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Diss Factsheets

Administrative data

Endpoint:
short-term repeated dose toxicity: oral
Type of information:
experimental study
Adequacy of study:
key study
Study period:
17 Feb - 22 Mar 2005
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
study well documented, meets generally accepted scientific principles, acceptable for assessment
Remarks:
The present study is a dose-range-finding study for a one-generation study.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2005
Report date:
2005

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
- Principle of test: Exploratory, dose-range-finding study for a one-generation reproduction toxicity study. Repeated dose toxicity was assessed after 5 weeks administration of the test substance via diet.
- Short description of test conditions: Test conditions were similar to OECD TG 407 without detailed examinations.
- Parameters analysed / observed: clinical signs of toxicity, body weight, food intake, gross necropsy, organs weights of spleen, liver and kidney, histopathology of spleen, liver, and kidney
GLP compliance:
no
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
-
EC Number:
448-100-7
EC Name:
-
Cas Number:
70441-63-3
Molecular formula:
C9H12FN
IUPAC Name:
4-fluoro-N-(propan-2-yl)aniline

Test animals

Species:
rat
Strain:
Wistar
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River, Sulzfeld, Germany
- Age at study initiation: about 6 weeks
- Mean body weight at study initiation: males: 146 g (range: 133 - 161 g); females: 119 g (range: 108 - 145 g)
- Housing: Animals were conventionally housed in Makrolon cages type IV on low-dust wooden granulate (Source: Ssniff Spezialdiäten Inc., Soest, Germany). Animals were group housed; 5 animals per cage. Environmental enrichment in form of wooden blocks was in place.
- Diet: fixed-formula standard diet Provimi Kliba 3883.9.25 meal (Provimi Kliba SA, Kaiseraugst, Switzerland), ad libitum
- Water: tap water in drinking water quality, ad libitum
- Acclimation period: 2 days

DETAILS OF FOOD AND WATER QUALITY
The nutritive composition and contaminant content of the standard diet were routinely checked and analyzed. The tap water complied with the current German Drinking Water Ordinance (December 1990, supplemented May 2001).

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): 55 ± 5
- Air changes (per hr): ≥10
- Photoperiod (hrs dark / hrs light): 12/12

IN-LIFE DATES: From: 17 Feb 2005 To: 22 Mar 2005

Administration / exposure

Route of administration:
oral: feed
Vehicle:
other: offered in diet
Details on oral exposure:
PREPARATION OF DOSING FORMULATION
The test substance was mixed into the diet intended for the following week according to the dose scheme. A mixing granulator (Lödige, Paderborn, Germany) was used. The mixtures were not longer used than 8 days. Stability of the test substance in the diet from 10 to 12000 ppm was demonstrated and amounts to 15 days.

DIET PREPARATION
- Rate of preparation of diet (frequency): once weekly
- Mixing appropriate amounts with (Type of food): Provimi Kliba 3883.9.25 meal
- Storage temperature of food: room temperature
Analytical verification of doses or concentrations:
no
Duration of treatment / exposure:
5 weeks
Frequency of treatment:
continuously in the diet
Doses / concentrationsopen allclose all
Dose / conc.:
100 ppm
Remarks:
actual test substance intake: male: 8 mg/kg bw/d; female: 10 mg/kg bw/d
Dose / conc.:
500 ppm
Remarks:
actual test substance intake: male: 42 mg/kg bw/d; female: 48 mg/kg bw/d
Dose / conc.:
2 500 ppm
Remarks:
actual test substance intake: male: 191 mg/kg bw/d; female: 180 mg/kg bw/d
Dose / conc.:
10 000 ppm
Remarks:
actual test substance intake: male: 564 mg/kg bw/d; female: 470 mg/kg bw/d
No. of animals per sex per dose:
5 animals/sex/dose
Control animals:
yes, plain diet
Details on study design:
- Dose selection rationale: The present study was a exploratory dose-range finding study. The dose levels were selected according to results of previous studies in rats.

Examinations

Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes.
- Time schedule: Twice daily, once daily on weekends and public holidays.
- Cage side observations checked in table (table 1) were included.

DETAILED CLINICAL OBSERVATIONS: Yes.
- Time schedule: Weekly.

BODY WEIGHT: Yes.
- Time schedule for examinations: Weekly.

FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each group determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes.
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes.

FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No.

OPHTHALMOSCOPIC EXAMINATION: No.

HAEMATOLOGY: No.

CLINICAL CHEMISTRY: No.

URINALYSIS: No.

NEUROBEHAVIOURAL EXAMINATION: No.

IMMUNOLOGY: No.
Sacrifice and pathology:
GROSS PATHOLOGY: Yes.
All animals sacrificed pre-scheduled or in moribund condition were killed by exsanguination under deep diethyl ether anesthesia and necropsied. Their orifices, external and internal organs and tissues were subjected to thorough gross pathological examination. Any changes were described in terms of localization, size, color, and consistency whenever present.
The organ weights of the liver, spleen, and kidneys were recorded.

HISTOPATHOLOGY: Yes.
Histopathological examinations were performed for the liver, spleen, and kidneys.
Statistics:
Treatment groups were compared with the control group.
Statistical evaluations on body weight and organ weight data were done using the Dunnett-test in connection with a variance analysis.

Results and discussion

Results of examinations

Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
At 10000 ppm all rats exhibited pallor, emaciation, and poor general condition.
No remarkable clinical findings were observed at dose levels of 2500 ppm and below.
Mortality:
mortality observed, treatment-related
Description (incidence):
Because of poor general condition, all animals receiving 10000 ppm were sacrificed pre-scheduled on study day 22 (test substance administration started on study day 1).
No mortality occured at dose levels of 2500 ppm and below.
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
At 10000 ppm, a clear body weight reduction was seen in male and female rats, which resulted in emaciation and need for pre-scheduled sacrifice.
No relevant changes in body weights were noted at dose levels of 2500 ppm and below. In fact, slightly but statistically significantly reduced or increased mean values of body weight found in males of the 100, 500, and 2500 ppm dose groups were incidential and, therefore, not toxicologically relevant (table 2).
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
At 10000 ppm reduced food intake was observed for both sexes. As a consequence of the reduced food intake at 10000 ppm the test substance intake was less than expected in this group.
No relevant changes in food intake were observed at dose levels of 2500 ppm and below.
At doses up to 2500 ppm the test substance intake increased roughly as expected from the dose factor (table 3).
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not examined
Haematological findings:
not examined
Clinical biochemistry findings:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
effects observed, treatment-related
Description (incidence and severity):
The absolute and relative spleen weights were dose-dependently increased at 100, 500, and 2500 ppm, which was statistically significant from 500 ppm onwards (table 4).
There were no test substance-related changes in absolute and relative liver and kidney weights up to 2500 ppm. The mean relative liver weight of 100 ppm dose group males was statistically significantly reduced. However, this finding is of no toxicological relevance, because of the single occurrence and because a dose-dependency is lacking.
Gross pathological findings:
effects observed, treatment-related
Description (incidence and severity):
Blackish discoloration of the spleen (starting at 100 ppm), kidneys (starting at 500 ppm), and liver (only 10000 ppm) were noted.
At dose levels ≥ 500 ppm the spleen frequently appeared swollen and/or enlarged (500 ppm: male: 4/5, female: 5/5; 2500 ppm: male: 5/5, female: 5/5;10000 ppm: male: 4/5, female: 5/5).
Neuropathological findings:
not examined
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Spleen:
- Increased blood content in dilated sinuses of the red pulp in 2/5 females of the 100 ppm dose group and in all animals of the higher dosages.
- Increased extramedullary hematopoiesis at all dose levels.
- Increased deposition of a brownish pigment (most likely of ferruginous origin) at dose levels ≥ 500 ppm.

Liver:
- Pigmented Kupffer cells preferably located in the periportal areas starting in males at dose levels ≥500 ppm and in females ≥2500 ppm.
- Periportal cytoplasmic change and, in one case, periportal degeneration and bile duct proliferation at 2500 ppm.
- Centrilobular cytoplasmic change and hypertrophy in males at 500 ppm.

Kidneys:
- Deposition of a brownish pigment in all animals at 2500 ppm.
- Tubular degeneration/regeneration in 1/5 males at 2500 ppm.
Histopathological findings: neoplastic:
not specified

Effect levels

Key result
Dose descriptor:
LOAEL
Effect level:
100 ppm
Based on:
test mat.
Sex:
male/female
Basis for effect level:
gross pathology
histopathology: non-neoplastic
organ weights and organ / body weight ratios

Target system / organ toxicity

Key result
Critical effects observed:
yes
Lowest effective dose / conc.:
100 ppm
System:
other: spleen
Organ:
spleen
Treatment related:
yes
Dose response relationship:
yes

Any other information on results incl. tables

Table 2: Body weight (g)

Sex m m m m m f f f f f
Dose (ppm) 0 100 500 2500 10000 0 100 500 2500 10000
Study day                    
1 143 144 147 147 149 120 117 120 121 118
8 163 171 172 174 129** 140 140 141 136 107**
15 178 190 190 201* 127** 156 160 157 153 105**
22 239 214* 210** 224 125** 175 176 168 164 100**
29 233 227 223 240   181 185 175 170  
34 276 271 269 267   194 200 187 182  

* p 0.05, ** p 0.01

Table 3: Calculated test substance intake (mg test substance/kg body weight/day)

Sex m m m m m f f f f f
Dose (ppm) 0 100 500 2500 10000 0 100 500 2500 10000
Study day                    
8 - 8 48 213 603 - 12 47 186 201
15 - 8 42 203 515 - 10 48 189 658
22 - 8 41 193 573 - 9 47 185 551
29 - 7 35 170   - 9 45 157  
34 - 9 42 175   - 9 54 184  

Table 4: Absolute and relative spleen weights

Sex m m m m m f f f f f

Dose (ppm)

0 100 500 2500 10000 0 100 500 2500 10000

Number of animals

5 5 5 5 - 5 5 5 5 -
Final body weight (g) 276 271 269 267   194 200 187 182  
SPLEEN                    
absolute weight (mg) 575 614 821** 1606**   427 488 668** 1215**  

relative weight

(mg/100 g bw)

208 227 307** 602**   219 245 358** 668**  

* p 0.05, ** p 0.01

Applicant's summary and conclusion

Conclusions:
Since treatment-related effects, especially regarding the spleen, were noticed from the lowest tested dose level of 100 ppm, 100 ppm is to be considered as Lowest Observed Adverse Effect Level (LOAEL) and no No Observed Adverse Effect Level (NOAEL) could be established in the present range finding study.