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EC number: 619-372-6 | CAS number: 98730-04-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
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- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Toxicity to reproduction
Administrative data
- Endpoint:
- two-generation reproductive toxicity
- Remarks:
- based on test type (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 18 January 1990 to 04 January 1991
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study compliant with test guidelines of the time. However, current guidelines for two-generation reproduction toxicity studies require additional endpoints. Available as unpublished report, fully adequate for assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 416 (Two-Generation Reproduction Toxicity Study)
- Version / remarks:
- 1983 (current guideline adopted 2001)
- Deviations:
- yes
- Remarks:
- (does not meet current guideline specification)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 83-4 (Reproduction and Fertility Effects)
- Version / remarks:
- 1982 (current guideline adopted 1998)
- Deviations:
- yes
- Remarks:
- (does not meet current guideline specification)
- Qualifier:
- according to guideline
- Guideline:
- other: MAFF Japan, Testing Guidelines for Toxicity Studies, No. 4200 (1985)
- Deviations:
- not specified
- Qualifier:
- according to guideline
- Guideline:
- other: Canada Health Protection Branch: Guidelines for Pesticide Toxicology Data Requirements (1981)
- Deviations:
- not specified
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 2,2-dichloro-1-[(3R)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one; 2,2-dichloro-1-[(3S)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one
- EC Number:
- 619-372-6
- Cas Number:
- 98730-04-2
- Molecular formula:
- C11H11Cl2NO2
- IUPAC Name:
- 2,2-dichloro-1-[(3R)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one; 2,2-dichloro-1-[(3S)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Strain: Sprague Dawley Crl:CD(SD)BR
- Age at study initiation: P generation approximately 6 weeks old
- Weight at study initiation: P generation males: 174-232 g; females: 143-175 g
- Housing: Individual in solid floor macrolone cages with stainless steel lids except during mating (one male with one female) and during lactation (one female with litter). Autoclaved sawdust bedding.
- Diet: Ssniff R10 powdered diet ad libitum
- Water: Tap water in plastic bottles ad libitum
- Acclimation period: P generation 8 days
ENVIRONMENTAL CONDITIONS
- Temperature: 19-25°C
- Humidity: 30-70%
- Air changes (per hour): Not reported
- Photoperiod: 12 hrs dark / 12 hrs light
IN-LIFE DATES: From: 18 January 1990 To: 04 January 1991
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: diet
- Details on exposure:
- DIET PREPARATION
- Frequency of preparation of diet: Monthly
- Mixing appropriate amounts with diet: The particle size of the test substance was reduced and standardised prior to use using a centrifugal laboratory mill. It was then admixed to the powdered diet in several steps (e.g. 1000 g and 10 kg pre-mixtures and 50 kg final mixture)
- Storage temperature of food: room temperature control and 50, 500 and 1000 ppm dose levels, -20°C for 10 ppm level - Details on mating procedure:
- - M/F ratio per cage: 1:1
- Length of cohabitation: Maximum of 21 days
- Proof of pregnancy: vaginal plug / sperm in vaginal smear referred to as day 0 of pregnancy
- After 2 weeks of unsuccessful pairing replacement of first male by another male with proven fertility.
- Further matings after two unsuccessful attempts: no
- After successful mating each pregnant female was caged: Individually - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples from each batch of test diet prepared, together with a reference sample of control diet, were analysed for achieved concentration and homogeneity. The stability of dietary preparations had already been confirmed in earlier studies.
After overcoming initial homogeneity problems, the dietary preparations were determined to be homogeneous and close to nominal concentrations and stable for the period of use. - Duration of treatment / exposure:
- P animals: For 14 weeks premating, up to 21 days mating, during pregnancy until weaning
F1 animals: For 14 weeks after weaning/premating, up to 21 days mating, during pregnancy until weaning - Frequency of treatment:
- Continuous
- Details on study schedule:
- - Pre-mating period P Generation: 14 weeks
- Selection of F parents from F1 generation at 21 days of age
- F1 parental animals not mated until 14 weeks after weaning
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 10, 50, 500 and 1000 ppm
Basis:
nominal in diet
- No. of animals per sex per dose:
- 25
- Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: On the basis of results from a dose-ranging reproduction study in the rat (Ciba-Geigy study number 89 1187, HLD project number 380-153).
- Positive control:
- No
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: daily
BODY WEIGHT: Yes
- Time schedule for examinations: Parental animals once weekly during pre-mating and mating periods and prior to terminal kill. Females were additionally weighed on days 0, 7, 14 and 20 post coitum and on days 1, 4, 7, 14 and 21 post partum.
FOOD CONSUMPTION:
- Time schedule for examinations: Parental animals twice per week during pre-mating period. Additionally food consumption for females was determined for days 0-3, 3-7, 7-10, 10-14, 14-20 post coitum and days 1-4, 4-7, 7-10, 10-12, 12-14, 14-15, 15-16, 16-17, 17-18, 18-19, 19-20 and 20-21 post partum (calculated as mean daily food consumption/measurement period).
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
OTHER:
- Date of mating
- Date of parturition
- Duration of gestation
- Abnormalities of nesting or nursing behaviour - Oestrous cyclicity (parental animals):
- Not examined
- Sperm parameters (parental animals):
- Not examined
- Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: Yes to 8 pups/litter (4/sex where possible); excess pups were killed and discarded.
PARAMETERS EXAMINED
- F1 and F2 offspring: number and sex of pups, live births, postnatal mortality, clinical condition, body weight, pinna unfolding, tooth eruption, eye opening, pupillary reflex and auditory response
GROSS EXAMINATION OF DEAD PUPS:
- yes, for external and visceral abnormalities - Postmortem examinations (parental animals):
- SACRIFICE
- Males: After the last litter of each generation was weaned.
- Females: After the lactation period or approximately day 26 post-coitum.
GROSS NECROPSY: Yes
- The uteri of apparently non-pregnant females were immersed in 10% ammonium sulphide to reveal evidence of implantations.
- Gross necropsy consisted of external and internal examinations including the cervical, thoracic, and abdominal viscera.
ORGAN WEIGHTS: Yes (all parental animals)
- organs weighed: epididymides, kidneys, liver, testes
HISTOPATHOLOGY: Yes
- Tissues examined (control and high dose animals only): Bile duct, cervix, coagulating gland, epididymides, kidneys, liver, ovaries, pituitary, prostate, seminal vesicles, stomach, testes, uterus, vagina, any macroscopically abnormal tissue - Postmortem examinations (offspring):
- SACRIFICE
- The F1 offspring not selected as parental animals and all F2 offspring were sacrificed at 21 days of age.
GROSS NECROPSY
- External and internal examinations including the cervical, thoracic, and abdominal viscera.
HISTOPATHOLOGY / ORGAN WEIGTHS: No - Statistics:
- Statistical analyses used the SAS software package release 6.03.
Analysis of variance with one factor treatment followed by the Student-Newman-Keuls test for multiple group comparisons: body weight, body weight gain, litter weight, organ weights, food consumption.
Analysis of variance with one factor treatment based on taking the ranks of the variables and followed by the Student-Newman-Keuls test for multiple group comparisons: mating performance, duration of gestation, mean pup weight, pup number, live birth index, viability indices, weaning index, pinna unfolding, hair growth, incisor eruption, eye opening. - Reproductive indices:
- For both generations the parental reproductive performance was assessed and the following calculated: mating performance, insemination index, fecundity index, fertility index, gestation index
- Offspring viability indices:
- Live birth index, pup viability index, weaning index and sex ratio.
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- no effects observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Tables 1 & 2
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Tables 1 & 2
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- Test substance intake: Table 3
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- no effects observed
Details on results (P0)
P generation: Body weights of males and females reduced in a dose dependent manner at dose levels of 500 ppm and 1000 ppm during the premating phase. Body weights of females during gestation and lactation was generally similar in all groups.
F1 generation: Decreased weaning weights on day 21 post-partum resulted in lower initial F1 parental body weights at 500 and 1000 ppm. Thereafter during the premating, gestation and lactation periods body weights at 500 and 1000 ppm were dose-dependently decreased.
FOOD CONSUMPTION (PARENTAL ANIMALS):
P generation: There was a marginal reduction in food consumption for males at 1000 ppm during the premating phase. For females in all groups, food consumption was similar during the premating, gestation and lactation periods.
F1 generation: Food consumption was slightly reduced at 1000 ppm for males and females during the premating phase and for females during gestation and lactation.
TEST SUBSTANCE INTAKE (PARENTAL ANIMALS):
Dietary concentrations of 10, 50, 500 and 1000 ppm are calculated to be equivalent to 0.8, 4, 40 and 80 mg/kg bw/day respectively based on food intake and body weight during the pre-mating periods.
Effect levels (P0)
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- fertility and reproductive performance
- Effect level:
- 1 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: highest dose tested equivalent to 80 mg/kg bw/day
- Dose descriptor:
- NOAEL
- Remarks:
- toxicity
- Effect level:
- 50 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: equivalent to 4 mg/kg bw/day. Reduced parental body weight and food consumption, reduced pup weight at weaning, at higher doses.
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- no effects observed
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Table 4
- Sexual maturation:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Histopathological findings:
- not examined
Details on results (F1)
F1a: Mean pup weights at 1000 ppm were significantly reduced on day 14 and mean pup weights at 500 and 1000 ppm were reduced on day 21.
F2a: Mean pup weights at 1000 ppm were significantly reduced on day 21.
PHYSICAL & FUNCTIONAL DEVELOPMENT (OFFSPRING):
There were no treatment-related effects on the physical development (incisor eruption, pinna unfolding, eye opening) of the F1a of F2a pups or on the outcome of the functional tests (pupillary reflex, auditory response) on either generation.
Effect levels (F1)
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- fertility and reproductive performance
- Generation:
- F1
- Effect level:
- 1 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: highest dose tested equivalent to 80 mg/kg bw/day
- Dose descriptor:
- NOAEL
- Remarks:
- toxicity
- Generation:
- F1
- Effect level:
- 50 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: equivalent to 4 mg/kg bw/day. Reduced parental body weight and food consumption, reduced pup weight at weaning, at higher doses.
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
Table 1: Intergroup comparison of mean body weight change (g) prior to and during mating
Dietary concentration of CGA154281 (ppm) |
||||||||||
Males |
Females |
|||||||||
0 |
10 |
50 |
500 |
1000 |
0 |
10 |
50 |
500 |
1000 |
|
P generation |
||||||||||
Days 1-99 |
307.9 |
292.5 |
298.3 |
277.7* |
268.0** |
115.2 |
109.5 |
108.6 |
104.2* |
94.7** |
F1 generation |
||||||||||
Days 1-99 |
401.6 |
404.2 |
399.8 |
369.5 |
352.9** |
193.6 |
190.1 |
182.5 |
179.5 |
168.8** |
* Statistically significant difference from control group mean, p<0.05 ** Statistically significant difference from control group mean, p<0.01 |
Table 2: Intergroup comparison of female body weight change (g) during pregnancy and lactation
Body Weight Change |
Dietary concentration of CGA154281 (ppm) |
||||
P Generation |
0 |
10 |
50 |
500 |
1000 |
Gestation days 0-20 |
106.20 |
111.47 |
104.51 |
108.29 |
108.88 |
Lactation days 1-21 |
24.69 |
30.59 |
19.70 |
25.77 |
40.07* |
F1 Generation |
|||||
Gestation days 0-20 |
117.01 |
114.10 |
110.48 |
105.10* |
99.63** |
Lactation days 1-21 |
28.41 |
42.93** |
30.73 |
37.00 |
40.88* |
P<0.05 * difference from control statistically significant
Table 3: Overall mean dose received (mg/kg/day)
Generation |
Sex |
Dietary concentration of CGA154281 (ppm) |
|||
10 |
50 |
500 |
1000 |
||
P Parents |
Males |
0.66 |
3.44 |
33.7 |
66.6 |
Females |
0.79 |
3.99 |
39.9 |
79.7 |
|
Mean |
0.73 |
3.72 |
36.8 |
73.2 |
|
F1 Parents |
Males |
0.80 |
4.07 |
44.0 |
86.4 |
Females |
0.89 |
4.42 |
47.6 |
90.5 |
|
Mean |
0.85 |
4.25 |
45.8 |
88.5 |
|
P + F1 Parents |
Mean |
0.79 |
3.99 |
41.3 |
80.1 |
Table 4: Pup body weights (g)
Pup body weight (g) |
Dietary concentration of CGA154281 (ppm) |
||||
F1a |
0 |
10 |
50 |
500 |
1000 |
day 1 post partum |
6.3 |
6.2 |
6.2 |
6.1 |
6.0 |
day 4 post partum |
8.2 |
7.9 |
8.2 |
7.7 |
7.5 |
day 7 post partum |
11.9 |
11.3 |
11.7 |
10.7 |
10.7 |
day 14 post partum |
24.4 |
23.5 |
23.3 |
22.3 |
21.8* |
day 21 post partum |
40.9 |
39.6 |
38.4 |
36.3* |
35.8* |
F2a |
|||||
day 1 post partum |
6.2 |
5.8 |
6.0 |
5.8 |
5.8 |
day 4 post partum |
7.9 |
7.6 |
8.3 |
7.3 |
7.6 |
day 7 post partum |
11.8 |
11.7 |
12.5 |
11.1 |
11.6 |
day 14 post partum |
25.2 |
24.7 |
25.5 |
23.4 |
23.0 |
day 21 post partum |
42.4 |
41.2 |
41.8 |
40.1 |
37.4* |
P<0.05 * difference from control statistically significant by analysis of variance followed by Student-Newman-Keuls test
Applicant's summary and conclusion
- Conclusions:
- Dietary administration of 500 or 1000 ppm CGA154281 over two generations resulted in lower body weights of the adult animals during the pre-mating period and lower body weights of the pups at weaning. There was no effect of CGA1545281 on fertility or reproductive performance in either generation and no effect on the number and viability of the pups born.
The NOAEL for toxicity was 50 ppm, corresponding to a mean daily intake of 4 mg/kg bw/day. The NOAEL for fertility and general reproductive performance was 1000 ppm corresponding to a mean daily intake of 80 mg/kg bw/day. - Executive summary:
- Groups of 25 male and 25 female Sprague-Dawley rats were given CGA154281 in the diet at nominal concentrations of 0, 10, 50, 500, and 1000 ppm continuously over two generations from the start of treatment until necropsy. After a pre-mating period, the P parental animals were mated and allowed to litter and to rear the F1a pups to weaning. After a 14 week post weaning maturation period the selected F1 parental animals were mated, allowed to litter and to rear the F2a pups to weaning. At 500 and 1000 ppm, effects in the P and Fl parental animals included reduced body weight and food consumption. For pups, mean body weight was significantly reduced on day 21 for both F1a and F2a pups at 1000 ppm and for F1a pups at 500 ppm. There were no adverse effects of 10 or 50 ppm CGA154281. There was no effect on fertility or general reproductive performance in either of the two generations at any dietary concentration of CGA154281 in this study.
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