Veronica beccabunga L.

Common Name: European speedwell

Synonyms and Other Names:

European speedwell, Water Pimpernel, Becky Leaves, Cow Cress, Horse Cress.



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Identification: Veronica beccabunga is an emergent perennial herb with horizontal or ascending stems that root at the nodes. The plant is smooth and shiny in appearance and has succulent, hollow stems that root and creep along the ground at the base. It has pairs of short, stalked, oval-oblong leaves that are thick and leathery in texture and are about 1 1/2 inch long, with slightly jagged or sinuated edges. Each pair of leaves has two flowers that stems from the upper leaf axils. Flowers are 2-4 inches long and about five millimeters wide with blue petals and a white eye. Occasionally, V. beccabunga flowers may be pink (Grieve 1995; Anderberg 2005).

Several subspecies of the plant occur. Studies of these species show that the plants present in eastern North America are of the beccabunga subspecies, which is distributed in Europe (Les and Stuckey 1985). V. beccabunga can be distinguished from the native Veronica americana by its leaf blades. In V. beccabunga, the blades are broadest above the middle and rounded at the apex. In V. americana, the leaf blades are broadest below the middle and the general outline of the leaf is thus more acute toward the apex. The style of V. beccabunga (part of the pistil that connects the stigma to the ovary) is distinctly shorter than the capsule, whereas V. americana styles are similar size as or slightly shorter than the capsules (Reznicek et al. 2011).


Size: to 2 ft.


Native Range: Europe, the Middle East, N. and W. Asia, and the Himalayas


Great Lakes Nonindigenous Occurrences: Veronica beccabunga was first observed in North America in 1876 in Hudson County, New Jersey, at the Bergen Tunnel (Les and Stuckey 1985). Infrequent in the United States, more common in the Great Lakes and Mid-Atlantic States where limited colonies are scattered. The first observation in the Great Lakes watershed is from Irondequoit, New York (Monroe County), in a wet meadow in 1915. The plant is currently distributed in northeastern North America from Michigan and Ohio to the St. Lawrence River in Quebec.


Table 1. Great Lakes region nonindigenous occurrences, the earliest and latest observations in each state/province, and the tally and names of HUCs with observations†. Names and dates are hyperlinked to their relevant specimen records. The list of references for all nonindigenous occurrences of Veronica beccabunga are found here.

Full list of USGS occurrences

State/ProvinceFirst ObservedLast ObservedTotal HUCs with observations†HUCs with observations†
19641964*
MI1849199617Au Sable; Betsie-Platte; Boardman-Charlevoix; Clinton; Great Lakes Region; Huron; Keweenaw Peninsula; Lake Huron; Northeastern Lake Michigan; Northwestern Lake Huron; Northwestern Lake Michigan; Pere Marquette-White; Southcentral Lake Superior; Southeastern Lake Michigan; Southwestern Lake Huron; St. Clair; St. Clair-Detroit
NY191519171Irondequoit-Ninemile
PA198519851Lake Erie

Table last updated 4/16/2024

† Populations may not be currently present.

* HUCs are not listed for areas where the observation(s) cannot be approximated to a HUC (e.g. state centroids or Canadian provinces).


Ecology: Veronica beccabunga occurs in most types of wetland and riparian habitats, although it is predominantly found on the muddy margins of brooks, rivers, ponds, and lakes (Lansdown 2013). While it is found at lake margins, it prefers lotic environments with cold, oxygen-rich waters and does not do as well in lentic environments (Les & Stuckey 1985). It is able to tolerate drying due to its ability to produce terrestrial forms along shores and it sometimes occurs in the draw-down zones of lakes and in ditches and canals where water is relatively shallow or the bank slopes are gentle enough to allow it to root (Lansdown 2013; Stodola 1967 in Les and Stuckey). Some observations of V. beccabunga indicate that this species is resilient to disturbance. V. beccabunga can be uprooted in storm events but it recovers quickly, and habitats that are affected by siltation are vulnerable to colonization (Haslam 1978 in Les & Stuckey 1985).

In Iran, V. beccabunga begins blooming in April or May, but in northern climates it is reported to flower as early as May or as late as August (Taheri & Shadkami-Till 2012; Anderberg 2005; Grieve 1995). This plant also is a resource for pollinating insects and some species of leaf eating insects throughout its native range (Taheri & Shadkami-Till 2012; Bienkowski & Orlova-Bienkowskaja 2015; Grieve 1995). The fly, Syritta pipians, Honey Bees, the larvae of the moth Athalia annulata, and the larvae of the beetle Phaedon armoraciae all have been reported to pollinate or feed on V. beccabunga (Bienkowski & Orlova-Bienkowskaja 2015; Grieve 1995).


Great Lakes Means of Introduction: An early record from solid ballast ground at Hunter’s Point, Long Island, New York in 1880, indicated that the plant was introduced in the solid ballast of ocean-going ships arriving from Eurasia. The species is commonly planted and the location of the first Great Lakes record at a cemetery (Reznicek et al 2011) suggests the species may have escaped cultivation in the region.


Great Lakes Status: Overwintering and reproducing with widespread distribution in all 5 Great Lakes basins.


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

EnvironmentalBeneficial


Current research on the environmental impact of Veronica beccabunga in the Great Lakes is inadequate to support proper assessment.

Although Veronica beccabunga is capable of forming large clonal stands (Grime et al, 1988) that can cover streams and significantly reduce native and wetland species (Mehrhoff et al, 2003), impacts are generally local.

There is little or no evidence to support that Veronica beccabunga has significant socio-economic impacts in the Great Lakes.

Veronica beccabunga has a moderate beneficial impact in the Great Lakes.

Veronica beccabunga is grown as an ornamental plant for butterfly and water gardens.  V. beccabunga was shown to have higher rates of accumulation of nitrogen and phosphorus (P) than other herbaceous plants growing in stream banks and peat bogs. V. beccabunga shoots had P and N concentrations of 4661 mg/kg and 17,000 mg/kg respectively (Parzych and Jonczak, 2018).

The leaves were once cultivated as an edible, bitter green. V. beccabunga has been used for a variety of different medical purposes. It was used as an antiscorbutic and often eaten with watercress. It was also applied to wounds, bruises, and burns. V. beccabunga has been reported to be used for scrofulous affections, impurity of blood, swelling, and gout (Grieve, 1995). In the past, this plant was occasionally used to treat scurvy (Usher 1974). Nanoparticles extracted from V. beccabunga have been shown to have antioxidants and antimicrobial properties (Seçkin, H. and I. Meydan, 2021). V. beccabunga was compared to other ethnomedicinal Romanian plants and had the highest total antioxidant capacity out of any of the plants (Papp et al., 2019).


Management: Regulations (pertaining to the Great Lakes region)
There are no known regulations for this species. Illinois regulates aquatic plants that are not explicitly approved. Therefore, V. beccabunga is restricted in Illinois.

Note: Check federal, state/provincial, and local regulations for the most up-to-date information.

Control
Biological
Interspecific competition with the similar North American Veronica americana is believed to have limited and slowed the spread of V. beccabunga. These species fulfill similar niches, so the presences of the native V. americana in undisturbed habitats may regulate the establishment of V. beccabunga (Les & Stuckey 1985).

Chemical
Doganlar (2012) evaluated the phytotoxicity and genotoxicity of atrazine, metalaxyl, ethion, disulfoton, and chloropyrifos on V. beccabunga. A mixture of these pesticides was found to cause decreases in total chlorophyll and protein at 1 ppm pesticide in 1 to 3 days of exposure. V. beccabunga was found to efficiently accumulate each chemical with chloropyrifos and atrazine being the highest accumulated pesticides respectively. Additionally, long-term exposure to strong doses (100 to 1000 ppb concentrations) of pesticides were found to have significant toxic effects on the antioxidant systems, hormone regulation, and DNA profiles in V. beccabunga.

Note: Check state/provincial and local regulations for the most up-to-date information regarding permits for control methods. Follow all label instructions.


Remarks: Several subspecies of the plant occur. Studies of these species show that the plants present in eastern North America are of the beccabunga subspecies which is distributed in Europe (Les and Stuckey 1985). In the past, this plant was occasionally used to treat scurvy (Usher 1974).   


References (click for full reference list)


Author: Cao, L. and P. Alsip


Contributing Agencies:
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Revision Date: 1/19/2024


Citation for this information:
Cao, L. and P. Alsip, 2024, Veronica beccabunga L.: 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=261&Potential=N&Type=0&HUCNumber=DHuron, Revision Date: 1/19/2024, Access Date: 4/16/2024

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.