pdf, 57.71Mb - Entomological Society of Canada
pdf, 57.71Mb - Entomological Society of Canada
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Pest Status<br />
Chapter 31<br />
Centaurea diffusa Lam. and C. maculosa<br />
Lam. s. lat., Diffuse and Spotted<br />
Knapweed (Compositae)<br />
P. HARRIS and I.H. MYERS<br />
Diffuse and spotted knapweed are herbaceous plants introduced from Europe to the dry<br />
grasslands <strong>of</strong> western <strong>Canada</strong> and other parts <strong>of</strong> North America. The combination <strong>of</strong><br />
their allelopathic properties (Fletcher & Renney 1963), low forage value. and drought<br />
adaptation have allowed these two knapweeds to displace most other herbaceous plants<br />
over large areas.<br />
Diffuse knapwced is typically a biennial. The species was recorded in Washington State<br />
in 1907 (Howell 1959) and early Canadian herbarium specimens suggest a northward<br />
spread into British Columbia: Oyama 1936, Penticton 1939, Grandforks 1940 (Groh<br />
1943); however, it may also have been introduced directly into the province with Turkestan<br />
alfalfa from the Caspian Sea region. Renney (1959) suggested that the weed occurred at<br />
Pritchard and Lytton, British Columbia, prior to 1930 and certainly other weeds from<br />
southern USSR were recorded at Kamloops (near Pritchard) as early as 1920 (Groh<br />
1940). From these beginnings the weed spread by 1972 to infest 25 952 ha <strong>of</strong> dryland range<br />
and roadside in British Columbia as well as small areas in Alberta (Watson & Renney<br />
1974). Distribution <strong>of</strong> diffuse knapweed in 1977 is shown in Fig. 4. In 1981 about 25 ha <strong>of</strong><br />
diffuse knapweed, 8 heavily infested. were found on one farm near Morden, Manitoba<br />
(B. Todd, 1982, personal communication). Harris & Cranston (1979) predicted that the<br />
relatively high availability <strong>of</strong> summer moisture in Manitoba would put it beyond the range<br />
<strong>of</strong> the weed. It is now not clear whether the potential <strong>of</strong> the weed was seriously<br />
underestimated or the infestation merely represented a local site anomaly as it was on a<br />
light soil with a southern exposure and dry. In 1982 several kilometers <strong>of</strong>railway track<br />
were found to be infested at Walsh, Saskatchewan. This is only a slight extension <strong>of</strong> the<br />
range from the stand at Irvine, Alberta (Fig. 4); but a small stand was also found on the<br />
railway track at Colonsay, Saskatchewan, which is southeast <strong>of</strong> Saskatoon (S. McKell,<br />
personal communication). Distance spread <strong>of</strong>the weed across the prairies <strong>of</strong>ten seems to<br />
be associated with railway ties or treated bridge timbers from British Columbia.<br />
It appears that diffuse knapweed will continue to spread until it dominates the herbaceous<br />
community in open uncultivated sites in the brown chernozem and brunisol soils <strong>of</strong><br />
southern British Columbia and the brown soils <strong>of</strong> Alberta and Saskatchewan. This<br />
involves about 7.5 million ha (Harris & Cranston 1979).<br />
Spotted knapweed is a short lived perennial. The first Canadian specimen was collected<br />
by McCoun from Victoria, British Columbia, in 1893 (Groh 1943). By 1972, it was<br />
estimated to have infested 2410 ha in British Columbia as well as several small stands in<br />
Alberta (Watson & Renney 1974); but these amounts are small compared to the estimated<br />
800000 ha in Montana, United States (Maddox 1979). The western Canadian distribution<br />
<strong>of</strong> the weed in 1977 is shown in Fig. 5.<br />
It is predicted that spotted knapweed will spread to dominate the herbaceous community<br />
in open uncultivated or lightly forested sites at the dry end <strong>of</strong> the Douglas fir zone<br />
in British Columbia and in the dark brown soils <strong>of</strong> Alberta and Saskatchewan. About 3.2<br />
million ha are vulnerable to invasion (Harris & Cranston 1979).<br />
Assuming that the two knapweeds spread to their predicted limits <strong>of</strong> approximately 10<br />
million ha. the loss in terms <strong>of</strong> dry native pasture species would be 2.5 million tonnes/year<br />
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