Crassula helmsii (Kirk) Cockayne

Common Name:

Synonyms and Other Names:

New Zealand Pygmy Weed, Tillaea recurva, Crassula recurva, Tillaea helmsii



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Identification: Crassula helmsii is an aquatic or semiterrestrial succulent perennial herb that ranges 10–130 cm in length.

Roots:  Can be floating or creeping depending on the growth form of the plant.
Stem: Round with roots forming at the nodes.
Leaves: Opposite, sessile, and succulent. Leaves are  4–20 mm long, 0.7–1.6 mm wide, linear-lanceolate to ovate-lanceolate, and acute.
Flowers: White or pinkish and borne singly in the axils of leaves.  Inflorescences have a diameter of 3–3.5 mm and are 4-merous. Petals are slightly longer than the sepals.
Fruits: Fruits are follicles containing 2–5 elliptical and smooth seeds about 0.5 mm long.


C. helmsii grows in three forms:

Form Characteristics: (EPPO 2007; DAISIE 2008).
Emergent Grows as stands of short, densely packed stems in water of 0.6 m or less in depth
Submerged Grows from a basal rosette, well rooted at the base, with long sparsely leaved stems that may reach the water surface
Terrestrial Creeping or erect stems and aerial leaves that are yellowish-green in color and succulent in appearance

 


Size: 10-130 cm long (EPPO 2007)


Native Range: Crassula helmsii is native to New Zealand and Australia (Brunet 2002).


This species is not currently in the Great Lakes region but may be elsewhere in the US. See the point map for details.

Ecology: Crassula helmsii inhabits the margins and shallow waters of freshwater lakes and ponds (Bridge 2005) and is found in ponds, lakes, gravel pits, and other static water bodies, and; also, streams with low flow (Brunet 2002). This species can grow near streams but usually establishes in lentic or very slow flowing regions (water velocity up to 0.3 m/s) Smith and Buckley, 2020). C. helmsii can inhabit a range of depths: from drying soils to submerged depths of 3 m (Dawson 1996). C. helmsii inhabits freshwater areas, with a range of nutrient levels. It is found in waters with pH from 4.29-9.57, and alkalinity from 0-0.92 m.eq/L. C. helmsii can tolerate drying for extended periods (Kirby, 1965, Dawson and Warman, 1987, and Smith and Buckley, 2020), and can survive in poor or rich phosphorus and potassium (Brunet 2002). Additionally, C. helmsii can survive CO2 concentrations as low as 3 mmol/m3, prolonged droughts up to 4 months, and high levels of metals (Smith and Buckley, 2020).  C. helmsii appears to do better in high light, but has also been found despite shading (Dawson and Warman 1987). This species has a temperature range of 0 to 25°C, including extended periods under snow (Kirby 1965, European and Mediterranean Plant Protection Organization 2007) and can withstand temperatures up to -6°C (Leach and Dawson 1999). C. helmsii propagates via vegetative fragmentation as small as 1 cm and is very tolerant of herbicides (Brunet, 2002 and Dawson, 1996).  C. helmsii can withstand warm water temperatures, so it may benefit from increased temperatures due to climate change.

Invasiveness may result, in part, from Crassulacean acid metabolism, which confers a competitive advantage in relation to growth through carbon conservation (Klavsen and Maberly 2009). C. helmsii is capable of outcompeting native species, increasing its ability to establish itself in a new region (Brower et al., 2017). Establishment is more likely in areas that are  eutrophic (van der Loop et al., 2020). C. helmsii is documented to occur growing as an understory layer associated with P. australis and may benefit from the expansion of P. australis australis in the Great Lakes region (Smith and Buckley, 2020).


Great Lakes Means of Introduction: Crassula helmsii has a low probability of introduction to the Great Lakes (Confidence level: High).

Potential pathway(s) of introduction: Aquarium or pond escape

This species has been found for sale at large outdoor stores (e.g., Lowe's Hardware mistakenly sold it under another name in Florida), as well as recommended for hobbyists online. It is unknown, however, if it is being bought and sold in the Great Lakes region. UK specimens are believed to come from a single introduction (Dawson 1994).  It has also been reported that this species can be easily dispersed by waterfowl and by attaching itself to equipment (Mumby et al., 2018)

C. helmsii is documented to occur growing as an understory layer associated with P. australis and may benefit from the expansion of P. australis australis in the Great Lakes region (Smith and Buckley, 2020).

 


Great Lakes Status: Crassula helmsii has been introduced to the United Kingdom (Bridge 2005), Belgium, Denmark, France, Germany, and the Netherlands (European and Mediterranean Plant Protection Organization 2007). Since C. helmsii’s introduction to the United Kingdom in 1956, this species has since spread throughout the British Isles (Brunet 2002).

Crassula helmsii has a moderate probability of establishment if introduced to the Great Lakes (Confidence level: High).

Crassula helmsii has a broad physiological tolerance and similar climates in its European range  (United Kingdom (Bridge 2005), Belgium, Denmark, France, Germany, and the Netherlands (European and Mediterranean Plant Protection Organization 2007) which suggests it would survive and reproduce in the Great Lakes. C. helmsii can overwinter in temperatures of 0°C. C. helmsii reproduces very easily and would likely spread once introduced.


Great Lakes Impacts:
Summary of species impacts derived from literature review. Click on an icon to find out more...

EnvironmentalSocioeconomicBeneficial



Crassula helmsii has the potential for high environmental impact if introduced to the Great Lakes.

C. helmsii shows extreme competitiveness, dominates many sites, and can cover the entire water surface (Brunet 2002) and is very tolerant of herbicides (Dawson 1996). Crassula helmsii suppresses surrounding epiphytic and planktonic algae more than the effect of shade (Brunet 2002). In some areas of the United Kingdom, C. helmsii is highly invasive and outcompetes native plant species by forming dense smothering mats of vegetation (Bridge 2005). This species has negatively affected the breeding success of the protected great crested newt Triturus cristatus potentially due to its rigid leaves which may make habitats unsuitable for egg laying (Watson 1999).  Additionally, this species can limit water circulation and change the oxygen regime Robert et al., 2013). C. helmsii can also influence macroinvertebrate community composition, increasing total overall abundance but decreasing evenness (Giordano, 2022).

Crassula helmsii has the potential for high socio-economic impact if introduced to the Great Lakes.

Crassula helmsii can clog drainage ditches (EPPO 2007) and can impact recreational use (EPPO 2007). In England C. helmsii is estimated to have cost angling 170,636 pounds across a 10km affected stretch of river and costs 1,450-7,225 pounds per pond to remove (Williams et al., 2010). Eradicating C. helmsii in a 4.5 ha area of Wadden Island cost 1.5 million euro (van der Loop et al.,  2022).

Crassula helmsii has the potential for moderate beneficial impact if introduced to the Great Lakes.

Studies have indicated that Crassula helmsii can be used for the control of a few other organisms. It is also a copper hyperaccumulater giving it the potential to be used as a method to reduce copper levels in polluted waterways. There is no evidence to suggest that this species is commercially, recreationally, or medically valuable.


References (click for full reference list)


Author: Fusaro, A., A. Davidson, K. Alame, M. Gappy, E. Baker, G. Nunez, J. Larson, W. Conard, P. Alsip and J. Van Zeghbroeck


Contributing Agencies:
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Revision Date: 3/20/2024


Citation for this information:
Fusaro, A., A. Davidson, K. Alame, M. Gappy, E. Baker, G. Nunez, J. Larson, W. Conard, P. Alsip and J. Van Zeghbroeck, 2024, Crassula helmsii (Kirk) Cockayne: U.S. Geological Survey, Nonindigenous Aquatic Species Database, Gainesville, FL, and NOAA Great Lakes Aquatic Nonindigenous Species Information System, Ann Arbor, MI, https://nas.er.usgs.gov/queries/greatlakes/FactSheet.aspx?Species_ID=3654&Potential=Y&Type=2&HUCNumber=DGreatLakes, Revision Date: 3/20/2024, Access Date: 4/19/2024

This information is preliminary or provisional and is subject to revision. It is being provided to meet the need for timely best science. The information has not received final approval by the U.S. Geological Survey (USGS) and is provided on the condition that neither the USGS nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.