Filipendula ulmaria (L.) Maxim.

Common Name: Queen of the meadow

Synonyms and Other Names:

Spiraea ulmaria, Ulmaria pentapetala, meadowsweet, meadwort, pride of the meadow, meadow-wort, meadow queen, lady of the meadow, dollof, meadsweet, and bridewort (WFO 2022).



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Identification: The species is an herbaceous perennial. F. ulmaria possesses rhizomal rootstalks capable of producing the shoot and roots of a new plant. Its stem is woody at its base and its  leaves are pinnately compound, dark green in color, with 5 pairs of leaflets, coarsely toothed and deeply veined. Leaves are hairy and whitish on the undersides. Leaflets occur on stems between leaves. The flowers are showy and fragrant. Branching panicles or cymes (erect clusters) of small, white­cream colored flowers. Individual flowers have 5 petals and numerous stamens, giving the flowers a "fuzzy" appearance.  Its seeds are spherical, irregular and twisting achene. They resemble cultivated garden Nasturtium seeds (MISIN 2022).


Size: 1-2m in height (Missouri Botanical Garden 2022)


Native Range: The species is native to Europe and western Asia (Flora of North America 2022, USDA 2022).


Great Lakes Nonindigenous Occurrences: First observed in the Great Lakes region in Ithaca, NY in 1916, the species has spread throughout the basin with multiple records in the ordinarily connected wetlands beginning in the mid 1940s.  The Wisconsin Department of Natural Resources verified a sighting of F. ulmaria in a wetland connected to the Great Lakes in 2021. It is unknown whether or not the species has since been eradicated (Wisconsin DNR 2022).


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 Filipendula ulmaria are found here.

Full list of USGS occurrences

State/ProvinceFirst ObservedLast ObservedTotal HUCs with observations†HUCs with observations†
IN192319231St. Joseph
MI200420042Great Lakes Region; Raisin
MN194220214Beaver-Lester; Cloquet; Lake Superior; St. Louis
NY191619161Seneca
PA195619561Upper Genesee
VT193719803Mettawee River; Otter Creek; Winooski River
WI199520211Beartrap-Nemadji

Table last updated 5/1/2024

† Populations may not be currently present.


Ecology: Often the dominant plant in the habitats it occupies, F. ulmaria is a resilient plant able to adapt to a variety of ecological conditions. Found in bogs, marshes, swamps, fens, dunes, roadside ditches, and along riverbanks, the species requires saturated soils. The species is frost tolerant but not salinity tolerant (Hanslin and Eggen 2005, Wisconsin DNR 2011). The species tolerates a variety of soil types ranging from sandy to clay soils and prefers alkaline soils (Wisconsin DNR 2011).   Filipendula ulmaria dominates the vegetation below the line of winter flooding and is a relatively anoxia-tolerant plant due to the capacity of its underground rhizomes to withstand prolonged oxygen deprivation (Barclay & Crawford 1982; Braendle & Crawford 1987). Rhizomes of this species can be kept in an anaerobic incubator for over 2 weeks and will resume shoot growth when planted with access to oxygen(Studerehrensberger, K., et al. 1993).  Filipendula ulmaria, however, is not capable of shoot extension under experimental anoxia and endures oxygen deprivation in a quiescent state therefore total inundation can impede growth (Barclay & Crawford 1982 Braendle & Crawford 1987, Johansson and Nilsson 2002). F. ulmaria reproduces both sexually and asexually via rhizomes.

In Falinska (1995), stages of clonal colony growth were identified. Colony establishment occurs for two or three growing seasons during which time the leaf rosette and the root system develop. During the subsequent growing seasons, 10-20% of plants produce one or two flowering shoots. Buried  seeds may remain viable for up to a year if in soil that is not waterlogged, however viability in a group of seeds is reduced to 10% or lower after two years (Bekker et al. 1998). The addition of phosphorus into soil appears to have a positive effect on germination rates (Bekker et al. 1998).

F. ulmaria has three known natural enemies. The rust pathogen Triphragmium ulmariae targets the petioles of F. ulmaria and causes mortality, primarily in seedlings. The other two are leaf beetles, Altica engstroemi J. Sahlberg and Galerucella. tenella (L.) (Wisconsin DNR 2011). These species are native to Eurasia. While consumed by herbivores such as moose and deer, those species do not show a preference for F. ulmaria (Axelsson and Stenberg 2014, Missouri Botanical Garden 2022).


Great Lakes Means of Introduction: Filipendula ulmaria has a high probability of introduction to the Great Lakes (Confidence level: High).

Potential pathway(s) of introduction: Natural dispersal, hitchhiking, unauthorized or intentional release, stocking, planting, escape from recreational culture, and escape from commercial culture.

F. ulmaria is already present in the Great Lakes region as it is sold at plant nurseries within the region and available for purchase via online vendors to gardeners who value its hardiness and attractiveness to pollinators (Stanton et al 2010; Hawkins et al. 2015). It is most likely that the plant will escape recreational cultivation through accidental planting and rhizomal spread. The seeds, measuring 2-3mm in diameter, may be spread through hitchhiking on boots and gardening equipment. Seeds can also be transported by water but are unlikely to germinate while completely submerged.


Great Lakes Status: The Wisconsin Department of Natural Resources verified a sighting of F. ulmaria in a wetland connected to the Great Lakes in 2021. It is unknown whether or not the species has since been eradicated (Wisconsin DNR 2022).

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

F. ulmaria’s native range in Europe and Asia includes areas climatically similar to the Great Lakes region. It is frost tolerant, anoxia tolerant, and able to grow in low nutrient conditions (Barclay & Crawford 1982; Braendle & Crawford 1987). While it prefers alkaline soils, the species can grow in a wide range of soil pH levels and is categorized as a generalist (Pauli et al. 2002). The species often outcompetes other organisms in its native habitat, becoming the dominant species in meadows or fens (Cherednichenko and Borodulina 2018).

However, climate change could make the Great Lakes basin less hospitable for the species. The species is not drought tolerant and requires shade (Nazrul-Islam 1983, Wisconsin DNR 2011). Increasing temperatures and increasing drought frequency and intensity would reduce the amount of habitat available for F. ulmaria to colonize. The species does not possess significant tolerance for salinity. Small amounts of saltwater reduce germination rates to near zero (Hanslin and Eggen, 2005). Rising salinity in the Great Lakes basin due to road salt runoff would slow establishment of the species.


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

EnvironmentalBeneficial


Filipendula ulmaria has the potential for high environmental impact if introduced to the Great Lakes.

The species is able to outcompete species for habitat, nutrients, and light, often becoming the dominant species in fen, marsh, and wet-soil meadow ecosystems. In Axelsson and Stenberg (2014), native fireweed had lower flowering rates, growth rates, branching patterns, and survival rates inside of F. ulmaria patches compared to outside of meadowsweet patches regardless of the presence of herbivores. The same study also found evidence of F. ulmaria altering predator-prey relationships between fireweed and moose. F. ulmaria conferred associational resistance to fireweed plants in close proximity to F. ulmaria patches, reducing herbivory by moose (Axelsson and Stenberg 2014). F. ulmaria is also a vector of two invertebrate species,  Altica engstroemi J. Sahlberg and Galerucella tenella (L.) that feed upon strawberry plants (Stenberg and Axelsson, 2008). Introduction of live plants from Europe could release those species into the Great Lakes region.

There is little or no evidence to support that Filipendula ulmaria has the potential for significant socioeconomic impacts if introduced to the Great Lakes.

Filipendula ulmaria has the potential for high beneficial impact if introduced to the Great Lakes.

Pollinators show preference to F. ulmaria flowers (Hawkins et al. 2015). The plant also functions as an important microhabitat.  Insect communities in F. ulmaria plants numbered 26 unique species employing a variety of life history strategies (Dreyer and Kirsch 1987). The species also assists in reducing nutrient loads. When placed in buffer strips surrounding agricultural fields, the presence of F. ulmaria aided the uptake of phosphorus and nitrogen (Kuusemets et al. 2001).

The species also possesses several medicinal and research applications. Meadowsweet has long been used by herbalists for its anti-inflammatory properties. The flowers contain tannins and salicylates and are thought to mildly reduce pain and fever. They have also been used to treat stomach complaints, such as heartburn. Some research in laboratory animals has been conducted to investigate their effectiveness for ulcers, but results are not conclusive (Flora of North America, 2022).Recent research of F. ulmaria and the compounds within the plants revealed additional properties. F. ulmaria extract is an effective inhibitor of colorectal carcinogenesis, reducing the formation of tumors and the frequency of malignant tumor growth (Bespalov et al. 2018). Extracts of F. ulmaria inhibited the growth of cell lines associated with melanoma, lung cancer, and breast adenocarcinoma (Lima et al. 2014). Extracts of the plant have also shown promise in the development of treatments for neurodegenerative disorders such as Parkinson’s and Alzheimer’s (Neagu et al. 2015). F. ulmaria was also identified as possessing multiple antimicrobial compounds with the potential to be used in antimicrobial biofilm products (French et al. 2018).

This species is widely available online in the ornamental and herbal medicine trades. Besides seeds and live plants, it is possible to buy ground herbs and essential oil products infused with F. ulmaria.


Management: Regulations (pertaining to the Great Lakes region)

This species is not on the Illinois Aquatic Life Approved Species List and is illegal to be imported or possessed alive without a permit (515 ILCS 5/20-90).

It is a restricted species in Wisconsin, where there is a ban on the transport, transfer and introduction of this species, but possession is allowed (Chapter NR 40, Wis. Adm. Code)

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

Control

Biological

No known biological control methods for this species are in use. However, F. ulmaria is a host for the fungus Triphragmium ulmariae, which causes meadowsweet rust gall on the petioles of plants, leading to chemically-induced swelling and often plant death, especially in seedlings (Burdon et al. 1995).

Physical

Physical control methods center on digging up and removing the entire plant, ensuring that the root system is removed, otherwise there is a risk of a regeneration via the rhizomes. Mowing the shoots can temporarily stunt growth, but over the course of a growing season the plant will regenerate (Kolos and Banaszuk 2021). Kolos and Banaszuk (2021) also found that mowing fields of F. ulmaria annually can lead to increases in its coverage.

Chemical

Herbicides containing glyphosate and mecoprop are effective in managing F. ulmaria populations (Marrs et al. 1989, Russo et al. 2020). However, F. ulmaria occasionally demonstrated a resistance to low levels of herbicide, increasing the odds that non-target species will be affected by herbicide applications (Marrs et al. 1989).

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


References (click for full reference list)


Author: Pfingsten, I.A. and D. Rose


Contributing Agencies:
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Revision Date: 1/16/2024


Citation for this information:
Pfingsten, I.A. and D. Rose, 2024, Filipendula ulmaria (L.) Maxim.: 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=3810&Potential=N&Type=0&HUCNumber=DGreatLakes, Revision Date: 1/16/2024, Access Date: 5/2/2024

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.