Datasheet
Cornus sericea (redosier dogwood)
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Pictures
Top of page| Picture | Title | Caption | Copyright |  | Title | Habit in a fen |
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| Caption | Cornus sericea with bright red stems in the fens of the Lodi Marsh, Wisconsin, USA. The posts in the background are permanent markers for a long-term study of Cornus sericea growth after cattle grazing. |
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| Copyright | Beth A. Middleton |
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| Habit in a fen | Cornus sericea with bright red stems in the fens of the Lodi Marsh, Wisconsin, USA. The posts in the background are permanent markers for a long-term study of Cornus sericea growth after cattle grazing. | Beth A. Middleton |
 | Title | Habitat |
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| Caption | Fen with tussock sedge (Carex stricta), various prairie marsh forbs and native Typha latifolia. Lodi Marsh, Wisconsin, USA. |
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| Copyright | Beth A. Middleton |
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| Habitat | Fen with tussock sedge (Carex stricta), various prairie marsh forbs and native Typha latifolia. Lodi Marsh, Wisconsin, USA. | Beth A. Middleton |
 | Title | Habitat |
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| Caption | Eupatorium maculatum, 'Joe Pye Weed' a tall sedge meadow forb which is shaded out by shrub growth. Lodi Marsh, Wisconsin, USA. |
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| Copyright | Beth A. Middleton |
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| Habitat | Eupatorium maculatum, 'Joe Pye Weed' a tall sedge meadow forb which is shaded out by shrub growth. Lodi Marsh, Wisconsin, USA. | Beth A. Middleton |
Identity
Top of pagePreferred Scientific Name
Preferred Common Name
Other Scientific Names
- Cornus stolonifera Michx., 1803
- Swida sericea (L.) Holub., 1838
- Swida stolonifera Rydb., 1931
- Thelycrania sericea (L.) Dandy
International Common Names
- English: redosier; red-osier; red-osier dogwood
- French: Cornouiller osier
Local Common Names
- Germany: Weiden-Hartriegel
EPPO code
Summary of Invasiveness
Top of pageC. sericea is native to North America, and occurs in wetlands from Alaska to Labrador, southward to northern Mexico along the Rocky Mountains (Karlsson, 2009). It occurs in the once glaciated regions of North America, and occurs locally southward (Viereck and Little, 1972). The species is listed as an invasive species by the European Plant Quarantine Data Retrieval System (EPPO, 2009b), and is on the “alert list” for Switzerland and Belgium (EPPO 2009b and IAS 2009, respectively). Elsewhere in northern Europe, it is considered an emerging invasive; the species has invasive tendencies where it has been introduced (EPPO, 2009b). Kelly (1990) lists nearly 20 instances of occurrence of the species in Ireland, mostly in wetland woods, where it may threaten biodiversity. Among the listed occurrences in Ireland, one is on an island, and likely to have established from a plant fragment washed ashore. Despite searching, Kelly (1990) did not find seedlings of this species in Irish habitats.
Taxonomic Tree
Top of page
- Domain: Eukaryota
- Kingdom: Plantae
- Phylum: Spermatophyta
- Subphylum: Angiospermae
- Class: Dicotyledonae
- Order: Cornales
- Family: Cornaceae
- Genus: Cornus
- Species: Cornus sericea
Notes on Taxonomy and Nomenclature
Top of pageCornus sericea is the revised taxonomic name, formerly known as Cornus stolonifera or Swida stolonifera (common names: red-osier dogwood and Seidiger Hartriegel, Lohmueller, 2008). Some cultivars include ‘Allerman’s Compact’, ‘Flaviramea’, ‘Hedgerows Gold’, ‘Isanti’, ‘Kelseyi’, ‘Silver and Gold’, and ‘Variegata’ (Rook, 2002).
C. sericea has straightforward morphology in the northeastern USA, but westward in North America, the species’ characteristics become less clear as it hybridizes with Cornus occidentalis. The hybrids have a diverse array of characteristics related to pubescence, flower size and endocarp characters (Rickett, 1944). Cornus alba of northern Asia is very similar to C. sericea, except that it does not form suckers (Kelly, 1990).
Description
Top of page
C. sericea is a deciduous shrub with brightly coloured (often red) stems in the winter. The stems root along nodes, and spread by layering (EPPO, 2009b). The clones form large dense patches, with individual plants up to 3.7 m tall (USDA-NRCS, 2009) in both native and invasive habitats. The leaves are ovate to elliptic, green above, with 20-40 mm petioles (Karlsson, 2009). Long peduncles hold corymb-like infloresences of 20-50 flowers, each with 4 tiny white petals (1-3 mm). Fruit is a white to lead colour, subglobose pyrene (USDA, 1948) with a rounded base, wider than long (3.5 to 6 mm), with eight ridges (Karlsson, 2009).
Plant Type
Top of pagePerennial
Seed propagated
Shrub
Vegetatively propagated
Woody
Distribution
Top of pageC. sericea is native to North America, from northern Canada to northern Mexico, at elevations below 2500 m. It is considered to be potentially invasive there (WBIS, 2009). In addition to the countries listed in the distribution table, this species is also present in Arizona (JT Kartesz, Biota of North America Program (BONAP), North Carolina, USA, unpublished data), Colorado (B Johnston, U.S. Forest Service, Lakewood, Colorado, unpublished data), Kansas (RL McGregor, USDA, personal communication, 2009), Kentucky (J Campbell, USDA, personal communication, 2009), Massachusetts (BA Sorrie, Massachusetts, USA, unpublished data) and Wisconsin (R Reed, Wisconsin, USA, unpublished data). The EPPO (2009b) considers the species an emerging invader in northern Europe.
Distribution Table
Top of pageThe distribution in this summary table is based on all the information available. When several references are cited, they may give conflicting information on the status. Further details may be available for individual references in the Distribution Table Details section which can be selected by going to Generate Report.
| Country | Distribution | Last Reported | Origin | First Reported | Invasive | References | Notes | NORTH AMERICA |
| Canada | | | | | | | |
| -Alberta | Present | | Native | | | Brouillet et al., 2006 | |
| -British Columbia | Present | | Native | | | Brouillet et al., 2006 | |
| -Manitoba | Present | | Native | | | Brouillet et al., 2006 | |
| -New Brunswick | Present | | Native | | | Brouillet et al., 2006 | |
| -Newfoundland and Labrador | Present | | Native | | | Brouillet et al., 2006 | |
| -Northwest Territories | Present | | Native | | | Brouillet et al., 2006 | |
| -Nova Scotia | Present | | Native | | | Brouillet et al., 2006 | |
| -Nunavut | Present | | Native | | | Brouillet et al., 2006 | |
| -Ontario | Present | | Native | | | Brouillet et al., 2006 | |
| -Prince Edward Island | Present | | Native | | | Brouillet et al., 2006 | |
| -Quebec | Present | | Native | | | Brouillet et al., 2006 | |
| -Saskatchewan | Present | | Native | | | Brouillet et al., 2006 | |
| -Yukon Territory | Present | | Native | | | Brouillet et al., 2006 | |
| Mexico | Localised | | Native | | | USDA-NRCS, 2009 | Limited distribution in northern Mexico including Chihuahua, Durango and Nuevo Leon |
| Saint Pierre and Miquelon | Present | | Native | | | Brouillet et al., 2006 | |
| USA | | | | | | | |
| -Alaska | Present | | Native | | | HITCHCOCK et al., 1969 | |
| -Arizona | Present | | Native | | | Kartesz, 1988 | |
| -California | Present | | Native | | | The Calflora Database, 2009; Jepson Manual, 2009 | |
| -Colorado | Present | | | | | USDA-NRCS, 2009 | |
| -Connecticut | Present | | Native | | | Dowhan, 1979 | |
| -Delaware | Present | | Native | | | Taber, 1960 | |
| -Idaho | Present | | Native | | | Davis, 1952 | |
| -Illinois | Present | | Native | | | Mohlenbrock, 1986 | |
| -Indiana | Present | | Native | | | Crovello et al., 1983 | |
| -Iowa | Present | | Native | | | Eilers & Roosa, 1991 | |
| -Maine | Present | | Native | | | Richards et al., 1983 | |
| -Maryland | Present | | Native | | | Brown & Brown, 1972 | |
| -Michigan | Present | | Native | | | Voss, 1985 | |
| -Minnesota | Present | | Native | | | Ownbey & Morley, 1991 | |
| -Montana | Present | | Native | | | HITCHCOCK et al., 1969 | |
| -Nebraska | Present | | Native | | | Barkley, 1977 | |
| -Nevada | Present | | Native | | | Kartesz, 1988 | |
| -New Hampshire | Present | | Native | | | Seymour, 1969 | |
| -New Jersey | Present | | Native | | | Hough, 1978 | |
| -New Mexico | Present | | Native | | | Martin & Hutchins, 1980 | |
| -New York | Present | | Native | | | Mitchell, 1986 | |
| -North Dakota | Present | | Native | | | Barkley, 1977 | |
| -Ohio | Present | | | | | Cooperrider, 1995 | |
| -Oregon | Present | | Native | | | HITCHCOCK et al., 1969; USDA-NRCS, 2009 | |
| -Pennsylvania | Present | | Native | | | Rhoads & McKinley, 1993 | |
| -Rhode Island | Present | | Native | | | Dowhan, 1979 | |
| -South Dakota | Present | | Native | | | Barkley, 1977 | |
| -Utah | Present | | Native | | | Welsh et al., 1987 | |
| -Vermont | Present | | Native | | | Atwood et al., 1973 | |
| -Virginia | Present | | Native | | | Harvill et al., 1977 | |
| -Washington | Present | | Native | | | HITCHCOCK et al., 1969 | |
| -West Virginia | Present | | Native | | | Strausbaugh & Core, 1977 | |
| -Wyoming | Present | | Native | | | Dorn, 1977 | |
EUROPE |
| Austria | Present | | Introduced | | | DAISIE, 2009; EPPO, 2009 | |
| Belgium | Present | | Introduced | 1885 | | DAISIE, 2009; EPPO, 2009; IAS, 2009 | |
| Czech Republic | Present | | Introduced | | | DAISIE, 2009; EPPO, 2009 | |
| Denmark | Widespread | | Introduced | | Invasive | Karlsson, 2009 | Introduced as an ornamental |
| Estonia | Present | | Introduced | | | EPPO, 2009 | |
| Finland | Widespread | | Introduced | | Invasive | Karlsson, 2009 | Introduced as an ornamental |
| France | Present | | Introduced | | | DAISIE, 2009 | Establishment pattern unknown |
| Germany | Present | | Introduced | | | EPPO, 2009 | |
| Hungary | Present | | Introduced | | | DAISIE, 2009 | Not established |
| Ireland | Present | | Introduced | | | EPPO, 2009; Kelly, 1990 | |
| Italy | Present only in captivity/cultivation | | Introduced | | | Garibaldi et al., 2003 | |
| Latvia | Present | | Introduced | | | DAISIE, 2009; EPPO, 2009 | |
| Russian Federation | Present | | Introduced | | | EPPO, 2009 | |
| Sweden | Widespread | | Introduced | | Invasive | Karlsson, 2009 | Introduced as an ornamental |
| Switzerland | Present | | Introduced | | Invasive | EPPO, 2009; EPPO, 2009 | |
| UK | Present | | Introduced | | | DAISIE, 2009; EPPO, 2009; Stace et al., 2009 | |
| -Scotland | Present | | Introduced | | Invasive | DAISIE, 2009 | Unknown status |
OCEANIA |
| Australia | Present | | Introduced | | | Gardening Australia, 2009; Randall, 2009 | |
History of Introduction and Spread
Top of pageC. sericea is a native to North America. The species was introduced in Europe (Belgium) as early as 1885 (IAS, 2009), and has been planted for ornamental purposes in Australia and Europe because of its attractive bark; some cultivars turn red in the winter season. In Europe, the distribution of the species is limited (EPPO, 2009b).
Risk of Introduction
Top of pageC. sericea may be a threat in Europe because of its invasive behaviour, and widespread usage as an ornamental species. The species is planted as an ornamental in Australia (Gardening Australia, 2009). It is listed as a black listed invasive species in Switzerland (EPPO, 2009b).
The species reproduces vegetatively by rooting along nodes and the lower stems (EPPO, 2009b). In native habitats such as sedge meadows and fens in North America, C. sericea colonizes far from clones of shrub by seed, but also advances via spreading (B Middleton, National Wetlands Research Center, Louisiana, USA, personal observation, 2009). Cattle grazing disturbs the soil, and allows C. sericea to establish if cattle grazing ceases (Middleton, 2002b).
Habitat
Top of pageIn North America, C. sericea is found mostly in northern climates, with some occurrences as far south as northern Mexico (USDA-FS, 2009) generally at elevations below 2500 m (EPPO, 2009b). The species can tolerate extreme conditions, including cold and submergence for several months (EPPO, 2009b). It is limited by high temperature at southern limits, e.g. New Mexico (USDA-FA, 2009). In sedge meadows grazed by cattle, the species can persist as a minor component of the wetland, even though the cattle browse the seedlings, saplings and full-grown shrubs of C. sericea. This shrub species may grow profusely after cattle are removed, so that C. sericea can be somewhat invasive in sedge meadows released from cattle grazing (Middleton, 2002a, b; Middleton et al., 2006).
Habitat List
Top of page| Category | Habitat | Presence | Status | | Brackish |
| Estuaries | Principal habitat | Natural |
| Freshwater |
| Lakes | Principal habitat | Natural |
| Ponds | Principal habitat | Natural |
| Reservoirs | Principal habitat | Natural |
| Rivers / streams | Principal habitat | Natural |
| Terrestrial-managed |
| Buildings | Secondary/tolerated habitat | Natural |
| Cultivated / agricultural land | Present, no further details | Harmful (pest or invasive) |
| Disturbed areas | Secondary/tolerated habitat | Harmful (pest or invasive) |
| Disturbed areas | Secondary/tolerated habitat | Natural |
| Industrial / intensive livestock production systems | Secondary/tolerated habitat | Natural |
| Managed forests, plantations and orchards | Secondary/tolerated habitat | Natural |
| Managed grasslands (grazing systems) | Secondary/tolerated habitat | Natural |
| Rail / roadsides | Secondary/tolerated habitat | Harmful (pest or invasive) |
| Rail / roadsides | Secondary/tolerated habitat | Natural |
| Urban / peri-urban areas | Secondary/tolerated habitat | Natural |
| Terrestrial-natural/semi-natural |
| Cold lands / tundra | Principal habitat | Natural |
| Natural forests | Principal habitat | Harmful (pest or invasive) |
| Natural grasslands | Present, no further details | Natural |
| Riverbanks | Principal habitat | Natural |
| Wetlands | Principal habitat | Harmful (pest or invasive) |
| Wetlands | Principal habitat | Natural |
Hosts/Species Affected
Top of pageInclude additional information not covered by the listing(s) above. Note any more specific information on stages of crop/plant growth most affected (e.g. to 40 days post-emergence). Cite important references here (rather than in above list).
Host Plants/Plants Affected
Top of page| Plant name | Family | Context | | Carex stricta | Cyperaceae | Unknown |
Growth Stages
Top of pagePre-emergence, Seedling stage, Vegetative growing stage
Biology and Ecology
Top of page
Genetics
2n = 22 (Karlsson, 2009).
Reproductive Biology
Seeds germinate in draw down, and are stored in the seed bank (USDA-FS, 2009). The seeds cold stratify in 90-120 days (Heit, 1968 in Baskin and Baskin, 1998), or as little as 30 days (Acharya et al., 1992 in Baskin and Baskin, 1998). Optimal germination temperatures are 10 to 30oC (Heit, 1968b in Baskin and Baskin, 1998) or 10–25oC (Acharya et al., 1992 in Baskin and Baskin, 1998).
Physiology and Phenology
In North America, C. sericea flowers from May to July, fruits from late July to October, and disperses from late July to October (USDA, 1948). Adult plants tolerate flooding for most of the growing season (USDA-FS, 2009). The minimum and maximum elevation ranges vary in the western states of the USA, with a minimum of 1036 m in Montana and a maximum elevation of 2896 m in Utah (USDA-FS, 2009). These differences in elevational preference may be related to water availability. The species grows best in wet areas, with 75% of full sunlight (USDA-FS, 2009). The phenology of flowering, leaf out, resting stage, red bark colour and leaf abscission varies across the latitudinal and longitudinal range of C. sericea in North America (USDA-FS, 2009).
Associations
In North America, C. sericea is associated with sedge meadows and fens in the north, which are dominated by Carex stricta and Calamagrostis canadensis. Rare forbs are often part of these systems (for list of forbs see Middleton, 2002b). C. sericea is also found as a riparian species in forest, woodland and grasslands, and thus is associated with a very wide variety of species (USDA-FS, 2009). In Europe, it is a species of wet woods (Kelly, 1990).
Environmental Requirements
Generally restricted to northern environments, and southward in mountainous areas.
Climate
Top of page| Climate | Status | Description | Remark | | C - Temperate/Mesothermal climate | Tolerated | Average temp. of coldest month > 0°C and < 18°C, mean warmest month > 10°C | |
| Cs - Warm temperate climate with dry summer | Tolerated | Warm average temp. > 10°C, Cold average temp. > 0°C, dry summers | |
| Cw - Warm temperate climate with dry winter | Tolerated | Warm temperate climate with dry winter (Warm average temp. > 10°C, Cold average temp. > 0°C, dry winters) | |
| D - Continental/Microthermal climate | Preferred | Continental/Microthermal climate (Average temp. of coldest month < 0°C, mean warmest month > 10°C) | |
| Df - Continental climate, wet all year | Preferred | Continental climate, wet all year (Warm average temp. > 10°C, coldest month < 0°C, wet all year) | |
| Ds - Continental climate with dry summer | Preferred | Continental climate with dry summer (Warm average temp. > 10°C, coldest month < 0°C, dry summers) | |
| Dw - Continental climate with dry winter | Preferred | Continental climate with dry winter (Warm average temp. > 10°C, coldest month < 0°C, dry winters) | |
| EF - Ice cap climate | Preferred | Ice cap climate (Average temp. all months < 0°C) | |
| ET - Tundra climate | Preferred | Tundra climate (Average temp. of warmest month < 10°C and > 0°C) | |
Air Temperature
Top of page| Parameter | Lower limit | Upper limit | | Absolute minimum temperature (ºC) | -38.9 | |
Rainfall
Top of page| Parameter | Lower limit | Upper limit | Description | | Mean annual rainfall | 457 | 1524 | mm; lower/upper limits |
Soil Tolerances
Top of pageSoil drainage
- free
- impeded
- seasonally waterlogged
Soil reaction
Soil texture
Special soil tolerances
Means of Movement and Dispersal
Top of pageNatural dispersal by seed is mainly via animals (USDA-FS, 2009). Clones spread readily via rooting by stems (EPPO, 2009b). Intentional introduction of the species has been for horticultural purposes in Europe and Australia (EPPO, 2009b).
Pathway Causes
Top of page| Cause | Notes | Long Distance | Local | References | | Botanical gardens/ zoos | | Yes | | EPPO, 2009; Gardening Australia, 2009 |
| Breeding/ propagation | | Yes | | |
| Digestion/excretion | North America | Yes | Yes | |
| Disturbance | North America | Yes | | Middleton, 2002; Middleton, 2002; USDA-FS, 2009 |
| Escape from confinement/ garden escape | Europe, Australia | Yes | | EPPO, 2009; Gardening Australia, 2009 |
| Hedges/ windbreaks | Europe | Yes | | EPPO, 2009 |
| Horticulture | Europe, Australia | Yes | | EPPO, 2009; Gardening Australia, 2009 |
| Internet sales | Europe, Australia | Yes | | EPPO, 2009; Gardening Australia, 2009 |
| Landscape improvement/ landscaping industry | Europe, Australia | Yes | | EPPO, 2009; Gardening Australia, 2009 |
| Ornamental purposes | Europe, Australia | Yes | | EPPO, 2009; Gardening Australia, 2009 |
Pathway Vectors
Top of page| Vector | Notes | Long Distance | Local | References | | Floating vegetation/debris | Parts of plant transported by water | Yes | | Kelly, 1990 |
| Livestock | Eaten and likely transported by water | Yes | | Kelly, 1990 |
| Mail/post | Horticulture trade | Yes | | EPPO, 2009 |
| Plants or parts of plants | Parts of plant transported by water | Yes | | Kelly, 1990 |
| Water | Parts of plant transported by water | Yes | | Kelly, 1990 |
Impact Summary
Top of page| Category | Impact | | Environment (generally) | Negative |
Environmental Impact
Top of pageImpact on Habitats
Due to the fact that C. sericea is a woody species, it may shade and replace grassland or herbaceous species in either native or invasive environments. The species may reduce biodiversity by reducing the growth and flowering of herbaceous species, e.g. in fens and sedge meadows in formerly grazed settings in North America (Middleton, 2002a). A proliferation of the species in ecosystems is likely to cause shifts in ecosystem function related to production, decomposition, and nutrient cycling.
Impact on Biodiversity
The species may reduce biodiversity by reducing the the growth and flowering of herbaceous species, e.g. in fens and sedge meadows in formerly grazing settings in North America (Middleton, 2002a). Similarly, it is thought to cause a reduction of biodiversity in woodland settings in Europe (Kelly, 1990).
Risk and Impact Factors
Top of pageImpact mechanisms
- Competition - monopolizing resources
- Competition - shading
- Herbivory/grazing/browsing
- Rapid growth
- Rooting
Impact outcomes
- Altered trophic level
- Damaged ecosystem services
- Ecosystem change/ habitat alteration
- Modification of nutrient regime
- Modification of successional patterns
- Monoculture formation
- Reduced native biodiversity
Invasiveness
- Abundant in its native range
- Benefits from human association (i.e. it is a human commensal)
- Fast growing
- Gregarious
- Has a broad native range
- Has high genetic variability
- Has high reproductive potential
- Has propagules that can remain viable for more than one year
- Highly adaptable to different environments
- Highly mobile locally
- Invasive in its native range
- Is a habitat generalist
- Long lived
- Pioneering in disturbed areas
- Proved invasive outside its native range
- Reproduces asexually
- Tolerant of shade
- Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
Likelihood of entry/control
- Difficult to identify/detect in the field
- Difficult/costly to control
- Highly likely to be transported internationally deliberately
Uses List
Top of pageAnimal feed, fodder, forage
Drugs, stimulants, social uses
Environmental
- Agroforestry
- Revegetation
- Wildlife habitat
General
Materials
Medicinal, pharmaceutical
- Source of medicine/pharmaceutical
Similarities to Other Species/Conditions
Top of page
Cornus alba is from northern Asia, but looks similar to C. sericea (Kelly, 1990). C. alba does not spread by suckers, whereas C. sericea has suckers and rooting branches. The fruits are drupe-like with several seeds (pyrene) in both species. C. alba has an ellipsoid pyrene tapering to a flat base, and C. sericea has a subglobose pyrene, rounded at the base (Karlsson, 2009).
Cornus sericea var. sericea hybridizes with Cornus sericea var. occidentalis westward in North America. The varieties of C. sericea may differ in characteristics, but generally overlap (Karlsson, 2009). The hybrids of these two types have a diverse array of characteristics related to pubescence, flower size and endocarp characters (Rickett, 1944).
Prevention and Control
Top of pagePrevention
SPS measures
The species is on alert lists in Belgium and Switzerland (IAS, 2009 and EPPO, 2009b, respectively).
Control
Physical/mechanical control
Can be controlled temporarily by cutting.
Biological control
Known diseases/parasites are not specific to C. sericea.
Chemical control
Control of shrubs using herbicides is more successful when sprayed early in the growing season (USDA-FS, 2009).
Ecosystem Restoration
In North America, C. sericea is often used to rehabilitate eroding stream banks, and terrestrial oil spills (USDA-FS, 2009). C. sericea is opportunistic, and spreads in sedge meadows and fens grazed by cattle. The cattle trample sedge tussocks, and allow a window of opportunity for colonization (Middleton, 1999). Although cattle continue to browse the shrubs and seedlings of C. sericea, the species exists in small amounts in the wetland. If grazing ceases, C. sericea spreads quickly and may dominate formerly grazed sedge meadows (Middleton, 2002a, b). Prescribed burning can increase the biodiversity of herbaceous species in such situations, by providing a short window of opportunity for flowering and seed set (Middleton, 2002a). C. sericea re-grows quickly from surviving roots and stems after fire, but it can be killed by hot fires (USDA-FS, 2009). Two years after a prescribed burn in Montana, C. sericea had regained 72% of its pre-fire dominance (Gordon, 1976). In Wisconsin, fire helps to maintain shrub-carrs (White, 1965; Warners, 1987).
Gaps in Knowledge/Research Needs
Top of pageAs ecosystem function shifts are likely in shrub communities of C. sericea, further research would be useful in both Europe and North America.
References
Top of pageAcharya SN, Chu CB, Hermesh R, Schaalje GB, 1992. Factors affecting red-osier dogwood seed germination. Canadian Journal of Botany, 70(5):1012-1016.
Atwood Jr JT, Countryman WD, Jervis RA, Miller DH, Seymour FC, Smith ML, 1973. Checklist of Vermont plants including all vascular plants growing without cultivation. Vermont, USA: Vermont Botanical and Bird Club.
Barkley TM, 1977. Atlas of the flora of the Great Plains. Ames, Iowa, : Iowa State University Press., 600 pp.
Baskin CC, Baskin JM, 1998. Seeds: ecology, biogeography, and evoluation of dormancy and germination. California, USA: Academic Press, 666 pp.
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Cooperrider TS, 1995. The Dicotyledoneae of Ohio. Part 2: Linaceae through Campanulaceae. Ohio, USA: Ohio State University Press, 656 pp.
Crovello TJ, Keller CA, Kartesz JT, 1983. The vascular plants of Indiana: A computer based checklist. Indiana, USA: University of Notre Dame Press, 136 pp.
DAISIE, 2009. Delivering Alien Invasive Species Inventories Europe. Brussels, Belgium: European Commission. http://www.europe-aliens.org/speciesFactsheet.do?speciesId=17173#
DAISIE, 2009. Delivering Alien Invasive Species Inventories for Europe. http://www.europe-aliens.org
Davis R, 1952. Flora of Idaho. Iowa, USA: WC Brown and Company, 828 pp.
Dorn RD, 1977. Manual of the vascular plants of Wyoming. 2 vols. New York, USA: Garland Publishing Inc., 1498 pp.
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EFloras, 2009. Madagascar Catalogue. http://www.efloras.org/florataxon.aspx?flora_id=12&taxon_id=10219
EFloras, 2009. Taiwan plant names. http://www.efloras.org/florataxon.aspx?flora_id=101&taxon_id=10219
Eilers LJ, Roosa DM, 1991. The vascular plants of Iowa. Iowa, USA: University of Iowa Press, 304 pp.
EPPO, 2009. Cornus sericea. EPPO's plant quarantine data retrieval system. Paris, France: EPPO. http://www.eppo.org/QUARANTINE/Alert_List/invasive_plants/Cornus_sericea.htm
EPPO, 2009. EPPO's plant quarantine data retrieval system. Paris, France: EPPO. http://www.eppo.org/DATABASES/pqr/pqr.htm
Gardening Australia, 2009. Fact sheet: winter interest plants. Melbourne, Australia: ABC. http://www.abc.net.au/gardening/stories/s2336829.htm
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Contributors
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14/09/09 Original text by:
Beth Middleton, USGS National Wetlands Research Center, 700 Cajundome Boulevard, Lafayette, LA 70506, USA
Distribution Maps
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- = Present, no further details
- = Evidence of pathogen
- = Widespread
- = Last reported
- = Localised
- = Presence unconfirmed
- = Confined and subject to quarantine
- = See regional map for distribution within the country
- = Occasional or few reports