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Frangula alnus


Frangula alnus Mill., commonly known as alder buckthorn or glossy buckthorn, is a multistemmed or small in the family , typically reaching heights of up to 7 meters with a main stem diameter of up to 25 centimeters. It is characterized by glossy, elliptical leaves 5-8 centimeters long, small greenish-yellow flowers less than 6 millimeters across arranged in umbellate clusters, and berry-like drupes that ripen from green to red to black, each containing two to three seeds. Native to temperate and boreal forests across (excluding and the far north), northern , and western , the species thrives in a variety of soils but prefers moist, nutrient-rich sites such as riverbanks, , and edges.
Introduced to in the late for ornamental purposes and rehabilitation, F. alnus has spread aggressively across the northeastern and and southeastern , invading , forests, and disturbed areas where it forms dense monocultures that suppress native plants, reduce , and alter through high decomposition rates. Its rapid radial growth—up to 6-7 meters per year in some stands—prolific seed production dispersed by birds, and ability to resprout vigorously after disturbance contribute to its invasiveness, often dominating over 90% of in affected and altering suitability for . The bark of F. alnus contains glycosides such as frangulin, which hydrolyze to yield active compounds, leading to its traditional and regulated medicinal use as a stimulant purgative in , though excessive consumption risks and dependency. Extracts from the plant also exhibit , , and properties in laboratory studies, supporting potential applications beyond laxation, but clinical evidence remains limited. As a , it facilitates in its native range but disrupts ecological balance as an exotic, prompting widespread management efforts including mechanical removal and application in invaded regions.

Taxonomy and systematics

Classification and synonyms

Frangula alnus Mill. is classified in the kingdom Plantae, phylum Streptophyta, class Equisetopsida, subclass Magnoliidae, order Rosales, family Rhamnaceae, genus Frangula. The species epithet alnus refers to its habitat association with alder trees, while the genus name distinguishes it from Rhamnus based on anatomical features such as the absence of a crystal lattice in the wood rays. The accepted binomial Frangula alnus was described by in 1768. Prior to its reclassification into Frangula, the species was commonly known under the synonym Rhamnus frangula L., proposed by in 1753, reflecting its earlier placement in the broader Rhamnus genus. Additional synonyms include Rhamnus frangula var. angustifolia Loudon and infraspecific taxa such as Frangula alnus f. angustifolia (W.R. Franz. ) A. Löve & D. Löve, though these pertain to variants rather than the nominate species. The taxonomic shift to Frangula emphasizes phylogenetic distinctions within , supported by morphological and molecular evidence distinguishing it from Rhamnus species like R. cathartica.

Etymology and historical naming

The genus name Frangula originates from the Latin verb frangere, meaning "to break," in reference to the fragile or brittle quality of the twigs and branches. This etymological root underscores the plant's mechanical properties, with multiple botanical references confirming the association with easily snapping wood. The specific epithet alnus alludes to the plant's common occurrence in moist, habitats alongside true alders of the Alnus, or to superficial resemblances in leaf form. This naming reflects observed ecological associations rather than close taxonomic relation, as Frangula alnus belongs to the family while Alnus is in . Historically, the species was initially classified by as Rhamnus frangula in his 1753 , grouping it with other buckthorns based on fruit and habit similarities. In 1768, transferred it to the segregate genus , distinguishing it from Rhamnus proper by features such as consistently hermaphroditic flowers and a five-lobed , rather than the dioecious or unisexual blooms typical of Rhamnus. This reclassification has persisted, with Frangula alnus Miller recognized as the valid binomial in modern , though Rhamnus frangula L. remains a in some older or regional floras. Common names like "alder buckthorn" or "breaking buckthorn" echo these etymological and historical elements, emphasizing habitat affinity and wood brittleness.

Description and morphology

Physical characteristics


Frangula alnus is a deciduous shrub or small tree that grows to heights of 3–7 m (10–23 ft), typically multi-stemmed from the base with a spreading crown and lacking thorns.
The bark on mature stems is gray to brown, smooth to slightly ridged, and marked by prominent white lenticels; young twigs are slender, hairless, and green to reddish-brown.
Leaves are simple, alternate (occasionally subopposite), elliptical to ovate or obovate, measuring 3–7 cm long and 1.5–4 cm wide, with glossy dark green upper surfaces, paler undersides, and entire to slightly wavy margins; they turn yellow in autumn.
Flowers are small (2–3 mm across), greenish-yellow, five-petaled, and borne in axillary umbels of 2–10 from May to June; they are functionally dioecious, with plants producing either mostly staminate or pistillate flowers.
Fruits are spherical drupes 6–8 mm in diameter, initially green, maturing to red then black from July to September, each containing 2–3 seeds; a single plant may bear fruits at various stages of ripeness simultaneously.

Reproduction and growth cycle


Frangula alnus flowers from late May through June in its native range, producing small, 4- to 5-merous creamy-green blooms in axillary umbels or solitary on new growth. These hermaphroditic flowers, measuring 2.5–3 mm, facilitate pollination primarily by insects, though the species can exhibit dioecious tendencies in some populations.
Following pollination, fruits develop as drupes that ripen from early July to September, shifting from green to black and containing 2–3 seeds each. Birds and small mammals consume the fruits, aiding seed dispersal via endozoochory; however, many seeds fall directly beneath parent plants, leading to dense seedling clusters. Seeds possess physiological dormancy, necessitating 90–120 days of cold stratification at 1–5°C to break, with optimal germination occurring in spring at soil temperatures of 20°C, yielding up to 70% success under favorable moist conditions.
Vegetative reproduction occurs through root suckering and resprouting from cut or damaged stems, enabling rapid clonal spread in disturbed sites. The species exhibits rapid juvenile growth, forming multi-stemmed shrubs initially before potentially developing into single-stemmed trees up to 7 m tall, with a prolonged growing season extending leaf production into late autumn before deciduous leaf drop. Plants reach reproductive maturity within 3–5 years under optimal conditions, sustaining annual cycles of flowering and fruiting thereafter.

Distribution and habitat

Native range

Frangula alnus is native to a broad region spanning Europe, western Asia, and northwestern Africa. In Europe, its distribution covers most temperate zones from Ireland and the British Isles eastward across the continent to the Urals and Caucasus, including southern boreal and cool temperate forests, though it becomes rarer in extreme northern and southern margins. The species extends into , reaching central and in the east, primarily in temperate biomes. In , it occurs in the northwest, specifically , , and . This native distribution reflects adaptation to and habitats across these Palearctic regions.

Introduced and invasive ranges

Frangula alnus was introduced to approximately 200 years ago, primarily as an ornamental , for hedgerows, forestry plantings, and wildlife habitat enhancement. In , introductions occurred around 100 years ago, with similar planting purposes. It has since become established across the northeastern and , as well as southeastern , including provinces such as , , , , , and . In its introduced range, Frangula alnus is widely regarded as invasive, particularly in moist woodlands, wetlands, forest understories, and disturbed sites. It forms dense thickets that suppress native vegetation through rapid growth, prolific seed production, and allelopathic effects from leaf litter, which inhibit germination and growth of understory plants. Birds and other wildlife facilitate its spread by dispersing viable seeds over long distances, enabling colonization of both open and forested habitats. In the U.S. Forest Service's eastern region assessment from 2004, it was classified as "highly invasive" due to its capacity to alter natural habitats and displace indigenous species. Regulatory measures reflect its invasive status: in , it is listed as a restricted , prohibiting transport or sale; Wisconsin bans its movement into ecosystems; and it is targeted for control in national parks like . No significant invasive populations are documented outside , though its potential for spread warrants monitoring in other temperate regions with suitable wetland habitats.

Ecology

Native ecosystem roles

In native Eurasian ecosystems, Frangula alnus primarily functions as a light-demanding pioneer , rapidly colonizing disturbed sites including clearings, edges, riverbanks, , wet heaths, and bogs, where it establishes early successional cover before yielding to more shade-tolerant competitors in maturing stands. It occupies moist, mildly acidic soils in diverse settings such as mixed boreal conifer s dominated by Picea abies and Betula spp., temperate broadleaf woodlands with Quercus and , and riparian alluvial zones featuring , , and Salix spp., typically from to 2,000 m elevation. The species supports pollinators through its spring flowers, which secrete nectar attracting honeybees (Apis mellifera), bumblebees (Bombus spp.), wasps, and flies. Its drupes provide winter forage for frugivorous birds like thrushes and for small mammals such as mice, while buoyant fruits enable hydrochorous dispersal and flotation for up to two weeks in freshwater, with primary seed spread mediated by birds and secondary contributions from mammals and gravity. Foliage serves as a key resource for herbivorous insects, particularly as the primary larval host plant for the brimstone butterfly (), thereby bolstering Lepidopteran populations in and understories.

Interactions in introduced ecosystems

In introduced ecosystems, particularly wetlands and forests of , Frangula alnus primarily interacts through intense competition with native vegetation, forming dense monocultures that suppress growth via shading and resource preemption. Its early leaf-out in spring—often by mid-April—and late retention of foliage into November create a prolonged canopy that reduces light availability for native herbaceous , leading to decreased cover (P=0.048) and woody (P<0.001) in invaded pine stands in New Hampshire. Studies in Illinois and Vermont wetlands document displacement of native s and forbs, with total richness declining in Allegheny National Forest savannas (P<0.002). However, impacts vary by invasion stage and site; a 27-year invasion in Quebec's Boisé des Terres Noires reserve showed only moderate homogenization of plant communities without strong shifts in diversity or abundance. Interactions with fauna include seed dispersal by birds such as and , which consume its fruits despite their laxative emodin content, facilitating rapid spread but potentially offering low nutritional value due to high sugar and low fat composition. It supports certain native insects, including a sevenfold population increase in (Callophrys henryi) in Ontario from 1980 to 1996, serving as a host plant. Arthropod assemblages on F. alnus in North American invasions feature high abundances of generalist orders like Hemiptera (39.8% of individuals) and Diptera (22.3%), including the invasive pest Drosophila suzukii that exploits fruits for reproduction, but lack specialist herbivores native to its European range, potentially reducing top-down control and enabling persistence. Saprophagous macroarthropod communities experience weak effects, with slight declines in richness and evenness (P<0.02) under dense invasions in Quebec, indicating limited disruption to detrital processes. Abiotic interactions involve alterations to soil nutrient dynamics, where F. alnus leaf litter—characterized by low carbon-to-nitrogen ratios (P=0.085 in Massachusetts sites)—decomposes rapidly, accelerating nitrogen mineralization and potentially favoring further invasion by nitrophilous exotics. In Wisconsin peatlands, its dominance correlates with shifts in soil microbial activity and earthworm abundance, enhancing nitrogen cycling but degrading conditions for oligotrophic natives. It also hosts pathogens like oat crown rust (Puccinia coronata) and alfalfa mosaic virus, which may spill over to native grasses and legumes, amplifying disease pressure in mixed communities. In wetland habitats, dense stands influence hydrology by stabilizing soils and intercepting precipitation, though direct water table effects remain site-specific and tied to invasion density.

Evidence on ecological impacts

Frangula alnus invasions in North American wetlands and forests lead to dense shrub layers that suppress native understory vegetation through shading and competition for resources, resulting in reduced species richness and altered community composition. Multiple field studies document declines in native herbaceous and woody plant diversity under F. alnus canopies, with one analysis of New England pine forests showing inhibited juvenile recruitment of canopy trees, favoring shade-tolerant species while reducing growth and survival of others across all tested taxa. In wetland habitats, this shading effect eliminates competing natives, promoting F. alnus dominance and simplifying vertical structure, as evidenced by surveys in the Great Lakes region where early leaf-out and prolonged retention exacerbate light limitation. Soil biogeochemistry is also modified by F. alnus, with empirical measurements from invaded Minnesota sites revealing elevated pH, nitrogen pools, and nutrient availability correlated with buckthorn abundance, potentially facilitating further invasion while disadvantaging oligotrophic native flora. These changes persist post-removal in some cases, indicating legacy effects on microbial communities and nutrient cycling that hinder restoration. However, not all biotic interactions show strong negative responses; a 27-year invasion study in a wet deciduous forest found minimal impacts on saprophagous macroarthropod diversity and abundance, suggesting context-dependent effects where plant community shifts dominate over detritivore alterations. Evidence for broader trophic impacts remains limited but includes facilitation of bird-dispersed spread via abundant fruits, though nutritional value for native herbivores is low, potentially reducing forage quality in invaded areas. In partially logged white pine stands, F. alnus density increases with disturbance intensity, amplifying invasion success and associated biodiversity losses compared to uncut sites. Overall, while many observational and experimental studies affirm negative ecological consequences—particularly in wetlands—some quantitative assessments highlight weaker or variable effects, underscoring the need for site-specific evaluation amid confounding factors like invasion age and co-occurring invasives.

Phytochemistry and toxicology

Key chemical compounds

The bark of Frangula alnus primarily contains hydroxyanthracene glycosides, a class of anthraquinone derivatives that constitute its key active chemical compounds and underpin its pharmacological effects, such as laxative activity through stimulation of colonic peristalsis. These glycosides are predominantly O-glycosides bound at positions 6 and/or 8 of the anthraquinone nucleus, with glucofrangulin A (1,8-dihydroxy-3-methyl-6-[(α-L-rhamnosyl-(1→2)-β-D-glucosyl)oxy]anthraquinone) being the most abundant, accounting for approximately 40% of the total hydroxyanthracene glycoside content. Other principal glycosides include glucofrangulin B (emodin 1-O-glucoside-8-O-rhamnoside), frangulin A (emodin 8-O-rhamnoside), and frangulin B (emodin 6-O-rhamnoside), alongside minor components such as emodin-8-O-β-D-glucoside and various frangula-emodin glycosides. Free aglycones, released via microbial hydrolysis in the gut, are present in trace amounts (typically less than 1% of total anthraquinones) and include emodin, aloe-emodin, chrysophanol, and physcion; emodin concentrations in bark extracts have been quantified at up to 2.03 mg/g dry weight. The European Pharmacopoeia specifies a minimum content of 7.0% glucofrangulins (expressed as ) in dried bark, reflecting standardized quality for medicinal use, though total hydroxyanthracene derivatives may range from 3-7% depending on harvest timing and storage, as glycosides hydrolyze to inactive forms if bark is not aged properly. Secondary compounds include flavonoids (e.g., quercetin and kaempferol glycosides), condensed tannins, and mucilage, which contribute to antioxidant properties but are not the dominant constituents. Fruits contain lower levels of similar anthraquinones but higher emodin and free aglycones, rendering them more acutely toxic than bark. Volatile oils in leaves and bark feature monoterpenes like geranial and caryophyllene oxide, but these are minor and not pharmacologically significant.

Toxicity and safety considerations

Frangula alnus contains anthraquinone glycosides such as and , which are responsible for its purgative effects and potential toxicity. All parts of the plant, particularly the fresh bark and fruits, are considered poisonous if ingested without proper preparation, leading to gastrointestinal irritation. In humans, ingestion typically causes low-severity poisoning characterized by nausea, vomiting, and diarrhea due to the glycosides stimulating bowel motility. The fruits are especially hazardous, containing high concentrations of toxic compounds that can induce severe laxative effects, and they should not be consumed raw. Fresh bark is overtly toxic and must be aged for at least one year to hydrolyze emodins into less irritating anthraquinones before medicinal use; unprocessed material can cause cramps, electrolyte imbalances, and dependency with prolonged exposure. In animals, the plant poses risks including documented poisoning in horses from branch ingestion, manifesting as colic and diarrhea. Fruits act as strong laxatives in birds, facilitating seed dispersal but potentially causing dehydration at high doses, though no widespread mortality is reported. Livestock may experience similar gastrointestinal distress if browsing occurs, though emodin's cytotoxicity requires further empirical validation in vivo. For safety in medicinal applications, processed alder buckthorn bark is likely safe for short-term oral use in adults (up to 8-10 days) as a stimulant laxative, but it can provoke abdominal cramps and is contraindicated in pregnancy, lactation, or cases of intestinal obstruction due to risks of fetal harm or infant diarrhea. Misuse may lead to hypokalemia, cardiac arrhythmias, or muscle weakness, particularly with concurrent digitalis therapy, emphasizing the need for medical supervision and avoidance in children or debilitated individuals. Handling requires gloves to prevent dermatitis in sensitive individuals.

Human uses

Medicinal applications

Frangula alnus bark, harvested after at least one year of aging to hydrolyze anthraquinone glycosides into active forms such as frangula-emodin and emodin, serves primarily as a stimulant laxative due to its anthranoid content, which irritates the colonic mucosa and promotes peristalsis. Traditional European pharmacopoeias, including those from the European Medicines Agency (EMA), endorse its use for short-term relief of occasional constipation in adults, typically at doses of 0.5–1.5 g of dried bark equivalent per day in decoction or extract form. Clinical comparisons indicate comparable efficacy to cascara sagrada (Rhamnus purshiana) for mild constipation, with onset of action within 6–12 hours, though rigorous randomized controlled trials remain limited, relying largely on historical use and pharmacological plausibility from anthraquinone mechanisms. Beyond laxation, the bark exhibits cholagogue properties, aiding bile flow, and has been employed historically for hepatic conditions like jaundice and cirrhosis, attributed to its bitter principles and mild tonic effects on digestion. In vitro studies demonstrate antioxidant and antimicrobial activities from anthraquinones, potentially supporting adjunctive roles in gut health, but human evidence for these is anecdotal or preliminary, with no established therapeutic indications beyond constipation. Claims of anticancer benefits, such as in the , lack substantiation from controlled trials, and exploratory research on emodin shows cytotoxicity against certain cell lines without clinical validation. Safety profiles emphasize short-term use only, as prolonged administration (>10 days) risks electrolyte depletion, particularly , and dependency via colonic inertia; fresh bark is contraindicated due to emetic . The contraindicates it in , , and intestinal obstruction, with interactions possible alongside cardiac glycosides or diuretics exacerbating loss. Despite traditional safety in moderated doses, modern oversight favors senna or bulk laxatives for chronic cases due to superior risk-benefit profiles in available data.

Ornamental and industrial uses

Frangula alnus has been employed in ornamental horticulture primarily for its glossy foliage, attractive berries, and adaptability to hedging. Historically introduced to North America in the 19th century, it was planted as a landscape shrub for hedges, windbreaks, and wildlife habitat enhancement due to its tolerance of wet soils and partial shade. Cultivars such as 'Fine Line' and 'Columnaris' are valued for their narrow, columnar growth habit, suitable for urban accents or tall hedges reaching 12-15 feet. However, its promotion in landscaping has declined owing to invasive tendencies in introduced regions. Industrially, the wood of Frangula alnus yields high-quality charcoal prized for gunpowder production and artistic applications, stemming from its dense, brittle structure. The bark and leaves extract a yellow dye, while unripe berries provide green pigments used in calico printing and the woollen trade; ripe berries yield blue or grey tones. Rotted bark has been processed for red dyes on wool, as documented in traditional European practices revived in experimental dyeing. Wood also serves for small-scale manufacturing of items like nails, shoe lasts, and veneer. These applications, largely historical, leverage the plant's phytochemical content but are limited by sustainability concerns in native Eurasian contexts.

Management and control

Control methods

control methods for Frangula alnus include hand-pulling or digging small seedlings and saplings when soil is moist to remove the entire , preventing resprouting. Larger stems can be cut or girdled by stripping to expose the layer over 6-10 inches of height, though repeated treatments over multiple seasons are often necessary as vigorous root sprouting commonly occurs. Mowing or repeated cutting (twice per season for 2-3 years) may reduce plant density and height but provides only temporary suppression without addressing roots. Chemical control is more effective for mature plants and involves cut-stump treatments, where stems are severed near ground level and immediately painted with herbicides such as or . Basal bark applications of sprayed around lower stems offer an alternative for plants under 6 inches in diameter. Optimal timing for these applications is late fall through early winter, when the plant translocates nutrients to , enhancing herbicide uptake and minimizing non-target impacts; however, resprouting may resume after 2-3 years, necessitating monitoring and follow-up. Prescribed fire can kill seedlings and top-kill mature individuals but induces prolific sprouting from roots, requiring repeated burns every 5-6 years or integration with other methods for long-term reduction. , combining mechanical removal, targeted herbicides, fire, and native revegetation, yields higher success rates, such as near-total elimination in treated sites where only 3 of 150 plants survived after multi-year efforts. Prevention of seed spread by targeting fruiting plants before mid-summer and restoring natural hydrology in wetlands further aids control. Biological options, including by goats or experimental biocontrol agents, show promise but lack widespread validation for eradication.

Regulatory measures and economic implications

In regions where Frangula alnus has become invasive, such as parts of North America, regulatory measures primarily aim to curb its spread through prohibitions on sale, transport, and planting. In Minnesota, it is designated a restricted noxious weed under state law, making importation, sale, and transport illegal. The sale of nonnative buckthorns, including F. alnus, is banned in Minnesota and Illinois to prevent further establishment. New York classifies it as prohibited following a high-risk assessment by the state Invasive Species Council for ecological damage. It appears on invasive species lists in multiple states, including Connecticut and Massachusetts, often triggering mandatory control on public lands. In its native range, regulations emphasize safe medicinal harvesting rather than restriction as a weed. The approves frangula bark (Frangulae cortex) for well-established use in short-term relief, but limits application to adults and adolescents over 12 years, for durations not exceeding one week, with bark requiring at least of aging to mitigate emodin-related toxicity. Economic implications in invaded ecosystems center on management costs outweighing benefits. Control via mechanical removal or herbicides incurs expenses of $500–$700 per acre in forested sites, as reported by in . Broader buckthorn management averages $202 per in Canadian contexts, reflecting labor and chemical inputs. These outlays stem from reduced timber productivity, altered , and losses, though overall direct economic damage remains modest compared to other invasives, with indirect effects like hosting crop pathogens such as soybean aphid. In native areas, extraction supports a niche pharmaceutical sector, historically valued for purgative compounds like frangulin, but current market scale is limited and regulated to ensure .

References

  1. [1]
    Frangula alnus - USDA Forest Service
    In North America, glossy buckthorn is commonly described in wet to moist habitats including bogs, fens, marshes, riverbanks, pond margins, and disturbed areas ...
  2. [2]
    Frangula alnus (alder buckthorn) | CABI Compendium
    Review of Natural Distribution. F. alnus is found throughout Europe, except Iceland and the extreme north, with a latitudinal limit for the species ranging from ...
  3. [3]
    glossy buckthorn: Frangula alnus (Rhamnales - Invasive Plant Atlas
    Frangula alnus invades moist woodlands and disturbed areas throughout the Northeast and Midwest. Its rapid growth and prolific seed production make this plant ...
  4. [4]
    Invasive Plant Profile: Glossy Buckthorn - National Park Service
    Aug 27, 2020 · Glossy buckthorn (Rhamnus frangula L.), is an invasive shrub species that has taken over the understories of many North American forests and wetlands.
  5. [5]
    Extracts from Frangula alnus Mill. and Their Effects on ... - NIH
    Oct 14, 2022 · They show antioxidant, antibacterial, fungicidal, antiviral, and anticancer properties, and are used in medicine as laxatives (mild agents ...
  6. [6]
    Frangula alnus - Global Invasive Species Database
    Aug 29, 2005 · It can grow in soils of any texture. In North America, wetlands are invaded by Frangula alnus. Frangula alnus is also a typical woody pioneer ...
  7. [7]
    Frangula alnus Mill. | Plants of the World Online | Kew Science
    Frangula alnus Mill. ; Phylum Streptophyta ; Class Equisetopsida ; Subclass Magnoliidae ; Order. Rosales ; Family. Rhamnaceae.
  8. [8]
    [PDF] Frangula alnus Global Invasive Species Database (GISD) 2025 ...
    Synonym. Rhamnus frangula , L. Rhamnus frangula var. angustifolia ,Loud. Rhamnus frangula subsp. columnaris ,hort. Similar species. Rhamnus cathartica.<|control11|><|separator|>
  9. [9]
    Frangula alnus - North Carolina Extension Gardener Plant Toolbox
    The genus name Frangula comes from the word "frango", meaning fragile or brittle, in reference to the tendency of the twigs to break easily. The species ...Missing: etymology | Show results with:etymology
  10. [10]
  11. [11]
  12. [12]
    Frangula alnus | Landscape Plants | Oregon State University
    It was subsequently separated by Phillip Miller in 1768 into the genus Frangula on the basis of its hermaphrodite flowers with a five-parted corolla (in Rhamnus ...
  13. [13]
    Glossy Buckthorn (Frangula alnus) - Illinois Wildflowers
    Description: This is usually a multistemmed shrub (less often a small tree) about 3-20' tall. The bark of older branches or trunks is gray and slightly ...Missing: morphology | Show results with:morphology<|separator|>
  14. [14]
    Glossy Buckthorn - Invasive Plants - Maine.gov
    Description: Perennial, deciduous, shrub or small tree, often multi-stemmed, can be single-trunked, to ~20' tall. Despite name, lacks thorns. Leaves: Simple, ...Missing: morphology | Show results with:morphology
  15. [15]
    Frangula alnus (European Alder-Buckthorn) - FSUS
    Common name: European Alder-Buckthorn, Glossy Buckthorn. Phenology: May-Jun; Jul-Sep. Habitat: Forested areas, other disturbed areas. Distribution: Native of ...
  16. [16]
    Rhamnus frangula L. - Nonindigenous Aquatic Species
    Glossy buckthorn is typically in bloom from late May until the first frost (WIDNR 2008). It produces fruit from early July through September, and it is not ...Missing: phenology | Show results with:phenology<|separator|>
  17. [17]
    Impact of Environmental Conditions on Seed Germination of Glossy ...
    Glossy buckthorn seeds exhibited physiological dormancy and required cold stratification to germinate. At 12 °C, only 14% of the seeds could germinate. At ...
  18. [18]
    [PDF] Buckthorns – Rhamnus cathartica & Frangula alnus
    The buckthorns reproduce sexually by seed and vegetatively through root suckering. Both buckthorns produce fruits that are readily eaten, and thus seeds are ...
  19. [19]
    Glossy Buckthorn: An Exotic Invasive Plant Fact Sheet
    Nov 14, 2011 · Therefore, it takes only one glossy buckthorn to produce a colony of reproducing plants if left unchecked. Cut or broken stems sprout and ...
  20. [20]
    [PDF] Glossy buckthorn - Michigan Natural Features Inventory
    Glossy buckthorn is a small tree or shrub with a spreading crown growing up to 6 m (20 ft) tall. Typically, it has multiple stems when young, and develops into ...Missing: cycle | Show results with:cycle
  21. [21]
    [PDF] Common buckthorn, Rhamnus cathartica - Vermont Invasives
    Plants mature at 5-6 years old. Seed production is prolific. Common buckthorn fruits ripen from August to September while glossy buckthorn fruits ripen earlier ...Missing: fruiting | Show results with:fruiting
  22. [22]
    Frangula alnus Glossy buckthorn - EuForGen
    Glossy buckthorn (Frangula alnus) is a deciduous, insect-pollinated, multi-stemmed tree native to Europe, North Africa, and Western Asia.
  23. [23]
    [PDF] Frangula alnus - Forest
    Its wide distribution covers most of the temperate forest zone of Europe up to the Urals and Caucasus, occurring even in the southern Boreal and cool ...Missing: scientific | Show results with:scientific<|separator|>
  24. [24]
    [PDF] Weed risk assessment for Frangula alnus Mill. (Rhamnaceae)
    May 15, 2025 · PLANT SPECIES: Frangula alnus Mill. (Rhamnaceae) (GBIF, 2021). SYNONYMS: Frangula alnus f. angustifolia W.R.Franz, Frangula alnus var.
  25. [25]
    Frangula alnus - GISD
    Aug 29, 2005 · Frangula alnus, commonly known as glossy buckthorn, is a shrub that can grow to seven metres and is sometimes considered a tree.Missing: etymology | Show results with:etymology
  26. [26]
    Frangula alnus | NatureServe Explorer
    Scientific Name: Frangula alnus P. Mill. Other Common Names: glossy buckthorn (EN). ,. Glossy Buckthorn (EN). ,. Nerprun bourdaine (FR). Kingdom: Plantae.
  27. [27]
    Spatial Patterns of Frangula alnus (Rosales: Rhamnaceae) - NIH
    Nov 1, 2023 · Glossy buckthorn (Frangula alnus) (Rosales: Rhamnaceae) is an invasive shrub from Europe, threatening native vegetation in open and ...
  28. [28]
    Glossy or alder buckthorn (Rhamnus frangula) - Minnesota DNR
    Introduced to North America as ornamental shrub, often planted in hedgerows. Glossy or alder buckthorn is on the MDA Restricted noxious weeds list in Minnesota.
  29. [29]
    Frangula alnus | University College Cork
    Frangula alnus, or Alder Buckthorn, is a deciduous tree with blackish brown bark, dark green glossy leaves, and small, dark purple or black berries. It has ...
  30. [30]
    Invasive Glossy Buckthorn (Frangula alnus) Has Weak Impact on ...
    The glossy buckthorn (Frangula alnus Miller) is a shrub in the buckthorn family (Rhamnaceae) and considered to be invasive in Eastern North America. Native to ...
  31. [31]
    Arthropods Associated with Invasive Frangula alnus (Rosales
    Nov 28, 2023 · Invasive plants pose a significant threat to native ecosystems, and understanding their interactions with local arthropod communities is ...
  32. [32]
    [PDF] EFFECTS OF THE INVASIVE SHRUB FRANGULA ALNUS ON SOIL ...
    assess soil impacts by the invasive species. Due ... reproduction of invasive Frangula alnus ... Effects of invasive alien Acacias on nutrient cycling in the.
  33. [33]
    Impact of the invasive shrub glossy buckthorn (Rhamnus frangula L ...
    The increasing dominance of glossy buckthorn in New England pine forests is likely to change the relative abundance of tree species in the forest canopy, and ...
  34. [34]
    Species Profile - Rhamnus frangula - Nonindigenous Aquatic Species
    Identification: Frangula alnus is a shrub or small tree with brownish gray bark speckled with easily distinguished elongated, lighter areas called lenticels ...<|separator|>
  35. [35]
    A tale of two studies: Detection and attribution of the impacts of ...
    Dec 13, 2017 · ... nutrient cycling and earthworms along two separate gradients of invasive shrub abundance. ... Frangula alnus and Lonicera spp., are known ...
  36. [36]
    [PDF] Factors Limiting the Success of Invasive Glossy Buckthorn (Frangula ...
    One particularly damaging invasive plant is glossy buckthorn (Frangula alnus, hereafter. “buckthorn”), a shrub native to Europe that has spread throughout ...
  37. [37]
    Effects of logging history on invasion of eastern white pine forests by ...
    ▻ Frangula alnus was present in all sampled white pine stands, even if uncut. ▻ F. alnus density was greater in partial- and clear-cut stands than uncut stands.
  38. [38]
    [PDF] Assessment report on Rhamnus frangula L. cortex - Draft
    Jan 16, 2019 · Frangula bark consists of the dried, whole or fragmented bark of the stems and branches of Rhamnus frangula L. (Frangula alnus Miller). It ...
  39. [39]
    Toxicity and antioxidant capacity of Frangula alnus Mill. bark and its ...
    Laxative property of F. alnus bark has been attributed to the presence of anthraquinone glycoside derivatives, glucofrangulins and frangulins; glucofrangulins ...
  40. [40]
    Anthraquinone profiles, antioxidant and antimicrobial properties of ...
    Apr 15, 2012 · The most represented anthraquinone derivatives in F. rupestris and F. alnus bark were physcion (0.11 mg/g) and emodin (2.03 mg/g), respectively.
  41. [41]
    [PDF] COMMUNITY HERBAL MONOGRAPH ON FRANGULA BARK ...
    (Frangula alnus Miller). It contains not less than 7.0 per cent of glucofrangulins, expressed as glucofrangulin A. (C27H30O14; Mr 578.5) and calculated with.<|control11|><|separator|>
  42. [42]
    Analysis of the volatile constituents of Frangula alnus Mill. from Iran
    May 17, 2017 · The essential oil of F. alnus contains epoxygeranial (6.0%) and geranial (5.5%) (as main oxygenated monoterpenes) and also caryophyllene oxide ( ...Missing: phytochemistry | Show results with:phytochemistry
  43. [43]
    Frangula alnus - Species Records | Boone County Arboretum
    All parts of the plant should be considered harmful or poisonous to humans if ingested. Nematodes, Japanese beetles, caterpillars, scale and stem cankers could ...Missing: toxicity animals
  44. [44]
    POISONOUS BERRIES – Alder buckthorn | looduskalender.ee
    Aug 11, 2013 · The fruits of the alder buckthorn are very TOXIC, they should on no account be eaten, and the bark of the tree is likewise toxic.Missing: parts | Show results with:parts
  45. [45]
    Frangula alnus Alder Buckthorn PFAF Plant Database
    Physical Characteristics​​ Frangula alnus is a deciduous Shrub growing to 5 m (16ft) by 4 m (13ft) at a slow rate. See above for USDA hardiness. It is hardy to ...Missing: morphology | Show results with:morphology
  46. [46]
    [Alder buckthorn poisoning in horses] - PubMed
    Seven cases of poisoning in horses are reported. This was caused by ingestion of branches of the alder buckthorn (Frangula alnus (mill.) syn. Rhamnus frangula L ...Missing: parts | Show results with:parts
  47. [47]
    Does buckthorn fruit harm birds? | UMN Extension
    Jan 17, 2024 · Buckthorn's fruit has a terrible laxative effect on birds. Whatever poison was in the fruit would help spread the invasive plant faster at the cost of the bird ...
  48. [48]
    Alder Buckthorn - Uses, Side Effects, and More - WebMD
    When taken by mouth: Alder buckthorn is LIKELY SAFE for most adults when taken by mouth for less than 8-10 days. Some people get uncomfortable cramps from alder ...
  49. [49]
    Buckthorn - Drugs and Lactation Database (LactMed®) - NCBI - NIH
    Jun 21, 2021 · Maternal intake of the cathartic buckthorn products might cause loose stools in breastfed infants and their use should be avoided.
  50. [50]
    Alder Buckthorn – Health Information Library | PeaceHealth
    20 to 30 mg of anthraquinone glycosides (calculated as glucofrangulin A) per day ... Use buckthorn (Rhamnus catartica, Rhamnus frangula, Frangula alnus) or alder ...Missing: glucosides | Show results with:glucosides
  51. [51]
    Frangula alnus|alder buckthorn/RHS Gardening
    Potentially harmful: Humans/Pets (dogs): Harmful if eaten. Wear gloves and other protective equipment when handling For further information and contact ...<|separator|>
  52. [52]
    Alder Buckthorn: Health Benefits, Side Effects, Uses, Dose ... - RxList
    Alder buckthorn is a type of laxative called a stimulant laxative. Stimulant laxatives can decrease potassium levels in the body.Missing: pharmacology | Show results with:pharmacology
  53. [53]
    Buckthorn bark - American Botanical Council
    Nov 1, 1984 · With long-term use/abuse: disturbances of electrolyte balance, especially potassium deficiency, albuminuria and hematuria. Pigment implantation ...
  54. [54]
    Frangula alnus Fine Line - Oregon State Landscape Plants
    Common name: Fine Line Alder Buckthorn. Pronunciation: FRANG-gew-la al-NUS. Family: Rhamnaceae. Genus: Frangula. Synonyms: Rhamnus alnifolia.
  55. [55]
    Frangula alnus 'Columnaris' - Plant Finder - Missouri Botanical Garden
    The genus name Frangula comes from the word "frango", meaning fragile or brittle, in reference to the tendency of the twigs of some species to break easily.Missing: etymology | Show results with:etymology
  56. [56]
    Invasive in the Spotlight: Glossy Buckthorn - UNH Extension
    Jul 24, 2019 · It is classified as an invasive species in New Hampshire because it creates dense thickets and outcompetes native plants. Glossy buckthorn leafs ...
  57. [57]
    Reviving an old shade of red: dyeing with rotted alder buckthorn bark
    Mar 23, 2025 · ... (Frangula alnus Mill.) bark was used to dye woollen yarn red. The bark was rotted by leaving it outside for weeks or months before dyeing.
  58. [58]
    Glossy buckthorn | (Frangula alnus) - Wisconsin DNR
    (Frangula alnus) ... An understory shrub or small tree grows up to 20' tall, often with several stems from the base and a spreading crown. Gray to brown bark with ...Missing: height | Show results with:height
  59. [59]
    Controlling buckthorn: the who, what, where, when and how
    Jun 3, 2024 · ... (Frangula alnus). The species arrived in Minnesota from Europe in the 1850s and was planted as an ornamental plant typically used in hedges.<|separator|>
  60. [60]
    Minnesota Noxious Weed List
    The "prohibited-eradicate noxious weeds" category includes noxious weeds that must be eradicated on all lands within the state. ... Frangula alnus Mill. 1999. 10.
  61. [61]
    Rhamnus frangula L. - Nonindigenous Aquatic Species
    The New York Invasive Species Council assessed F. alnus as having a high risk of causing ecological harm and recommended that its use be prohibited (New York ...
  62. [62]
    glossy buckthorn (Frangula alnus Mill.) - Invasive.Org
    Frangula alnus invades moist woodlands and disturbed areas throughout the Northeast and Midwest. Its rapid growth and prolific seed production make this plant ...
  63. [63]
    Frangulae cortex - herbal medicinal product
    Key facts ; English common name. Frangula bark ; Botanical name. Rhamnus frangula L. ; Therapeutic area. Constipation ; Status. F: Assessment finalised ; Date added ...
  64. [64]
    [PDF] NAME OF SPECIES: Rhamnus frangula - Wisconsin DNR
    Rhamnus frangula, also known as European alder buckthorn, is native to Northern Africa, Europe, and Central Asia, and is found in 34 WI counties.Missing: taxonomic | Show results with:taxonomic
  65. [65]
    Economic Impacts of Invasive Species to Canada's Forest Sector
    Buckthorn: The average cost to treat buckthorn was approximately $202/hectare. This cost can vary significantly depending on treatment method, product used, ...Missing: Alder | Show results with:Alder