Overview
Comprehensive Description
Comments
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Hilty, J. Editor. 2013. Illinois Wildflowers. World Wide Web electronic publication. flowervisitors.info, version 04/2013.
See: Botanical Terminology and Line Drawings, Ecological Terminology, Website Description, Links to Other Websites, Reference Materials
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Description
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Hilty, J. Editor. 2013. Illinois Wildflowers. World Wide Web electronic publication. flowervisitors.info, version 04/2013.
See: Botanical Terminology and Line Drawings, Ecological Terminology, Website Description, Links to Other Websites, Reference Materials
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Description
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Description
General: Honeysuckle family (Caprifoliaceae). Native shrubs growing 2-4(-8) m tall, less commonly small single-stemmed trees, young twigs soft and pithy but the wood hard; bark thin, grayish to dark brown, irregularly furrowed and ridged. The pinnately compound leaves are deciduous, opposite, about 15-35 cm long, odd-pinnate with (3-)5-9 serrate leaflets 2-15 cm long, often with a long stalk, often asymmetrical at the base. Elderberry leaves, especially on seedlings or shrub-sized plants (without fruits or flowers) resemble California walnut (Juglans hindsii) and Oregon ash (Fraxinus latifolia). The inflorescence is flat-topped, 4-20(-30) cm across, broader than high; flowers bisexual, the corollas small, white to cream, rotate, 5-lobed, with a pleasant, yet slightly rancid odor. Fruit is berry-like, 5-6 mm wide, with 3-5 nutlets, blue- to purple-black at maturity with a white-waxy bloom and appearing powder blue. The common name “elder” is from the Anglo-Saxon “ellen,” meaning fire-kindler, the dry, pithy stems; blue from the fruit color.
Distribution: Common elderberry is common along stream banks, river banks, and open places in riparian areas lower than < 3000 m. From west Texas north to Montana, western Alberta, and southern British Columbia, and all other western states, south into northwest Mexico. For current distribution, please consult the Plant Profile page for this species on the PLANTS Web site.
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Alternative names
Arizona elderberry, American elder, sweet elder, wild elder, flor sauco, tree of music, Danewort, Walewort, New Mexican elderberry, velvet-leaf elder, hairy blue elderberry, and dwarf elder. Taxonomically, there have been recent changes in this elderberry species. It was previously divided into Sambucus coriacea, Sambucus orbiculata, Sambucus velutina, and Sambucus caerulea (Munz 1968). This species is known in some floras as Sambucus mexicana.
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Distribution
Range and Habitat in Illinois
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Hilty, J. Editor. 2013. Illinois Wildflowers. World Wide Web electronic publication. flowervisitors.info, version 04/2013.
See: Botanical Terminology and Line Drawings, Ecological Terminology, Website Description, Links to Other Websites, Reference Materials
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Localities documented in Tropicos sources
Canada (North America)
United States (North America)
Caribbean (Caribbean)
Mexico (Mesoamerica)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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Villarreal Q., J. A. 2003. Sambucaceae. Fl. Veracruz 129: 1–8.
http://www.tropicos.org/Reference/1024417
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Localities documented in Tropicos sources
Costa Rica (Mesoamerica)
Honduras (Mesoamerica)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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SPECIMEN BASED RECORD. Published protolog data.
http://www.tropicos.org/Reference/9990002
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Nelson, C. 1976. Algunas plantas del Departamento de Ocotepeque, Honduras. Ceiba 20(1): 27–41.
http://www.tropicos.org/Reference/5266
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Localities documented in Tropicos sources
United States (North America)
Canada (North America)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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Fernald, M. 1950. Manual (ed. 8) i–lxiv, 1–1632. American Book Co., New York.
http://www.tropicos.org/Reference/1327
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Localities documented in Tropicos sources
United States (North America)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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Fernald, M. 1950. Manual (ed. 8) i–lxiv, 1–1632. American Book Co., New York.
http://www.tropicos.org/Reference/1327
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Localities documented in Tropicos sources
Canada (North America)
United States (North America)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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Fernald, M. 1950. Manual (ed. 8) i–lxiv, 1–1632. American Book Co., New York.
http://www.tropicos.org/Reference/1327
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Localities documented in Tropicos sources
United States (North America)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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Anonymous. 1986. List-Based Rec., Soil Conserv. Serv., U.S.D.A. Database of the U.S.D.A., Beltsville.
http://www.tropicos.org/Reference/1103
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Localities documented in Tropicos sources
Canada (North America)
Costa Rica (Mesoamerica)
El Salvador (Mesoamerica)
Guatemala (Mesoamerica)
Mexico (Mesoamerica)
Nicaragua (Mesoamerica)
Panama (Mesoamerica)
United States (North America)
Bolivia (South America)
Brazil (South America)
Colombia (South America)
Ecuador (South America)
Venezuela (South America)
Note: This information is based on publications available through Tropicos and may not represent the entire distribution. Tropicos does not categorize distributions as native or non-native.
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Forzza, R. C. & et al. 2010. 2010 Lista de espécies Flora do Brasil. http://floradobrasil.jbrj.gov.br/2010/.
http://www.tropicos.org/Reference/100002289
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SPECIMEN BASED RECORD. Published protolog data.
http://www.tropicos.org/Reference/9990002
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Killeen, T. J., E. García Estigarribia & S. G. Beck. (eds.) 1993. Guia Arb. Bolivia 1–958. Herbario Nacional de Bolivia & Missouri Botanical Garden, La Paz.
http://www.tropicos.org/Reference/1000017
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Anonymous. 1986. List-Based Rec., Soil Conserv. Serv., U.S.D.A. Database of the U.S.D.A., Beltsville.
http://www.tropicos.org/Reference/1103
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Linares, J. L. 2003 [2005]. Listado comentado de los árboles nativos y cultivados en la república de El Salvador. Ceiba 44(2): 105–268.
http://www.tropicos.org/Reference/1029566
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Funk, V. A., P. E. Berry, S. Alexander, T. H. Hollowell & C. L. Kelloff. 2007. Checklist of the Plants of the Guiana Shield (Venezuela: Amazonas, Bolivar, Delta Amacuro; Guyana, Surinam, French Guiana). Contr. U.S. Natl. Herb. 55: 1–584.
http://www.tropicos.org/Reference/1033072
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Gleason, H. A. 1968. The Sympetalous Dicotyledoneae. vol. 3. 596 pp. In H. A. Gleason Ill. Fl. N. U.S. (ed. 3). New York Botanical Garden, New York.
http://www.tropicos.org/Reference/1707
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Nash, D. L. 1976. Caprifoliaceae. In: D. L. Nash (ed.), Flora of Guatemala - Part X, Number 4. Fieldiana, Bot. 24(11/4): 275–296.
http://www.tropicos.org/Reference/5248
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Solomon, J. C. 2001. Caprifoliaceae. En: W.D. Stevens, C. Ulloa, A. Pool & O.M. Montiel (eds.). Fl. Nicaragua. Monogr. Syst. Bot. Missouri Bot. Gard. 85(1): 585–586.
http://www.tropicos.org/Reference/1028750
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Jørgensen, P. M. & S. León-Yánez. (eds.) 1999. Catalogue of the vascular plants of Ecuador. Monogr. Syst. Bot. Missouri Bot. Gard. 75: i–viii, 1–1181.
http://www.tropicos.org/Reference/42250
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Breedlove, D. E. 1986. Flora de Chiapas. Listados Floríst. México 4: i–v, 1–246.
http://www.tropicos.org/Reference/513
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Radford, A. E., H. E. Ahles & C. R. Bell. 1968. Man. Vasc. Fl. Carolinas i–lxi, 1–1183. University of North Carolina Press, Chapel Hill.
http://www.tropicos.org/Reference/636
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Correll, D. S. & M. C. Johnston. 1970. Man. Vasc. Pl. Texas i–xv, 1–1881. The University of Texas at Dallas, Richardson.
http://www.tropicos.org/Reference/1493
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Small, J. K. 1933. Man. S.E. Fl. i–xxii, 1–1554. Published by the Author, New York.
http://www.tropicos.org/Reference/1515
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Ibarra-Manriquez, G. & S. S. Colin. 1995. Lista floristica comentada de la Estacion de Biologia Tropical "Los Tuxtlas", Veracruz, Mexico. Revista Biol. Trop. 43(1–3): 75–115.
http://www.tropicos.org/Reference/1001850
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Great Plains Flora Association. 1986. Fl. Great Plains i–vii, 1–1392. University Press of Kansas, Lawrence.
http://www.tropicos.org/Reference/637
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Godfrey, R. K. & J. W. Wooten. 1981. Aquatic Wetland Pl. S.E. U.S. Dicot. 933 pp. Univ. Georgia Press, Athens.
http://www.tropicos.org/Reference/1711
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Idárraga-Piedrahita, A., R. D. C. Ortiz, R. Callejas Posada & M. Merello. 2011. Flora de Antioquia. Catálogo de las Plantas Vasculares, vol. 2. Listado de las Plantas Vasculares del Departamento de Antioquia. Pp. 1-939.
http://www.tropicos.org/Reference/100008595
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D'Arcy, W. G. 1987. Flora of Panama. Checklist and Index. Part 1: The introduction and checklist. Monogr. Syst. Bot. Missouri Bot. Gard. 17: v–xxx, 1–328.
http://www.tropicos.org/Reference/1289
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National Distribution
Canada
Origin: Unknown/Undetermined
Regularity: Regularly occurring
Currently: Unknown/Undetermined
Confidence: Confident
United States
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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Adaptation
Elderberry grows on moist, well-drained sunny sites, usually occurring in early seral communities or in openings in moist forest habitats (slopes, canyons, cliff bases, streamsides, streambanks) and moist areas within drier, more open habitats (sagebrush, mountain brush, pinyon-juniper, ponderosa pine, often along fence rows and roads); at elevations of 3-3000 meters. Elderberry is a dominant understory species in riparian woodlands. It can persist past seral stages as scattered individuals in open forests, woodlands, chaparral, or riparian zones. This species flowers from May to September and fruits from July to October. Common elderberry is more common on warmer sites than red elderberry (Sambucus racemosa), although they overlap in habitat preference.
In California, common riparian woodland associates are valley oak (Quercus lobata), interior live oak (Quercus wislizenii), California walnut (Juglans hindsii), and California sycamore (Platanus racemosa). Box elder (Acer negundo), Oregon ash (Fraxinus latifolia), alder (Alnus rhombifolia), and willow (Salix gooddingii, Salix exigua, Salix lasiandra, and Salix laevigata) are particularly prevalent in the subcanopy. Understory species are mostly shrubs, including elderberry (Sambucus mexicana), buttonbush (Cephalanthus occidentalis), blackberry (Rubus spp.), and California rose (Rosa californica). Lianas, such as poison oak (Toxicodendron diversiloba) and California grape (Vitis californica) are a dominant feature. Herbaceous vegetation is 1% cover except in openings where tall forbs may occur.
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Physical Description
Morphology
Type Information
Catalog Number: US 1384978
Collection: Smithsonian Institution, National Museum of Natural History, Department of Botany
Verification Degree: Original publication and alleged type specimen examined
Preparation: Pressed specimen
Collector(s): A. Tonduz
Year Collected: 1890
Locality: Volcan Barba, Rancho Flores, Costa Rica, Central America
- Isosyntype: Donnell Smith, J. 1898. Bot. Gaz. 25: 146.
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Catalog Number: US 341447
Collection: Smithsonian Institution, National Museum of Natural History, Department of Botany
Verification Degree: Original publication and alleged type specimen examined
Preparation: Pressed specimen
Collector(s): R. Plaskett
Year Collected: 1898
Locality: Santa Lucia Mountains., Monterey / San Luis Obispo, California, United States, North America
- Holotype: Greene, E. L. 1910. Leafl. Bot. Observ. Crit. 2: 99.
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Ecology
Habitat
Range and Habitat in Illinois
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Hilty, J. Editor. 2013. Illinois Wildflowers. World Wide Web electronic publication. flowervisitors.info, version 04/2013.
See: Botanical Terminology and Line Drawings, Ecological Terminology, Website Description, Links to Other Websites, Reference Materials
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Dispersal
Establishment
All elderberry plants with evidence of valley elderberry longhorn beetle use (i.e. emergence holes or presence of adults) should be transplanted, as they provide habitat for a threatened species under The Endangered Species Act. For further technical information, call a representative of the U.S. Fish and Wildlife Service.
Cut tree back to 3 to 6 feet from the ground or to 50 percent of its height (whichever is greater) by removing branches and stems above this height. The trunk and all stems greater than 1.5 inches in diameter can be replanted.
If the presence of tunnels excavated by the beetle larvae inside the elderberry stem and trunk are detected, place pruned material next to transplanted elderberries.
Move plant by the root ball. Keep the root ball wet.
Place transplant in holes 3 to 4 feet deep.
Construct circular water retention basin from the excavated earth about 8-10 feet in diameter and 12 to 14 inches high. Plant the main trunk of an elderberry in the center of each water basin. Plant other stems that have been rooted around the circumference of the basin.
Saturate soil with water. Irrigate as necessary, especially through first growing season.
Elderberry produces a good seed crop almost every year. The seeds are dispersed by birds and other animals that eat the fruit. The seeds have a hard seed coat and embryo dormancy and may remain viable for up to 16 years in storage. Without pretreatment, seed germination may be delayed from 2 to 5 years after planting. Plants may flower and fruit after only 2-3 years and can reach full size in 3-4 years. They are said to be “short-lived.” Vegetative reproduction is limited to coppicing if the stems are killed or injured.
Seeds:
Elderberry grows best from seed.
Elderberry fruits are collected when ripe and spread in thin layers to dry.
To separate seeds from fruits either 1) run fruit through a macerator with water and the pulp and empty seeds float; 2) crush, dry and use without separating fruits and seeds; and 3) for small amounts of fruit they can be cleaned in a fruit blender.
• Elderberry seed can be stored dry at 41 °F for several years.
• Elderberry seeds can be sown in the fall soon after collection, or stratified and sown in the spring. In either case, germination is often not complete until the second spring.
• A seedling density of 35 plant per square foot is sought. Seeds are sown 1/4 inch deep in drills and covered with about 3/8 inch of sawdust mulch.
• In the greenhouse, seeds are warm stratified for two months in a mixture of peat, vermiculite, and sand at 21° to 30°C; (70 to 85°F). Seeds are then placed close to the soil surface in flats in the greenhouse. There are usually several hundred seeds in one seed flat.
• Seedlings are then potted from the flats in deep 3" pots.
• After one season of growth, the seedlings are field planted in the fall or spring when they are 6 to 8 months old. If planted in the fall irrigation may not be necessary in moist sites. In drier sites or with spring planting, irrigation will be required for seedling establishment.
Cuttings:
• Cuttings of elderberry tend to have lower survival success than establishment from seed.
• Use hardwood cuttings from previous seasons growth.
• Take "heel cuttings" from older wood, so inner pith is not exposed.
• Cuttings should be at least 10", and have at least two nodes. Cuttings are placed in 4" pots with perlite and peat. Plants are kept moist.
• Cuttings have a fragile root system, with high mortality occurring when transplanted. Care should be taken to be very gentle with delicate roots when transplanting.
• The cuttings, which do survive, seem to establish and grow faster. Plant biomass production, height, flowering and seed set is more rapid than with seedlings.
Transplanting Trees and Stems:
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Associations
Flower-Visiting Insects of Common Elderberry in Illinois
(Bees collect pollen, other insects feed on pollen; observations are from Robertson)
Bees (long-tongued)
Apidae (Apinae): Apis mellifera fq; Anthophoridae (Ceratinini): Ceratina dupla dupla
Bees (short-tongued)
Halictidae (Halictinae): Halictus parallelus, Lasioglossum cinctipes, Lasioglossum imitatus fq, Lasioglossum versatus, Lasioglossum zephyrus fq; Andrenidae (Andreninae): Andrena imitatrix imitatrix
Flies
Syrphidae: Allograpta obliqua fq, Chalcosyrphus nemorum, Eristalis dimidiatus, Eristalis tenax, Eupeodes americanus, Mallota bautias fq, Ocyptamus fascipennis, Spilomyia alcimus fq, Syritta pipiens, Syrphus ribesii fq; Bombyliidae: Anthrax oedipus, Hemipenthes sinuosa; Muscidae: Musca domestica, Neomyia cornicina; Anthomyiidae: Delia platura; Fanniidae: Fannia manicata
Beetles
Cerambycidae: Euderces picipes; Dermestidae: Attagenus megatoma fq; Melyridae: Malachius erichsonii; Scarabaeidae (Cetoniinae): Euphoria fulgida; Scraptiidae: Pentaria trifasciatus
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Hilty, J. Editor. 2013. Insect Visitors of Illinois Wildflowers. World Wide Web electronic publication. illinoiswildflowers.info, version (05/2013)
See: Abbreviations for Insect Activities, Abbreviations for Scientific Observers, References for behavioral observations
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mainly hypophyllous colony of Ramularia hyphomycetous anamorph of Ramularia sambucina causes spots on live leaf of Sambucus canadensis
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Sambucus canadensis
No available public DNA sequences.
Download FASTA File
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Statistics of barcoding coverage: Sambucus canadensis
Public Records: 1
Specimens with Barcodes: 2
Species With Barcodes: 1
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Statistics of barcoding coverage: Sambucus nigra canadensis
Public Records: 0
Specimens with Barcodes: 2
Species With Barcodes: 1
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Conservation
Conservation Status
National NatureServe Conservation Status
Canada
Rounded National Status Rank: NNR - Unranked
United States
Rounded National Status Rank: N5 - Secure
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NatureServe Conservation Status
Rounded Global Status Rank: T5 - Secure
Reasons: Throughout United States and eastern Canada except for Great Basin and Pacific northwest.
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Status
Please consult the PLANTS Web site and your State Department of Natural Resources for this plant’s current status, such as, wetland indicator values. Western riparian ecosystems have been greatly altered by human activity. Riparian forests have been reduced to fragmented, discontinuous patches because of human intervention. For example, estimates are that 70 - 90 percent of the natural riparian ecosystems in the U.S. have been lost to human activities. Regional losses in these ecosystems have been estimated to exceed 98% in the Sacramento Valley in California. Many factors have contributed to these resource losses, including the following: natural resource use; urbanization; alteration of stream flows through dam construction and ground-water withdrawal; modification of biotic conditions through grazing, agriculture, introduction of non-native species; and alteration within watersheds.
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Management
Cultivars, improved and selected materials (and area of origin)
These plant materials are somewhat available from commercial sources. Contact your local Natural Resources Conservation Service (formerly Soil Conservation Service) office for more information. Look in the phone book under ”United States Government.” The Natural Resources Conservation Service will be listed under the subheading “Department of Agriculture.”
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In six riparian restoration projects carried out in California, competition from exotic weed species was a key factor in mortality and site failure (Baird 1989). On small sites, hand weeding around trees and shrubs is the most effective means of weed control. One way to avoid competition from weeds on larger sites is to remove the surface soil, although this has the disadvantage of removing nutrients, mycorrhizal fungi, bacteria, and insect and invertebrate populations critical to a healthy habitat. A cover crop of native wildflowers was also used to control weeds, with wildflower seeds hand-broadcast over the site. On wetter, heavier soils this does not seem to provide effective weed control.
There is considerable evidence that fertilization can favor exotic weeds over native plants. Inoculation with mycorrhizal fungi enables seedlings of some species to better utilize limited supplies of both water and nutrients. Inoculation of transplanted shrubs may be accomplished through inclusion of large (1.2 m deep by 2.8 m wide) root balls with plants. Smaller, more economical soil plugs scattered throughout the site serve the same purpose. The number of soil plugs needed to ensure the establishment of soil flora is directly related to the distance of the restoration site from a similar, mature community.
Given that elderberry provides habitat for the federally listed valley longhorn elderberry beetle, livestock grazing of elderberry is not recommended. Livestock grazing can alter vegetative structure and composition of riparian habitat. Overgrazing by livestock and big game frequently changes plant species composition and growth form, density of stands, vigor, seed production of plants, and insect production.
Clear-cutting or seed tree cutting with high soil disturbance sometimes favors the development of elderberry in a seral community. It recovers well from heavy grazing in the Great Basin. For use in site stabilization or rehabilitation, seeds may be planted directly or seedlings and 1-2-year old stock may be transplanted. It also grows from transplanted seedlings, cuttings, and rootstocks.
Elderberry usually is not present in the understory of closed-canopy forests, and when fire occurs in these, regeneration occurs from seed banks that may occur between 2-10 cm deep in the soil, the seeds deposited from off-site dispersal or from plants of an earlier community. Fire scarifies the hard seed coat of buried seeds and stimulates their germination, which usually occurs the first growing season after the fire. Subsequent burns may eliminate elderberry since it spreads slowly by seed. Fire kills above-ground parts but the root crown may sprout but a severe fire can kill the root and stem buds from which sprouting occurs.
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Relevance to Humans and Ecosystems
Benefits
Cultivation
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Hilty, J. Editor. 2013. Illinois Wildflowers. World Wide Web electronic publication. flowervisitors.info, version 04/2013.
See: Botanical Terminology and Line Drawings, Ecological Terminology, Website Description, Links to Other Websites, Reference Materials
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Uses
Ethnobotanic: Only the blue or purple berries of elderberry are edible. Edible berries and flower are used for medicine, dyes for basketry, arrow shafts, flute, whistles, clapper sticks, and folk medicine. The active alkaloids in elderberry plants are hydrocyanic acid and sambucine. Both alkaloids will cause nausea so care should be observed with this plant. Elderberries are high in Vitamin C. The red berries of other species are toxic and should not be gathered.
The wood is hard and has been used for combs, spindles, and pegs, and the hollow stems have been fashioned into flutes and blowguns.
Elderberries are quite edible. The blue or purple berries are gathered and made into elderberry wine, jam, syrup, and pies. The entire flower cluster can be dipped in batter and fried while petals can be eaten raw or made into a fragrant and tasty tea. The flowers add an aromatic flavor and lightness to pancakes or fritters.
The elderberry is of well-known value to the Indians of North America and the many purposes it serves (Barrow 1967). Elderberry is highly prized by both Spaniards and Cahuillas. Throughout the months of July and August the small clusters of berries are gathered in large quantities. These clusters are dried carefully on the drying floor and preserved in considerable amounts. When wanted, they are cooked into a rich sauce that needs no sweetening. A Cahuilla family during this season of the year will subsist largely on these messes of "sauco." Frequently, the elderberry was so greatly enjoyed that families would live for weeks on little else. Many were dried for use in the winter, and were either re-cooked or eaten raw. Elderberries are still highly prized for food by modern Indian people.
Elderberry twigs and fruit are employed in creating dyes for basketry. These stems are dyed a very deep black by soaking them for a week or so in a wash made from the berry stems of the elderberry (Barrows 1967). The Cahuilla split basketry materials from the aromatic sumac (Rhus trilobata).
Elderberry branches were used to make the shaft of arrows. Flutes and whistles were constructed by boring holes into stems hollowed out with hot sticks. Clapper sticks were made by splitting the stem and clapping the two halves against each other. Clapper sticks were used ceremonially in the round-house to accompany singing and dancing. The pith of the stems was used as tinder, and the stem itself was employed as a twirling stick for starting the fire. Hollowed-out elderberry stems can be made into squirt guns.
In the middle ages elderberry was considered a Holy Tree, capable of restoring good health, keeping good health, and as an aid to longevity.
Fruits of elderberry are gathered from the wild for wine, jellies, candy, pies, and sauces. The plants are commercially cultivated for fruit production in Oregon. Sambucus canadensis and S. nigra have long been used in the same way, and cultivars of both have been developed. All parts of the elderberry plant are considered to be a valuable healing plant in many folk medicine traditions (Hutchens 1991, Walker et al. 1993; Barrett et al. 1933; Clarke 1977). Elderberry flowers contain flavenoids and rutin, which are known to improve immune function, particularly in combination with vitamin “C.” The flowers also contain tannins, which account for its traditional use to reduce bleeding, diarrhea, and congestion.
The flowers are the mildest part of the plant and prepared as a tea, are used to break dry fevers and stimulate perspiration, aid headache, indigestion, twitching eyes, dropsy, rheumatism, appendix inflammation, bladder or kidney infections, colds, influenza, consumption (bleeding in lungs), and is helpful to newborn babies (Hutchens 1991). Used as a wash, the flowers or leaves are good for wounds, sprains, and bruises, as well as for sores on domestic animals. The leaves, which are stronger, have a slightly laxative property. Applied externally, leaves, flowers, bark and twigs are excellent as a poultice, mixed equally with chamomile, for soreness, inflammations, joint stiffness, and to reduce the swelling of bee stings. The flowers and berries, employed as a diuretic, can aid arthritis and rheumatism. Steeped in water, the flowers are used externally to aid in complexion beauty, tone and soften the skin, and lighten freckles or spots. The berry juice made into salve aids burns and scalds. The juice taken internally will act as a purgative.
Livestock: Elderberry is a useful range plant for domestic livestock, but is not equally palatable during all seasons. It is usually receives limited browsing in the spring and to a much greater extent in the late summer and fall. The leaves are eagerly devoured after the first heavy frost in the fall. Because many branches are beyond the reach of the animals, utilization is less destructive. Browse rating: Good for goats; good to fair for sheep; good to poor for deer; fair for cattle; and fair to poor for horses (Sampson and Jesperson 1981).
Wildlife: Structurally complex riparian vegetation communities provide many different habitats and support a diverse array of animal species. Different groups of animals occupy or use the different layers of vegetation, and this multi-story arrangement is often present nowhere else in the arid landscapes. Canopies of plants growing on stream banks provide shade, cooling stream water, while roots stabilize and create overhanging banks, providing habitat for fish and other aquatic organisms.
Game birds, squirrels and other rodents, and several kinds of browsers also feed on the fruit or foliage of elderberry. Bears love to eat the elderberry fruits while deer, elk, and moose browse on the stems and foliage. The elderberries are important sources of summer food for many kinds of songbirds. For example, the western bluebird, indigo bunting, common house finch, red-shafted flicker, ash-throated flycatcher, black-headed grosbeak, scrub jay, Stellar jay, ruby-crowned kinglet, mockingbird, red-breasted nuthatch, Bullock’s oriole, hooded oriole, song sparrow, white-crowned sparrow, western tanager, California thrasher, russet-backed thrush, brown towhee, Audubon warbler, cedar waxwing, Lewis and Nuttall's woodpecker, wren-tit, grouse, pheasant, and pigeons all eat elderberries (Martin et al. 1951).
The valley elderberry longhorn beetle (VELB) (Desmocerus californicus dimorphus) was listed as threatened under The Endangered Species Act on August 8, 1980. The elderberry beetle is endemic to moist valley oak riparian woodlands along the margins of rivers and streams in the lower Sacramento and upper San Joaquin Valley of California where elderberry grows. The primary threat to the VELB is loss of habitat, insecticide and herbicide use, and lack of elderberry shrubs/trees as a food plant for the beetle. The mitigation for VELB habitat loss, considered a taking under The Endangered Species Act, is quite stringent (U.S. Fish and Wildlife Service Mitigation Guidelines).
In general, longhorn beetles are characterized by somewhat elongate and cylindrical bodies with long antennae, often in excess of 2/3 of the body length. Male VELB have a metallic-green pattern of 4 oblong maculations, surrounded by a bright red-orange border. The body length is about 13-21 mm, and antennae are about a long as the body. Females are more robust, with body length about 18-25 mm, and the dark pattern is not reduced.
Elderberry is planted because of its forage and cover value, productivity, adaptability, and ease of establishment. It is a useful ground cover for stabilizing streambanks and eroding sites. It provides food, cover, perching, and nesting sites for many species of birds and food and cover for various other wildlife, and it is important as browse for mule deer and elk. In the spring the leaves may be strongly scented and less palatable, but they sweeten and become more palatable by fall.
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Wikipedia
Sambucus canadensis
Sambucus canadensis (American Elderberry) is a species of elderberry native to a large area of North America east of the Rocky Mountains, and south through eastern Mexico and Central America to Panama. It grows in a variety of conditions including both wet and dry soils, primarily in sunny locations.
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Growth
It is a deciduous suckering shrub growing to 3 m or more tall. The leaves are arranged in opposite pairs, pinnate with five to nine leaflets, the leaflets around 10 cm long and 5 cm broad. In summer, it bears large (20–30 cm diameter) corymbs of white flowers above the foliage, the individual flowers 5–6 mm diameter, with five petals.
The fruit is a dark purple to black berry 3–5 mm diameter, produced in drooping clusters in the fall. The berries and flowers are edible, but other parts of the plant are poisonous, containing toxic calcium oxalate crystals.
Characteristics
It is closely related to the European Sambucus nigra, and some authors treat it as conspecific[citation needed], under the name Sambucus nigra subsp. canadensis.
Uses
Uses for the fruit include medicinal products,[citation needed] wine, jelly and dye. Leaves and inner bark can be used as an insecticide and a dye.[1] Stems can be hollowed out and used for spouts, musical instruments, and toys.
Leaves, stems, roots, and unripe fruits of S. canadensis are toxic due to the presence of cyanogenic glycosides and alkaloids.[2]
Research on elderberries is being conducted at the University of Missouri's South West Center in Mount Vernon and at the Missouri State Fruit Experiment Station in Mountain Grove.
References
- ^ http://www.pfaf.org/database/plants.php?Sambucus+canadensis
- ^ Poisonous Plants: Sambucus canadensis
- Germplasm Resources Information Network: Sambucus canadensis
- Missouri Plants: Sambucus canadensis
- USDA Plants Profile: Sambucus nigra subsp. canadensis
- Sambucus nigra ssp. canadensis Images at Bioimages, Vanderbilt University.
- Missouri State Fruit Experiment Station
Media related to Sambucus canadensis at Wikimedia Commons
Data related to Sambucus canadensis at Wikispecies
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Names and Taxonomy
Taxonomy
Comments: Most North American material is often treated as the distinct species, S. canadensis; here treated as a ssp. of S. nigra. This record also includes material of the southwestern U.S. and tropics sometimes referred to as S. mexicana.
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