BIOLOGICAL
CONTROL AGAINST FRUIT FLIES IN
PACIFIC ISLAND COUNTRIES AND TERRITORIES
Despite large amounts of effort devoted to
the use of biological control agents (predators and parasitoids) to control
fruit flies, there have been relatively few instances that may be regarded as
sustainable successes.
Generally, predators have little effect on
fruit fly populations in an orchard or vegetable production situation. Invertebrate predators may include spiders, ants, carabid beetles, assassin
bugs, staphylinid beetles and probably others. In Crete, olive flies (B.
oleae) are reduced by birds that eat 81% of infested fruits. In consuming
the fruits, predators, unfortunately, also consume parasitoids so there is an
indirect adverse effect. In the endemic forest habitat, however, predation by
fruit-eating vertebrates, such as birds and primates, results in marked
reductions in fruit fly numbers.
The use of parasitoids to
control fruit flies biologically has always had wide appeal, but tropical
fruit flies have not, in general, proved to be good targets for biological
control. The most documented research on using parasitoids to reduce fruit fly
populations has been in Hawaii, where a large number of species have been
introduced and released to control oriental fruit
fly (Bactrocera dorsalis), Mediterranean fruit fly
(Ceratitis capitata), and melon
fly (Bactrocera cucurbitae). The parasitoids belong to the
families Braconidae (see picture below), Chalcididae and Eulophidae. Releases
of a range of parasitoids resulted in up to 95% reductions in populations of
Mediterranean and oriental fruit flies. Also, in normally heavily infested
commercial fruits, levels of damage caused by fruit flies were reduced to a
point where fruits were virtually free from infestation. These results were
due mainly to the establishment of the wasp Fopius arisanus and, to a
lesser extent, the establishment of Fopius vandenboschii and
Diachasmimorpha longicaudata. By 1968, it was claimed that oriental fruit
fly was no longer a major pest of many kinds of fruits, except guava. This
level of control, however, has not been sustained. Oriental fruit fly and
Mediterranean fruit fly are still very serious pests of a wide range of fruits
and vegetables. Inundative releases of laboratory-reared parasitoids may be an
appropriate option and is being researched in Hawaii.
|

|
|
Fruit fly parasitoid
wasp Diachasmimorpha kraussi (Photo: M.W.Johnson, University of
California) |
In Australia, there are several native
parasitoids of Queensland fruit fly (B. tryoni), but they exert very
little control on populations of fruit flies. CSIRO introduced several species
of parasitoids into Australia in the 1950s. F. arisanus apparently bred
in seven dacine and trypetine hosts, but by 1966, neither F. arisanus nor
D. longicaudata affected the incidence of Queensland fruit fly. Now,
only F. arisanus is established.
In PICTs, there are only a few native
parasitoids of fruit flies. For example, Diachasmimorpha hageni and Psyttalia
fijiensis were recorded in Fiji as early as 1916. Parasitism levels of
5-10% were recorded in 1935. These promising results, together with results
from Hawaii, saw a major effort to introduce parasitoids to Fiji and Cook
Islands between 1927 and 1935 and in the 1950s. Parasitoids such as F.
arisanus, D. longicaudata, Aceratoneuromyia indica, Tetrastichus
giffardianus and Psyttalia concolor were introduced into Fiji.
At least sixteen species of parasitoid wasps
have been introduced or naturally occur in Cook Islands, Fiji islands, Guam,
New Caledonia, Commonwealth of Northern Mariana Islands, Samoa, Papua New
Guinea, Solomon Islands, Tonga, Vanuatu, Federated States of Micronesia and
Palau. Two of the most common and widespread are Fopius arisanus and Diachasmimorpha
longicaudata. F. arisanus is native to Asia. The adult wasp inserts
its ovipositor into the fruit through the fruit fly’s egg-laying puncture
and lays a tiny egg inside the fruit fly’s egg. The parasitoid larva lives
inside the host (fruit fly larva) until the host has pupated in the ground.
At
that point, the parasitoid larva kills its host and completes its development,
feeding on the host flesh. Consequently, a parasitoid emerges from the pupa
instead of an adult fly. Female F. arisanus search for their hosts
mostly on fruits in trees, and rarely forage on the ground. Because it attacks
at the early stages of host maturity, this species generally outcompetes other
parasitoid species. D. longicaudata, is native to the Indo-Pacific
region, including Papua New Guinea, and is also present in Guam, Commonwealth
of the Northern Mariana Islands, Fiji Islands and New Caledonia. Parasitoids
infest third instar larvae of fruit flies, puncturing through the fruit’s
skin with its very long ovipositor. By preference, it attacks ripe and fallen
fruits and spends lots of time foraging on the ground.
Table: Fruit fly parasitoids recorded in
Pacific Island countries and territories. N = Native; I = introduced at an
unknown date; 1951 = introduced at a known date.
|
|
Cook Islands |
Fiji Islands |
Guam |
Micro-
nesia
(FSM) |
New Cale-
donia |
Northern Marianas |
Palau |
Papua New Guinea |
Samoa |
Solomon Islands |
Tonga |
Vanuatu |
|
Braconidae: Biosteres sp |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
N |
|
Braconidae: Diachasmimorpha hageni |
-
|
N |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
|
Braconidae: Diachasmimorpha kraussi |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
N |
-
|
N |
-
|
-
|
|
Braconidae: Diachasmimorpha
longicaudata |
-
|
1951 |
N |
1997 |
N |
N |
-
|
N |
-
|
-
|
-
|
-
|
|
Braconidae: Fopius arisanus |
I |
1951 |
-
|
1997 |
-
|
-
|
N |
-
|
I |
-
|
I |
-
|
|
Braconidae: Fopius deeralensis |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
N |
-
|
-
|
-
|
-
|
|
Braconidae: Opius froggatti |
-
|
-
|
-
|
-
|
N |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
|
Braconidae: Opius sp |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
N |
-
|
-
|
-
|
-
|
|
Braconidae: Psyttalia fijiensis |
-
|
N |
-
|
-
|
N |
-
|
-
|
N |
-
|
-
|
N ? |
-
|
|
Braconidae: Psyttalia fletcheri |
-
|
-
|
1950 |
-
|
-
|
-
|
-
|
-
|
-
|
1997 |
-
|
-
|
|
Eulophidae: Aceratoneuromyia indica |
-
|
1938 |
1952 |
-
|
-
|
-
|
-
|
-
|
1935 |
-
|
-
|
-
|
|
Eulophidae: Tetrastichus giffardianus |
- |
1935 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
Pteromalidae: Pachycrepoideus
vindemiae |
-
|
N |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
|
Pteromalidae: Spalangia cameroni |
-
|
1927 |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
|
Pteromalidae: Spalangia endius |
-
|
N |
-
|
-
|
N |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
|
Pteromalidae: Spalangia sp |
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
-
|
? |
-
|
Recent surveys in PICTs during the Regional
Fruit Fly Project, which began in 1991, show that parasitism levels are still
relatively low, generally at less than 10%. This level of parasitism is
consistent with parasitism levels throughout northern Australia and Southeast
Asia. There are occasions when levels of parasitism exceed 60%, but this is
usually towards the end of a major fruiting season, e.g. guava. From
these results, no special effort has been made in PICTs to encourage
augmentative releases of existing parasitoids. However, field control systems
based on protein bait sprays take cognizance of the need to conserve
parasitism levels that now occur naturally.
With respect to melon fly in Solomon
Islands, the parasitoid Psyttalia fletcheri was introduced from
Hawaii in 1997, with the aim of reducing its populations to a level that may
reduce the pressure on the efficacy of protein bait sprays. As the populations
of mango fly (B. frauenfeldi) are extremely high throughout the year on
Pohnpei and Kosrae Islands in the Federated
States of Micronesia, F. arisanus and D. longicaudata were
introduced in 1997 on Pohnpei and Kosrae Islands, respectively. F. arisanus has become quickly established on Pohnpei, but
it is too early to assess its long term impact on mango fly populations.
The
establishment of D. longicaudata on Kosrae is being been confirmed at
present.
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