Cornus racemosa

Lam.

Gray Dogwood

G5Secure Found in 2 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Identity
Unique IDELEMENT_GLOBAL.2.139198
Element CodePDCOR010L0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderCornales
FamilyCornaceae
GenusCornus
Synonyms
Cornus foemina ssp. racemosa(Lam.) J.S. WilsonSwida racemosa(Lamarck) Moldenke
Other Common Names
Cornouiller à grappes (FR) gray dogwood (EN)
Concept Reference
Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Taxonomic Comments
Sometimes included in Cornus foemina as C. foemina ssp. racemosa; Kartesz (1994 checklist and 1999 floristic synthesis) treats as a distinct species, as do many authors.
Conservation Status
Review Date2016-05-12
Change Date2016-05-12
Edition Date1988-02-22
Edition AuthorsC. CONVERSE, 1984, UPDATE BY NANCY ECKARDT, MRO (1988)
Range Extent Comments
Cornus racemosa is native to North America and occurs in dry to moist open sites from central Maine to southern Ontario and Minnesota, south to Delaware, Maryland and Virginia and west to Kentucky, Missouri, and Oklahoma (Fernald 1950). Wilson (1965) lists C. racemosa as a subspecies of C. foemina; C. foemina subsp. racemosa occurring in the northeast U.S. from Maine to Minnesota, south to Missouri and east to Virginia, C. foemina subsp. foemina occurring in the southeast from S. Carolina to Florida west to Arkansas and eastern Texas (Wilson 1965).
Threat Impact Comments
Cornus spp. are natural early successional components of many woodland ecosystems in North America. They have many adaptions that enable them to take advantage of open areas, including a large number of seeds, vigorous seedlings and rapid subsequent growth, dispersal by birds, and high tolerance to adverse conditions such as drought and shade (Smith 1975, citing Auclair and Cottam 1971). Rapid and extensive cloning by rhizomatous growth allows dogwood species to create dense thickets which crowd out desired grasses, sedges and forbs, and alter wildlife habitat. Invasion of dogwood, along with other woody species, into prairies and wetlands became more extensive mainly due to the post-settlement decline in wildfires.

Woody plant invasion of floodplains is a concern in some areas, particularly in the western U.S., where stream diversion has greatly reduced the flow in rivers. Water diversion can reduce river flow to the extent that dogwoods and other woody plants invade the floodplain, reducing river channel width and drastically altering wildlife habitat. For example, woody plant invasion, including C. drummondii, willows (Salix spp.), green ash (Fraxinus pensylvanica) and black locust (Robinia pseudoacacia), has reduced channel area of the Platte River in Nebraska by 50-85%, resulting in a loss of up to 97% of the roosting habitat for sandhill and whooping cranes and many other migratory birds (Currier 1987).
Ecology & Habitat

Habitat

Gray dogwood occurs in thickets and moist soil in riparian zones, roadsides, on sandy slopes and limestone ridges (Soper and Heimburger 1982).

Ecology

Populations: Dogwood invasion of grasslands from swales, ravines, and woodland edges of floodplains is accelerated by vegetative reproduction and tolerance to wind, full exposure or partial shade, and dry soils (Pound and Clements 1900, Costello 1931, Steyermark 1940, Albertson and Weaver 1945, Weaver 1965, Duxbury 1982).

As density within a dogwood thicket increases, groundcover vegetation decreases and may become entirely absent (Aikman 1928, Weaver 1965). Annual weeds sometimes grow beneath dogwood (Duxbury 1982, Nyboer pers. comm. 1983), and bur oak (Quercus macrocarpa) may invade dogwood thickets (Albertson and Weaver 1945, Aikman 1928). Dogwood may persist and sometimes dominate the understory of woods (Duxbury 1982).

Reproduction

Sexual reproduction: These dogwoods probably reach sexual maturity in three to four years. There is one viable seed per drupe in all four species (Stephens 1973). A complex of hybrids exists between C. drummondii, C. racemosa (C. foemina subsp. racemosa) and C. foemina (subsp. foemina). The hybrids have high pollen viability, robust growth, and fruit sometimes larger and more plentiful than that of the parent (Wilson 1965).

Seed dispersal: Seeds are dispersed by a variety of birds, including crows, vireos, redheaded woodpeckers and bluebirds (Ridley 1930), autumn through winter (Stephens 1973). Availability of perching sites may be important in dispersal. Smith (1975) included C. racemosa in his study of re-vegetation of forest openings, and found that most seeds were deposited by birds within 25 meters of the seed source, often in the shade near perching sites. About 25% of the dispersed seeds left the study area after consumption by long-distance flying birds.

Germination: Germination usually occurs in the spring following seed production and dispersal to a favorable site, but may be delayed a year due to a dormant embryo, hard pericarp (Brinkman 1974), and possible chemical inhibition by the pulp (Goodwin 1948). Mechanical and chemical scarification and stratification techniques are used commercially to stimulate germination in dogwood (Brinkman 1974). C. racemosa and C. stolonifera are described by Krefting and Roe (1949) as having "double dormancy", or requiring two periods of stratification for germination. C. stolonifera seeds that were treated first with acids then with cold stratification experienced almost 100% germination, whereas germination was much lower for those seeds receiving cold treatment only. However, seeds of both species that were twice stratified by passage through quail or pheasant gut plus cold treatment also gave relatively low percent germination. The authors suggested that this was due to a large amount of variability in the extent of scarification from the bird gizzards. Some seeds are injured or overstratified in the bird gut and some are left unscathed or understratified (Krefting and Roe 1949). Smith (1975) described C. racemosa as fruiting abundantly but having very low germinability, depending instead on vegetative reproduction to enhance its propagation. Germination tests of scarified and stratified C. drummondii seeds have shown a 25% germination in three samples after 50 days (Brinkman 1974).

Seedling establishment: Some Cornus spp. shrub seedlings are tolerant of variable light intensities, and may become established in woodland edges, within woods, or in open areas (Gatherum et al. 1963, Smith 1975). Seedlings may invade grasslands alone or with other woody plants (McClain pers. comm.).

Asexual reproduction: C. drummondii, C. racemosa, C. stolonifera and C. obliqua reproduce most successfully by vegetative growth following seedling establishment. Thickets may expand by adventitious underground shoot growth or rhizomatous growth (Stephens 1973, Wilson 1965, Smith 1975).
Other Nations (2)
CanadaN5
ProvinceRankNative
OntarioS5Yes
QuebecS3Yes
ManitobaS3Yes
United StatesNNR
ProvinceRankNative
OhioSNRYes
North CarolinaS1Yes
ArkansasSNRYes
DelawareSHYes
MarylandS4Yes
West VirginiaS4Yes
WisconsinSNRYes
MaineSNRYes
IllinoisSNRYes
IowaS5Yes
PennsylvaniaS5Yes
NebraskaSNRYes
VirginiaS5Yes
South DakotaSNRYes
VermontS5Yes
New HampshireSNRYes
MissouriSNRYes
TexasSNRYes
New YorkS5Yes
MassachusettsSNRYes
KentuckyS2Yes
New JerseyS5Yes
AlabamaSNRYes
District of ColumbiaSNRYes
MinnesotaSNRYes
MichiganSNRYes
North DakotaSNRYes
ConnecticutSNRYes
IndianaS5Yes
Rhode IslandSNRYes
Plant Characteristics
Economic Value (Genus)Yes
Roadless Areas (2)
Virginia (1)
AreaForestAcres
Ramseys Draft AdditionGeorge Washington National Forest12,781
Wisconsin (1)
AreaForestAcres
09011 - Flynn Lake Study AreaChequamegon-Nicolet National Forest5,951
References (6)
  1. Fernald, M. L. 1950. Gray's manual of botany. 8th edition. Corrected printing (1970). D. Van Nostrand Company, New York. 1632 pp.
  2. Flora of North America Editorial Committee (FNA). 2016. Flora of North America north of Mexico. Vol. 12. Magnoliophyta: Vitaceae to Garryaceae. Oxford Univ. Press, New York. xxiv + 603 pp.
  3. Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
  4. Little, E.L., Jr. 1979. Checklist of United States trees (native and naturalized). Agriculture Handbook No. 541. U.S. Forest Service, Washington, D.C. 375 pp.
  5. Soper, J. H., and M. L. Heimburger. 1982. Shrubs of Ontario. Royal Ontario Museum, Toronto, Canada. 495 pp.
  6. Weakley, A.S. 2020. Flora of the Southeastern United States. 20 October 2020 Edition. University of North Carolina Herbarium (NCU), North Carolina Botanical Garden, University of North Carolina at Chapel Hill.