Gymnocoronis spilanthoides

Abstract

EPPO BulletinVolume 47, Issue 3 p. 544-548 Normes OEPP EPPO StandardsFree Access Gymnocoronis spilanthoides First published: 17 November 2017 https://doi.org/10.1111/epp.12430AboutSectionsPDF ToolsRequest permissionExport citationAdd to favoritesTrack citation ShareShare Give accessShare full text accessShare full-text accessPlease review our Terms and Conditions of Use and check box below to share full-text version of article.I have read and accept the Wiley Online Library Terms and Conditions of UseShareable LinkUse the link below to share a full-text version of this article with your friends and colleagues. Learn more.Copy URL Share a linkShare onFacebookTwitterLinkedInRedditWechat Identity Scientific name: Gymnocoronis spilanthoides (D. Don ex Hook. & Arn.) DC. Synonyms: Alomia spilanthoides D. Don ex Hook., Alomia spilanthoides D. Don ex Hook. & Arn., Gymnocoronis attenuata DC., Gymnocoronis spilanthoides var. attenuata (DC.) Baker, Gymnocoronis subcordata DC., Piqueria attenuata (DC.) Gardner, Piqueria subcordata (DC.) Gardner The Plant List (http://www.theplantlist.org/tpl1.1/record/gcc-39812). Taxonomic position: Tracheophyta; Liliopsida; Asterales; Asteraceae (Compositae); Eupatorieae; Adenostemmatinae. Common names: Senegal tea (plant), Falscher Wasserfreund (German), vízibojt (Hungarian), jazmin del banado (swamp jasmine) (Spanish), 裸冠菊 luo guan ju (Chinese); English names used in plant trade: temple plant, spade-leaf plant, water snowball (USA), giant green hygro, costata. EPPO code: GYNSP. Phytosanitary categorization: EPPO A2 List no. 411 Geographical distribution Native range South America: Argentina, Bolivia, Brazil, Paraguay, Peru, Uruguay. Introduced range EPPO region: Hungary and Italy. Asia: China, Japan, India, Taiwan. Oceania: Australia, New Zealand. History of introduction and spread Gymnocoronis spilanthoides has a native range within South America (Brazil, Argentina, Paraguay, Uruguay, Bolivia and Peru), mostly centred around Uruguay and Paraguay (King & Robinson, 1987) and is becoming an invasive alien species in several regions of the world. The species is problematic in Australia, New Zealand, Japan, China and Taiwan and has recently naturalized in Italy. Gymnocoronis spilanthoides is cultivated in the USA but is not reported as naturalized there (Weed Science Society of America (WSSA), 2012). Records of this species from Central American countries probably refer to another species, Gymnocoronis latifolia (or up to four species depending on the taxonomy) (Turner, 1997). The species was reported from India (reputedly the source of introduction to Australia through the aquarium trade) by Parsons & Cuthbertson (2001). There are relatively recent records of naturalization in Japan (in 1995), Taiwan (in 2001) and mainland China (in 2007) (Kodono, 2004; Wang et al., 2010; Wu et al., 2010). Kodono (2004) reports this species as rapidly naturalizing, occurring from Kyushu to central Japan. Gymnocoronis spilanthoides was reported as casual in 1988 in Hungary, occurring in the thermal waters of Lake Héviz and ditches near Keszthely (Szabó, 2002; Lukács et al., 2016). Ardenghi et al. (2016) report two naturalized occurrences in north-western Italy (Lombardia region). The population in Italy stretches along the water body for 519 m, and occupies the whole canal width (1–4 m) (Ardenghi et al., 2016). Gymnocoronis spilanthoides was first reported as a naturalized species in Australia, reported from Taree in New South Wales (NSW) in 1980 (Parsons & Cuthbertson, 2001). It has since spread in NSW and also naturalized in the states of Victoria and Queensland. It has been eradicated from an ornamental pond site in Perth and Margaret River in Western Australia, the only known sites in that state (Hussey et al., 2007). In New Zealand, G. spilanthoides was first recorded as naturalized on the Papakura Stream in South Auckland in 1990 (Timmins & Mackenzie, 1995) and has since been found through much of lowland North Island and two South Island sites, the furthest south being in Canterbury (43.4°S). Morphology Plant type Emergent amphibious aquatic perennial herb. Description Gymnocoronis spilanthoides is an emergent perennial herb, either forming upright bushes up to 1.5 m tall, tangled sprawling floating mats or occasionally fully submerged in shallow water (see Fig. 1). Plants reproduce by seed and vegetative fragmentation, with detached stems rooting at the nodes and thus forming new colonies. Stems are pale green (rarely reddish), either round or six- to eight-angled in cross section, erect or scrambling, up to 1.5 m long and 20 mm across, with hollow internodes, inflated and buoyant. Leaves lanceolate or ovate, opposite, 50–200 mm long 25–75 mm wide, serrate with wavy margins, veins pinnate. Submerged foliage usually entire but with wavy margins, petiolate, 10–70 mm long. Inflorescence glandular hairy, terminal, a cyme of capitula (flowerheads). Capitula discoid, with white (or pinkish) florets, 3.5–4 mm long, subtended by a single row of green involucral bracts, 15–20 mm across, highly scented and very attractive to butterflies. Fruit is an achene, lacking a pappus, pale brown, slightly curved with prominent ribs, 1.2 mm long and 0.5 mm across (Parsons & Cuthbertson, 2001; New Zealand Plant Conservation Network, 2013; Ardenghi et al., 2016). Seed set variable, with 6–19% of florets producing seed (Vivian-Smith et al., 2005). Adventitious roots commonly developing on the nodes. Figure 1Open in figure viewerPowerPoint Gymnocoronis spilanthoides emerging from water body (image courtesy of Paul Champion). Biology and ecology General Dense emergent beds of G. spilanthoides sprawling over shallow margins of water bodies limit the growth of submerged and other emergent plant species. These beds prevent wind-induced mixing of the water column, causing reductions in dissolved oxygen that may result in anoxia with serious effects on fish and invertebrate species. The plant also increases evapotranspiration, resulting in water loss. These dense plant beds can impede water flow, promoting flooding and also obstructing navigation and recreation (Parsons & Cuthbertson, 2001). Habitats Within its introduced range, G. spilanthoides grows in wetlands, particularly degraded waterways (CRC for Australian Weed Management, 2003) forming marginal clumps on the edge of slow-flowing or still water bodies, also forming dense sprawling floating mats in rivers (including tidally influenced areas) and reservoirs, irrigation channels, ponds, lakes, canals and ditches. It also grows in marshes and swamps, especially where nutrient enriched (CRC for Australian Weed Management, 2003). Gymnocoronis spilanthoides established but did not persist in a rice field in Italy (Ardenghi et al., 2016). Environmental requirements In cooler parts of its introduced range, G. spilanthoides is a summer green, dying back to a perennial rootstock or to submerged plants, even under ice (New Zealand Plant Conservation Network, 2013, P Champion, Pers. Obs. (2016) National Institute of Water and Atmospheric Research Ltd). Burnett (2008) cultivated G. spilanthoides in Hamilton, New Zealand (37.8°S) with water temperature fluctuations between 7 and 23°C. The author then manipulated temperatures either 2, 4 or 6°C above or below ambient temperatures (Burnett et al. 2007) in separate tanks all otherwise experiencing outdoor ambient conditions. Gymnocoronis spilanthoides survived all treatments and all measured growth parameters (stem number, height, percentage cover, biomass) increased with increasing temperature. All treatments apart from +6°C died off to basal rootstocks during winter. The southernmost naturalized G. spilanthoides population was the Waimakariri River margin in Canterbury, New Zealand (43.4°S). Ardenghi et al. (2016) reported Italian sites in the north-west (45.2°N) that experienced hot summers (monthly mean summer temperature approximately 30°C) and relatively cold winters (monthly mean January ≤−1°C). Seed set has been recorded at many New Zealand, Australian and Italian sites (Vivian-Smith et al., 2005; Panetta, 2010; New Zealand Plant Conservation Network, 2013; Ardenghi et al., 2016), with low numbers of seed set. However, germination rates were high over a range of fluctuating temperatures 5/15°C, 10/20–25/15°C or at 25°C (Vivian-Smith et al., 2005; Ardenghi et al., 2016). Seed bank persistence was estimated at more than 16 years until viability was reduced below 1%, but would be much shorter if exposed to daylight (Panetta, 2010). Some field sites are situated on tidally influenced rivers, but tolerance to salinity is unknown. Gymnocoronis spilanthoides has high growth rates under ideal conditions; a shoot growth of 150 mm per week was measured in New South Wales (Parsons & Cuthbertson, 2001). Natural enemies There are no known natural enemies for G. spilanthoides within the EPPO region. Due to early management intervention in Australia and New Zealand, which has restricted the invasive range of the species, biological control has not been researched (Australian Government, 2016). Uses and benefits Gymnocoronis spilanthoides is widely sold as an ornamental species within the EPPO region, including internet trade (Brunel, 2009; Ardenghi et al., 2016). The species is also sold/exchanged between aquarists. The Ornamental Aquatic Trade Association (UK based) carried out a survey with its members in August 2016 requesting information on the number and value of G. spilanthoides stock sold at in the calendar year for 2015. Thirty-three members responded to this survey and detailed that a total of 75 700 G. spilanthoides plants were sold in the UK in 2015 with a value of GBP 112 955. The species is highly regarded as an ornamental pond plant as its flowers are very attractive to some butterflies, especially monarch butterflies in Australasia and the USA (Speichert & Speichert, 2007), and Kodono (2004) reports the plant is cultivated by butterfly enthusiasts in Japan. Kodono (2004) also reports the plant being promoted in Japan for water purification. Pathways for movement Plants for planting is considered the main pathway for entry into the EPPO region. From this pathway, individual plants can be transferred to suitable habitats through either intentional introductions into the environment or unintentionally through the disposal of aquarium material. Consideration can be given to river systems within the EPPO region which are connected to countries outside the EPPO region. It is possible that the use of recreational equipment (e.g. fishing or canoeing gear) could spread the species, particularly as seeds or seedlings, although this is not likely to be significant pathway at present given the rarity of the plant within the EPPO region. However, there are campaigns within the European Union (EU) to raise awareness of the movement of invasive alien plants by this pathway. For example, the ‘Check, Clean and Dry’ campaign in Great Britain highlights the need to inspect and treat recreational material following use. Impact Effects on plants CRC for Australian Weed Management (2003) states that G. spilanthoides threatens biodiversity and causes other environmental damage. Although only in the early stages of establishment, this weed has the potential to seriously degrade Australia's ecosystems. Because G. spilanthoides grows very quickly, it can rapidly cover water bodies with a floating mat, excluding other plants and the animals that rely on them. Water quality may decline if large amounts of the plant die off and rot under water. Environmental and social impact Gymnocoronis spilanthoides has been recorded as colonizing a rice field in Italy (Ardenghi et al., 2016) and this could have potential economic impacts relating to crop yields unless managed (Fig. 2). The effects of flooding will potentially be made much worse because infestations block drainage channels – although financial figures for this are lacking. Recreational activities (e.g. by preventing access to the water body), irrigation and navigation may also be affected (Parsons & Cuthbertson, 2001). Figure 2Open in figure viewerPowerPoint Gymnocoronis spilanthoides encroaching into a rice field in Italy (Claudio Ballerini). Control Manual control has been successful in reducing small infestations of G. spilanthoides, either by hand removal, raking or drainage machinery (Parsons & Cuthbertson, 2001). Plants may be disposed of by drying and burning (CRC for Australian Weed Management, 2003). Care is required not to leave plant fragments that can regenerate into new plants or be spread by water movements to new locations (van Oosterhout, 2010). Re-establishment from seed germination is likely once the plant becomes established in a wetland or aquatic site, requiring follow-up control for many years (Panetta, 2010). In Lake Biwa (Japan) a concerted hand removal programme has resulted in a decrease in abundance and area occupied by G. spilanthoides over 3 years, with eradication anticipated in the near future (Kaneko, 2012). Glyphosate has been found to give poor control of G. spilanthoides (Sainty & Jacobs, 2003), with this herbicide poorly translocating into below-ground or underwater parts and in many cases being adsorbed onto the silt coating plants (P. Champion, 2016, pers. obs.). The selective broad-leaf herbicide metsulfuron-methyl does provide good control and has been permitted for minor use on the species in aquatic situations in Australia (van Oosterhout, 2010; New South Wales Department of Primary Industries, 2014) and New Zealand where the majority of field sites of G. spilanthoides have been eradicated using this herbicide (Champion et al., 2002; Champion & Clayton, 2003). Products should be used following the instructions on the label and in line with the relevant plant protection product regulations. Regulatory status Europe (overall): G. spilanthoides was included on the EPPO ‘Alert List’ in 2009. It was removed from this list and transferred to the ‘Observation List’ in 2012. Gymnocoronis spilanthoides was also assessed under an all-taxa horizon scanning exercise designed to help prioritize risk assessments for the ‘most threatening new and emerging invasive alien species’ in Europe (Roy et al., 2015); G. spilanthoides scored 625 representing a high probability of arrival, establishment, spread and threat to biodiversity and associated ecosystem services across the EU within the next 10 years. In 2016, G. spilanthoides was identified as a priority for risk assessment within the requirements of Regulation 1143/2014 (Branquart et al., 2016; Tanner et al., 2017). A subsequent pest risk analysis concluded that G. spilanthoides had a high phytosanitary risk to the endangered area (EPPO, 2017) and was added to the EPPO A2 List of pests recommended for regulation. At the time of publishing, G. spilanthoides is being considered for inclusion on the EU list of Union concern. Gymnocoronis spilanthoides is designated as an invasive alien species according to the Invasive Alien Species Act of Japan (Muranaka et al., 2005). In New Zealand, G. spilanthoides is listed on the National Plant Pest Accord prohibiting it from sale and commercial propagation and distribution, and it is declared an unwanted organism under the Biosecurity Act 1993 (Hicks, 2001). It is subjected to eradication programmes by regional councils throughout its New Zealand range (Champion et al., 2014). It is listed as an Environmental Weed by Howell (2008). In Australia, G. spilanthoides is on the Federal Alert List for Environmental Weeds, a list of 28 non-native plants that threaten biodiversity and cause other environmental damage. Although only in the early stages of establishment, these weeds have the potential to seriously degrade Australia's ecosystems. It is subject to statutory management in most Australian states including New South Wales, Queensland, South Australia, Western Australia, Tasmania and Lord Howe Island (Parsons & Cuthbertson, 2001). Csurhes & Edwards (1998) evaluated this species as a potential environmental weed, with a low probability of achieving eradication. Gymnocoronis spilanthoides is not on the Federal or any state Noxious Weed list (USDA National Resources Conservation Service 2016). Acknowledgements This datasheet is an output of DG Environment, LIFE funding under the project LIFE15 PRE-FR 001: Mitigating the threat of invasive alien plants in the EU through pest risk analysis to support the EU Regulation 1143/2014. The datasheet was produced following an expert working group that risk analysed G. spilanthoides for the EPPO region in October 2016. The composition of the expert working group was: D. Chapman (Centre for Ecology and Hydrology, UK), A. Petroeschevsky (Australia), D. 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