Alnus glutinosa (L.) Gaertn.

Common Name: Black alder

Synonyms and Other Names:

Alnus alnus (L.) Britton, Betula alnus var. glutinosa L., Betula glutinosa (L.) Lam., European alder, Black European alder

U.S. Geological SurveyCopyright Info

Identification: Alnus glutinosa is usually a medium-sized tree, with a pyramidal or narrowly oval, sparse crown, the base of which is low (if the specimen grows in isolation), though in forests most individuals have straight stems with an umbrella-shaped crown. It rarely grows as a shrub, unless in extreme habitats or if the original stem has been cut at the base. The stem rarely achieves a dbh of over 50 cm but may grow up to 80-100 cm dbh in exceptional cases. The root system is usually not deep and can sometimes be very shallow when the ground water level is high, and roots bear nodules with bacteria (Schinzia mollis) that assimilate atmospheric nitrogen. In boggy conditions the roots are differentiated into horizontal ones with nodules, and stronger almost vertical roots which grow deeper into the soil and lift the tree up, forming characteristic mounds (Piotrowska 1960) and contain aerenchymatic tissue (McVean 1956). The bark of young trees is dark brown and rather smooth, becoming almost black with linear crevices. Leaves alternate, simple, oval or transversely ovate, usually with a retuse apex; margins doubly serrate; dark green above and lighter green below; 4-11 (-14) cm long and 3.5-11 cm broad. Young leaves are sticky to the touch. The species in monoecious, with male catkins 8-12 (-16) cm long, reddish or brownish (with red anthers), loose, protruding from a 7 mm long peduncle; female catkins 3.5 mm long, reddish or brownish, clustered in groups of 3-5, each on a peduncle. Fruits are small, winged seeds grouped in cone-like green strobiles, becoming dark brown or black in late autumn.

Several cultivars including pyramidal forms and trees with finely dissected leaves.

European alder is similar to the native shrub alders found along the streams in the American Northwest but can be distinguished by the notch at the apex of its leaves (Gubanov et al. 2003). Speckled alder (Alnus rugosa) has leaves with a distinct (acute) tip, usually shrubbier than A. glutinosa.

Size: 80 feet

Native Range: Alnus glutinosa has a broad natural range that includes most of Europe except the Arctic and extends into North Africa and Asia. The review of its natural distribution is based mainly Boratynski (1980), also drawing from Hegi (1957) and Ball (1964). Its natural distribution ranges from 63 N (although there are isolated populations up to about 66 N) in Scandinavia, to 36 N in North Africa (Algeria). It is present in almost the whole of Europe (except southwest Spain, northern Scandinavia and northwest Russia). It also grows spontaneously in the Atlas Mountains (Algeria and Morocco) and in some places in northern Turkey, Georgia and on the southern shore of the Caspian Sea (northern Iran). The eastern limit of its continuous range is situated in the vicinity of the border between Russia and Kazakhstan (where some isolated localities have been found up to 76 E).

Map Key
This map only depicts Great Lakes introductions.

Great Lakes Nonindigenous Occurrences: Alnus glutinosa is a moderate to serious invasive species of wet sites in USA, maritime Canada, Australia, India, Republic of Korea,and New Zealand. The species became naturalized in New Zealand in 1914 (Owen 1996). Widespread in the Great Lakes by 1913, now being present in 18 states of USA: CT, DC, DE, IA, IL, IN, KS, MA, MI, MN, MO, NJ, NY, OH, PA, TN, VT, WI.

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 Alnus glutinosa are found here.

State/ProvinceYear of earliest observationYear of last observationTotal HUCs with observations†HUCs with observations†
Michigan1913201811Black-Macatawa; Detroit; Great Lakes Region; Huron; Kalamazoo; Little Calumet-Galien; Manistee; Ottawa-Stony; Pere Marquette-White; St. Clair-Detroit; St. Joseph
New York200820084Eastern Lake Erie; Great Lakes Region; Oneida; Seneca
Ohio200820084Lake Erie; Lower Maumee; Southern Lake Erie; Western Lake Erie
Pennsylvania200820081Lake Erie
Wisconsin200820083Manitowoc-Sheboygan; Northwestern Lake Michigan; Pike-Root

Table last updated 10/17/2019

† 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: Alnus glutinosa establishes readily in wetlands and riparian habitats and forms pure stands or thickets in disturbed wetland sites (Gilman and Watson 1993). It prefers damp or wet ground, often found beside rivers, ponds and canals or in a type of wet woodland called carr, accompanied by willows. Pollination and seed dispersal are by wind. It is relatively variable species and it often hybridizes with other alders. It has been classified as tetraploid (2n=28), hexaploid (2n=42) and octoploid (2n=56).

In the UK, A. glutinosa starts to flower in February when the temperature reaches 10-13°C (McVean 1953). Alnus glutinosa is a light-demanding species and seedlings do not usually survive in the shade of mature trees (Pancer-Kotejowa and Zarzycki 1980). Trees may live up to 100 years (Jaworski 1995), but sometimes on poor sites it may only live for 20-25 years (Savill 1991). The presence of symbiotic bacteria in the root nodules (Akkermans 1978; Van Dijk 1978) enables A. glutinosa to grow on soils that are poor in nitrogen. The root system of specimens growing on flooded soils is differentiated into horizontal roots (with nodules) and the stronger, almost vertical ones that grow deeper. The oxygen conditions in the roots are also improved by aerenchymatic tissue inside roots which have developed under water (McVean 1956). The species is monoecious. Reproduction is mainly by seed, but coppices readily after felling. The seeds are orthodox. Alnus glutinosa grows naturally in various temperate localities with the climate ranging from seasonally cold to warm. Climate data are based on the natural distribution and relevant climatic information (Walter and Lieth 1960).

According to Jurkevic et al. (1968), A. glutinosa grows well where there is a mean annual temperature from 4.0 to 7.5 C, and a mean annual rainfall from 400 to 700 mm. If climatic data from the whole natural range of the species is taken into account, the ecological amplitude of A. glutinosa appears much broader. The estimated mean annual temperature range is 1-18 C and mean annual rainfall range 400-1300 mm. Alnus glutinosa is highly resistant to seasonal frost as it grows in areas where the temperatures drop to -40 C, with the absolute minimum being -49 C, though extremely cold temperatures result in lower annual growth (Jurkevic et al. 1968).  Alnus glutinosa is, however, susceptible to drought (Fabijanowski and Zarzycki 1961). Alnus glutinosa grows naturally mainly on histosols and sometimes on gleysols or fluvisols (FAO 1988; Pancer-Kotejowa and Zarzycki 1980). The species is very resistant to flooding and waterlogging.

Alnus glutinosa grows better on flat areas or even in hollows, and it is one of the most suited species for planting on the banks of the lowland rivers, streams, along ditches, lakes and ponds. The altitudinal distribution ranges from sea level (sometimes even below, in depressions) up to high altitude sites, especially in the mountains located in the south of its range. The maximum altitude for the natural occurrence of A. glutinosa differs in various mountains: up to 1800 m altitude in the Alps (Hegi 1957), 1500 m in Macedonia (Jovanovic 1970), 1300 m in the Carpathians (Blattny and Stastny 1959; Savulescu 1952).

Dozens of insects and diseases have been observed in association with black alder, but few cause serious damage (Funk 1990).

Means of Introduction: Deliberate release.The seeds float well, traveling efficiently when rivers are flowing rapidly (McVean 1953), and also eaten by various wildlife (Gilman and Watson 1993). It has been widely introduced as an ornamental and for soil stabilization and continues to be promoted even in countries where it is known to be invasive.

Status: Established, naturalized.

Great Lakes Impacts:  

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

Alnus glutinosa has been identified as an invasive plant capable of displacing desirable vegetation (Herron et al. 2007, NatureServe 2010). It is associated with a number of nitrogen-fixing actinomycetes fungi that directly increase soil nitrogen concentrations (Hall et al. 1979). In general, black alder is an ornamental species, but its use in the Great Lakes varies. It may be discouraged for use in natural areas due to its reported ability to form monocultures (Eckel 2003, NatureServe 2010). With the potential to dominate wetland communities, the Ontario Invasive Plants Working Group has labeled A. glutinosa as a top priority for management (Havinga 2000).

Black alder is a pioneer species capable of modifying the environment by colonizing exposed soils, fixing nitrogen, and producing copious amounts of litter (Funk 1990, USDA NRCS 2006). Black alder leaf litter easily leaches water-soluble organic substances that may alter soil conditions and impact nearby plants (Funk 1990). Areas planted with black alder at a mine restoration site in Kentucky had twice as much leaf litter and higher concentrations of soluble salts than areas without black alder. This leaf litter also resulted in significantly more acidic spring soil (Plass 1977).
Results from a study conducted by Vogel et al. (1997) suggest that as atmospheric carbon dioxide concentration increases, nitrogen fixing species such as black alder will be able to fix more atmospheric nitrogen. This will lead to an increase in nitrogen concentration (above current fixation rates) in leaves and, ultimately, in soils via leaf litter decomposition (Vogel et al. 1997).

Black alder could further impact water courses by de-oxygenating the water, shading out other species, and degrading habitat. Black alder’s dense root system is capable of trapping sediment and subsequently altering water flow in wetland ecosystems (Funk 1990). European alder hybridizes readily with many other alders (Funk 1990).

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

Current research on the beneficial effects of Alnus glutinosa in the Great Lakes is inadequate to support proper assessment.
This tree has both ornamental and practical value. While it is not considered a commercially-valuable hardwood, Alnus glutinosa is kept by some US nurseries to meet the demand for use in orchards (as a windbreak) and at mine revegetation sites (Mikola 1958, USDA NRCS 2006). However, the wood may be used for carving and the leaves for medicinal purposes (Mills et al. 1993). Within its native range, black alder is used for furniture, wooden-ware, cooperage, charcoal, and wood fiber industries (Genys 1988).

In a supercritical carbon dioxide extraction of A. glutinosa, β-sitosterol and eleven pentacyclic triterpenes were identified (Felföldi-Gáva et al. 2012). These compounds have a variety of potential pharmacological applications, including stunting cancer tumor growth and protecting against the side effects of chemotherapy and radiation treatment (Laszvzyk 2009, MDidea 2010). This group of compounds has also been found to have anti-inflammatory, antioxidant, antimicrobial, and antiviral properties, as well as cardiovascular benefits (MDidea 2010, Patocka 2003). One identified compound, betulinic acid, has been demonstrated to have antiviral properties against HIV (DeClercq 2000).

Black alder acts as a significant source of nitrogen that typically becomes available for other species and has been shown to increase growth in nearby trees (Funk 1990, Mikola 1958, Plass 1977). For this reason, black alder is sometimes recommended as a nurse crop (a species interplanted with the species of interest in order to assist in its growth) for numerous hardwood tree species (Bohanek and Groninger 2005, Plass 1977, Shepperd and Jones 1985, Vogel 1981).

Due to its ability to fix nitrogen and its capability to colonize acidic soils, black alder can aid in the restoration of disturbed sites and spoil banks (Funk 1990). In an evaluation of the soil remediation ability of trees, A. glutinosa not only caused the largest accumulation of organic carbon and total nitrogen of all examined tree species, but also was associated with the most acidic soils (Chodak and Niklinska 2010). When interplanted on coal mine reclamation sites, black alder’s presence was associated with the doubling in size of adjacent yellow-poplar (Liriodendron tulipifera), white ash (Fraxinus americana), and American sycamore (Plantanus occidentalis) (Vogel 1981). In a seven year study of shale mining reclamation sites in Estonia, black alder stands showed high survival and productivity rates, as well as reduced soil pH and phosphorous concentration (Kuznetsova et al. 2011). Notably, black alder may escape from reclaimed mine soils and grow naturally in surrounding areas.

Black alder may provide food for deer, rabbits, hares, and several bird species. Black alder seeds are released from cones throughout the winter, potentially benefiting seed-eating birds. Additionally, black alder could improve earthworm habitat (Funk 1990).


Regulations (pertaining to the Great Lakes region)
There are conflicting recommendations on the regulation of black alder. Indiana recommends that this species be inter-planted to improve soil quality and “protect other valuable trees” (IDNR n.d.). The state also includes black alder on a list of invasive exotics plants whose “use in landscaping and re-vegetation projects should be avoided or limited when possible” (Homoya 2010). Black alder is also listed as a “plant to avoid” in Wisconsin’s planting guide (WDNR n.d.). It is a recommended tree for urban environments in Minnesota (Johnson and Himanga 2009).

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

For the most effective control, the US Forest Service (2006) recommends treating black alder with a combination of physical and chemical methods.

There are no known biological control methods for this species.

Trees should be felled and then herbicide applied to the stumps to prevent sprouting (USDA NRCS 2006).

Effective herbicides include napropamide (preemergence) (Willoughby et al. 2007), glyphosate via exposed stump application (Kelly and Southwood 2006) triclopyr triethylamine via foliar application (Champion et al. 2008).

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

Remarks: Alnus glutinosa has been called A . vulgaris in some older literature; that name was not validly published.


References: (click for full references)

Akkermans, A.D.L.  1978.  Root nodule symbioses in non-leguminous N2-fixing plants. In: Y.R. Dommergues and S.V. Krupa eds. Interactions between non-pathogenic soil microorganisms and plants. Elsevier Scientific Publishing Co. Amsterdam, Oxford & New York. pp. 335—372.

Ball, P.W. 1964. Alnus. In: Tutin TG, ed. Flora Europaea. Vol. 1. Cambridge University Press, Cambridge, U.K.

Blattny, T. and T. Stastny. 1959. Prirodzené rozsirenie lesných drevin na Slovensku. Bratislava, Slovakia. pp. 404.

Bohanek, J.R., and J.W. Groninger. 2005. Productivity of European black alder (Alnus glutinosa) interplanted with black walnut (Juglans nigra) in Illinois. Agroforestry Systems 64: 99—106.

Boratynski, A. 1980. Systematics and geographic distribution of alders. In: Nasze drzewa lesne. Monografie popularnonauk. Tom (Vol.) 8. Polish Acad. of Sciences, Inst. Of Dendrology, PWN, Warszawa-Poznan. pp. 35—71.

Champion, P.D., T.K. James, and E.C. Carney. 2008. Evaluation of triclopyr trithylamine for the control of wetlands weeds. New Zealand Plant Protection 61:374—377.

Chodak, M., and M. Niklinska. 2010. The effect of different tree species on the chemical and microbial properties of reclaimed mine soils. Biology and Fertility of Soils 46(6):555—566.

DeClercq, E. 2000. Novel compounds in preclinical/early clinical development for the treatment of HIV infections. Reviews in Medical Virology 10: 225—277.

Eckel, P.M. 2003. Two problems in Betulaceae along the Niagara River: Alnus glutinosa and Betula cordifolia. Clintonia 18(4):3—4.

Fabijanowski, J. and K. Zarzycki. 1961. Wplyw obnizenia poziomu wód gruntowych na roslinnosc w zwiazku z budowa odkrywkowej kopalni siarki w Piasecznie. Ekologia Polska 7:203—213.

Food and Agriculture Organization (FAO). 1988. Soil Map of the World. Revised Legend. Reprinted with corrections. World Soil Resources Report 60. FAO/UNESCO, Rome, Italy.

Felföldi-Gáva, A., S. Szarka, B. Simándi, B. Blazics, B. Simon, and Á. Kéry. 2012. Supercritical fluid extraction of Alnus glutinosa (L.) Gaertn. The Journal of Supercritical Fluids 61:55—61.

Funk, D.T. 2009. Alnus glutinosa (L.) Gaerth. European alder. USDA Forest Service, Northeastern Area, State and Private Forestry. Available Accessed 22 June 2009.

Funk, D.T. 1990. Alnus glutinosa (L.) Gaertn.: European alder. Silivics of North American: 1. conifers; 2. hardwoods. Agriculture Handbook 654.   U.S. Department of Agriculture, Forest Service. Available Accessed 2011.

Genys, J.B. 1988. Intraspecific variation among 28 difference sources of black alder, Alnus glutinosa (Betulaceae). Castanea 53(1):71—79.

Gilman, E.F. and D.G. Watson. 1993. Alnus glutinosa. Environmental Horticulture Department, Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida.  Available Accessed 22 June 2009.

Gubanov, I.A., K.V. Kiseleva, V.S. Novikov, and V.N. Tihomirov. 2003. An illustrated identification book of the plants of Middle Russia. Vol. 2: Angiosperms (dicots: archichlamydeans). Institute of Technological Researches, Moscow, Russia. 666 pp.  

Hall, R.B., H.S. McNabb, Jr., C.A. Maynard, and T.L. Green. 1979. Toward development of optimal Alnus glutinosa symbioses. Botanical Gazette 140 (Supplement: Symbiotic Nitrogen Fixation in Actinomycete-Nodulated Plants): S120—S126.

Havinga, D. 2000. Sustaining biodiversity: a strategic plan for managing invasive plants in southern Ontario. Ontario Invasive Plants Working Group. City of Toronto. Toronto, Ontario. 28 pp.

Hegi, G. 1957. Illustrierte Flora von Mitteleuropa. Vol. 3. Hansen, München, Germany. 898 pp.

Herron, P.M., C.T. Martine, A.M. Latimer, and S.A. Leicht-Young. 2007. Invasive plants and their ecological strategies: prediction and explanation of woody plant invasion in New England. Diversity and Distributions 13(5):633—644.

Homoya, M.A. 2010. Invasive exotic plants in Indiana natural areas. Available Accessed 2 February 2012.

Indiana Department of Natural Resources (IDNR). n.d. Tree Species Information. Available Accessed 2 February 2012.

Jaworski, B. 1995. Silviculture characteristics of forest trees. Gutenberg, Kraków, Poland. 237 pp.

Johnson, G.R., and K.M. Himanga. 2009. Recommended trees for southeast Minnesota: an ecosystem approach. University of Minnesota Extension Service. Available Accessed 2011.

Jovanovic, B. 1970. Alnus. In: Josifovic M. ed. Flora S. R. Srbije, pp102-106. Serbian Academy of Science and Art, Beograd, Serbia.

Jurkevic, I. D., V.S. Gel'tman, and N.F. Lovcij. 1968. Types and associations of Alnus glutinosa forests. Izdatel'stvo 'Nauki i Tehnika', Minsk, Russia. 376 pp.

Kelly, A., and R.R. Southwood. 2006. Restoration of the littoral margin by removing trees from the lake edge at Cockshoot Broad, Norfolk, England. Conservation Evidence 3:71—72.

Kuznetsova, T., A. Lukjanova, M. Mandra, and K. Lõhmus. 2011. Aboveground biomass and nutrient accumulation dynamic in young black alder, silver birch and Scots pine plantations on reclaimed oil shale mining areas in Estonia. Forest and Ecology Management 262(2): 56—64.

Laszvzyk, M.N. 2009. Pentacyclic triterpenes of lupane, oleanane and ursane groups as tools in cancer therapy. Planta Medica 75(15): 1549—1560.

McVean, D.N. 1953. Alnus glutinosa (L.) Gaertn. Journal of Ecology 41(2): 447—466.  

McVean D.N. 1956. Ecology of Alnus glutinosa (L.) Gaertn. IV: Root system. Journal of Ecology 44(1): 216—225.

MDidea. 2010. Exporting Division of Extracts Professionals. Pentacyclic triterpenes (PCTs) as inhibitors of inflammation. Available Accessed 16 February 2012.

Mikola, P. 1958. Liberation of nitrogen from alder leaf litter. Acta Forestalia Fennica 67: 1—10.

Mills, E.L., J.H. Leach, J.T. Carlton, and C.L. Secor. 1993. Exotic species in the Great Lakes: a history of biotic crises and anthropogenic introductions. Journal of Great Lakes Research 19(1): 1—54.

NatureServe. 2010. NatureServe Explorer. Version 7.1. Available

Owen, S.J. 1996. Ecological weeds on conservation land in New Zealand: a database. Department of Conservation, Wellington, New Zealand. 118 pp.

Patocka, J. 2003. Biologically active pentacyclic triterpenes and their current medicine signification. Journal of Applied Biomedicine 1: 7—12.

Plass, W.T. 1977. Growth and survival of hardwood and pine interplanted with European alder. USDA Forest Service Research Paper NE-376. Northeastern Forest Experiment Station, Upper Darby, PA. 10 pp.

Savill, P.S. 1991.  The Silviculture of Trees used in British Forestry.  CAB International. 143 pp.

Savulescu, T. 1952. Flora Republicii Populare Române. Vol. 1. Editura Academiei R.P.R., Bucharest, Romania. 718 pp.

Shepperd, W.D., and J.R. Jones. 1985. Nurse crop. General Technical Report RM-119. USDA, Forest Service, Rocky Mountain Forest and Range Experiment Station. Fort Collins, CO. 181–184.

U.S. Forest Service. 2006. Weed of the week: European alder. Forest Health Staff. Available Accessed 9 February 2012.

United States Department of Agriculture (USDA) and Natural Resources Conservation Service (NRCS). 2006. Plant fact sheet: European black alder, Alnus glutinosa L. USDA National Plant Data Team Materials Program. Available Accessed 7 August 2012.

Van Dijk, C.  1978.  Spore formation and endophyte diversity in root nodules of Alnus glutinosa (L.) Vill.  New Phytologist 81(3): 601—615.

Vogel, C.S., P.S. Curtis, and R.B. Thomas. 1997. Growth and nitrogen accretion of di-nitrogen-fixing Alnus glutinosa (L.) Gaertn. under elevated carbon dioxide. Plant Ecology 130(1): 63—70.

Vogel, W.G. 1981. A guide for revegetating coal minesoils in the eastern United States. General Technical Report NE-68. USDA, Forest Service, Northeastern Forest Experiment Station, Broomall, PA. 190 pp.

Walter, H. and H. Leith. 1960. World atlas of climate diagrams. [Klimadiagramm=Weltatlas.] Gustav Fisher Verlag, Jena, Germany. 86 pp.

WDNR. n.d. So, what should I plant? Trees, shrubs, and vines with wildlife. Wisconsin Department of Natural Resources. Available Accessed 2 February 2012.

Willoughby, I., F.L. Dixon, D.V. Clay, and R.L. Jinks. 2007. Tolerance of broadleaved tree and shrubs seedlings to preemergence herbicides. New Forests 34(1): 1—12.


Author: Cao, L., J. Larson, L. Berent, and A. Fusaro

Contributing Agencies:

Revision Date: 6/13/2012

Citation for this information:
Cao, L., J. Larson, L. Berent, and A. Fusaro, 2020, Alnus glutinosa (L.) Gaertn.: U.S. Geological Survey, Nonindigenous Aquatic Species Database, Gainesville, FL, and NOAA Great Lakes Aquatic Nonindigenous Species Information System, Ann Arbor, MI,, Revision Date: 6/13/2012, Access Date: 8/4/2020

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.