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University Studies
WARF INSTITUTE INC, Madison, Wisconsin
Study showing the contamination hazard of the automatic pyrethrin dispensers
in still air environment
In the continuing study of the automatic pyrethrin dispenser, Mr GL Bischoff,
representing CAP, Inc., of Orange, California, requested that WARF Institute
Inc., conduct a still air study using two representative food products which
would be present in an institutional kitchen or food preparation area. The protocol
for the study imposed abnormally severe conditions to the study. These conditions
are:
1. Still Air All ventilation and access to the test chambers are to
be sealed off
2. Food Exposure The selected food samples are to be open to the atmosphere
for twelve continuous hours
The test results confirm the relative unstable nature of pyrethrin to exposure
in that the test data confirms no measurable residue. The details of the exposure
methods and room descriptions are attached.
Following exposure the samples were collected and stored under freezing conditions
until analysis. The method used for residues of pyrethrin is found in the Food
and Drug Administration Pesticide Analytical Manual, Volume II, Pesticide Reg.
Sec. 120, 128. The limits of detection for the two materials are 1.5 ug/75 grams
sugar and 4.0 ug/beef steak. The results of the analysis are given in the attached
protocol. Sample numbers refer to the positions located on the floor plans.
RESULTS
| Location Number |
Exposure Time |
Sample Description |
Pyrethrins |
| 1 |
12hr |
Sugar/Beef Steak |
N.D. |
| 2 |
12hr |
Sugar/Beef Steak |
N.D. |
| 3 |
12hr |
Sugar/Beef Steak |
N.D. |
| 4 |
12hr |
Sugar/Beef Steak |
N.D. |
| 5 |
12hr |
Sugar/Beef Steak |
N.D. |
| 6 |
12hr |
Sugar/Beef Steak |
N.D. |
| 7 |
12hr |
Sugar/Beef Steak |
N.D. |
| 8 |
12hr |
Sugar/Beef Steak |
N.D. |
N.D. None Detected
UNIVERSITY OF ILLINOIS COLLEGE OF AGRICULTURE
Intermittent Pyrethrin Dispensers (IPD) and the probability of contamination
The studies completed at the University of Illinois on behalf of C.A.P. have
shown that virtually no food residue hazard exists with the proper use of the
IPD units.
A mathematical explanation of the emission rates and a degradation study of
the materials is meaningful.
One IPD unit operating under recommended guidelines (100mg into 6,000 cubic
feet) will result in a mathematically potential residue of 0.0066 ppm Pyrethrins,
0.0133 ppm Piperonyl Butoxide and 0.0223 ppm MGK 264 after one hour of operation
on a small 300 gram TV dinner. This residue assumes complete fallout and 100
percent deposit on a square foot basis, which of course is unrealistic. Our
tests have shown that only 1% of the aerosol emission is recoverable from a
surface. When the residue tested above is applied to the TV dinner the resultant
residue would be beyond the limits of detection.
The degradation rate of pyrethrin and the three synergists vary.
Half life studies indicate that MGK 264 is the first to go with piperonyl butoxide
the last. It is interesting to note that when tropital is present the formulation
tends to degrade at a greater rate than with other synergists, probably due
to volatilisation. The following time loss study was used to determine the relative
rates of degradation. The table cannot be applied to the same materials when
emitted from IPD units as the particle size would increase the degradation rates
significantly. Due to the ephemeral nature of the materials the table below
reflects the appropriate half life values. The deposition of the materials was
made at a rate of 1500 micrograms per square foot. This was accomplished by
depositing a measured quantity of each material on individual sheets of filter
paper 9cm in diameter.
Half life MGK 264 4hr
Half life Tropital 8hr
Half life Piperonyl Butoxide 72hr
Half life Pyrethrin 7hr
From this data was calculated that the loss rate per hour for the material on
a square foot basis is:
MGK 264 188.0 ug
Tropital 94.0 ug
Piperonyl Butoxide 7.80 ug
Pyrethrin 107.0 ug
If one compares the rate of gain or accumulation from one IPD operating in a
6,000 cubic foot area and assuming that 100% of the material would fall out
and deposit on a square foot basis. The following would result in one hour:
MGK 264 19.2 us/sq. ft
Tropital 11.6 ug/sq. ft
Piperonyl Butoxide 11.7 ug/sq. ft
Pyrethrin 5.8 ug/sq. ft
Tests have shown however that the actual rate of accumulation is about 1% of
the above. These calculations further point out the improbability of accumulative
residue as indeed the tests at the University of Illinois have shown.
Highly exaggerated use condition
tests gave data showing insignificant levels of pyrethrin and the synergists
were present in food after 21 days of continuous exposure. Other tests reflected
no residue in milk or meat after 24 hours of exaggerated exposure.
With the data accumulated on the
fallout hazard inherent with the IPD in food areas plus the instability of compounds
it is a simple matter of arithmetic to determine that if pesticide residues
were present, these residues would be far below the technical limits of the
analytical method. In a recent test using tropital in place of piperonyl butoxide
in still air after 12 hours of exposure the possible residues were less than
1 part per billion in meats, foods, sugar and coffee. Indeed the background
interference of substances in the food made it impossible to detect pyrethrin,
tropital or MGK 264.
In summary degradation rates far
exceed accumulation rates when applied to the emission level of the IPD. This
accounts for the lack of measurable residues in foods even when exposed under
maximum conditions.
BIOLOGICAL TESTING LABORATORY, MINNEAPOLIS, MINNESOTA
-Intermittent Aerosol Efficacy House flies in a 5,400 cubic foot chamber
Sample:
Konk Odourless
1.07% d-trans Allethrin
2.14% Piperonyl Butoxide
2.14% MGK 264
94.65% Inert Ingredients
Method:
Approximately 600 house flies (Musca
domestica, F58t-II strain) were released into the 5,400 cubic foot chamber.
The intermittent device was centred on a wall, 7 feet from the floor. The test
aerosol unit, equipped with a metered valve, was placed in the device. The device
was turned on, activating the aerosol valve every 15 minutes. Knockdown counts
were taken hourly, for the first five hours, with a handheld counter. The test
continued for 24 hours. The aerosol was weighed before spraying and again after
spraying to determine dosage. A large dish containing sugarwater soaked pads
was provided throughout the test period. The test was run in triplicate.
Modifications:
Device sprayed every 8 _ minutes.
Knockdown counts were taken for the first four hours. Untreated controls run
by releasing house flies into the chamber and taking knockdown counts as in
actual test.
Summarised Results:
|
|
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Average % Knockdown
|
Avg % Mortality
|
| |
Avg Dosage |
1 Hr |
2 Hrs |
3 Hrs |
4 Hrs |
24 Hours |
| Konk |
8.27g |
44 |
73 |
83 |
92 |
100 |
| Untreated
Control |
-- |
03 |
06 |
07 |
10 |
11 |
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