. (1998); Murchie et al. (2003)|
|Horticulture||Movement of containerised plants||Yes||Yes||Blackshaw (1992); Cannon et al. (1999); Dynes et al. (2001); Willis and Edwards (1977)|
|Landscape improvement||Movement of topsoil||Yes||Christensen and Mather (1995)|
|Nursery trade||Importation of containerised plants from New Zealand seems the most likely mechanism of invasion||Yes||Yes||Blackshaw and Stewart (1992); Cannon et al. (1999); Dynes et al. (2001); Stewart and Blackshaw (1993); Willis and Edwards (1977)|
|Ornamental purposes||Associated with botanic gardens||Yes||Boag et al. (1994a); Willis and Edwards (1977)|
Pathway VectorsTop of page
|Land vehicles||Could be moved on soil attached to farm equipment||Yes|
|Plants or parts of plants||Probably both adults and egg capsules could be introduced in this way||Yes||Yes||Blackshaw and Stewart (1992); Cannon et al. (1999); Dynes et al. (2001); Willis and Edwards (1977)|
|Soil, sand and gravel||Local movement of topsoil and dung can facilitate flatworm spread||Yes||Murchie et al. (2003)|
Plant TradeTop of page
|Plant parts liable to carry the pest in trade/transport||Pest stages||Borne internally||Borne externally||Visibility of pest or symptoms|
|Bulbs/Tubers/Corms/Rhizomes||arthropods/adults; nematodes/eggs||Yes||Pest or symptoms usually visible to the naked eye|
|Growing medium accompanying plants||arthropods/adults; nematodes/eggs||Yes||Pest or symptoms usually visible to the naked eye|
|Roots||arthropods/adults; nematodes/eggs||Yes||Pest or symptoms usually visible to the naked eye|
|Plant parts not known to carry the pest in trade/transport|
|Stems (above ground)/Shoots/Trunks/Branches|
Impact SummaryTop of page
Economic ImpactTop of page
The economic impact of A. triangulatus is by reducing earthworm activity, which then limits plant growth. It is likely that the most serious impact will be in pasture. There are two reasons for this. First, A. triangulatus is commonest in relatively wet mild climates that are suited for grass production. Second, arable cultivation in itself is physically damaging to both earthworms and flatworms.
As highlighted by Alford (1998), one of the main economic effects of flatworm infestation could be limitations on trade. This applies to international trade and also to local trade in the sense that a garden centre, nursery or topsoil distributor may be held liable for distributing a harmful invasive species.
Environmental ImpactTop of page
Impact on Habitats
A decline in earthworms could have knock-on effects on earthworm-feeding wildlife (Alford, 1998). In the UK and Ireland, most vulnerable are badgers, hedgehogs, moles (not Ireland) and many familiar garden and farmland bird species (e.g. blackbirds, thrushes, rooks and lapwings). Earthworms are also an important food source for many invertebrates: e.g. carabid beeles (Symondson et al., 2000), testacellid snails and indigenous flatworm species. The only specific study on this topic was done on moles (Talpa europaea) in southwest Scotland. Boag (2000) found a significant negative relationship between the presence of A. triangulatus and that of moles.
Threatened SpeciesTop of page
Social ImpactTop of page
A. triangulatus is a garden pest spread by the movement of plants. Gardening is a popular hobby and many gardeners exchange plants through semi-formal networks such as gardening societies. Inadvertent spread of A. triangulatus has happened by this mechanism and therefore, where A. triangulatus is present, movement of containerised plants should be minimised.
Risk and Impact FactorsTop of page
- Proved invasive outside its native range
- Has a broad native range
- Highly mobile locally
- Benefits from human association (i.e. it is a human commensal)
- Long lived
- Has high reproductive potential
- Changed gene pool/ selective loss of genotypes
- Damaged ecosystem services
- Ecosystem change/ habitat alteration
- Host damage
- Modification of hydrology
- Modification of nutrient regime
- Negatively impacts agriculture
- Negatively impacts livelihoods
- Reduced native biodiversity
- Threat to/ loss of native species
- Negatively impacts trade/international relations
- Highly likely to be transported internationally accidentally
- Difficult to identify/detect as a commodity contaminant
- Difficult/costly to control
UsesTop of page
A. triangulatus does not burrow but rather squeezes through gaps in the soil. It therefore does not confer the same aeration and drainage benefits as earthworm burrowing.
DiagnosisTop of page
Diagnosis is by morphological features or species-specific DNA diagnostic primers. A. triangulatus is a distinctive species and microscope or molecular means for identification are rarely necessary. Jones (2005) provides user-friendly description of British terrestrial flatworms, including A. triangulatus.
Detection and InspectionTop of page
A. triangulatus is mainly detected by visual inspection under plant pots, stones, wood, plastic sheeting and other debris on the soil surface (EPPO, 2001). The flatworm may also be detected by use of the expulsion techniques (e.g. formalin or mustard) used to assess earthworm populations (Gunn, 1992; Murchie et al., 2003). Shelter traps may be placed on the soil surface, these can be pieces of wood, tiles or plastic bags filled with soil. A sampling strategy to quantify the detection of the New Zealand flatworm was published by Boag et al. (2010).
Similarities to Other Species/ConditionsTop of page
A. triangulatus could be confused with other flatworm species but is considerably larger that the native Microplana flatworms in Ireland and GB. The ‘Australian flatworm’, Australoplana sanguinea is similar in body shape but is orange. Terrestrial leeches also have a cursory similarity but are segmented.
Prevention and ControlTop of page
Due to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.
A. triangulatus is considered an indirect plant pest by the European and Mediterranean Plant Protection Organisation (EPPO). The EPPO standard ‘Import requirements concerning A. triangulatus’ relate to the importation of containerised plants and specify: 1) plants should be grown on raised and slatted benches; 2) or come from an area free from A. triangulatus; 3) or a representative sample of the product should be examined and found free of A. triangulatus; 4) or the consignment should be subject to heat treatment.
Cultural Control and Sanitary Measures
It is possible to inoculate depleted sites with earthworms (van der Werff et al., 1998), although this would only be justified if A. triangulatus were removed and would be dependent on the scale of their impact on the earthworm population. Given time and removal of flatworm predation, it is expected that earthworms will naturally recolonise infested areas.
Gaps in Knowledge/Research NeedsTop of page
More research is required on mechanisms to control A. triangulatus or prevent spread. From a practical viewpoint, hot-water phytosanitation provides a relatively cheap and easy means of disinfecting containerised plants. However, the precise temperatures required, the penetration of heat into compost or soil and the resilience of egg capsules to this treatment need to be determined.
ReferencesTop of page
Baird J; Fairweather I; Murchie AK, 2005. Long-term effects of prey-availability, partnering and temperature on overall egg capsule output of 'New Zealand flatworms', Arthurdendyus triangulatus. Annals of Applied Biology, 146(3):289-301. http://www.blackwell-synergy.com/servlet/useragent?func=showIssues&code=aab
Baird J; McDowell SDR; Fairweather I; Murchie AK, 2005. Reproductive structures of Arthurdendyus triangulatus (Dendy): seasonality and the effect of starvation. Pedobiologia, 49(5):435-442. http://www.sciencedirect.com/science/journal/00314056
Baird J; Murchie AK; Fairweather I, 2000. Hatch of New Zealand flatworm egg capsules at different temperatures. In: Proceedings of Environ 2000, Biology and Environment: Proceedings of the Royal Irish Academy 100B. 138.
Baker GH; Carter PJ; Barrett VJ, 1999. Influence of earthworms, Aporrectodea spp. (Lumbricidae), on pasture production in south-eastern Australia. Australian Journal of Agricultural Research, 50(7):1247-1257.
Blackshaw RP, 1991. Mortality of the earthworm Eisenia fetida (Savigny) presented to the terrestrial planarian Artioposthia triangulata (Dendy) (Tricladida:Terricola). Annals of Applied Biology, 118(3):689-694.
Blackshaw RP, 1996. Control options for the New Zealand flatworm. In: Brighton Crop Protection Conference: Pests & Diseases - 1996: Volume 3: Proceedings of an International Conference, Brighton, UK, 18-21 November 1996. Farnham, UK: British Crop Protection Council, 1089-1094.
Blackshaw RP; Stewart VI, 1992. Artioposthia triangulata (Dendy, 1894), a predatory terrestrial planarian and its potential impact on lumbricid earthworms. Agricultural Zoology Reviews, 5:201-219; 45 ref.
Boag B, 2000. The impact of the New Zealand flatworm on earthworms and moles in agricultural land in western Scotland. Aspects of Applied Biology [Farming systems for the new Millenium, 18-20 December 2000, Churchill College, Cambridge, UK.], No. 62:79-84.
Boag B; Deeks L; Orr A; Neilson R, 2005. A spatio-temporal analysis of a New Zealand flatworm (Arthurdendyus triangulatus) population in western Scotland. Annals of Applied Biology, 147(1):81-88. http://www.blackwell-synergy.com/servlet/useragent?func=showIssues&code=aab
Boag B; Evans KA; Neilson R; Yeates GW; Johns PM; Mather JG; Christensen OM; Jones HD, 1995. The potential spread of terrestrial planarians Artioposthia triangulata and Australoplana sanguinea var. alba to continental Europe. Annals of Applied Biology, 127(2):385-390.
Boag B; Evans KA; Yeates GW; Johns PM; Neilson R, 1995. Assessment of the global potential distribution of the predatory land planarian Artioposthia triangulata (Dendy) (Tricladida, Terricola) from ecoclimatic data. New Zealand Journal of Zoology, 22:311-318.
Boag B; Jones HD; Evans KA; Neilson R; Yeates GW; Johns PM, 1998. The application of GIS techniques to estimate the establishment and potential spread of Artioposthia triangulata in Scotland. Pedobiologia [OECD Workshop on Terrestrial Flatworms, New Zealand, 1998.], 42(5/6):504-510.
Boag B; Jones HD; Neilson R, 2006. Proceedings of the 10th International Symposium on Flatworm Biology, Innsbruck, Austria, July 2006. Innsbruck, Austria: The James Hutton Institute.
Boag B; Jones HD; Neilson R; Santoro G, 1999. Spatial distribution and relationship between the New Zealand flatworm Arthurdendyus triangulata and earthworms in a grass field in Scotland. Pedobiologia, 43(4):340-344.
Boag B; MacKenzie K; McNicol JW; Neilson R, 2010. Proceedings of Crop Protection in Northern Britain., UK 45-50.
Boag B; Neilson R, 2006. Impact of New Zealand flatworm on agriculture and wildlife in Scotland. Proceedings Crop Protection in Northern Britain, 51-55.
Boag B; Neilson R; Scrimgeour CM, 2006. Degrowth phenomenon in the planarian Arthurdendyus triangulatus (Tricladida: Terricola) as measured by stable isotopes. Biology and Fertility of Soils, 43:267-270.
Boag B; Palmer LF; Neilson R; Chambers SJ, 1994. Distribution and prevalence of the predatory planarian Artioposthia triangulata (Dendy) (Tricladida: Terricola) in Scotland. Annals of Applied Biology, 124(1):165-170.
Boag B; Palmer LF; Neilson R; Legg R; Chambers SJ, 1997. Distribution, prevalence and intensity of earthworm populations in arable land and grassland in Scotland. Annals of Applied Biology, 130:153-165.
Boag B; Yeates GW; Johns PM, 1998. Limitations to the distribution and spread of terrestrial flatworms with special reference to the New Zealand flatworm (Artioposthia triangulata). Pedobiologia [OECD Workshop on Terrestrial Flatworms, New Zealand, 1998.], 42(5/6):495-503.
Christensen OM; Mather JG, 1998. The 'New Zealand flatworm', Artioposthia triangulata, in Europe: the Faroese situation. Pedobiologia [OECD Workshop on Terrestrial Flatworms, New Zealand, 1998.], 42(5/6):532-540.
Ernst G; Emmerling C, 2009. Impact of five different tillage systems on soil organic carbon content and the density, biomass, and community composition of earthworms after a ten year period. European Journal of Soil Biology, 45(3):247-251. http://www.sciencedirect.com/science/journal/11645563
Fraser PM; Boag B, 1998. The distribution of lumbricid earthworm communities in relation to flatworms: a comparison between New Zealand and Europe. In: Pedobiologia, 42(5/6) [ed. by Yeates, G. W.]. 542-553.
Gibson PH; Cosens D; Buchanan K, 1997. A chance field observation and pilot laboratory studies of predation of the New Zealand flatworm by the larvae and adults of carabid and staphylinid beetles. Annals of Applied Biology, 130(3):581-585.
Gibson PH; Cosens DJ, 2004. The predation of slugs by the New Zealand flatworm, Arthurdendyus triangulatus (Dendy) (Terricola: Geoplanidae). British Journal of Entomology and Natural History, 17(1):35-38.
Greenslade P; Stevens I; Edwards R, 2007. Invasion of two exotic terrestrial flatworms to subantarctic Macquarie Island. Polar Biology, 30(8):961-967. http://www.springerlink.com/content/k580171665141u68/?p=69eaa3fc633a44a0a8645b8e1c5ba64b&pi=1
Haria AH; McGrath SP; Moore JP; Bell JP; Blackshaw RP, 1998. Impact of the New Zealand flatworm (Artioposthia triangulata) on soil structure and hydrology in the UK. Science of the Total Environment, 215(3):259-265.
IPPC-Secretariat, 2005. Identification of risks and management of invasive alien species using the IPPC framework. Proceedings of the workshop on invasive alien species and the International Plant Protection Convention, 22-26 September 2003. xii + 301 pp.
Jones HD; Boag B, 1996. The distribution of New Zealand and Australian terrestrial flatworms (Platyhelminthes: turbellaria: tricladida: terricola) in the British Isles- the Scottish survey and MEGALAB WORMS. Journal of Natural History, 30(7):955-975.
Jones HD; Gerard BM, 1999. A new genus and species of terrestrial planarian (Platyhelminthes; Tricladida; Terricola) from Scotland, and an emendation of the genus Artioposthia. Journal of Natural History, 33(3):387-394.
Jones HD; Santoro G; Boag B; Neilson R, 2001. The diversity of earthworms in 200 Scottish fields and the possible effect of New Zealand land flatworms (Arthurdendyus triangulatus) on earthworm populations. Annals of Applied Biology, 139(1):75-92.
McGee C; Wisdom GB; Fairweather I; Blackshaw RP; McIlroy J; Walker B, 1998. Characterization of the proteins present in the mucus of the flatworm Artioposthia triangulata (Dendy). Comparative Biochemistry and Physiology B-Biochemistry & Molecular Biology, 119:293-298.
Moore JP; Dynes C; Murchie AK, 1998. Status and public perception of the 'New Zealand flatworm', Artioposthia triangulata (Dendy), in Northern Ireland. Pedobiologia [OECD Workshop on Terrestrial Flatworms, New Zealand, 1998.], 42(5/6):563-571.
Murchie AK; Gordon AW, 2013. The impact of New Zealand flatworms Arthurdendyus triangulatus on earthworm populations in the field. Biological Invasions, 15(3):569-586.
Murchie AK; Mac an Tsaoir S, 2006. High densities of 'New Zealand flatworms', Arthurdendyus triangulatus (Dendy), in experimental orchard plots in Northern Ireland and implications for thatch formation. Tearmann, No.5:23-28.
Murchie AK; Moore JP; Walters KFA; Blackshaw RP, 2003. Invasion of agricultural land by the earthworm predator, Arthurdendyus triangulatus (Dendy). Pedobiologia [7th International Symposium on Earthworm Ecology, Cardiff, Wales, 1-6 September 2002.], 47(5/6):920-923.
Neilson R; Boag B; Smith M, 2000. Earthworm 13C and 15N analyses suggest that putative functional classifications of earthworms are site-specific and may also indicate habitat diversity. Soil Biology and Biochemistry, 32:1053-1061.
Parker B; O'Neill T; Green K; Drakes D; Perkins S; Lole M; Mills K; Cuthbertson A, 2005. UK Application of Methyl Bromide and its Alternatives. ADAS. Report to: Defra (Global Atmosphere Division) Contract no. CPEG 16. UK Application of Methyl Bromide and its Alternatives. ADAS. Report to: Defra (Global Atmosphere Division) Contract no. CPEG 16. 161 pp.
Rae RG; Robertson J; Wilson MJ, 2005. Susceptibility of indigenous UK earthworms and an invasive pest flatworm to the slug parasitic nematode Phasmarhabditis hermaphrodita. Biocontrol Science and Technology, 15(6):623-626. http://journalsonline.tandf.co.uk/link.asp?id=100635
Schrader G; Unger JG, 2003. Plant quarantine as a measure against invasive alien species: the framework of the International Plant Protection Convention and the plant health regulations in the European Union. Biological Invasions, 5:357-364.
Scottish Executive Rural Affairs Department, 2000. Biological and ecological studies of the New Zealand flatworm, Arthurdendyus triangulatus: towards a comprehensive risk assessment for the UK. Scottish Executive Rural Affairs Department, Flexible Fund Project No. CSL/002/96. Biological and ecological studies of the New Zealand flatworm, Arthurdendyus triangulatus: towards a comprehensive risk assessment for the UK. Scottish Executive Rural Affairs Department, Flexible Fund Project No. CSL/002/96. 125 pp.
Stewart VI, 1993. The biology of the terrestrial planarian Artioposthia triangulata (Dendy 1894) and its genetic variation in colonised habitats. Belfast, Northern Ireland: The Queen's University of Belfast,.
Stewart VI; Blackshaw RP, 1993. Genetic variation in populations of the terrestrial planarian Artioposthia triangulata (Dendy), and evidence for passive dispersal in Northern Ireland. Annals of Applied Biology, 123(2):459-468.
Symondson WOC; Glen DM; Erickson ML; Liddell JE; Langdon CJ, 2000. Do earthworms help to sustain the slug predator Pterostichus melanarius (Coleoptera: Carabidae) within crops? Investigations using monoclonal antibodies. Molecular Ecology, 9(9):1279-1292.
Boag B, Palmer L F, Neilson R, Chambers S J, 1994. Distribution and prevalence of the predatory planarian Artioposthia triangulata (Dendy) (Tricladida: Terricola) in Scotland. Annals of Applied Biology. 124 (1), 165-170. DOI:10.1111/j.1744-7348.1994.tb04124.x
Jones H D, Boag B, 1996. The distribution of New Zealand and Australian terrestrial flatworms (Platyhelminthes: turbellaria: tricladida: terricola) in the British Isles-the Scottish survey and MEGALAB WORMS. Journal of Natural History. 30 (7), 955-975. DOI:10.1080/00222939600770511
Seebens H, Blackburn T M, Dyer E E, Genovesi P, Hulme P E, Jeschke J M, Pagad S, Pyšek P, Winter M, Arianoutsou M, Bacher S, Blasius B, Brundu G, Capinha C, Celesti-Grapow L, Dawson W, Dullinger S, Fuentes N, Jäger H, Kartesz J, Kenis M, Kreft H, Kühn I, Lenzner B, Liebhold A, Mosena A (et al), 2017. No saturation in the accumulation of alien species worldwide. Nature Communications. 8 (2), 14435. http://www.nature.com/articles/ncomms14435
OrganizationsTop of page
Denmark: Aarhus University, Nordre Ringgade 1, 8000 Aarhus C, http://www.au.dl/en
UK: FERA (The Food and Environment Research Agency), Sand Hutton, York, Y0411LZ, http://www.fera.defra.gov.uk
UK: The James Hutton Institute, Invergowrie, Dundee, DD2 5DA, http://www.hutton.ac.uk/
Northern Ireland: Agri-Food & Biosciences Institute (AFBI), Newforge Lane, Belfast, BT9 5PX, http://www.afbini.gov.uk
Scotland: Science and Advice for Scottish Agriculture (SASA), 1 Roddinglaw Road, Edinburgh, EH12 9FJ, http://www.sasa.gov.uk
New Zealand: University of Canterbury UC, Private Bag 4800, Christchurch 8140, http://www.canterbury.ac.nz
ContributorsTop of page
29/09/09 Original text by:
Archie Murchie, Agri-Food and Biosciences Institute, Applied Plant Science Division, Newforge Lane, Belfast, BT9 5PX. Northern Ireland, UK
Distribution MapsTop of page
Select a dataset
CABI Summary Records
Unsupported Web Browser:
One or more of the features that are needed to show you the maps functionality are not available in the web browser that you are using.
Please consider upgrading your browser to the latest version or installing a new browser.
More information about modern web browsers can be found at http://browsehappy.com/