Artemisia dracunculus

L.

Dragon Wormwood

G5Secure Found in 90 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Identity
Unique IDELEMENT_GLOBAL.2.154282
Element CodePDAST0S0H0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderAsterales
FamilyAsteraceae
GenusArtemisia
Synonyms
Artemisia dracunculoidesPursh
Other Common Names
Estragon (FR) tarragon (EN) Wild Tarragon (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
Two subspecies of A. dracunculus (glauca and dracunculus) were recognized by Kartesz (1994), but Kartesz (1999) and the Flora of North America (vol. 19 2006) considers them to be synonyms. A. dracunculus "apparently intergrades to a limited extent with Artemisia campestris subsp. caudata, especially in the southern Great Plains." (Great Plains Flora Association 1986)
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-05-16
Change Date1987-09-30
Edition Date2000-01-21
Edition AuthorsSusan Spackman, David Anderson, and Steve Thomas (1/00); rev. Eric Nielsen (1/00)
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences81 to >300
Rank Reasons
This species is quite widely distributed and very common, at least in portions of its range. It is described as weedy (Weber and Wittmann 1996a, Weber and Wittmann 1996b) and appears to have been introduced in parts of its range. The current level of harvest of this species for spices and for medicinal purposes does not seem to be compromising any populations.
Range Extent Comments
A. dracunculus occurs in eastern Europe and Asia, and throughout much of western North America, south from Alaska to northern Mexico, and westwards from Ontario, Wisconsin, Illinois, and Texas (USDA-NRCS 1999, Great Plains Flora Association 1986, Hulten 1968, Kartesz 1999). A. dracunculus also in occurs in New York and a few adjoining states (USDA-NRCS 1999), though these may represent more recent human introductions, as they are not listed in earlier journals (Gleason and Cronquist 1963). The Alaskan and many European populations may also result from human introductions (Hulten 1968). The taxon present in Manitoba is Artemisia dracunculus ssp. glauca, where it is at its northeastern limit and occurs in the southern third of the province, west of the Red River valley (Manitoba Conservation Data Centre).
Occurrences Comments
Tens of thousands of populations are extant rangewide, with large areas of Nevada, Wyoming, British Columbia, Nebraska, and Arizona reportedly occupied by this species. Wyoming: >100; British Columbia: common; Manitoba: 21-100; Ontario: one, presumed at the eastern edge of its native range, though possibly adventive because it is near a railroad track; Nevada: very widespread, both geographically and in elevation; Kansas: 50-75, overlooked and underrepresented in herbaria; Illinois: two; Nebraska: common; California: common; Colorado: "frequent and often weedy" (Weber and Wittmann 1996a, Weber and Wittmann 1996b).; Missouri: 5 historical occurrences ssp. glauca; Arizona: occurs through much of the state (Kearney and Peebles 1951); Idaho: extremely common, in some places with weedy tendencies; New York: considered a rare introduction (Natural Heritage Programs and Conservation Data Centres).
Threat Impact Comments
There are no reports from botanists that there is evidence of plant collecting or any obvious impacts on the species due to this practice. However, given the ubiquity of this species, and the multitude of uses that this plant serves, it is certainly being collected to at least a small extent. Robyn Klein (pers. comm.) states that this and other species of Artemisia are collected for medicinal uses and to make smudge bundles, but that it is unlikely that it is in danger of overharvesting.

In Manitoba, Native Americans may collect this species as they do other Artemisia spp. for cultural/medicinal use. Collection of Artemisia species has been observed in and around reserves (Manitoba Conservation Data Centre).

It is listed as "an herb that can be commonly gathered" (Frontier Co-op 2000). It is collected by hand, which is laborious. Other species, such as A. tridentata and A. ludoviciana, are more commonly collected than this species (Robyn Klein pers. comm.).

An individual from the U.S. herbal medicinal industry states that this plant receives minor usage outside its use as a spice (French tarragon), for which it is cultivated and imported (McGuffin pers. comm.).

In North America, towards the eastern edges of its range, many of the habitats which may have supported this species have been destroyed over the last 200 years for agriculture, urban or suburban development, and materials mining. Also along this eastern zone, it is possible that habitat degradation is a significant threat to remaining populations; natural communities in this region are often greatly dissected by agriculture and development, and subsequent alterations in landscape processes are altering many habitats. In contrast, threats to the habitat of this species towards the interior of its range (the Great Plains, Rocky Mountains, Great Basin, etc.) may be merely sporadic at this time. In Manitoba, threats are grazing, mowing, and tillage (Manitoba Conservation Data Centre). Current rates of wild harvest of this species do not appear to be having a noticeable impact, but renewed interest in this species as a medicinal herb is likely to result in increased wild harvest in the future (Edward Fletcher pers. comm.).
Ecology & Habitat

Habitat

A. dracunculus occurs to elevations of 3700m in dry open habitats, including prairies, rocky slopes, and roadsides (Cronquist et al. 1972, Hulten 1968). Habitat descriptions for this species frequently appear to be vague; the reason for this may be its frequent occurrence in a high number of community types. In Utah, ten community types are described for this species, including rabbitbrush shrublands, pinyon-juniper woodlands, and spruce-fir forests (Welsh et al. 1993). It is considered to be somewhat weedy in Colorado (Weber and Wittmann 1996a). It is described in Arizona from open coniferous forests and chaparral, from 3500-9000 feet (Kearney and Peebles 1951, Arizona Heritage Data Management System).
Other Nations (2)
CanadaN5
ProvinceRankNative
Northwest TerritoriesS2Yes
OntarioS1Yes
SaskatchewanS4Yes
Yukon TerritoryS3Yes
AlbertaS4Yes
British ColumbiaS5Yes
ManitobaS4Yes
United StatesN5
ProvinceRankNative
TexasSNRYes
MissouriSHYes
NevadaS4Yes
CaliforniaSNRYes
KansasS2Yes
ArizonaSNRYes
New MexicoSNRYes
New YorkSNANo
AlaskaS1Yes
NebraskaSNRYes
OregonSNRYes
ColoradoS5Yes
New JerseySNRYes
MassachusettsSNRYes
OklahomaSNRYes
MontanaS4Yes
WyomingS5Yes
ConnecticutSNANo
UtahSNRYes
WashingtonSNRYes
IowaS3Yes
IllinoisS1Yes
MinnesotaSNRYes
South DakotaSNRYes
North DakotaSNRYes
IdahoSNRYes
WisconsinS2Yes
Plant Characteristics
Economic Value (Genus)Yes
Roadless Areas (90)
Arizona (2)
AreaForestAcres
Lime CreekTonto National Forest42,568
Salt HouseApache-Sitgreaves National Forests21,848
California (58)
AreaForestAcres
AntimonyLos Padres National Forest40,911
Arroyo SecoAngeles National Forest4,703
Barker ValleyCleveland National Forest11,940
Bear MountainLos Padres National Forest913
Birch CreekInyo National Forest28,816
Black ButteLos Padres National Forest5,116
Black CanyonInyo National Forest32,421
Boundary Peak (CA)Inyo National Forest210,884
Cactus Springs BSan Bernardino National Forest3,106
CajonSan Bernardino National Forest7,548
CalienteCleveland National Forest5,953
ColdwaterCleveland National Forest8,402
Coyote NorthInyo National Forest11,932
Coyote SoutheastInyo National Forest53,159
Crystal CreekSan Bernardino National Forest6,783
Cucamonga AAngeles National Forest1,249
Cucamonga BSan Bernardino National Forest11,933
Cutca ValleyCleveland National Forest14,530
DardanellesEldorado National Forest8,110
Domeland Add.Sequoia National Forest3,046
Eagle PeakCleveland National Forest6,481
Fish CanyonAngeles National Forest29,886
Granite PeakSan Bernardino National Forest450
Greenhorn CreekSequoia National Forest28,226
Hoover - NorthHumboldt-Toiyabe National Forest1,574
Horse Creek RidgeSan Bernardino National Forest8,969
Horse Mdw.Inyo National Forest5,687
HortonInyo National Forest5,717
Iceberg - Mill CreekHumboldt-Toiyabe National Forest26,988
Log Cabin SaddlebagInyo National Forest15,165
Magic MountainAngeles National Forest15,542
Mill CreekSequoia National Forest27,643
Mill PeakSan Bernardino National Forest7,884
MonoLos Padres National Forest28,141
Mt. OlsenInyo National Forest2,161
Nevahbe RidgeInyo National Forest302
PaiuteInyo National Forest58,712
Pleasant ViewAngeles National Forest26,395
Pyramid Peak BSan Bernardino National Forest7,194
Raywood Flat ASan Bernardino National Forest41
Raywood Flat BSan Bernardino National Forest11,373
Rouse HillSan Bernardino National Forest13,745
San Gabriel AddAngeles National Forest2,527
San SevaineSan Bernardino National Forest6,866
Sawmill - BadlandsLos Padres National Forest51,362
Sespe - FrazierLos Padres National Forest106,910
Sheep MountainAngeles National Forest21,098
Sill HillCleveland National Forest5,294
Soldier CanyonInyo National Forest40,589
South SierraInyo National Forest41,853
Strawberry PeakAngeles National Forest7,245
SugarloafSan Bernardino National Forest8,206
Table Mtn.Inyo National Forest4,215
TinemahaInyo National Forest27,060
TuleAngeles National Forest9,861
WestforkAngeles National Forest4,407
WildhorseCleveland National Forest1,483
WoodpeckerSequoia National Forest11,936
Colorado (1)
AreaForestAcres
Bristol HeadRio Grande NF46,087
Montana (1)
AreaForestAcres
North AbsarokaCuster National Forest21,063
Nevada (9)
AreaForestAcres
Boundary Peak (NV)Inyo National Forest21,851
Chineese Camp (NV)Humboldt-Toiyabe National Forest15,207
Pine Grove SouthHumboldt-Toiyabe National Forest88,945
Rose - GalenaHumboldt-Toiyabe National Forest3,711
Snake - Big WashHumboldt-Toiyabe National Forest4,146
Snake - ChokecherryHumboldt-Toiyabe National Forest30,845
Snake - MurphyHumboldt-Toiyabe National Forest27,064
Snake - Peacock CynHumboldt-Toiyabe National Forest1,069
West Walker (NV)Humboldt-Toiyabe National Forest5,683
New Mexico (8)
AreaForestAcres
Alamo CanyonSanta Fe National Forest8,639
Columbine - Hondo Wilderness Study AreaCarson National Forest43,739
Dry CreekGila National Forest26,719
Guaje CanyonSanta Fe National Forest6,104
Latir PeakCarson National Forest3,573
NolanGila National Forest13,051
RendijaSanta Fe National Forest2,176
Ryan HillCibola National Forest34,201
South Dakota (2)
AreaForestAcres
Cheyenne RiverBuffalo Gap National Grassland7,572
Red ShirtBuffalo Gap National Grassland17,007
Utah (7)
AreaForestAcres
418016Uinta National Forest35,240
418025Uinta National Forest32,698
Boulger - Black CanyonManti-Lasal National Forest23,286
Horse Mountain - Mans PeakManti-Lasal National Forest22,159
Mt. NaomiWasatch-Cache National Forest41,922
Stansbury MountainsWasatch-Cache National Forest39,696
Temple PeakWasatch-Cache National Forest24,081
Wyoming (2)
AreaForestAcres
Mosquito Lake - Seven LakesBridger-Teton National Forest51,950
West Slope WindsBridger-Teton National Forest143,252
References (17)
  1. Cronquist, A., A. H. Holmgren, N. H. Holmgren, J. L. Reveal, and P. K. Holmgren. 1994. Intermountain flora: Vascular plants of the Intermountain West, U.S.A., Volume 5. The New York Botanical Garden, Bronx, NY.
  2. Douglas, George. Botanist, British Columbia Conservation Data Centre. Personal communication.
  3. Edward J. Fletcher Strategic Sourcing, Inc.
  4. Flora of North America Editorial Committee (FNA). 2006a. Flora of North America north of Mexico. Vol. 19. Magnoliophyta: Asteridae, part 6: Asteraceae, part 1. Oxford University Press, New York. xxiv + 579 pp.
  5. Gleason, H.A., and A. Cronquist. 1963. Manual of vascular plants of northeastern United States and adjacent Canada. D. Van Nostrand Company, New York, NY. 810 pp.
  6. Great Plains Flora Association. 1986. Flora of the Great Plains. University of Kansas Press, Lawrence. 1392 pp.
  7. Hulten, E. 1968. Flora of Alaska and neighboring territories. Stanford Univ. Press, Palo Alto, CA. 1008 pp.
  8. 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.
  9. Kartesz, J.T. 1999. A synonymized checklist and atlas with biological attributes for the vascular flora of the United States, Canada, and Greenland. First edition. In: Kartesz, J.T., and C.A. Meacham. Synthesis of the North American Flora, Version 1.0. North Carolina Botanical Garden, Chapel Hill, N.C.
  10. Kearney, T.H., R.H. Peebles, and collaborators. 1951. Arizona flora. 2nd edition with Supplement (1960) by J.T. Howell, E. McClintock, and collaborators. Univ. California Press, Berkeley. 1085 pp.
  11. Klein, Robyn. Instructor, Sweetgrass School of Herbalism. Personal communication.
  12. McGuffin, Michael. Personal communication. American Herbal Products Association, Silver Spring MD
  13. Swink, F., and G. Wilhelm. 1994. Plants of the Chicago Region. Morton Arboretum. Lisle, Illinois.
  14. U.S. Department of Agriculture, Natural Resources Conservation Service. 1999. November 3-last update. The PLANTS database. Online. Available: http://plants.usda.gov/plants. Accessed 2000-Jan.
  15. Weber, W.A., and R.C. Wittmann. 1996a. Colorado flora: Eastern slope. Revised edition. Univ. Press of Colorado, Niwot, Colorado. 524 pp.
  16. Weber, W.A., and R.C. Wittmann. 1996b. Colorado flora: Western slope. Univ. Press of Colorado, Niwot, Colorado. 496 pp.
  17. Welsh, S.L., N.D. Atwood, S. Goodrich, and L.C. Higgins (eds.) 1993. A Utah flora. 2nd edition. Brigham Young Univ., Provo, Utah. 986 pp.