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pdf, 57.71Mb - Entomological Society of Canada

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Pest Status<br />

Background<br />

Chapter 27<br />

Acroptilon repens (L.) DC., Russian<br />

Knapweed (Compositae)<br />

A.K. WATSON and P. HARRIS<br />

Acrop,ilon repens (L.) DC. (Centaurea repens L.) is native to Mongolia. Western<br />

Turkestan, Iran, Turkish Armenia and Asia Minor (Moore & Frankton 1974). and was<br />

first introduced into <strong>Canada</strong> about 1900 as a contaminant <strong>of</strong> Turkestan alfalfa seed (Groh<br />

1940). Russian knapweed is now widespread in the southern parts <strong>of</strong> the four western<br />

provinces and is also found in southern Ontario. although most infestations are relatively<br />

small (50% <strong>of</strong> infestations in Saskatchewan are less than one acre in size) (Watson 1980).<br />

This noxious weed has a well developed, extensive root system which is the major<br />

means <strong>of</strong> reproduction and spread (Frazier 1944). It forms dense infestations in cultivated<br />

fields, in grain and alfalfa fields. in pastures, along roadsides and irrigation ditches and in<br />

waste places. Russian knapweed is apparently indifferent to crop association and is able<br />

to survive in almost any crop in tillable soil (Rogers 1928). Infested fields commonly<br />

have knapweed densities <strong>of</strong> 100-300 shootslm 2 which suppress and essentially eliminate<br />

other plant growth (Selleck 1964). In addition to its intense competitive ability, Russian<br />

knapweed is poisonous to horses (Younget al. 1970). Actual crop losses and other losses<br />

due to Russian knapweed have not been determined nor estimated in <strong>Canada</strong>.<br />

Because <strong>of</strong> its serious threat to Canadian agriculture, Russian knapweed was designated<br />

as a "prohibited noxious weed" in the Federal Seeds Act (Agriculture <strong>Canada</strong><br />

1967). The benefit <strong>of</strong> this is debatable as it is difficult to collect viable seed in <strong>Canada</strong><br />

(Watson 1975) and germination rarely occurs in the field (Selleck 1964). Control <strong>of</strong> this<br />

persistent perennial weed is difficult as its extensive root system is not adversely<br />

affected by cultivation and the weed is relatively resistant to commonly used herbicides.<br />

Picloram (4-amino-3,5.6-trichloropicolinic acid) and glyphosate [N-(phosphonomethyl)<br />

glycine) are two <strong>of</strong> the more effective herbicides for Russian knapweed control (Alley &<br />

Humberg 1979). The biology <strong>of</strong> Russian knapweed has recently been reviewed (Watson<br />

1980).<br />

In North America, Russian knapweed is relatively free <strong>of</strong> specialized parasites and is not<br />

extensively attacked by polyphagous feeders, but in its native range, Russian knapweed<br />

is the host <strong>of</strong> a number <strong>of</strong> specialized organisms (Watson 1980). The potential biological<br />

control agents <strong>of</strong> Russian knapweed include seven organisms that attack the seed head:<br />

a seed gall mite (Aceria acropliloni V. Shev. & Kov.), three Diptera (Dasyneura sp.,<br />

Urophora maura (Frfld.), Urophora kasochstanica V. Richter) and three Coleoptera<br />

(Larinus bardus Gyll., Larinus jaceae Fabr., Rhynchaenus dislans Faust); a stem gall<br />

former (Aulacida acroptilonica Beliz); a leaf and stem rust (Puccinia acroptili Syd.); and<br />

a leaf and stem gall nematode (Paranguina picridis Kirj. & Ivan.) (Watson 1980).<br />

105

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