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.
| Population localities | Last Observation | Presumed Status | Land Status | Extent | Number Individuals1 |
|---|---|---|---|---|---|
| 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 |