Dwarf woolly-heads, specific populations, COSEWIC assessment status report: chapter 5

Habitat

Habitat requirements

Southern Mountain Population

The Princeton unit occurs in a rainshadow cast by the Coast-Cascade Mountains. The resulting continental climate has cool winters with low to moderate snowfall. The growing season is relatively long (about 95 frost-free days), warm (about 1,028-1,266 growing degree days > 5°C) and dry (185-313 mm growing season precipitation). There are substantial growing season moisture deficits (Lloyd et al. 1990).

The species occurs on calcareous clay soils along pond margins and in shallow depressions which are dominated by annual plants which can take advantage of the brief period of favourable growing conditions. The leading species include Plagiobothrys scouleri (Scouler’s popcornflower) and Polygonum polygaloides ssp. confertiflorum (Close-flowered knotweed). Common associates include Myosurus minimus (tiny mousetail), Alopecurus carolinianus (Carolina meadow-foxtail), Gnaphalium palustre (lowland cudweed), and Deschampsia danthonioides (annual hairgrass). The most commonly associated perennial plant is Danthonia unispicata (One-spike oatgrass) (Douglas et al. 2003). The surrounding area is composed of shrub/grassland dominated by Artemisia tridentata, Pseudoroegneria spicata and Hesperostipa comata as well as open to closed woodlands dominated by Pinus ponderosa (Ponderosa pine) and Pseudotsuga menziesii (Douglas-fir).

Prairie Population

The prairie population occurs in a semi-arid region with very cold winters and short, warm summers. Most of the precipitation falls in summer, with 75-130 mm in June but an average of less than 50 mm per month in July and August (Hare and Thomas 1979).

In the Prairie Population, sites tend to occur on shallowly depressional, seasonally flooded sites such as Solonetzic pans, slough margins and ephemeral wetlands with sandy bottoms (Hudson pers. comm. 2005; Porter 2005 pers. comm., Romuld pers. comm. 2005; Wallis pers. comm. 2005; Bush pers. comm. 2005). There does not appear to be any consistent suite of associated species but vegetation data is lacking for most sites (Douglas et al.2000). The surrounding uplands tend to support grassland vegetation dominated by Hesperostipa comata, H. curtiseta, Pascopyrum smithii, Elymus lanceolatus, Koeleria macrantha and Bouteloua gracilis.

Trends

There is no reliable information regarding the rates of change in extent of occurrence, area of occupancy or habitat suitability in either unit.

Habitat protection/ownership

The three localities of the Southern Mountain Population occur on a private ranch within the Agricultural Land Reserve (Table 1). Two of the Prairie Population localities occur in protected areas. Most of the other localities occur on provincial crown land or land ownership is unknown.

Table 1. Psilocarphus brevissimus population data.
Population localities Last Observation Presumed Status Land Status Extent Number IndividualsFootnote1
Prairie 1 C. Wallis 1989 extant protected < 1 acre ? - several hundred
Prairie 2 M. Romuld 1990 extant protected < 1 acre ? - >50
Prairie 3 K. Tannas 1989 extant unknown < 2 ha ? – (50-100)
Prairie 4 C. Wallis 1985 extant crown < 1 acre ? – (100-1000)
Prairie 5 D. Bush 1997 extant unknown < 2 ha ? - >2,700
Prairie 6 D. Bush 1996 extant unknown < 1 ha 0 – (100-1000)
Prairie 7 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 8 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 9 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 10 D. Bush 1996 extant private < 1 ha 0 – (100-1000)
Prairie 11 D. Bush 1996 extant unknown < 1 ha 0 – (100-1000)
Prairie 12 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 13 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 14 E. Moss 1927 historic unknown unknown unknown
Prairie 15 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 16 C. Wallis 1979 extant crown < 1 acre 0 – (100-1000)
Prairie 17 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 18 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 19 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 20 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 21 D. Bush 1996 extant unknown < 1 ha 0 – (100-1000)
Prairie 22 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 23 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 24 D. Bush 1996 extant crown < 1 ha 0 – (100-1000)
Prairie 25 D. Bush 1996 extant private < 1 ha 0 – (100-1000)
Prairie 26 E. Moss 1953 historic unknown unknown unknown
Prairie 27 C. Wallis 2003 extant private < 1 acre ~1,000
Prairie 28 J. Hudson 1979 extant leased crown? ~ 1 acre locally abundant
Prairie 29 J. Hudson 1979 extant leased crown? ~ 1 acre scarce
Prairie 30 J. Hudson 1980 extant leased crown? ~ 1 acre small amount
Prairie 31 Harris and Harris 1999 extant unknown unknown ? - ~ 200
Prairie 32 Harris and Harris 1999 extant unknown unknown ? - 1,000
Prairie 33 Harris and Harris 1999 extant unknown unknown ? - 50
Prairie 34 Harris and Lamont 1999 extant unknown unknown ? - 1,000
Prairie 35 Harris and Lamont 1999 extant unknown unknown ? - 200
Prairie 36 Harris and Lamont 1999 extant unknown unknown ? - 200
Prairie 37 Harris and Harris 1999 extant unknown unknown ? - 500
Prairie 38 Harris and Harris 1999 extant unknown unknown ? - 10
Prairie 39 Harris and Harris 1999 extant unknown unknown ? - 50
Prairie 40 Harris and Harris 1999 extant unknown unknown ? - 75
Prairie 41 Harris and Harris 1999 extant unknown unknown ? - 10
S. Mtn. 1 Lomer 1996 extant private <0.1 ha 30-300
S. Mtn. 2 Douglas 2002 extant private 0.1 ha 225 – (1-2 million)
S. Mtn. 3 Lomer 2002 extant private <0.1 ha 450 – 7,700

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