Houseflies and other peridomestic
fly species can be
important vectors of diseases such as shigellosis, other diarrhoeal diseases,
and trachoma. Natural disasters can
exacerbate the unsanitary conditions that increase fly populations.
As far as possible, flies should be kept away from
young children and food by fly-proofing houses, particularly kitchens, and
covering stored food.
Before adopting a control strategy, a thorough understanding of the local fly
population’s breeding, feeding and resting habits, as well as susceptibility
to insecticides is necessary.
The breeding sites of houseflies and related species
are animal and human excreta and a wide variety of other organic matter,
particularly domestic garbage. Environmental
sanitation is the fundamental measure for fly control. Proper processing
and disposal of refuse, manure, compost and other organic waste is of prime
importance in the elimination of fly breeding sites. This approach is called Integrated vector management (IVM). More at: http://whqlibdoc.who.int/hq/2004/WHO_CDS_CPE_PVC_2004_10.pdf
Insecticides should be used only as a supplement to environmental management
control methods, not as a substitute. Given that insecticide resistance is
widespread, especially to organochlorines and
organophosphates, it is strongly recommended that insecticides be used
judiciously, and backed up by effective resistance management. The
insecticide label recommendations should hence be carefully followed.
Safety precautions
Insecticide application should be carried by
out exclusively by trained personnel to ensure sound management and effective
use, supported by monitoring and evaluation.
Always wear protective gear when handling
insecticides as they can be absorbed through the eyes, mouth, nose and
skin.
If skin contact occurs immediately wash the
exposed parts with plenty of soap and water. Always wash hands, face and exposed
skin after every application of insecticides.
Proper maintenance and operation of equipment,
is essential to the safety of operators and others in the environment.
Keep insecticide supplies in original
containers under lock and key, in dry, well ventilated, places,
where flooding is unlikely to occur.
Disposed off empty insecticide containers by
crushing and burying them in a safe place away from water sources and
inhabited areas to prevent reuse.
Space treatment is the most effective method of rapidly reducing fly density
inside or outside houses. However, there is no residual effect of the
insecticide and rapid repopulation of the treated area often occurs.
Portable cold or thermal fog generators are used for
indoor treatment. For outdoor treatment, vehicle-mounted foggers
are most appropriate. Portable equipment can be used in areas where vehicle
access is limited.
Space treatment should be applied every day for 1-2 weeks to kill adults as they emerge
from breeding sites in the area. Once under control, the spraying interval
can be extended to once or twice a week, depending on the rate of immigration
of flies from outside the control area.
Suitable insecticides for space treatment against flies are listed in
Tables 1 and 2. For indoor treatment, water based or deodorized kerosene
formulations of the less hazardous insecticides are recommended.
Food and water should be protected during indoor
space treatment and people and animals should be kept out of the way of
outdoor space sprayers. Read and follow the product label and local
regulations. Larviciding
Larviciding as a fly control measure has many drawbacks. Fly breeding substrates
tend to accumulate and change continuously and therefore frequent treatments
with larvicides are required. The penetration and
distribution of the larvicide in the substrate is
often problematic, the natural predators of fly larvae may be killed if
non-selective treatments are used, and exposure to insufficient
concentrations of insecticide in the breeding substrates may favour the
development of resistance.
In areas where fly breeding (e.g. refuse, animal or
human excrement) is confined to localized sites, carefully targeted larviciding at regular intervals may be indicated. Larvicides are applied at a rate sufficient to wet the
upper 10-15 cm of the breeding substrate.
Insect growth regulators (IGRs) are preferred for
use as larvicides as they are chemically unrelated
to adulticides (Table 3). Although many compounds
belonging to the traditional insecticide classes are also active against fly
larvae, they should in general be reserved for control of adult flies, to
minimize the selection pressure for resistance. The use of pyrethroids in particular should be reserved for space
treatment.
Table
1. Suitable insecticides for space treatment for fly control
|
Insecticide
|
Chemical
Typea
|
Dosage of
a.i.b
(g/ha)
|
WHO hazard
classification
of active ingredient
(Class) c
|
|
Chlorpyrifos-methyl
|
OP
|
100-150
|
U
|
|
Diazinon
|
OP
|
336
|
II
|
|
Dimethoate
|
OP
|
224
|
II
|
|
Malathion
|
OP
|
672
|
III
|
|
Naled
|
OP
|
224
|
II
|
|
Pirimiphos-methyl
|
OP
|
250
|
III
|
|
Bioresmethrin
|
PY
|
5-10
|
U
|
|
Cypermethrin
|
PY
|
2-5
|
II
|
|
Cyphenothrin
|
PY
|
5-10
|
II
|
|
d-d-trans-cyphenothrin
|
PY
|
2.5-5
|
NA
|
|
Deltamethrin
|
PY
|
0.5-1.0
|
II
|
|
Esfenvalerate
|
PY
|
2-4
|
II
|
|
Etofenprox
|
PY
|
10-20
|
U
|
|
Lambda-cyhalothrin
|
PY
|
0.5-1.0
|
II
|
|
Permethrin
|
PY
|
5-10
|
II
|
|
d-phenothrin
|
PY
|
5-20
|
U
|
|
Resmethrin
|
PY
|
2-4
|
III
|
a OP =
organophosphate, PY = pyrethroids.
b a.i. = active ingredient.
c Class II =
moderately hazardous; Class III = slightly hazardous;
Class U= unlikely to pose an acute hazard in
normal use; NA = not available.
Table 2: Pyrethroid
mixtures used in cold and thermal fog formulations for fly control
|
Pyrethroid mixtures
|
Concentration (g a.i.a/ha)
|
|
Cold fog
|
Thermal fog
|
|
Permethrin +
|
5.0-7.5
|
5.0-15.0
|
|
S-bioallethrin +
|
0.075-0.75
|
0.2-2.0
|
|
Piperonyl butoxide
|
5.25-5.75
|
9.0-17.0
|
|
|
|
|
|
Bioresmethrin +
|
-
|
5.5
|
|
S-bioallethrin +
|
-
|
11.0-17.0
|
|
Piperonyl butoxide
|
-
|
0-56
|
|
|
|
|
|
Phenothrin +
|
5.0-12.5
|
4.0-7.0
|
|
Tetramethrin +
|
2.0-2.5
|
1.5-16.0
|
|
Piperonyl butoxide
|
5.0-10.0
|
2.0-48.0
|
|
|
|
|
|
Etofenprox +
Pyrethrins +
|
5-10
0.18-0.37
|
5-10
0.18-0.37
|
|
Piperonyl butoxide
|
10-20
|
10-20
|
|
|
|
|
|
Lambda-cyhalothrin
+
|
0.5
|
0.5
|
|
Tetramethrin +
|
1.0
|
1.0
|
|
Piperonyl butoxide
|
1.5
|
1.5
|
|
|
|
|
|
Cypermethrin +
|
2.8
|
2.8
|
|
S-bioallethrin +
|
2
|
2
|
|
Piperonyl butoxide
|
10
|
10
|
|
|
|
|
|
Tetramethrin +
|
12-14
|
12-14
|
|
d-phenothrin
|
6-7
|
6-7
|
|
|
|
|
|
d-tetramethin +
|
1.2-2.5
|
1.2-2.5
|
|
Cyphenothrin
|
3.7-7.5
|
3.7-7.5
|
|
|
|
|
|
d-tetramethrin +
|
1.2-2.5
|
1.2-2.5
|
|
d,d-trans-cyphenothrin
|
2-8
|
2-8
|
|
|
|
|
|
Deltamethrin +
|
0.3-0.7
|
0.3-0.7
|
|
S-bioallethrin +
|
0.5-1.3
|
0.16-1.3
|
|
Piperonyl butoxide
|
1.5
|
1.5
|
a a.i. = active ingredient.
Table 3. Insecticides
used as housefly larvicides
|
Insecticide
|
Chemical
typea
|
Dosage
g a.i./m2
|
WHO hazard classification
of active ingredient
(Class) b
|
|
Diflubenzuron
|
IGR
|
0.5-1.0
|
U
|
|
Cyromazine
|
IGR
|
0.5-1.0
|
U
|
|
Pyriproxifen
|
IGR
|
0.05-0.1
|
U
|
|
Triflumuron
|
IGR
|
0.25 - 0.5
|
U
|
aIGR = insect growth regulator.
b Class U= unlikely to pose an acute hazard in
normal use.
|