Smooth Goosefoot - Chenopodium subglabrum
Chenopodium leptophyllum var. subglabrum
State Rank Reason (see State Rank above)
Smooth goosefoot is known from just a few locations in Montana, one of which may be extirpated. It occupies an early-succession habitat that is vulnerable to loss of natural disturbance regimes such as fire and flooding. Invasion of exotic plants may also pose a threat. Population data and trend monitoring data are lacking though the populations likely flucuate widely from year to year.
- Details on Status Ranking and Review
Score2-3 - Very Small to Small: Population size is imprecisely known but is believed to be <10,000 individuals.
Score1 - Peripheral, Disjunct or Sporadic Distribution in MT: Widespread species that is peripheral, disjunct or sporadically distributed within MT such that it occurs in <5% of the state (<7,500 sq. miles or the combined area of Beaverhead and Ravalli Counties) or is restricted to 4-5 sub-basins.
Area of Occupancy
Score2 - Low: Generally occurring in 4-10 Subwatersheds (6th Code HUC’s).
Score2 - High: Species is restricted to a highly specialized and limited habitat and is typically dependent upon unaltered, high-quality habitat (C Values of 8-10).
CommentSpecies requires sandy sites, which are early successional or maintained by disturbance events.
ScoreNA - Rank factor not assessed.
ScoreNA - Rank factor not assessed.
CommentPotential threats are undocumented.
Score1 - Moderate Vulnerability: Specific biological attributes, unusual life history characteristics or limited reproductive potential makes the species susceptible to extirpation from stochastic events or other adverse impacts to its habitat and slow to recover.
Raw Conservation Status Score
8 to 9 total points scored out of a possible 13 (Rarity factors only).
Smooth Goosefoot is an annual with erect, simple, or highly stems 2-3 (8) dm high. The alternate leaves are linear with entire margins, single veined, glabrous, up to 3 cm long. The small, green flowers are grouped in remote clusters in simple or branched spikes. Each flower lacks petals but has 5 glabrous sepals and 5 stamens. The 1-seeded fruit is compressed hemispheric and is relatively large; 1-2 mm across, exposing a jet-black fruit at maturity that readily separates from the pericarp (fruit wall).
Fruiting occurs in late June-July.
Chenopodium fremontii also has narrow, entire-margined leaves, but they are larger and have three veins rather than just one. Chenopodium leptophyllum is similar but its leaves are grayish-mealy rather than nearly glabrous. Hitchcock et al. (1964, Vascular Plants of the Pacific Northwest Vol. 2) treats Chenopodium leptophyllum and C. subglabrum as conspecific.
In MT known from Cascade, Fergus, Garfield, Sheridan and Carter counties; elsewhere WA east to AB and MB, south to NV, CO, NE and IA (Lesica 2012. Manual of Montana Vascular Plants. BRIT Press. Fort Worth, TX).
Observations in Montana Natural Heritage Program Database
Number of Observations:
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Map Help and Descriptions
(Observations spanning multiple months or years are excluded from time charts)
Smooth goosefoot grows in extremely loose, sandy soils and tends to occupy early successional, sparsely vegetated habitats. The unconsolidated sandy substrate is nutrient poor and droughty. In Montana, it inhabits sand dunes and occasional river sandbars or sandy terraces. In Alberta, Saskatchewan and Manitoba, the species is generally found on south- or west-facing, actively eroding slopes at the edge of stabilizing sand, and sometimes in dune slacks (Smith and Bradley 1990). Associates at a site in Harding County, South Dakota include Sporobolus cryptandrus, Chenopodium ambrosioides, Ambrosia acanthicarpa, Oryzopsis hymenoides, and Rumex venosus. (Legumes were noted to be absent.)
Ecological Systems Associated with this Species
Smooth goosefoot is an annual that grows in habitats with loose sand deposited by wind or water. Populations are small, and are likely to migrate in position over time (Heidel 1990). The largest populations are in areas of finer and more compacted sand, and it rarely grows in highly unstable sand. It may occur in stabilized sand, however, populations in these habitats are always small. It cannot survive where succession leads to a continuous vegetation cover, and is vulnerable to competition from weedy exotics such as Melilotus officinalis and Euphorbia esula.
Like most members of the Goosefoot Family, this species is tolerant of both xeric and alkali-impregnated conditions (Smith and Bradley 1990). Like other species of the genus, it is wind-pollinated and is likely to have seeds that can survive one or more years until they germinate. It produces relatively few seeds per plant, so seedling establishment is presumed critical in its life history. Smooth goosefoot is an annual; populations develop from seed each year, and therefore population size is likely to fluctuate widely between years.
Populations of the species are dependent on areas of active, drifting sand, most of which are now under cultivation. Stabilization of the remaining sand dune habitat is also a problem. Wallis and Wershler have suggested lack of fire as a major factor in stabilization of southern Alberta sand dunes (Smith and Bradley 1990; see also Lesica and Cooper 1998). Grazing is also thought to be important in maintaining a portion of unstabilized sandy habitats within these areas. A combination of fire and grazing during appropriate seasons is most effective in keeping blowouts active (Smith and Bradley 1990). Several sites in Alberta are leased for grazing, and include the largest provincial populations of the species.
In Alberta, one of the principal threats to this species is the invasion of non-native plants - particularly crested wheatgrass and sweet clovers - along oil and gas access roads and well-sites (Smith and Bradley 1990). Noxious weeds like Euphorbia esula (leafy spurge) can take over this species' habitat and already pose a threat elsewhere in its range (Smith and Bradley 1990). Tamarix chinensis (tamarisk), which has major impacts on river sandbar habitats, is invading the Powder River basin, where smooth goosefoot was first collected in Montana, in 1973.
- Additional ReferencesLegend: View Online Publication
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- Heidel, B. 1990. Inventory of rare plant species in Theodore Roosevelt National Park, Billings and McKenzie counties, North Dakota. Report to the National Park Service. North Dakota Natural Heritage Inventory, Bismarck, North Dakota. 112 pp.
- Heidel, B.L. and K.H. Dueholm. 1995. Sensitive plant survey in the Sioux District, Custer National Forest, 1994, Carter County, Montana and Harding County, South Dakota. Unpublished report to the Custer National Forest. Montana Natural Heritage Program, Helena, Montana. 95 pp. plus appendices.
- Heidel, B.L., S.V. Cooper and C. Jean. 2000. Plant species of special concern and plant associations of Sheridan County, Montana. Report to U.S. Fish and Wildlife Service. Montana Natural Heritage Program, Helena, Montana. 96 p.
- Hitchcock, C. L., A. Cronquist, M. Ownbey, and J. W. Thompson. 1964. Vascular Plants of the Pacific Northwest. Part 2: Salicaceae to Saxifragaceae. University of Washington Press, Seattle. 597 pp.
- Lesica, P. & S. V. Cooper. 1998. Succession and disturbance in sandhills vegetation: constructing models for managing biological diversity. Conservation Biology 13:293-302.
- Lesica, P., M.T. Lavin, and P.F. Stickney. 2012. Manual of Montana Vascular Plants. Fort Worth, TX: BRIT Press. viii + 771 p.
- Seipel, T.F. 2006. Plant species diversity in the sagebrush steppe of Montana. M.Sc. Thesis. Bozeman, MT: Montana State University. 87 p.
- Smith, B. and C. Bradley. 1990. Status report on smooth goosefoot (Chenopodium subglabrum (S. Wats.) (A. Nels.) a threatened species in Canada. Unpublished report. Committee on the Status of Endangered Wildlife in Canada, Calgary, AB 52 pp.
- Vanderhorst, J.P., S.V. Cooper, and B.L. Heidel. 1998. Botanical and vegetation survey of Carter County, Montana. Unpublished report prepared for the Bureau of Land Management. Montana Natural Heritage Program, Helena. 116 pp. + app.