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Introductory

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
ABBREVIATION : CARDRA SYNONYMS : Lepidium draba L. [25,31] SCS PLANT CODE : CADR COMMON NAMES : heart-podded hoary cress hoary cress whitetop pepperweed TAXONOMY : The currently accepted scientific name of heart-podded hoary cress is Cardaria draba (L.) Desv. [8,12,17,23]. It is a member of the Cruciferae family. Heart-podded hoary cress was originally placed in the genus Lepidium [34]. There are two recognized varieties of heart-podded hoary cress [9,23,31]: C. d. var. draba C. d. var. repens (Schrenk) O. E. Schulz According to Hickman [12], C. d. var. repens is a hybrid of C. draba and C. chalepensis (lens-podded hoary cress) (L.) Hand. It was originally thought that there was only one species of Cardaria in North America. In 1933, Bellue reported three distinct species. Some taxonomists still do not distinguish between the three hoary cresses [22]. LIFE FORM : Forb FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Lora L. Esser, August 1994 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Esser, Lora L. 1994. Cardaria draba. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
GENERAL DISTRIBUTION : Heart-podded hoary cress is a weed of Eurasian origin that is invading rangelands throughout North America [8,18,35]. It is widespread in the United States except along the southern boundary of the western and south-central states [30]. It has been collected in every province of Canada except Prince Edward Island, New Brunswick, and Newfoundland [22]. ECOSYSTEMS : Heart-podded hoary cress is found in nearly all FRES ecosytems. STATES : AL AK AZ AR CA CO CT DE FL GA ID IL IN IA KS KY LA ME MD MA MI MN MS MO MT NE NV NH NJ NM NY NC ND OH OK OR PA RI SC SD TN TX UT VT VA WA WV WI WY AB BC MB NT NS ON PQ SK YT ADMINISTRATIVE UNITS : CARE COLM DEWA JODA MEVE NOCA OLYM SAMO TICA YELL BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 3 Southern Pacific Border 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : NO-ENTRY SAF COVER TYPES : Heart-podded hoary cress is found in nearly all SAF cover types. SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Heart-podded hoary cress is found in saltcedar (Tamarix ramosissima) communities in Utah; in a study relating plant cover to saltcedar age, heart-podded hoary cress occurred only in stands 6.0 to 9.6 years old, with average cover of 25 percent [4]. It occurs in antelope bitterbrush/rough fescue (Purshia tridentata/Festuca scabrella) and antelope bitterbrush/bluebunch wheatgrass (Pseudoroegneria spicata) habitat types in southwestern Montana [10]. In Oregon, heart-podded hoary cress occurs in basin big sagebrush (Artemesia tridentata ssp. tridentata) and Wyoming big sagebrush (A. tridentata ssp. wyomingensis) communities [18,27].

VALUE AND USE

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Heart-podded hoary cress is generally considered unpalatable to livestock. However, sheep eat plants in early growth stages, and cattle ingest seedheads [18,25]. PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : Although heart-podded hoary cress contains glucosinolates and is potentially mildly toxic [18], nutritional levels are adequate to meet the requirements of most classes of livestock, especially in the early growth stages. Foliage becomes coarse and bitter as it matures [18,25]. Mean nutrient composition of whole heart-podded hoary cress plants collected at five dates from eight sites in eastern Oregon, 1988 is as follows [18]: Phenology rosette bolting early bloom full bloom full seed % dry weight (4-12) (4-24) (5-12) (6-10) (7-7) dry matter 22.6 22.6 27.6 33.4 95.9 crude protein 28.8 29.5 20.3 11.3 7.9 ndf * 13.1 16.0 23.9 34.9 52.8 adf ** 12.0 13.4 21.6 28.8 41.8 cellulose 9.9 11.2 17.0 22.0 32.1 lignin 1.9 2.3 4.4 5.9 9.4 ether extract 1.6 1.5 1.9 2.2 2.4 in-vitro *** 77.3 74.7 69.8 64.9 49.1 * neutral detergent fiber ** acid detergent fiber *** in-vitro organic matter digestibility COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : Heart-podded hoary cress seed may be used as a substitute for pepper [22]. MANAGEMENT CONSIDERATIONS : Heart-podded hoary cress is classified as a noxious weed in 24 states and 4 provinces [22,36]. Control is difficult because of the perennial root system, abundant seed production, and diverse habitat of the plant. In the absence of a competitor, a single plant spread over an area 12 feet (3.6 m) in diameter in 1 year [20]. Irrigation facilitates the spread and establishment of heart-podded hoary cress by transporting root material from neglected ditch banks [22]. Control Methods - Mechanical: Cultivation alone will control heart-podded hoary cress when tillage begins at flowerbud time and is repeated every 10 days throughout the growing season [19]. In Manitoba and Alberta, it takes 3 years of intensive tillage to kill the root system of heart-podded hoary cress [22]. Flooding can kill heart-podded hoary cress. Seeds buried in moist compacted manure for 1 month lose their viability [22]. Early spring plowing and planting to a cereal crop can control heart-podded hoary cress [25]. Biological: Dense stands of established perennial grasses provide some resistance to invasion and spread of heart-podded hoary cress if grazing is not excessive [19]. Chemical: Several herbicides can control heart-podded hoary cress. They are most effective if applied during the early bud stage or late fall rosette stage [16,19,32]. Spraying followed by spring mowing can control up to 90 percent of heart-podded hoary cress [25]. Dense stands of grass, mowed only when necessary and treated with a selective herbicide, are best for controlling heart-podded hoary cress. Refer to publication [32] for information on effective herbicides and application procedures. Heart-podded hoary cress has some forage value, but until research better evaluates its toxicity, McInnis [18] recommends the following cautionary measures when allowing livestock to graze infested rangelands: provide supplemental iodine, graze mature and nonlactating animals, and provide alternate grazing areas.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
GENERAL BOTANICAL CHARACTERISTICS : Heart-podded hoary cress is a rhizomatous perennial herb with numerous, erect or ascending stems. It grows from 8 to 20 inches (20-50 cm) tall [16,17]. Leaves are elliptic to oblong, and 1.6 to 4 inches (4-10 cm) long [17,30]. The fruit is an indehiscent, glabrous, heart-shaped to oval silicle. It is 0.14 to 0.18 inch (3.5-4.5 mm) long and wide, with two seeds [19,22,30]. Roots usually occur at depths of 29-32 inches (74-81 cm) [22], but have penetrated to a depth of 30 feet (9 m) in the Pacific Northwest [25]. RAUNKIAER LIFE FORM : Hemicryptophyte Geophyte REGENERATION PROCESSES : Sexual: Heart-podded hoary cress reproduces by seed. It is self-incompatible and is pollinated by insects [16,22]. One plant can produce from 1,200 to 4,800 seeds. There is no mechanism for seed dispersal. Seed viability the first season may be as high as 84 percent, but can drop to 31 percent by the second year and 0 percent by the third year [18,20]. Cotyledons appear aboveground 5 to 6 weeks after planting and grow to maximum size in about 3 weeks. During this period, the first leaves emerge and form a loose rosette. Stems arise from the center of each rosette in late April [19,22]. Vegetative: Heart-podded hoary chess spreads vigorously by creeping roots. Lateral perennial roots spread and produce new rosettes and flowering shoots. One plant can eventually result in a large colony [2,20]. Within 3 weeks of germination, a seedling root can begin producing buds; if these are at or near the soil surface they may produce new rosettes [18,22]. Buds borne at deeper levels may develop as rhizomes. In the absence of competition, one plant can produce 455 shoots the first year [18]. SITE CHARACTERISTICS : Heart-podded hoary cress is widespread in fields, waste places, meadows, pastures, and along roadsides [14,16,22,30]. It also invades cropland [9]. It is most often found in open, unshaded areas on disturbed, generally saline soils [12,17,22], but can grow on almost any soil [25]. In Canada, heart-podded hoary cress, like other Cardaria species, may grow better in moist than dry conditions [22]. Elevation: Heart-podded hoary cress is found from 4,224 to 8,857 feet (1,280-2,684 m) in Utah, 5,214 to 6,402 feet (1,580-1,940 m) in Montana, 2,310 to 3,960 feet (700-1,200 m) in Oregon, 3,500 to 8,500 feet (1,050-2,550 m) in Colorado, and at less than 3,960 feet (1,200 m) in California [10,11,12,18,27,35]. SUCCESSIONAL STATUS : Facultative Seral Species Heart-podded hoary cress invades disturbed sites and may move into productive sites when growing conditions are ideal [12,17]. It does best in open, unshaded areas and can replace fields of alfalfa (Medicago sativa) if not controlled [22,25]. SEASONAL DEVELOPMENT : Heart-podded hoary cress flowering dates for several states are as follows: California Mar-June [23] Kansas May-June [2] Illinois Apr-June [21] Nebraska May-July [8] Great Plains Apr-Aug [9] In Oregon, heart-podded hoary cress seed matures in late July and early August [22].

FIRE ECOLOGY

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
FIRE ECOLOGY OR ADAPTATIONS : Heart-podded hoary cress probably survives fire due to the presence of perennating buds located on an extensive underground root system. Because of high germination in new seed, it may colonize from new soil-stored seed after fire. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Geophyte, growing points deep in soil

FIRE EFFECTS

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
IMMEDIATE FIRE EFFECT ON PLANT : Heart-podded hoary cress is probably top-killed by fire. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Heart-podded hoary cress probably sprouts from rhizomes and establishes from seed after fire. At the John Day Fossil Beds National Monument in Oregon, prescribed fires were conducted in the fall of 1987 and the spring of 1988 in basin big sagebrush-bluebunch wheatgrass communities. Heart-podded hoary cress was not present in the prefire communities, but appeared in trace amounts on the fall burn and at 2 percent in 1989 on spring burn [27]. Because of its rapid growth, heart-podded hoary cress may be favored by severe fires that temporarily reduce competition from native species. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : If soils are disturbed by severe fire or by fire suppression activities, heart-podded hoary cress may be favored.

REFERENCES

SPECIES: Cardaria draba | Heart-Podded Hoary Cress
REFERENCES : 1. Bare, Janet E. 1979. Wildflowers and weeds of Kansas. Lawrence, KS: The Regents Press of Kansas. 509 p. [3801] 2. Barkley, T. M. 1983. Field guide to the common weeds of Kansas. Lawrence, KS: University Press of Kansas. 164 p. [3802] 3. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434] 4. Brotherson, Jack D.; Carman, John G.; Szyska, Lee A. 1984. Stem-diameter age relationships of Tamarix ramosissima in central Utah. Journal of Range Management. 37(4): 362-364. [9921] 5. Dorn, Robert D. 1977. Flora of the Black Hills. [Place of publication unknown]: Robert D. Dorn and Jane L. Dorn. 377 p. [820] 6. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 7. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others]. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998] 8. Gleason, Henry A.; Cronquist, Arthur. 1991. Manual of vascular plants of northeastern United States and adjacent Canada. 2nd ed. New York: New York Botanical Garden. 910 p. [20329] 9. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 10. Guenther, Glen E.; Wambolt, Carl L.; Frisina, Michael R. 1993. Characteristics of bitterbrush habitats that influence canopy cover and mule deer browsing. Journal of Environmental Management. 36: 175-181. [22528] 11. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 12. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of California. Berkeley, CA: University of California Press. 1400 p. [21992] 13. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 14. Kearney, Thomas H.; Peebles, Robert H.; Howell, John Thomas; McClintock, Elizabeth. 1960. Arizona flora. 2d ed. Berkeley, CA: University of California Press. 1085 p. [6563] 15. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation of the conterminous United States. Special Publication No. 36. New York: American Geographical Society. 77 p. [1384] 16. Lacey, John R.; Lacey, Celestine A. 1985. Controlling pasture and range weeds in Montana. Bulletin 362. Bozeman, MT: Montana State University, Cooperative Extension Service. 33 p. [1397] 17. Lackschewitz, Klaus. 1991. Vascular plants of west-central Montana--identification guidebook. Gen. Tech. Rep. INT-227. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 648 p. [13798] 18. McInnis, Michael L.; Larson, Larry L.; Miller, Richard F. 1993. Nutrient composition of whitetop. Journal of Range Management. 46(3): 227-231. [23337] 19. Miller, Timothy W.; Callihan, Robert H. 1991. Hoary cress and related whitetops (Cardaria draba, C. pubescens and C. chalapensis). PNW 359. Corvallis, OR: Pacific Northwest Extension Service. 4 p. [23332] 20. Miller, Richard F. 1986. Whitetop what?. Grazier. Corvallis, OR: Oregon State University, Extension Service; 249: 3-4. [23412] 21. Mohlenbrock, Robert H. 1986. (Revised edition). Guide to the vascular flora of Illinois. Carbondale, IL: Southern Illinois University Press. 507 p. [17383] 22. Mulligan, Gerald A.; Findlay, Judy N. 1974. The biology of Canadian weeds. 3. Cardaria draba, C. chalepensis, and C. pubescens. Canadian Journal of Plant Science. 54(1): 149-160. [23339] 23. Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA: University of California Press. 1905 p. [6155] 24. Nickerson, Mona F.; Brink, Glen E.; Feddema, Charles, compilers. 1977. Principal range plants of the central and southern Rocky Mountains: names and symbols. Gen. Tech. Rep. RM-20. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 121 p. [1752] 25. Pacific Northwest Extension Service. 1974. Hoary cress. PNW 116. Corvallis, OR; Pullman, WA; Moscow, ID: Pacific Northwest Extension Service. 3 p. [6558] 26. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 27. Sapsis, David S. 1990. Ecological effects of spring and fall prescribed burning on basin big sagebrush/Idaho fescue--bluebunch wheatgrass communities. Corvallis, OR: Oregon State University. 105 p. Thesis. [16579] 28. Seymour, Frank Conkling. 1982. The flora of New England. 2d ed. Phytologia Memoirs 5. Plainfield, NJ: Harold N. Moldenke and Alma L. Moldenke. 611 p. [7604] 29. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090] 30. U.S. Department of Agriculture, Agricultural Research Service. 1971. Common weeds of the United States. New York: Dover Publications, Inc. 463 p. [2378] 31. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. [23104] 32. U.S. Department of Agriculture, U.S. Department of the Interior; Range Seeding Equipment Committee. 1959. Handbook: Chemical control of range weeds. Washington, DC: [Publisher unknown]. 93 p. [12129] 33. U.S. Department of the Interior, Bureau of Land Management, Oregon State Office. 1985. Final Northwest Area noxious weed control program environmental impact statement. Portland, OR. 295 p. [12796] 34. Voss, Edward G. 1985. Michigan flora. Part II. Dicots (Saururaceae--Cornaceae). Bull. 59. Bloomfield Hills, MI: Cranbrook Institute of Science; Ann Arbor, MI: University of Michigan Herbarium. 724 p. [11472] 35. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. [2944] 36. Mitich, Larry W.; Kyser, Guy B. 1992. Impact of exotic weeds in the United States. In: Lym, Rodney G., ed. Proceedings, Western Society of Weed Science; 1992 March 10-12; Salt Lake City, UT. [Place of publication unknown]. Western Society of Weed Science: 86-93. [20616]

Index

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