Cookies on Invasive Species Compendium

Like most websites we use cookies. This is to ensure that we give you the best experience possible.

Continuing to use www.cabi.org means you agree to our use of cookies. If you would like to, you can learn more about the cookies we use.

Datasheet

Cornus sericea (redosier dogwood)

Summary

  • Last modified
  • 16 July 2013
  • Datasheet Type(s)
  • Invasive Species
  • Host Plant
  • Preferred Scientific Name
  • Cornus sericea
  • Preferred Common Name
  • redosier dogwood
  • Taxonomic Tree
  • Domain: Eukaryota
  •     Kingdom: Plantae
  •         Phylum: Spermatophyta
  •             Subphylum: Angiospermae
  •                 Class: Dicotyledonae
  • Summary of Invasiveness
  • C. 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 (Vi...

Don't need the entire report?

Generate a print friendly version containing only the sections you need.

Generate report

Pictures

Top of page
PictureTitleCaptionCopyright
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.
TitleHabit in a fen
CaptionCornus 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.
CopyrightBeth A. Middleton
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.
Habit in a fenCornus 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
Fen with tussock sedge (Carex stricta), various prairie marsh forbs and native Typha latifolia. Lodi Marsh, Wisconsin, USA.
TitleHabitat
CaptionFen with tussock sedge (Carex stricta), various prairie marsh forbs and native Typha latifolia. Lodi Marsh, Wisconsin, USA.
CopyrightBeth A. Middleton
Fen with tussock sedge (Carex stricta), various prairie marsh forbs and native Typha latifolia. Lodi Marsh, Wisconsin, USA.
HabitatFen with tussock sedge (Carex stricta), various prairie marsh forbs and native Typha latifolia. Lodi Marsh, Wisconsin, USA.Beth A. Middleton
Eupatorium maculatum, 'Joe Pye Weed' a tall sedge meadow forb which is shaded out by shrub growth. Lodi Marsh, Wisconsin, USA.
TitleHabitat
CaptionEupatorium maculatum, 'Joe Pye Weed' a tall sedge meadow forb which is shaded out by shrub growth. Lodi Marsh, Wisconsin, USA.
CopyrightBeth A. Middleton
Eupatorium maculatum, 'Joe Pye Weed' a tall sedge meadow forb which is shaded out by shrub growth. Lodi Marsh, Wisconsin, USA.
HabitatEupatorium 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 page

Preferred Scientific Name

  • Cornus sericea L., 1753

Preferred Common Name

  • redosier dogwood

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

  • CRWSR (Cornus sericea)

Summary of Invasiveness

Top of page

C. 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 page

Cornus 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 page

C. 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 page

The 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.

CountryDistributionLast ReportedOriginFirst ReportedInvasiveReferencesNotes

NORTH AMERICA

Canada
-AlbertaPresentNativeBrouillet et al., 2006
-British ColumbiaPresentNativeBrouillet et al., 2006
-ManitobaPresentNativeBrouillet et al., 2006
-New BrunswickPresentNativeBrouillet et al., 2006
-Newfoundland and LabradorPresentNativeBrouillet et al., 2006
-Northwest TerritoriesPresentNativeBrouillet et al., 2006
-Nova ScotiaPresentNativeBrouillet et al., 2006
-NunavutPresentNativeBrouillet et al., 2006
-OntarioPresentNativeBrouillet et al., 2006
-Prince Edward IslandPresentNativeBrouillet et al., 2006
-QuebecPresentNativeBrouillet et al., 2006
-SaskatchewanPresentNativeBrouillet et al., 2006
-Yukon TerritoryPresentNativeBrouillet et al., 2006
MexicoLocalisedNativeUSDA-NRCS, 2009Limited distribution in northern Mexico including Chihuahua, Durango and Nuevo Leon
Saint Pierre and MiquelonPresentNativeBrouillet et al., 2006
USA
-AlaskaPresentNativeHITCHCOCK et al., 1969
-ArizonaPresentNativeKartesz, 1988
-CaliforniaPresentNativeThe Calflora Database, 2009; Jepson Manual, 2009
-ColoradoPresentUSDA-NRCS, 2009
-ConnecticutPresentNativeDowhan, 1979
-DelawarePresentNativeTaber, 1960
-IdahoPresentNativeDavis, 1952
-IllinoisPresentNativeMohlenbrock, 1986
-IndianaPresentNativeCrovello et al., 1983
-IowaPresentNativeEilers & Roosa, 1991
-MainePresentNativeRichards et al., 1983
-MarylandPresentNativeBrown & Brown, 1972
-MichiganPresentNativeVoss, 1985
-MinnesotaPresentNativeOwnbey & Morley, 1991
-MontanaPresentNativeHITCHCOCK et al., 1969
-NebraskaPresentNativeBarkley, 1977
-NevadaPresentNativeKartesz, 1988
-New HampshirePresentNativeSeymour, 1969
-New JerseyPresentNativeHough, 1978
-New MexicoPresentNativeMartin & Hutchins, 1980
-New YorkPresentNativeMitchell, 1986
-North DakotaPresentNativeBarkley, 1977
-OhioPresentCooperrider, 1995
-OregonPresentNativeHITCHCOCK et al., 1969; USDA-NRCS, 2009
-PennsylvaniaPresentNativeRhoads & McKinley, 1993
-Rhode IslandPresentNativeDowhan, 1979
-South DakotaPresentNativeBarkley, 1977
-UtahPresentNativeWelsh et al., 1987
-VermontPresentNativeAtwood et al., 1973
-VirginiaPresentNativeHarvill et al., 1977
-WashingtonPresentNativeHITCHCOCK et al., 1969
-West VirginiaPresentNativeStrausbaugh & Core, 1977
-WyomingPresentNativeDorn, 1977

EUROPE

AustriaPresentIntroducedDAISIE, 2009; EPPO, 2009
BelgiumPresentIntroduced1885DAISIE, 2009; EPPO, 2009; IAS, 2009
Czech RepublicPresentIntroducedDAISIE, 2009; EPPO, 2009
DenmarkWidespreadIntroducedInvasiveKarlsson, 2009Introduced as an ornamental
EstoniaPresentIntroducedEPPO, 2009
FinlandWidespreadIntroducedInvasiveKarlsson, 2009Introduced as an ornamental
FrancePresentIntroducedDAISIE, 2009Establishment pattern unknown
GermanyPresentIntroducedEPPO, 2009
HungaryPresentIntroducedDAISIE, 2009Not established
IrelandPresentIntroducedEPPO, 2009; Kelly, 1990
ItalyPresent only in captivity/cultivationIntroducedGaribaldi et al., 2003
LatviaPresentIntroducedDAISIE, 2009; EPPO, 2009
Russian FederationPresentIntroducedEPPO, 2009
SwedenWidespreadIntroducedInvasiveKarlsson, 2009Introduced as an ornamental
SwitzerlandPresentIntroducedInvasiveEPPO, 2009; EPPO, 2009
UKPresentIntroducedDAISIE, 2009; EPPO, 2009; Stace et al., 2009
-ScotlandPresentIntroducedInvasiveDAISIE, 2009Unknown status

OCEANIA

AustraliaPresentIntroducedGardening Australia, 2009; Randall, 2009

History of Introduction and Spread

Top of page

C. 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).

Introductions

Top of page
Introduced toIntroduced fromYearReasonIntroduced byEstablished in wild throughReferencesNotes
Natural reproductionContinuous restocking
AustraliaNorth America Horticulture (pathway cause)Gardening Australia, 2009Not considered invasive
EuropeNorth America1885Horticulture (pathway cause)YesEPPO, 2009Considered an emerging invader in Europe

Risk of Introduction

Top of page

C. 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 page

In 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
CategoryHabitatPresenceStatus
Brackish
EstuariesPrincipal habitatNatural
Freshwater
LakesPrincipal habitatNatural
PondsPrincipal habitatNatural
ReservoirsPrincipal habitatNatural
Rivers / streamsPrincipal habitatNatural
Terrestrial-managed
BuildingsSecondary/tolerated habitatNatural
Cultivated / agricultural landPresent, no further detailsHarmful (pest or invasive)
Disturbed areasSecondary/tolerated habitatHarmful (pest or invasive)
Disturbed areasSecondary/tolerated habitatNatural
Industrial / intensive livestock production systemsSecondary/tolerated habitatNatural
Managed forests, plantations and orchardsSecondary/tolerated habitatNatural
Managed grasslands (grazing systems)Secondary/tolerated habitatNatural
Rail / roadsidesSecondary/tolerated habitatHarmful (pest or invasive)
Rail / roadsidesSecondary/tolerated habitatNatural
Urban / peri-urban areasSecondary/tolerated habitatNatural
Terrestrial-natural/semi-natural
Cold lands / tundraPrincipal habitatNatural
Natural forestsPrincipal habitatHarmful (pest or invasive)
Natural grasslandsPresent, no further detailsNatural
RiverbanksPrincipal habitatNatural
WetlandsPrincipal habitatHarmful (pest or invasive)
WetlandsPrincipal habitatNatural

Hosts/Species Affected

Top of page

Include 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 nameFamilyContext
Carex strictaCyperaceaeUnknown

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
ClimateStatusDescriptionRemark
C - Temperate/Mesothermal climateToleratedAverage temp. of coldest month > 0°C and < 18°C, mean warmest month > 10°C
Cs - Warm temperate climate with dry summerToleratedWarm average temp. > 10°C, Cold average temp. > 0°C, dry summers
Cw - Warm temperate climate with dry winterToleratedWarm temperate climate with dry winter (Warm average temp. > 10°C, Cold average temp. > 0°C, dry winters)
D - Continental/Microthermal climatePreferredContinental/Microthermal climate (Average temp. of coldest month < 0°C, mean warmest month > 10°C)
Df - Continental climate, wet all yearPreferredContinental climate, wet all year (Warm average temp. > 10°C, coldest month < 0°C, wet all year)
Ds - Continental climate with dry summerPreferredContinental climate with dry summer (Warm average temp. > 10°C, coldest month < 0°C, dry summers)
Dw - Continental climate with dry winterPreferredContinental climate with dry winter (Warm average temp. > 10°C, coldest month < 0°C, dry winters)
EF - Ice cap climatePreferredIce cap climate (Average temp. all months < 0°C)
ET - Tundra climatePreferredTundra climate (Average temp. of warmest month < 10°C and > 0°C)

Air Temperature

Top of page
ParameterLower limitUpper limit
Absolute minimum temperature (ºC)-38.9

Rainfall

Top of page
ParameterLower limitUpper limitDescription
Mean annual rainfall4571524mm; lower/upper limits

Soil Tolerances

Top of page

Soil drainage

  • free
  • impeded
  • seasonally waterlogged

Soil reaction

  • acid
  • alkaline
  • neutral

Soil texture

  • heavy
  • light
  • medium

Special soil tolerances

  • infertile
  • saline
  • sodic

Natural Enemies

Top of page
Natural enemyTypeLife stagesSpecificityReferencesBiological control inBiological control on
Botryosphaeria dothideaPathogenRootsnot specificSchoeneweiss, 1979
Erysiphe tortilisPathogenLeavesnot specificSwiderska et al., 2005
Lambdina fiscellariaHerbivoreLeavesnot specificTorgersen & Baker, 1969
Septoria cornicolaPathogenLeavesnot specificGaribaldi et al., 2003; Mmbaga & Sauvé, 2004

Means of Movement and Dispersal

Top of page

Natural 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
CauseNotesLong DistanceLocalReferences
Botanical gardens/ zoosYesEPPO, 2009; Gardening Australia, 2009
Breeding/ propagationYes
Digestion/excretionNorth AmericaYesYes
DisturbanceNorth AmericaYesMiddleton, 2002; Middleton, 2002; USDA-FS, 2009
Escape from confinement/ garden escapeEurope, AustraliaYesEPPO, 2009; Gardening Australia, 2009
Hedges/ windbreaksEuropeYesEPPO, 2009
HorticultureEurope, AustraliaYesEPPO, 2009; Gardening Australia, 2009
Internet salesEurope, AustraliaYesEPPO, 2009; Gardening Australia, 2009
Landscape improvement/ landscaping industryEurope, AustraliaYesEPPO, 2009; Gardening Australia, 2009
Ornamental purposesEurope, AustraliaYesEPPO, 2009; Gardening Australia, 2009

Pathway Vectors

Top of page
VectorNotesLong DistanceLocalReferences
Floating vegetation/debrisParts of plant transported by waterYesKelly, 1990
LivestockEaten and likely transported by waterYesKelly, 1990
Mail/postHorticulture tradeYesEPPO, 2009
Plants or parts of plantsParts of plant transported by waterYesKelly, 1990
WaterParts of plant transported by waterYesKelly, 1990

Impact Summary

Top of page
CategoryImpact
Environment (generally)Negative

Environmental Impact

Top of page

Impact 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 page

Impact 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 page

Animal feed, fodder, forage

  • Forage

Drugs, stimulants, social uses

  • Smoking

Environmental

  • Agroforestry
  • Revegetation
  • Wildlife habitat

General

  • Botanical garden/zoo

Materials

  • Baskets

Medicinal, pharmaceutical

  • Source of medicine/pharmaceutical

Wood Products

Top of pageBaskets

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 page

Prevention

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 page

As 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 page

Acharya 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.

Brouillet L, Coursol F, Favreau M, 2006. VASCAN. The database of Canadian vascular plants. Montreal, Canada: Herbier Marie-Victorin, Institut de Recherche en Biologie Vegetale. http://www.botany.ubc.ca/herbarium/vascular/index.html

Brown RG, Brown ML, 1972. Woody plants of Maryland. Maryland, USA: Port City Press, 347 pp.

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.

Dowhan JJ, 1979. Preliminary checklist of the vascular flora of Connecticut (growing without cultivation). Connecticut, USA: State Geological and Natural History Survey of Connecticut.

EFloras, 2009. Arboles y arbustos de los Andes del Ecuador. http://www.efloras.org/florataxon.aspx?flora_id=201&taxon_id=10219

EFloras, 2009. Flora of Chile. http://www.efloras.org/florataxon.aspx?flora_id=60&taxon_id=10219

EFloras, 2009. Flora of China. http://www.efloras.org/florataxon.aspx?flora_id=2&taxon_id=200005226

EFloras, 2009. Flora of Pakistan. http://www.efloras.org/browse.aspx?flora_id=5&name_str=Cornus+sericea

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

Garibaldi A, Bertetti D, Gullino ML, 2003. First report of septoria leaf spot on Cornus sericea in Italy. Plant Disease, 87(2):204.

Gordon FA, 1976. Srping burning in an aspen-conifer stand for maintenance of moose habitat, West Boulder River, Montana. In: Proceedings, Montana Tall Timbers Fire Ecology Conference and Intermountain Fire Research Council Fire and Land Management Symposium; 1974 October 8-10; Missoula, MT Florida, USA: Tall Timbers Research Station, 501-538.

Harvill AM, Stevens CE, Ware DME, 1977. Atlas of the Virginia flora, Part I. Pteridophytes through monocotyledons. Virginia, USA: Virginia Botanical Associates, 59 pp.

Heit CE, 1968. Propagation from seed. 15. Fall planting of shrub seeds for successful seedling production. American Nurseryman, 128(4):8-10, 70-80.

Hitchcock CL, Cronquist A, Ownbey M, Thompson JW, 1969. Vascular plants of the Pacific Northwest. Seattle, USA: University of Washington Press, 914 pp.

Hough M, 1978. New Jersey wild plants. New Jersey, USA: Harmony Press, 34 pp.

IAS, 2009. Invasive alien species in Belgium. Belgium: IAS. http://ias.biodiveristy.be/ias/species/show/106

Jepson Manual, 2009. Jepson Online Interchange California Floristics. California, USA: University of California. http://ucjeps.berkeley.edu/interchange/I_treat_indexes.html

Karlsson T, 2009. Flora Nordica. Stockholm, Sweden: Swedish Royal Academy of Sciences.

Kartesz JT, 1988. A flora of Nevada. Nevada, USA: University of Nevada, Nevada.

Kelly DL, 1990. Cornus sericea L. in Ireland: an incipient weed of wetlands. Watsonia, 18:33-36.

Lohmueller FA, 2008. The botanical system of the plants. http://www.f-lohmueller.de/botany/phyta_0.htm

Martin AD, Zim HS, Nelson AL, 1951. American wildlife and plants. A guide to wildlife food habits. New York, USA: Dover Publications, 500 pp.

Martin WC, Hutchins CR, 1980. A flora of New Mexico. Vaduz, Germany: Strauss & Cramer, 1026 pp.

Middleton B, 2002. Nonequilibrium dynamics of sedge meadows grazed by cattle in southern Wisconsin. Plant Ecology, 161(1):89-110.

Middleton B, 2002. Winter burning and the reduction of Cornus sericea in sedge meadows in Southern Wisconsin. Restoration Ecology, 10(4):723-730.

Middleton BA, 1999. Wetland restoration, flood pulsing and disturbance dynamics. New York, USA: John Wiley and Sons, 388 pp.

Middleton BA, Holsten B, Diggelen Rvan, 2006. Biodiversity management of fens and fen meadows by grazing, cutting and burning. Applied Vegetation Science, 9:307-316.

Mitchell RS, 1986. A checklist of New York State plants. Contributions of a flora of New York State, Checklist III. New York State Bulletin, 458.

Mmbaga MT, Sauvé RJ, 2004. Multiple disease resistance in dogwoods (Cornus spp.) to foliar pathogens. Journal of Arboriculture, 30(2):101-107.

Mohlenbrock RH, 1986. Guide to the vascular flora of Illinois. Illinois, USA: Southern Illinois University Press, 500 pp.

Ownbey GB, Morley T, 1991. Vascular plants of Minnesota: A checklist and atlas. Minnesota, USA: University of Minnesota Press, 307 pp.

Press JR, Shrestha KK, Sutton DA, 2000. Annotated checklist of the flowering plants of Nepal [ed. by Press JR, Shrestha KK, Sutton DA]. London, UK: Natural History Museum Publications, x + 430 pp.

Randall RP, 2009. The introduced flora of Australia and its weed status. CRC for Australian Weed Management. Glen Osmond, Australia: University of Adelaide. http://www.weedscrc.org.au/documents/intro_flora_australia.pdf

Rhoads AF, McKinley Klein W Jr, 1993. The vascular flora of Pennsylvania: annotated checklist and atlas. Philadelphia, USA; American Philosophical Society, 636 pp.

Richards CD, Hyland F, Eastman LM, 1983. Revised check-list of the vascular plants of Maine. Bulletin of the Josselyn Botanical Society, 11.

Rickett HW, 1944. Cornus stolonifera and Cronus occidentalis. Brittonia, 5:149-59.

Rogers LL, Applegate RD, 1983. Dispersal of fruit seeds by black bear. Journal of Mammology, 64(2):310-311.

Rook EJS, 2002. Cornus sericea. www.rook.org/earl/bwca/nature/shrubs/cornusser.html

Schoeneweiss DF, 1979. Protection against stress predisposition to Botryosphaeria canker in containerized Cornus stolonifera by soil injection with benomyl. Plant Disease Reporter, 63(10):896-900.

Seymour FC, 1969. The flora of New England. New Hampshire, USA: Charles E. Tuttle Company, 596 pp.

Stace C, Meijden Rder , Kort Ide, 2009. Interactive flora of NW Europe. Amsterdam, The Netherlands: Netherlands Global Biodiversity Information Facility (NLBIF). http://nlbif.eti.uva.nl/bis/flora.php?menuentry=soorten&id=3076

Strausbaugh PD, Core EL, 1977. Flora of West Virginia, 2nd edition. West Virginia Bulletin:1079 pp.

Swiderska U, Woczanska A, Kozowska M, Muenko W, Mamczarz M, 2005. Recent collections of powdery mildews (Erysiphales) in Poland. Acta Mycologica, 40(1):49-61.

Taber WS, 1960. Delaware trees, 2nd edition. Delaware, USA: Delaware State Forestry Department, 254 pp.

The Calflora Database, 2009. Calflora: Information on California plants for education, research and conservation. California, USA: Calflora. http://www.calflora.org

Torgersen TR, Baker BH, 1969. The occurrence of the hemlock looper (Lambdina fiscellaria (Guenee) (Lepidoptera: Geometridae) in southeast Alaska, with notes on its biology. Research Note, Pacific North-West Forest and Range Experiment Station, U.S. Forest Servie, USDA., 6 pp.

USDA, 1948. Woody-Plant Seed Manual. USDA Forest Service Miscellaneous Publication No. 654, Washington, DC.

USDA-ARS, 2009. Germplasm Resources Information Network (GRIN). Online Database. Beltsville, Maryland, USA: National Germplasm Resources Laboratory. https://npgsweb.ars-grin.gov/gringlobal/taxon/taxonomysearch.aspx

USDA-FS, 2009. Cornus sericea database. Washington DC, USA: US Forest Service. http://www.fs.fed.us/database/feis/plants/shrub/corser/all.html

USDA-NRCS, 2009. The PLANTS Database. Baton Rouge, USA: National Plant Data Center. http://plants.usda.gov/

Viereck LA, Little EL Jr, 1972. Alaska trees and shrubs. Agriculture Handbook 410. Washington DC, USA: US Department of Agriculture.

Voss EG, 1985. Michigan flora. Michigan, USA: Cranbrook Institute of Science, 488 pp.

Warners DP, 1987. Effects of burning on sedge meadow studied (Wisconsin). Restoration and Management Notes, 5(2):90-91.

WBIS, 2009. Wisconsin Botanical Information System. Wisconsin, USA: Wisconsin State Herbarium. http://www.botany.wisc.edu/cgi-bin/detail.cgi?SpCode=CORSTO

Welsh SL, Atwood ND, Higgins LC, Goodrich S, 1987. A Utah flora. No. Provo, Utah: Brigham Young University Press. Great Basin Naturalist Memoirs. Utah, USA: Brigham Young University Press, 986 pp.

White KL, 1965. Shrub-carrs of southeastern Wisconsin. Ecology, 46(3):286-304.

Xiang JQ, 2009. Biogeography of Cornus. North Carolina, USA: North Carolina State University. http://www4.ncsu.edu/~qyxiang/cornusbiogeography.html

Links to Websites

Top of page
WebsiteURLComment
Integrated Taxonomic Information Systemhttp://www/itis.usda.gov
USDA-PLANTShttp://plants.usda.gov
NOBANIS: North European and Baltic Network on Invasive Alien Specieshttp://www.nobanis.org
Belgian Biodiversity Platformhttp://www.biodiversity.be/

Organisations

Top of page

France: European and Mediterranean Plant Protection Organisation (EPPO), OEPP/EPPO, 1 rue Le Notre, 75016 Paris, http://www.eppo.org/

Contributors

Top of page

14/09/09 Original text by:

Beth Middleton, USGS National Wetlands Research Center, 700 Cajundome Boulevard, Lafayette, LA  70506, USA

Distribution Maps

Top of page
Distribution map Austria: Present, introduced
DAISIE, 2009; EPPO, 2009Australia: Present, introduced
Gardening Australia, 2009; Randall, 2009Belgium: Present, introduced
DAISIE, 2009; EPPO, 2009; IAS, 2009Canada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countryCanada
See regional map for distribution within the countrySwitzerland: Present, introduced, invasive
EPPO, 2009; EPPO, 2009Czech Republic: Present, introduced
DAISIE, 2009; EPPO, 2009Germany: Present, introduced
EPPO, 2009Denmark: Widespread, introduced, invasive
Karlsson, 2009Estonia: Present, introduced
EPPO, 2009Finland: Widespread, introduced, invasive
Karlsson, 2009France: Present, introduced
DAISIE, 2009UK: Present, introduced
DAISIE, 2009; EPPO, 2009; Stace et al., 2009UK
See regional map for distribution within the countryHungary: Present, introduced
DAISIE, 2009Ireland: Present, introduced
EPPO, 2009; Kelly, 1990Italy: Present only in captivity/cultivation, introduced
Garibaldi et al., 2003Latvia: Present, introduced
DAISIE, 2009; EPPO, 2009Mexico: Localised, native
USDA-NRCS, 2009Mexico: Localised, native
USDA-NRCS, 2009Saint Pierre and Miquelon: Present, native
Brouillet et al., 2006Russian Federation: Present, introduced
EPPO, 2009Russian Federation: Present, introduced
EPPO, 2009Sweden: Widespread, introduced, invasive
Karlsson, 2009USA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the countryUSA
See regional map for distribution within the country
  • = 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
Download KML file Download CSV file
Creative Commons Licence
This work is licensed under a Creative Commons Attribution-NonCommercial-ShareAlike 3.0 Unported License.

Please click OK to ACCEPT or Cancel to REJECT

Creative Commons Licence
This work is licensed under a Creative Commons Attribution-NonCommercial-ShareAlike 3.0 Unported License.

Please click OK to ACCEPT or Cancel to REJECT

Distribution map (asia) Russian Federation: Present, introduced
EPPO, 2009
Distribution map (europe) Austria: Present, introduced
DAISIE, 2009; EPPO, 2009Belgium: Present, introduced
DAISIE, 2009; EPPO, 2009; IAS, 2009Switzerland: Present, introduced, invasive
EPPO, 2009; EPPO, 2009Czech Republic: Present, introduced
DAISIE, 2009; EPPO, 2009Germany: Present, introduced
EPPO, 2009Denmark: Widespread, introduced, invasive
Karlsson, 2009Estonia: Present, introduced
EPPO, 2009Finland: Widespread, introduced, invasive
Karlsson, 2009France: Present, introduced
DAISIE, 2009UK: Present, introduced
DAISIE, 2009; EPPO, 2009; Stace et al., 2009Scotland: Present, introduced, invasive
DAISIE, 2009Hungary: Present, introduced
DAISIE, 2009Ireland: Present, introduced
EPPO, 2009; Kelly, 1990Italy: Present only in captivity/cultivation, introduced
Garibaldi et al., 2003Latvia: Present, introduced
DAISIE, 2009; EPPO, 2009Russian Federation: Present, introduced
EPPO, 2009Sweden: Widespread, introduced, invasive
Karlsson, 2009
Distribution map (africa)
Distribution map (north america) Alberta: Present, native
Brouillet et al., 2006British Columbia: Present, native
Brouillet et al., 2006Manitoba: Present, native
Brouillet et al., 2006New Brunswick: Present, native
Brouillet et al., 2006Newfoundland and Labrador: Present, native
Brouillet et al., 2006Nova Scotia: Present, native
Brouillet et al., 2006Northwest Territories: Present, native
Brouillet et al., 2006Nunavut: Present, native
Brouillet et al., 2006Ontario: Present, native
Brouillet et al., 2006Prince Edward Island: Present, native
Brouillet et al., 2006Quebec: Present, native
Brouillet et al., 2006Saskatchewan: Present, native
Brouillet et al., 2006Yukon Territory: Present, native
Brouillet et al., 2006Mexico: Localised, native
USDA-NRCS, 2009Saint Pierre and Miquelon: Present, native
Brouillet et al., 2006Alaska: Present, native
HITCHCOCK et al., 1969Arizona: Present, native
Kartesz, 1988California: Present, native
The Calflora Database, 2009; Jepson Manual, 2009Colorado: Present
USDA-NRCS, 2009Connecticut: Present, native
Dowhan, 1979Delaware: Present, native
Taber, 1960Iowa: Present, native
Eilers & Roosa, 1991Idaho: Present, native
Davis, 1952Illinois: Present, native
Mohlenbrock, 1986Indiana: Present, native
Crovello et al., 1983Maryland: Present, native
Brown & Brown, 1972Maine: Present, native
Richards et al., 1983Michigan: Present, native
Voss, 1985Minnesota: Present, native
Ownbey & Morley, 1991Montana: Present, native
HITCHCOCK et al., 1969North Dakota: Present, native
Barkley, 1977Nebraska: Present, native
Barkley, 1977New Hampshire: Present, native
Seymour, 1969New Jersey: Present, native
Hough, 1978New Mexico: Present, native
Martin & Hutchins, 1980Nevada: Present, native
Kartesz, 1988New York: Present, native
Mitchell, 1986Ohio: Present
Cooperrider, 1995Oregon: Present, native
HITCHCOCK et al., 1969; USDA-NRCS, 2009Pennsylvania: Present, native
Rhoads & McKinley, 1993Rhode Island: Present, native
Dowhan, 1979South Dakota: Present, native
Barkley, 1977Utah: Present, native
Welsh et al., 1987Virginia: Present, native
Harvill et al., 1977Vermont: Present, native
Atwood et al., 1973Washington: Present, native
HITCHCOCK et al., 1969West Virginia: Present, native
Strausbaugh & Core, 1977Wyoming: Present, native
Dorn, 1977
Distribution map (central america) Mexico: Localised, native
USDA-NRCS, 2009
Distribution map (south america)
Distribution map (pacific) Australia: Present, introduced
Gardening Australia, 2009; Randall, 2009