Boltonia decurrens

(Torr. & Gray) Wood

Decurrent False Aster

G2Imperiled (G2G3) Found in 1 roadless area NatureServe Explorer →
G2ImperiledGlobal Rank
HighThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.161342
Element CodePDAST1E040
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderAsterales
FamilyAsteraceae
GenusBoltonia
Other Common Names
claspingleaf doll's daisy (EN) Claspingleaf Doll's-daisy (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
Formerly classified as Boltonia asteroides var. decurrens or B. latisquama var. decurrens; now recognized as a distinct species (B. decurrens) by Flora of North America (2006) and Kartesz (1994), the U.S. Fish and Wildlife Service, and the Illinois and Missouri Heritage Programs.
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2015-08-04
Change Date2013-12-05
Edition Date2015-08-04
Edition AuthorsMarian Smith, Southern Illinois Univ., Edwardsville, Illinois, rev. Maybury/Schwegman (1996), rev. Treher (2013), rev. Treher (2015)
Threat ImpactHigh
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Number of Occurrences21 - 80
Rank Reasons
Historically known from almost contiguous populations along a 400 km stretch within the Illinois and Mississippi River floodplain, this species is reduced to about 40 populations of highly variable size. Habitat destruction and modification are believed to be the reasons for the decline. The species is dependent on periodic disturbance from major floods and seasonal fluctuations in water levels; however, the flood regime and seasonal water levels have been altered or stabilized by dams and levees and much former habitat has been modified into agricultural land. An increase in the amount of silt deposited on the floodplains (due to agricultural practices and extensive leveeing) has had a particularly detrimental effect. In spite of its rarity and geographic restriction, in good years large populations of this species may reach 10,000 individual plants. Also, a high level of genetic diversity is apparently present in the species as a whole. However, populations that are surviving on sites disturbed by human activities, rather than by flooding, are precarious - regular cultivation, intensive mowing, and heavy herbicide use could cause declines.
Range Extent Comments
Historical collection records reveal that Boltonia decurrens once occurred in almost contiguous populations along a 400 km stretch between LaSalle, Illinois and St. Louis, Missouri within the Illinois and Mississippi River floodplain. A disjunct population, reported in 1976, but not found since, is known from Cape Girardeau, MO, about 195 km down the Mississippi River from St. Louis (Schwegman and Nyboer, 1985). The species is currently limited to disjunct populations from Woodford County, Illinois to Madison County, Illinois. In some years, ephemeral populations occur in St. Charles County, Missouri, in the area of confluence of the Mississippi and Illinois Rivers.
Occurrences Comments
The number of distinct occurrences varies depending on the water fluctuations but currently 40-43 occurrences are extant. In 1989, following extensive searches by the Illinois and Missouri Departments of Conservation, a total of 18 populations were discovered in Illinois and 10 in Missouri (U.S. Fish and Wildlife Service, 1990). Following the flood of 1993, the number of populations declined to 10. By the end of the summer of 1994, population number had recovered again. In spite of record flooding on the Illinois River in the spring of 1995, the total number of populations of Boltonia decurrens increased to 34 in 1995. USFWS (2012), a high of 43 populations. Because of the vulnerability of this species to changes in flooding regime, population number is expected to continue to fluctuate in upcoming years.
Threat Impact Comments
Boltonia decurrens is threatened primarily by anthropogenic disturbance of natural habitat. Principal threats include flood-control measures; agricultural use of marginal river-bottom land; increased siltation of floodwater, which decreases light availability and prevents germination and seedling establishment; herbicide use for weed control; and marina construction. Because B. decurrens is a successional species that requires high light levels, it is also threatened by alterations in the flooding regime, which may result in succession of habitats to shade-producing species.
Ecology & Habitat

Diagnostic Characteristics

Daisy-like inflorescences composed of perfect yellow disk flowers and white to pale violet pistillate ray flowers; strongly decurrent leaves; lack of rhizomes. Boltonia asteroides var. recognita has decurrent leaves and lacks rhizomes, and also has a strong tendency to have larger flowers, more frequently with violet colored rays (Schwegman and Nyboer, 1985).

Habitat

Colonizes periodically disturbed riverine moist soil habitats (Smith et al. 2005). In general, sites where the species is successful in reproducing sexually and maintaining a self-sustaining population are characterized by moist, sandy soil and regular disturbance, preferably periodic flooding, which maintains open areas with high light levels. Analysis of 19th-century habitat data taken from herbarium sheets indicates that natural habitat was the shores of lakes and the banks of streams, including the Illinois River. In these habitats, regular flooding prevented succession, allowing sunlight to reach the seedlings. Boltonia decurrens is still found in these occasional natural habitats, but it is now primarily restricted to disturbed lowland areas, where it appears to be dependent on human activities (mowing, cultivation) for survival. Germination and seedling establishment do not occur where the soil surface is shaded, such as in places where natural succession has been uninterrupted for a period of 3-5 years. Seed germination is also inhibited by silt deposition.

Ecology

Boltonia decurrens blooms from August through October throughout its range (Schwegman and Nyboer, 1985). Little variance has been noted in time of anthesis for populations from different locations; however, there is a great deal of variance in the size of plants at anthesis. Plants which have overwintered (either seedlings or vegetatively-produced rosettes) are generally >1.5 m when flowering is initiated, as compared to seedlings which germinate in spring and flower in late summer of the same year (flowering individuals have been noted which were <0.5 m in height). Anthesis does not appear to be related to either photoperiod or temperature at the time of flowering but occurs in response to bolting, which in rosettes, at least, is dependent upon pre-treatment with low temperature. In any given cohort, some seedlings will bolt and flower without cold treatment and some do not flower until they have overwintered. The mechanism for these differing responses is unknown (Smith, 1991).

Both seedlings and vegetatively-produced rosettes can withstand prolonged periods of flooding (Stoecker, Smith and Melton, 1995), and have been observed to develop while completely submerged, to bolt above water level, flower and produce seeds (Smith, 1990). Seeds are conditionally dormant (Baskin and Baskin, 1988), with freshly-produced seeds germinating at warmer temperatures (30C) and those which have after-ripened germinating at a wider range of temperatures (10 - 30C). Peak germination appears to be in spring (Smith, 1991). Seeds stored in a refrigerator at 4C for 6 years are still viable (ca. 50% germination percentage), and a recent study indicates that in the field seeds remain viable in the soil for at least two years (Smith, 1994). In spite of its threatened status and restricted range, preliminary isozyme data developed by Thomas Ranker (University of Colorado, Boulder) from seeds collected from three populations in Illinois in 1994 indicate that there is a high level of genetic diversity (Smith, 1995). This rare species is much more variable, by all the measures examined, than most rare or geographically-restricted plant species, and is even slightly more variable than the average plant species regardless of rarity, distribution, or a variety of other life-history characteristics (Hamrick and Godt, 1990).

Reproduction

Achenes float and are often dispersed by flowing water (Baskin and Baskin 2002).

Vegetative reproduction occurs through shoots formed from a basal rosette (Smith and Keevin 1998).
The species is primarily outcrossing, but some selfing occurs (Smith, 1995). Pistillate ray flowers and perfect disk flowers produce morphologically distinct achenes in inflorescences of approximately 350 flowers in a 1:5 ray to disk ratio. Seed production is prolific with an average of ca. 50,000 seeds produced per plant (Smith & Keevin 1998; Smith, 1990). Germination is ca. 60% under laboratory conditions (Smith, 1990), but seedling survival in the field is <1%. However under optimal conditions, the average plant produces 40,000 seedlings but the rate of seedling survival is low (Smith & Keevin 1998). In late fall, as each flowering individual dies, leaving no persistent root stock, basal rosettes develop independent root systems. The rosettes overwinter, bolt the following spring and flower.
Palustrine Habitats
HERBACEOUS WETLANDFORESTED WETLANDRiparian
Other Nations (1)
United StatesN2
ProvinceRankNative
MissouriS1Yes
IllinoisS2Yes
Threat Assessments
ThreatScopeSeverityTiming
2 - Agriculture & aquaculturePervasive - largeSerious or 31-70% pop. declineHigh (continuing)
2.1 - Annual & perennial non-timber cropsPervasive - largeSerious or 31-70% pop. declineHigh (continuing)
7 - Natural system modificationsPervasive - largeSerious or 31-70% pop. declineHigh (continuing)
7.2 - Dams & water management/usePervasive - largeSerious or 31-70% pop. declineHigh (continuing)
7.3 - Other ecosystem modificationsPervasive - largeSerious or 31-70% pop. declineHigh (continuing)
9 - PollutionPervasive - largeSerious or 31-70% pop. declineHigh (continuing)
9.3 - Agricultural & forestry effluentsPervasive - largeSerious or 31-70% pop. declineHigh (continuing)

Plant Characteristics
DurationANNUAL, BIENNIAL, Short-lived
Economic Value (Genus)No
Roadless Areas (1)
Idaho (1)
AreaForestAcres
Bear CreekCaribou-Targhee National Forest118,582
References (20)
  1. Baskin, C.C., and J.M. Baskin. 1988. Germination ecophysiology of herbaceous plant species in a temperate region. American J. Botany 75: 286-305.
  2. Bellrose, F.D., F.L. Paveglio, and D.W. Steffeck. 1979. Waterfowl populations and the changing environment of the Illinois River Valley. Illinois Natural History Survey Bull. 32: 1-51.
  3. Hamrick, J.L., and M.J.W. Godt. 1990. Allozyme diversity in plant species. In A.H.D. Brown, M.T. Clegg, A.L. Kahler, and B.S. Weir (eds.). Plant population genetics, breeding, and genetic resources, Sinauer Associates, Incorporated, Sunderland.
  4. Herkert, J., ed. 1991c. Endangered and threatened species of Illinois: Status and distribution. Volume 1 - Plants. Illinois Endangered Species Protection Board, Springfield. 158 pp.
  5. Illinois Endangered Species Protection Board. 1989. Checklist of endangered and threatened animals and plants of Illinois. 24 pp.
  6. 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.
  7. Schwegman, J.E., and R.W. Nyboer. 1985. The taxonomic and population status of Boltonia decurrens (Torrey and Gray) Wood. Castanea 50(2): 112-115.
  8. Smith, M. 1990. Basic life history characteristics of Boltonia decurrens (decurrent false aster.) Unpublished report to the U. S. Army Corps of Engineers. St. Louis, MO. 12 pp.
  9. Smith, M. 1991. Life history of the decurrent false aster. Unpublished report to the Illinois Dept. Conservation. Springfield. 12 pp.
  10. Smith, M. 1993. Regeneration and maintenance of decurrent false aster populations. Unpublished report to the Illinois Dept. Conservation. Springfield. 23 pp.
  11. Smith, M. 1994. Effects of the flood of 1993 on the decurrent false aster (Boltonia decurrens). Unpublished report to the U. S. Army Corps of Engineers. St. Louis, MO. 10 pp.
  12. Smith, M. 1995. Effects of the flood of 1993 on population status of the decurrent false aster. Preliminary report to the National Science Foundation and the U. S. Fish and Wildlife Service. 9 pp.
  13. Smith, M., H. Caswell, and P. Mettler-Cherry 2005. Stochastic flood and precipitation regimes and the population dynamics of a threatened floodplain plant. Ecological Applications 15:1036-1052.
  14. Smith, M., Y. Wu, and O. Green. 1993. Effect of light and water stress on photosynthesis and biomass production in Boltonia decurrens (Asteraceae), a threatened species. American J. Botany 80(8): 859-864.
  15. Stoecker, M.A., M. Smith and E.D. Melton. 1995. Survival and aerenchyma development under flooded conditions of <i>Boltonia decurrens</i>, a threatened floodplain species, and <i>Conyza canadensis</i>, a widely distributed competitor. American Midland Naturalist 134: 117-126.
  16. U.S. Fish and Wildlife Service (USFWS). 1976. Endangered Species Technical Bull. July 1976.
  17. U.S. Fish and Wildlife Service (USFWS). 1988. Proposal to determine <i>Boltonia decurrens</i> (decurrent false aster) to be a threatened species. Federal Register 53(37): 5598-5602.
  18. U.S. Fish and Wildlife Service (USFWS). 1990. Decurrent False Aster Recovery Plan. U.S. Fish and Wildlife Service, Twin Cities, MN. 26 pp.
  19. U.S. Fish and Wildlife Service (USFWS). 2012. Decurrent False Aster (<i>Boltonia decurrens</i>) 5-Year Review: Summary and Evaluation. U.S. Fish and Wildlife Service, Midwest Region, Rock Island Ecological Services Field Office, Moline, Illinois.
  20. Wilson, J.H., ed. 1984. Rare and endangered species of Missouri. Missouri Dept. Conservation. 171 pp.