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pdf, 57.71Mb - Entomological Society of Canada

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Releases and Recoveries<br />

HyJemya senecieJJa<br />

Meade (Diptera:<br />

Muscidae)<br />

Tyriajacobaeae (L.)<br />

(Lepidoptera:<br />

Arctiidae)<br />

(a) Ecology<br />

Senecio j(lcoh(l('(l L. . 197<br />

H. senecie/la larvae reduce seed production by feeding in ragwort flower heads. The<br />

biology was described by Miller (1970). and an unsuccessful attempt to establish it in<br />

British Columbia and Prince Edward Island in 1968 was reported by Harris el 01. (1971).<br />

The fly has been established in New Zealand where it infested up to 77% <strong>of</strong> the heads at<br />

peak flowering but the effect <strong>of</strong> the reduced seed production on ragwort density was not<br />

determined. The fly was established in California and probably in Oregon and<br />

Washington (Frick 19690) but the California site was subsequently destroyed (Julien<br />

1981).<br />

(b) Releases<br />

A summary <strong>of</strong> releases in the current review period is shown in Table 50; none <strong>of</strong> them<br />

became established. At least part <strong>of</strong> the problem was poor synchrony between emergence<br />

<strong>of</strong> the flies and ragwort flowering: in 1970 the H. seneciella were received in May<br />

and placed outside in a field cage in Prince Edward Island. The flies emerged between 8<br />

and 17 June but the host plant did not flower until August. In 1971 emergence was<br />

delayed until the second half <strong>of</strong> July but still did not result in establishment (L.<br />

Thompson. 1981. personal communication). The results from British Columbia were<br />

similar.<br />

Establishment in the United States was obtained with much larger releases <strong>of</strong> circa<br />

2000 flies. As egg viability was circa 25% (Frick 1969b) a larger release than that used in<br />

<strong>Canada</strong> is necessary. The problem with the synchronism <strong>of</strong> fly emergence can probably<br />

be overcome by releasing the mature larvae at the end <strong>of</strong> the summer; this could be done<br />

with the Oregon or Washington stock providing that it is free <strong>of</strong> parasites. The value <strong>of</strong><br />

establishing the fly is less clear since most ragwort reproduction in pastures is by vegetative<br />

propagation from existing plants. It is unlikely that the fly would survive in stands<br />

defoliated by cinnabar larvae which consume the flowers preferentially.<br />

Releases<br />

Field collected larvae from Nova Scotia were released at two sites in New Brunswick in<br />

1970 and at seven sites in Ontario in 1979 and 1981 (Table 50). These were the only<br />

releases since those reported by Harris el 01. (1971). Establishment occurred at both<br />

sites in New Brunswick resulting in widespread defoliation <strong>of</strong> tansy ragwort but on a<br />

long-term basis this is a less than desirable level <strong>of</strong> control. The insect did not become<br />

established in Ontario, possibly because <strong>of</strong> predation by ants (Alex, 1981, personal<br />

communication). About 20% <strong>of</strong> the Ontario shipment died in transit indicating that the<br />

popUlation was heavily stressed and probably diseased.

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