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Background<br />

Table 73<br />

D. Testing <strong>of</strong> Parasitoids<br />

I.W. VARTY<br />

D. Testing <strong>of</strong> parasitoids 267<br />

The two strategies for biological control <strong>of</strong> the spruce budwonn, CJwristoneura fwniferatUl<br />

(Clem.), by parasitoids are the introduction <strong>of</strong> exotic species and the manipulation <strong>of</strong><br />

native ones. Most entomologists agree that the best prospects for introduction are those<br />

species that parasitize Choristoneura spp. (or near relatives) in spruce (Picea spp.) and fir<br />

(Abies spp.) forests in similar climatic zones abroad. The problem is to be ready for<br />

opportunities in those few years when pest outbreaks overseas permit sizeable collections<br />

<strong>of</strong> candidate parasitoids. The manipulation <strong>of</strong> native parasitoids <strong>of</strong>fers two other avenues<br />

for action: inundative release <strong>of</strong> laboratory-reared stock, and management <strong>of</strong> forest<br />

habitats to favour the dynamics <strong>of</strong> parasitoid response to available hosts.<br />

Efforts to establish exotic parasitoids in spruce budworm populations <strong>of</strong> eastern<br />

<strong>Canada</strong> have not succeeded. In 1944-53, large numbers <strong>of</strong> four species (two tachinids,<br />

one sarcophagid, and one ichneumonoid) from unidentified western spruce budworms<br />

(British Columbia) were released at various sites from Manitoba to Newfoundland. In<br />

1948-56, 12 ichneumonoid species from European hosts, especially Choristoneura<br />

murinana (Hb.) (France, Germany, Czechoslovakia), were released in small numbers<br />

in northwestern Ontario and Quebec. No evidence <strong>of</strong> the establishment <strong>of</strong> any introduced<br />

species has been produced (McGugan & CoppeI1962), and there were no explanations<br />

<strong>of</strong> the causes <strong>of</strong> failure. Interest in further introductions was inhibited by these failures<br />

and by lack <strong>of</strong> sources <strong>of</strong> parasitoids abroad. However, during the 1960s unsuccessful<br />

efforts were made to obtain three ichneumonoids specific to C. murinana (Miller &<br />

Angus 1971).<br />

Interest was renewed when an outbreak <strong>of</strong> Choristoneura diversana (Hb.) on Japanese<br />

(todo) fir (Abies firma Sieb & Zucc.) in Hokkaido, Japan, occurred in the late 1960s.<br />

Collaboration among four institutes (Hokkaido Forest Experimental Station, Maritimes<br />

Forest Research Centre, Commonwealth Institute <strong>of</strong> Biological Control, and the Agriculture<br />

<strong>Canada</strong> Research Station at Belleville, Ontario) resulted in the shipment <strong>of</strong><br />

parasitoids by air from Japan to New Brunswick in 1970-75 (Tables 73 and 74). Further,<br />

a small collection <strong>of</strong> parasitoids from C. murinana in Czechoslovakia was shipped to New<br />

Brunswick in 1972. These introductions are detailed below.<br />

In the early 1970s, the theory that spruce budworm epidemics may start in isolated<br />

local epicentres led to interest in methods <strong>of</strong> quelling incipient outbreaks over small<br />

areas. At the Laurentian Forest Research Centre this interest developed into a research<br />

study <strong>of</strong> the native egg parasitoid, Trichogramma minutum Ril., as a candidate for<br />

inundative release, now briefly reported. As pressure to find a biological alternative to<br />

Open releases and recoveries <strong>of</strong> parasitoids against Choristoneura fumiferana (Clem.)<br />

Year <strong>of</strong><br />

Species and province Year Origin Number recovery<br />

Agria housei Shewell 1971 Ontario (laboratory 2800 1971<br />

New Brunswick culture) (14 adults)<br />

Nil in 1972-73<br />

Lissonota sp. 1973 Japan 59 Nil in 1974<br />

New Brunswick

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