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Diss Factsheets

Administrative data

Endpoint:
acute toxicity: inhalation
Type of information:
experimental study
Adequacy of study:
key study
Study period:
1987
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1988
Report date:
1988

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 403 (Acute Inhalation Toxicity)
GLP compliance:
yes (incl. QA statement)
Test type:
standard acute method
Limit test:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
(2RS,3RS)-3-(2-chlorophenyl)-2-(4-fluorophenyl)-[(1H-1,2,4-triazol-1-yl)methyl]oxirane
EC Number:
406-850-2
EC Name:
(2RS,3RS)-3-(2-chlorophenyl)-2-(4-fluorophenyl)-[(1H-1,2,4-triazol-1-yl)methyl]oxirane
Cas Number:
133855-98-8
Molecular formula:
C17 H13 Cl F N3 O
IUPAC Name:
1-{[(2R,3R)-3-(2-chlorophenyl)-2-(4-fluorophenyl)oxiran-2-yl]methyl}-1H-1,2,4-triazole

Test animals

Species:
rat
Strain:
Wistar
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Dr. K. Thomae GmbH, Biberach, Germany
- Weight at study initiation: males 273 +/- 8.6 g, females 193 +/- 6.2 g
- Age at study initiation: 8-9 weeks
- Housing: In groups of 5 in Type -D-III cages
- Diet ad libitum: Pelleted Kliba rat diet 343,
- Water ad libitum: Tap water
- Acclimation period: 1 week

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20- 24
- Humidity (%): 30 - 70
- Photoperiod (hrs dark / hrs light): 12/12

Administration / exposure

Route of administration:
inhalation: dust
Type of inhalation exposure:
nose/head only
Vehicle:
air
Remarks:
supplied via a central air-conditioning system
Mass median aerodynamic diameter (MMAD):
3.9 µm
Geometric standard deviation (GSD):
2.3
Details on inhalation exposure:
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
The animals were placed in tubes of the head-nose inhalation system INA 20 (BASF AG, chamber volume: 55l) with their snouts in an inhalation chamber with excess pressure. The test substance was dosed unchanged.
The dust/air mixture was generated by means of a microgenerator and the concentration was adjusted by varying the rotation of the metering disc. The supply air was conditioned via a central air-conditioning system and the air flow was set at 1500 l/h. Temperatures in the exposure system were 19 - 25°C.
By means of an exhaust air system the pressure ratios in the inhalation system were adjusted in such a way that the amount of exhaust air was about 10% lower (excess pressure). This ensured that the mixture of the test substance and air was not diluted with laboraoty air in the breathing zones of the animals.
AIR SAMPLING FOR ANALYSIS OF TEST MATERIAL CONCENTRATIONS, METHOD FOR PARTICEL SIZE ANALYSIS
Samples of the test atmosphere (1l) were taken adjacent to the animals’ nose once an hour with an air flow of 1.25 m/s. The concentration was determined gravimetrically.
Particle size analysis was done 30 minutes after the beginning of the test. A sample of 9 l was analyzed using an impactor. The MMAD was 3.9 µM and the GSD was 2.3. The respirable dust fraction was determined as 77%.
Analytical verification of test atmosphere concentrations:
yes
Remarks:
Gravimetric determination of the inhalation atmosphere concentration
Duration of exposure:
4 h
Concentrations:
The mean analytical concentration of 4 samples was 5.26 +/-0.07 mg/l. The nominal concentration was 63 mg/l.
No. of animals per sex per dose:
5 males per dose, 5 females per dose
Control animals:
no
Details on study design:
Duration of observation period following administration: 14 days
- Frequency of observations for clinical symptoms: Several times during exposure, afterwards at least once daily at workday.
- Frequency of observations for mortality: Daily
- Frequency of weighing: On first day (before exposure), day 7 and day 14.
- Necropsy of survivors performed: yes, all animals were sacrificed and subjected to gross pathology at study termination.
Statistics:
The statistical evaluation of the concentration/effect relationship was carried out on the basis of the binomial test (Wittig, H.: Mathematische Statistik 1974, pp. 32 35) in accordance with tables of the BASF Computer Center.
The calculation of the particle size distribution was carried out in the Department of Toxicology of BASF Aktiengesellschaft on the basis of mathematical methods for evaluating particle measurements (Silverman, L.: Particle Size Analysis in Industrial Hygiene, 1971, pp. 235 -259).

Results and discussion

Effect levels
Sex:
male/female
Dose descriptor:
LC50
Effect level:
> 5.3 mg/L air (analytical)
Based on:
test mat.
Exp. duration:
4 h
Remarks on result:
other: No mortality occured.
Mortality:
No mortality occured.
Clinical signs:
other: During exposure accelerated breathing and a slight reddish discharge from noses were seen. The slight reddish discharge persisted after exposure but no abnormalities were detected from day one onward.
Body weight:
The body weight gain of male and female rats in the test group was comparable to the historical control (for details see Table 1).
Gross pathology:
Upon necropsy no pathological findings were observed.
Other findings:
Signs of airway irritation during and shortly after exposure; no symptoms thereafter.
MMAD = 3.9µm

Applicant's summary and conclusion

Interpretation of results:
GHS criteria not met
Conclusions:
The median lethal dose via inhalation of the test item in rats is higher than 5.3 mg/L.
Executive summary:

The substance was tested for its acute inhalation toxicity. The test method was based on EPA (FIFRA) and OECD 403 guidelines. GLP requirements were fulfilled. 5 mal and 5 female Wistar rats were exposed to a concentration of 5.3 mg/L of the test substance for a period of 4 hours. During and up to one day after the exposure inhalation specific clinical symptoms were observed. No mortality occurred. Thus, the inhalation LC50 (4h) in rats is higher than 5.3 mg/L.