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Toxicological information

Acute Toxicity: inhalation

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Administrative data

Endpoint:
acute toxicity: inhalation
Type of information:
experimental study
Adequacy of study:
supporting study
Study period:
1994/02 to 1994/08
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1994
Report date:
1994

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
EPA OPP 81-3 (Acute inhalation toxicity)
Version / remarks:
FIFRA § 10, Subdivision F, 1984
Deviations:
no
Qualifier:
equivalent or similar to guideline
Guideline:
EU Method B.2 (Acute Toxicity (Inhalation))
Deviations:
no
GLP compliance:
yes
Test type:
traditional method
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
N-cyclopropyl-1,3,5-triazine-2,4,6-triamine
EC Number:
266-257-8
EC Name:
N-cyclopropyl-1,3,5-triazine-2,4,6-triamine
Cas Number:
66215-27-8
Molecular formula:
C6H10N6
IUPAC Name:
N2-cyclopropyl-1,3,5-triazine-2,4,6-triamine
Test material form:
solid: particulate/powder
Remarks:
Fine white powder
Specific details on test material used for the study:
Storage: Room temperature

Test animals

Species:
rat
Strain:
Sprague-Dawley
Remarks:
HSD
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS:
Acclimation Period: At least 4 days
Weight When Tested: Males (179-225 g); Females(195-242 g)
Age: Young adult
Housing: One per cage

ENVIRONMENTAL CONDITIONS:
Temperature Range: 67-77 °F (19.4-25 °C)
Humidity Range: 30-80%
12-hour light/dark cycle
10-12 air changes/hour

Administration / exposure

Route of administration:
inhalation: aerosol
Type of inhalation exposure:
nose only
Vehicle:
air
Mass median aerodynamic diameter (MMAD):
>= 3.92 - <= 6.68 µm
Geometric standard deviation (GSD):
>= 2.075 - <= 4.142
Remark on MMAD/GSD:
The MMAD’s were 6.68 µm ±1.48 for the 3.60 mg/L (3600 mg/m3) concentration and 3.92 µm ±1.48 for the 0.744 mg/L (744 mg/m3) concentration.
GSD ranges: (2.947 to 4.142) at 3.60 mg/L concentration and (2.075 to 4.027) at 0.744 mg/L concentration.
Details on inhalation exposure:
A 500 L nose-only stainless steel, dynamic flow inhalation chamber was utilized in this experiment. The body of the chamber has 25 ports in 5 rows. Polycarbonate cones are inserted into 10 designated individual ports. The test material is introduced through the opening in the top of the chamber. The bottom section has a corresponding air outlet and a drain valve for cleaning the chamber. The individual polycarbonate cones (tubes) are tapered at one end to t the shape of the animal’s head and the back portion is sealed with a polycarbonate cap. The cones containing the animals fit tightly into the ports, and are sealed with "0" rings.
Analytical verification of test atmosphere concentrations:
yes
Duration of exposure:
4 h
Concentrations:
The mean concentration was 0.744 or 3.6 mg/L (744 or 3600 mg/m3).
No. of animals per sex per dose:
5
Control animals:
yes
Remarks:
A control group of 5 rats/sex was exposed to air only under similar experimental conditions.
Details on study design:
On Day 0 of the study, 5 Sprague Dawley rats/sex/group were exposed nose-only for a single 4-hour period to an aerosol generated from undiluted cyromazine technical at a mean concentration of 0.744 or 3.6 mg/L (744 or 3600 mg/m3). A control group of 5 rats/sex was exposed to air only under similar experimental conditions. During the 4- hour period 4 samples of the tested atmosphere were taken at regular intervals for the determination of exposure levels. Particle size distribution was also determined during exposure. Clinical signs were recorded twice on the day of exposure and at least daily thereafter for up to 17 days. Body weights were measured prior to exposure, on day 7 and at the day of termination. At termination of the study, all animals were subjected to gross necropsy.

Results and discussion

Preliminary study:
Trial assays were conducted using different methods of aerosolizing the test material into the exposure chamber in attempts to determine which method(s) would produce the highest concentration and a mass median aerodynamic diameter (MMAD) between 1 and 4 µm.
Effect levels
Key result
Sex:
male/female
Dose descriptor:
LC50
Effect level:
> 3.6 mg/L air
Based on:
test mat.
Exp. duration:
4 h
Mortality:
No mortality occurred.
Clinical signs:
other: Decreased activity, piloerection at both concentrations, and additionally nasal discharge at the higher concentration tested. All animals appeared normal two days post treatment and for the rest of the study period.
Body weight:
Body weight gain was unaffected with the exception of two females exposed to 3.6 mg/L and two control females, which lost weight between days 0 and 7.
Gross pathology:
Gross necropsy revealed discoloration of the lungs in animals of all groups.

Any other information on results incl. tables

Table 1:


Exposure parameters












































Parameter



Value



Low Concentration



 High Concentration



Nominal concentration



4.51 mg/L



45.4 mg/L



Analytical concentration



0.7443 mg/L



3.597 mg/L



Standard deviation (SD)



1.48



1.48



MMAD ± SD (µm)



3.92



6.68



% of particles collected



50% with MMAD < 5.90µm



50% with MMAD < 3.54µm



 



84% with MMAD < 23.79µm



84% with MMAD < 7.35µm


Applicant's summary and conclusion

Interpretation of results:
GHS criteria not met
Conclusions:
The acute inhalation LC50 value for cyromazine in male and female Sprague Dawley rats under the examined conditions was found to be greater than 3.6 mg/L air (maximum attainable concentration).
Executive summary:

Two groups of Sprague-Dawley rats (5/sex/group) were exposed for four hours to an aerosol generated from undiluted Cyromazine in a nose-only inhalation at a mean concentration of 0.744 or 3.60 mg/L (744 or 3600 mg/m3). A control group consisting of 5 males and 5 females was exposed to room air only for four hours under similar experimental conditions. There was no mortality during the study. Clinical signs of toxicity in the test groups included activity decrease and piloerection at both levels, and nasal discharge at the 3.60 mg/L level. All animals were asymptomatic on Day 2. Body weights were essentially unaffected by exposure, except for two females at the 3.60 mg/L level that lost weight between Days 0 and 7. Control animals appeared normal throughout the study. The gross necropsies of control as well as test animals showed some discoloration of lungs. The acute inhalation LD50 for Cyromazine is greater than the maximum attainable concentration of 3.60 mg/L.