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SPECIES:  Grindelia squarrosa
Creative Commons photo, copyright 2015 Richard Spellenberg.

 


Introductory

SPECIES: Grindelia squarrosa
AUTHORSHIP AND CITATION : Walsh, Roberta A. 1993. Grindelia squarrosa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.usda.gov/database/feis/plants/forb/grisqu/all.html []. ABBREVIATION : GRISQU SYNONYMS : NO-ENTRY SCS PLANT CODE : GRSQ COMMON NAMES : curlycup gumweed tarweed resinweed curly-top gumweed sticky-heads gumweed TAXONOMY : The currently accepted scientific name of curlycup gumweed is Grindelia squarrosa (Pursh) Dunal [10,14]. It is in the sunflower family (Asteraceae). Recognized varieties are: Grindelia squarrosa var. squarrosa [1,10,12] Grindelia squarrosa var. nuda (Wood) Gray [1,10,14] Grindelia squarrosa var. quasiperennis Lunnell [10,14] Grindelia squarrosa var. serrulata (Rydb) Steyerm. [10,12] LIFE FORM : Forb FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY

DISTRIBUTION AND OCCURRENCE

SPECIES: Grindelia squarrosa
GENERAL DISTRIBUTION : Curlycup gumweed is native to much of the area from Manitoba south to Texas and east to Idaho and Arizona.  It is naturalized in eastern North America and the Pacific Coast states [16,17]. ECOSYSTEMS :    FRES15  Oak - hickory    FRES17  Elm - ash - cottonwood    FRES20  Douglas-fir    FRES21  Ponderosa pine    FRES26  Lodgepole pine    FRES29  Sagebrush    FRES30  Desert shrub    FRES31  Shinnery    FRES34  Chaparral - mountain shrub    FRES35  Pinyon - juniper    FRES36  Mountain grasslands    FRES38  Plains grasslands    FRES39  Prairie    FRES40  Desert grasslands STATES :      AZ  CA  CO  CT  ID  IL  IN  IA  KS  ME      MA  MI  MN  MO  MT  NE  NV  NH  NJ  NM      NY  ND  OH  OK  OR  PA  RI  SD  TX  UT      WA  WI  WY  AB  BC  MB  ON  PQ  SK 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     7  Lower 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 :    K011  Western ponderosa forest    K012  Douglas-fir forest    K016  Eastern ponderosa forest    K017  Black Hills pine forest    K018  Pine - Douglas-fir forest    K022  Great Basin pine forest    K023  Juniper - pinyon woodland    K037  Mountain-mahogany - oak scrub    K038  Great Basin sagebrush    K039  Blackbrush    K040  Saltbush - greasewood    K041  Creosotebush    K046  Desert: vegetation largely lacking    K047  Fescue - oatgrass    K050  Fescue - wheatgrass    K051  Wheatgrass - bluegrass    K055  Sagebrush steppe    K056  Wheatgrass - needlegrass shrubsteppe    K057  Galleta - three-awn shrubsteppe    K063  Foothills prairie    K064  Grama - needlegrass - wheatgrass    K065  Grama - buffalograss    K066  Wheatgrass - needlegrass    K067  Wheatgrass - bluestem - needlegrass    K068  Wheatgrass - grama - buffalograss    K069  Bluestem - grama prairie    K070  Sandsage - bluestem prairie    K071  Shinnery    K074  Bluestem prairie    K075  Nebraska Sandhills prairie    K081  Oak savanna    K082  Mosaic of K074 and K100    K098  Northern floodplain forest SAF COVER TYPES :     42  Bur oak     62  Silver maple - American elm     67  Shin (Mohrs) oak    210  Interior Douglas-fir    218  Lodgepole pine    220  Rocky Mountain juniper    229  Pacific Douglas-fir    230  Douglas-fir - western hemlock    237  Interior ponderosa pine    239  Pinyon - juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Associates of curlycup gumweed in sagebrush-grassland vegetation in southeastern Montana include big sagebrush (Artemisia tridentata), plains prickly pear (Opuntia polyacantha), western wheatgrass (Pascopyrum smithii), buffalo grass (Buchloe dactyloides), and blue grama (Bouteloua gracilis) [30]. Associates of curlycup gumweed on shortgrass rangeland in fair condition in eastern Colorado include blue grama, buffalo grass, rush skeletonplant (Lygodesmia juncea), wavyleaf thistle (Cirsium undulatum), pricklepoppy (Argemone intermedia), and crazyweeds (Oxytropis spp.) [20]. Associates of curlycup gumweed in tallgrass and mixed-grass prairie in southwestern Oklahoma include big bluestem (Andropogon gerardii var. gerardii), little bluestem (Schizachyrium scoparium), Indiangrass (Sorghastrum nutans), sideoats grama (Bouteloua curtipendula), and switchgrass (Panicum virgatum) [25]. Associates of curlycup gumweed on land adjacent to creek bottoms in central Montana include wheatgrasses (Agropyron and Pascopyrum spp.), foxtail barley (Critesion jubatum), brome (Bromus spp.), desert saltgrass (Distichlis stricta), big sagebrush, silver sagebrush (Artemisia cana), greasewood (Sarcobatus vermiculatus), and rubber rabbitbrush (Chrysothamnus nauseosus) [26].

MANAGEMENT CONSIDERATIONS

SPECIES: Grindelia squarrosa
IMPORTANCE TO LIVESTOCK AND WILDLIFE : Curlycup gumweed was eaten by sage grouse chicks aged 5 to 8 weeks in central Montana.  It was used by 28 percent of chicks and made up 3 percent by volume of crop contents.  At ages 9 to 12 weeks it was used by 39 percent of chicks and made up 4 percent of crop contents.  It was not used by chicks younger than 5 weeks old [26]. PALATABILITY : Curlycup gumweed is unpalatable to cattle, sheep, and horses [8,19], though sheep will occasionally crop flower heads in the absence of other forage [17].  Tannins, volatile oils, resins, bitter alkaloids, and glucosides give curlycup gumweed an unpleasant taste [1]. NUTRITIONAL VALUE : The energy value and protein value of curlycup gumweed for livestock is poor.  Its food value for several species of wildlife in some western states is [8]:                               MT       ND       UT      Elk                     ----     ----     poor      Mule deer               ----     ----     poor      Pronghorn               ----     ----     poor      Upland game birds       good     good     fair      Waterfowl               ----     ----     poor      Small nongame birds     fair     good     fair      Small mammals           ----     ----     fair COVER VALUE : The cover value of curlycup gumweed for several species of wildlife in some western states is [8]:                              MT       ND       UT      Elk                    ----     ----     poor      Mule deer              poor     fair     poor      White-tailed deer      ----     fair     ----      Pronghorn              good     fair     poor      Upland game birds      fair     fair     fair      Waterfowl              ----     fair     poor      Small nongame birds    fair     fair     fair      Small mammals          ----     poor     fair VALUE FOR REHABILITATION OF DISTURBED SITES : Curlycup gumweed occurred in only trace amounts on unreclaimed and reclaimed bentonite mine spoils in southeastern Montana.  It occurred in greater abundance on adjacent grasslands [30]. Curlycup gumweed was used in a roadside reseeding project in southern Wisconsin.  It showed a high ability to survive and grow under adverse conditions.  Seedlings transplanted easily to the field and grew rapidly.  Results for both direct seeding and seedling transplant were excellent [24]. OTHER USES AND VALUES : Native Americans used curlycup gumweed extracts to treat asthma, bronchitis, colic, and skin rash [17].  The Pawnees boiled the flower heads and leaves, and used the decoction for bathing saddle sores and other skin irritations [1].  Today, medicinal uses include treatment of bronchial spasm, whooping cough, asthma, and rashes caused by poison ivy (Toxicodendron radicans) [17].  Curlycup gumweed extract is valuable as a stimulant, sedative, astringent, purgative, emetic, diuretic, antiseptic, and disinfectant [1]. Curlycup gumweed is used as an ornamental.  It produces flowers over a long period, even when the soil is poor and dry [1]. OTHER MANAGEMENT CONSIDERATIONS : Curlycup gumweed increases with grazing [18] and has a negative economic impact on rangelands [8].  It forms dense, brushlike cover in rangelands where there is much broken sod [35].  In the Central Great Plains, it is not usually found on ranges of excellent or good condition, but is found on ranges in fair condition [20]. Curlycup gumweed stems, leaves, and flowers produce a sticky exudate. The coats of livestock can become gummed with it [2]. Curlycup gumweed is drought resistant due to deep roots and resinous secretions [1]. Curlycup gumweed is a facultative selenium absorber [1].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Grindelia squarrosa
GENERAL BOTANICAL CHARACTERISTICS : Curlycup gumweed is a warm-season [17] perennial or biennial native forb [8].  It grows 0.33 to 3.3 feet (0.1-1 m), with one to several branched stems [14,12].  Flower heads are several to numerous.  The floral disk is 0.6 to 2.75 inches (1.5-7 cm) wide.  The fruit is an achene [14]. Curlycup gumweed is taprooted, and develops a short, vertical rhizome. The root system extends 6.5 feet (2 m) into the soil [1], with extensive shallow root development [35].
Creative Commons photo, copyright 2010 Barry Breckling.
RAUNKIAER LIFE FORM : 
Geophyte

REGENERATION PROCESSES : 
Curlycup gumweed is a biennial or short-lived perennial which reproduces
by seed [12].  Seeds have a pappus [14], and are dispersed by wind.

Curlycup gumweed seeds were stratified for 10 weeks with a cold, damp
regime.  When planted, germination time was 3 days [24].

SITE CHARACTERISTICS : 
Curlycup gumweed favors dry areas, but grows on moist soils that lack
other vegetation [17].  It is most common in dry prairies, waste places,
roadsides, railroads, depleted rangelands, and abandoned croplands.  It
often forms almost pure stands [14,15,31].

Curlycup gumweed growth is poor to fair on gravel, clay, and dense clay,
and good in sandy loam, loam, and clayey loam.  It makes fair growth on
saline soils, good growth on gentle and moderate slopes, and fair growth
on steep slopes.  Optimum soil depth is 10 to 20 inches (25-50 cm) [8].

In eastern North Dakota, curlycup gumweed occurred on saltflats and in
wet lowlands where salinity ranged up to 1.3 percent [28].

Curlycup gumweed occurs at the following elevations [8,15,29]:

                   Elevation (feet)    Elevation (m)

          CO         3,500-8,500        1,067-2,590
          MT         3,200-6,700          975-2,042
          SD         3,600-5,000        1,097-1,524
          UT            5,000              1,524
          WY         3,600-8,600        1,097-2,621

SUCCESSIONAL STATUS : 
Curlycup gumweed is subdominant in climax prairie communities [6].  It
also occurs on disturbed sites [14].  It is highly drought resistant,
and may be abundant after dry periods [17].  However, by 1943 curlycup
gumweed in the mixed-grass prairie of Kansas showed only partial
recovery from the great drought of the 1930s [7].

In a black-tailed prairie dog town in a tallgrass prairie in
southwestern Oklahoma, prairie dogs of one colony progressively
retreated from the outside of the colony toward its center prior to
abandoning it.  Plant succession at this site was studied the summer
after the animals left.  Order of succession was apparent in concentric
rings of vegetation circumscribing a bare area at the center of the
colony.  Curlycup gumweed did not occur in the most recently abandoned
area, the colony center.  It did occur in longer-abandoned, surrounding
rings in association with annual threeawn (Aristida oligantha) and other
short grasses, forbs, and mid-sized grasses such as sideoats grama.  It
was not found in the undisturbed peripheral rings, which supported
climax tall grasses such as big bluestem [25].

SEASONAL DEVELOPMENT : 
Curlycup gumweed forms a rosette the first year.  The next summer, the
plant grows erect stems which branch considerably and produce many
flower heads [12,35].

Curlycup gumweed flowering times are [1,10,14,22,23,31]:

                    Begin         Peak           End
                  Flowering     Flowering     Flowering

     CA             July          ----        September
     CO             June         August       September
     IL             July          ----        September
     KS             July          ----        October
     MT             July         August       August
     ND             July         August       September
     WY             July         August       September
     Great Plains   July          ----          ----
     New England    July          ----        September

In North Dakota, curlycup gumweed began growth in May, and by the end of
May had attained 50 percent of its yearly growth [13].  Curlycup gumweed
attained maximum height in August.  The average length of flowering
period was 41 days; the median date when flowering was 95 percent
complete was September 4 [4].

FIRE ECOLOGY

SPECIES: Grindelia squarrosa
FIRE ECOLOGY OR ADAPTATIONS : Curlycup gumweed may sprout from its short, vertical rhizome after fire. However, no information was available concerning its sprouting performance. Curlycup gumweed seeds probably establishes on burned sites by wind-dispersed seed. FIRE REGIMES : Find fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes". POSTFIRE REGENERATION STRATEGY :    Rhizomatous herb, rhizome in soil    Initial-offsite colonizer (off-site, initial community)    Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Grindelia squarrosa
IMMEDIATE FIRE EFFECT ON PLANT : Curlycup gumweed is probably top-killed by fire. PLANT RESPONSE TO FIRE : Curlycup gumweed colonizes disturbed areas, and establishes or increases after fire. Curlycup gumweed was a trace species with 0.1 percent cover before a natural range fire occurred in a cheatgrass (Bromus tectorum)-sand dropseed (Sporobolus cryptandrus)-red threeawn (Aristida longiseta) community during the summer of 1956.  It was not present the first growing season following the fire, in 1957.  At the end of the next growing season, its cover was 1.2 percent.  During the next 2 years it was present only in trace amounts [5]. Curlycup gumweed populations increased following a 1983 or 1984 wildfire of unknown intensity and season in a 9,600 square foot (800 sq m) area in central Utah [21]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : The Research Project Summary Vegetation response to restoration treatments in ponderosa pine-Douglas-fir forests of western Montana provides information on prescribed fire and postfire response of plant community species including curlycup gumweed. FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Grindelia squarrosa
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Changes in composition of a Bromus        tectorum-Sporobolus cryptandrus-Aristida longiseta community following        fire. Utah Academy Proceedings. 41(I): 53-57.  [626]  6.  Clements, Frederic E. 1936. Nature and structure of the climax. Journal        of Ecology. 24: 252-284.  [11729]  7.  Coupland, Robert T. 1958. The effects of fluctuations in weather upon        the grasslands of the Great Plains. Botanical Review. 24(5): 273-317.        [12502]  8.  Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information        network (PIN) data base: Colorado, Montana, North Dakota, Utah, and        Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior,        Fish and Wildlife Service. 786 p.  [806]  9.  Eyre, F. H., ed. 1980. Forest cover types of the United States and        Canada. Washington, DC: Society of American Foresters. 148 p.  [905] 10.  Fernald, Merritt Lyndon. 1950. Gray's manual of botany. [Corrections        supplied by R. C. Rollins]. Portland, OR: Dioscorides Press. 1632 p.        (Dudley, Theodore R., gen. ed.; Biosystematics, Floristic & Phylogeny        Series; vol. 2).  [14935] 11.  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] 12.  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] 13.  Goetz, Harold. 1963. Growth and development of native range plants in        the mixed grass prairie of western North Dakota. Fargo, ND: North Dakota        State University. 141 p. Thesis.  [5661] 14.  Great Plains Flora Association. 1986. Flora of the Great Plains.        Lawrence, KS: University Press of Kansas. 1392 p.  [1603] 15.  Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed.        Chicago: The Swallow Press Inc. 666 p.  [6851] 16.  Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific        Northwest. Seattle, WA: University of Washington Press. 730 p.  [1168] 17.  Johnson, James R.; Nichols, James T. 1970. Plants of South Dakota        grasslands: A photographic study. Bull. 566. Brookings, SD: South Dakota        State University, Agricultural Experiment Station. 163 p.  [18500] 18.  Joyce, JoAnne; Morgan, John P. 1989. Manitoba's tall-grass prairie        conservation project. In: Bragg, Thomas B.; Stubbendieck, James, eds.        Prairie pioneers: ecology, history and culture: Proceedings, 11th North        American prairie conference; 1988 August 7-11; Lincoln, NE. Lincoln, NE:        University of Nebraska: 71-74.  [14021] 19.  Kaul, Robert P.; Keeler, Kathleen H. 1980. Effects of grazing and        juniper-canopy closure on the prairie flora in Nebraska high-plains        canyons. In: Kucera, Clair L., ed. Proceedings, 7th North American        prairie conference; 1980 August 4-6; Springfield, MO. Columbia, MO:        University of Missouri: 95-105.  [2923] 20.  Klipple, G. E.; Costello, David F. 1960. Vegetation and cattle responses        to different intensities of grazing on short-grass ranges on the Central        Great Plains. Technical Bulletin No. 1216. Washington, DC: U.S.        Department of Agriculture. 82 p.  [4284] 21.  McArthur, E. Durant; Blauer, A. Clyde; Stevens, Richard. 1990. Forage        kochia competition with cheatgrass in central Utah. In: McArthur, E.        Durant; Romney, Evan M.; Smith, Stanley D.; Tueller, Paul T., compilers.        Proceedings--symposium on cheatgrass invasion, shrub die-off, and other        aspects of shrub biology and management; 1989 April 5-7; Las Vegas, NV.        Gen. Tech. Rep. INT-276. Ogden, UT: U.S. Department of Agriculture,        Forest Service, Intermountain Research Station: 56-65.  [12736] 22.  Mohlenbrock, Robert H. 1986. (Revised edition). Guide to the vascular        flora of Illinois. Carbondale, IL: Southern Illinois University Press.        507 p.  [17383] 23.  Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA:        University of California Press. 1905 p.  [6155] 24.  Nuzzo, Victoria. 1978. Propagation and planting of prairie forbs and        grasses in southern Wisconsin. In: Glenn-Lewin, David C.; Landers, Roger        Q., Jr., eds. Proceedings, 5th Midwest prairie conference; 1976 August        22-24; Ames, IA. Ames, IA: Iowa State University: 182-189.  [3379] 25.  Osborn, Ben; Allan, Philip F. 1949. Vegetation of an abandoned        prairie-dog town in tall grass prairie. Ecology. 30: 322-332.  [3998] 26.  Peterson, J. G. 1970. The food habits and summer distribution of        juvenile sage grouse in central Montana. Journal of Wildlife Management.        34(1): 147-155.  [7527] 27.  Raunkiaer, C. 1934. The life forms of plants and statistical plant        geography. Oxford: Clarendon Press. 632 p.  [2843] 28.  Redmann, R. E. 1972. Plant communities and soils of an eastern North        Dakota prairie. Bulletin of the Torrey Botanical Club. 99(2): 65-76.        [3639] 29.  Schripsema, Janet R. 1978. Ecological changes on pine-grassland burned        in spring, late spring and winter. Rapid City, SD: South Dakota State        University. 99 p. Thesis.  [2092] 30.  Sieg, Carolyn Hull; Uresk, Daniel W.; Hansen, Richard M. 1983.        Plant-soil relationships on bentonite mine spoils and sagebrush-        grassland in the northern High Plains. Journal of Range Management.        36(3): 289-294.  [4642] 31.  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] 32.  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] 33.  U.S. Department of Agriculture, Agricultural Research Service. 1971.        Common weeds of the United States. New York: Dover Publications, Inc.        463 p.  [2378] 34.  U.S. Department of Agriculture, Soil Conservation Service. 1982.        National list of scientific plant names. Vol. 1. List of plant names.        SCS-TP-159. Washington, DC. 416 p.  [11573] 35.  Weaver, J. E. 1968. Prairie plants and their environment: A fifty-year        study in the Midwest. Lincoln, NE: University of Nebraska Press. 276 p.        [17548] 36.  Whitson, Tom D., ed. 1987. Weeds and poisonous plants of Wyoming and        Utah. Res. Rep. 116-USU. Laramie, WY: University of Wyoming, College of        Agriculture, Cooperative Extension Service. 281 p.  [2939] 37.  U.S. Department of Agriculture, Forest Service, Region 1. 1973. The use        of herbicides in vegetation management. Environmental Impact Statement:        Final. Missoula, MT. 87 p.  [7845] 38.  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]

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