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EC number: 265-745-8 | CAS number: 65405-77-8
- 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
- Nanomaterial dustiness
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- Nanomaterial pour density
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- Nanomaterial catalytic activity
- 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

Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 5th May 1994 to 31st May 1994
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results. The study report was conclusive, equivalent to a valid guidelines and the study was conducted under GLP conditions. The study was performed with test material being used to support the substance on the basis of read-across.
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
Refer to justification in seciton 13
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 996
- Report date:
- 1996
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.31 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 25485-88-5
- Cas Number:
- 25485-88-5
- IUPAC Name:
- 25485-88-5
- Reference substance name:
- Benzoic acid, 2-hydroxy-, cyclohexyl ester
- IUPAC Name:
- Benzoic acid, 2-hydroxy-, cyclohexyl ester
- Test material form:
- liquid
- Details on test material:
- - Name of test material (as cited in study report): CHS/Cyclohexylsalicilate
- Physical state: colurless liquid
- Storage condition of test material: room temperature
- Molecular formula (if other than submission substance): C13H16O3
- Molecular weight (if other than submission substance): 220.27
- Smiles notation (if other than submission substance): C(=O)(c1c(O)cccc1)OC1CCCCC1
- Structural formula attached as image file (if other than submission substance): see Fig. 1
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Wiga GmbH, D-97633 Sluzfeld, Germany
- Age at study initiation: 8 weeks
- Weight at study initiation: mean approximately 214 g
- Housing: Individually in Makrolon Type M3 cage
- Diet: pelleted Altromin Maintenance Diet 1324 ad libitum
- Water: tap water ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 21-25 °C
- Humidity: 44-75%:
- Air changes: 10-15 per hr
- Photoperiod: 12 hrs dark / 12 hrs light
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: arachadis oil
- Details on exposure:
- VEHICLE
- Concentration in vehicle: 0% (group 1), 0.8% (group 2), 2.4% (group 3) and 7.2% (group 4).
- Amount of vehicle (if gavage): 5 mL/kg bw - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The test material in the vehicle was analysed once in the study. The concentrations of the test material in the vehicle were dtermined by HPLC the concentrations found are as follows:
0.4 g/50 mL (eq. 40 mg/kg) = 0.415 g/50 mL ± 0.007
1.2 g/50 mL (eq. 120 mg/kg) = 1.260 g/50 mL ± 0.014
3.6 g/50 mL (360 mg/kg) = 3.720 g/50 mL ± 0.014 - Details on mating procedure:
- Mated animals were provided by the supplier.
- Duration of treatment / exposure:
- Days 6 to 15 of the gestation period.
- Frequency of treatment:
- Daily
- Duration of test:
- Until day 20 post coitum
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Remarks:
- Group 1
- Dose / conc.:
- 40 mg/kg bw/day (nominal)
- Remarks:
- Group 2
- Dose / conc.:
- 120 mg/kg bw/day (nominal)
- Remarks:
- Group 3
- Dose / conc.:
- 360 mg/kg bw/day (nominal)
- Remarks:
- Group 4
- No. of animals per sex per dose:
- 24
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least twice daily (working days)
BODY WEIGHT: Yes
- Time schedule for examinations: day 0, 6, 16 and 20 post coitum.
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 20
- Organs examined: gross macroscopic examination of all maternal organs with emphasis on the uterus, uterine contents, position of the foetuses in the uterus and the number of corpora lutea. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: half per litter
- Skeletal examinations: Yes: half per litter
- Head examinations: Yes: half per litter - Statistics:
- The following statistical methods were used:
- if the variables could be assumed to follow a normal distribution, the Dunnett-test, based on pooled variance, was applied for the comparison between the treated groups and the control group.
- the Steel-test was applied when the data could not be assumed to follow a normal distribution.
- Fisher's exact test for 2x2 tables was applied if the variables could be dichotomised without the loss of information (Bonferroni-Holm-corrected). - Indices:
- Body weight gains of the maternal animals from days 0-6, 6-16, 16-20 and 6-20 post coitum were calculated.
The individual placentae and the body weight gains of the foetuses were recorded.
For the reproduction data, group mean values were calculated on a per dam basis and a percentage group basis. Only dams with live foetuses on day 20 post coitum were included in the calculations.
Mean foetal weights were calculated from the individual foetal weights on a per litter basis/group.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Gross pathological findings:
- no effects observed
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Effects on pregnancy duration" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsMaternalAnimals.MaternalDevelopmentalToxicity.EffectsOnPregnancyDuration): no effects observed - Changes in number of pregnant:
- no effects observed
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
No deaths occurred in the controls or any of the test groups.
No treatment-related symptoms were observed in all treatment groups.
Body weights of the pregnant females were essentially similar in all groups. Mean corrected body weight gain of groups 3 and 4 were statistically different when compared to the group 1.
No treatment-related differences were noted between the mean reproduction data of the groups 2 - 4 when compared to group 1. In groups 2-4, the sum of post-implantation loss was decreased (level 5%). In groups 2 and 4, the sum of the total embryonic deaths was decreased (level 5%) and in group 3 (level 1%). In the groups 2 and 4, the sum of the total foetuses was increased (level 5%) and in the group 3 (level 1%). These findings were considered to be incidental and within the normal range.
No macroscopic changes were noted in the dams of any of the groups.
Effect levels (maternal animals)
- Dose descriptor:
- NOEL
- Effect level:
- 360 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Maternal abnormalities
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Skeletal malformations:
- effects observed, non-treatment-related
- Visceral malformations:
- effects observed, non-treatment-related
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
The weights of the live foetuses exhibited no significant differences on a litter and individual basis i.e. mean weight between the control group and the treatment groups.
The weights of the placenta showed no significant differences between the control and treatment groups. The mean value of the uteri, including content, showed an increase in groups 2 -4 (level 5%).
The sex ratio of the foetuses was not affected by treatment with the test material.
No macroscopical findings were noted at external examination of the foetuses which were considered to be an effect of the treatment with the test material. In group 1, were noted a beginning hydrops, spina bifida, exencephalia, micrognathia and one foetus with paleness. In group 3 were noted a hydrops, missing tail and one foetus with missing mandibula, no orifice and two dead foetuses. In group 4 were noted two foetuses with one common placenta.
Visceral examination:
Group 1: 140 examined foetuses
9 hydronephrosis
12 ureter waved
9 ureter dilatation
2 bronchial tree dilated
1 runt
1 hydrocephalus internus
Group 2: 152 examined foetuses
21 hydronephrosis
12 ureter waved
9 ureter dilatation
Group 3: 152 examined foetuses
16 hydronephrosis
16 ureter waved
8 ureter dilatation
2 gut protrusion our of abdomen (artefact)
Group 4: 162 foetuses examined
12 hydronephrosis
2 ureter waved
5 ureter dilatation
1 hematoma periorbital
1 runt
The visceral examination of the preserved foetuses did not reveal and treatment-related abnormalities.
Skeletal examination of foetuses:
General observations:
The statistically significant differences were considered to be incidental. The findings concerning the ossification of the foetal skeleton showed no dose-relationship i.e. there was no indication for an abnormal ossification of the foetal skeleton, skull bones, sternebrae and coccygeal vertebrae in the treated groups compared to the controls.
Retardations:
No relevant findings in any of the groups.
Variations:
The statistical analysis of the findings sternebrae, incompletely ossified, ossified or abnormally ossified, does not indicate a dose-relationship i.e. no disturbance of the ossification of the sternebrae could be observed in any of the treated groups when compared to the controls. Concerning the number of ribs, the statistically significant difference was considered to be incidental.
Malformations:
Group 1 - one case (skull bones irregular placed, micrognathia, vertebrae (cervical/thoracal/lumbal/sacral) cleaved), coccygeal vertebrae non ossified.
Group 2 - no variations
Group 3 - two cases (micrognathia; skull bones partially ossified, vertebral column caudal non ossified)
Group 4 - no variations
Effect levels (fetuses)
open allclose all
- Dose descriptor:
- NOEL
- Effect level:
- 360 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: teratogenicity
- Dose descriptor:
- NOEL
- Effect level:
- 360 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: embryotoxicity
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 1: Summary of performance of mated females
Group |
1 |
2 |
3 |
4 |
Dose (mg/kg) |
0 |
40 |
120 |
360 |
No. of mated females |
24 |
24 |
24 |
24 |
No. of pregnant females |
23 |
23 |
23 |
22 |
No. of mortalities |
0 |
0 |
0 |
0 |
No. of females included in statistical analysis (females with live foetuses at termination) |
23 |
23 |
23 |
22 |
Table 2: Mean differences in dam body weights
Days post coitum |
|
||||
Group (mg/kg) |
0 - 6 (% gain) |
6 - 16 (% gain) |
16 - 20 (% gain) |
6 - 20 (% gain) |
Corrected body weight gain (%) |
1 (0) |
49.0 (22.6) |
83.3 (31.4) |
56.1 916.1) |
139.3 (52.5) |
22.9 |
2 (40) |
50.0 (23.2) |
86.8 (32.7) |
59.3 (16.9) |
146.2 (55.1) |
21.7 |
3 (120) |
50.4 (23.4) |
83.2 (31.3) |
59.6 (17.1) |
142.8 (53.7) |
19.5 |
4 (360) |
50.2 (24.2) |
80.0 (31.0) |
56.2 (16.6) |
136.2 (52.8) |
17.6 |
Table 3: Summary of dam body weights
Day post coitum |
Group 1 (0 mg/kg) |
Group 2 (40 mg/kg) |
Group 3 (120 mg/kg) |
Group 4 (360 mg/kg) |
0 |
216.6 |
215.2 |
215.6 |
207.5 |
6 |
265.6 |
265.2 |
266.0 |
257.7 |
16 |
348.9 |
352.0 |
349.2 |
337.7 |
20 |
405.0 |
411.4 |
408.8 |
393.9 |
Table 4: Summary of reproduction data (dams with live foetuses)
|
Group 1 (0 mg/kg) |
Group 2 (40 mg/kg) |
Group 3 (120 mg/kg) |
Group 4 (360 mg/kg) |
Number of dams |
23 |
23 |
23 |
22 |
Corpora lutea |
382 |
385 |
378 |
381 |
Mean |
16.6 |
16.7 |
16.4 |
17.3 |
S.D. |
1.8 |
2.3 |
2.3 |
1.9 |
Implantation sites |
329 |
346 |
335 |
333 |
% of corpora lutea |
86.1 |
89.9 |
88.6 |
87.4 |
Mean |
14.3 |
15.0 |
14.6 |
15.1 |
S.D. |
2.1 |
2.0 |
2.3 |
1.6 |
Pre-implantation loss |
53 |
39 |
43 |
48 |
% of corpora lutea |
13.9 |
10.1 |
11.4 |
12.6 |
Post-implantation loss |
35 |
17 # |
16 # |
19 # |
% of implantation sites |
10.6 |
4.9 |
4.8 |
5.7 |
Embryonic deaths: total |
35 |
17 # |
14 ## |
19 # |
Embryonic resorptions |
34 |
13 |
11 |
14 |
% of implantation sites |
10.3 |
3.8 |
3.3 |
4.2 |
Mean |
1.5 |
0.6 |
0.5 |
0.6 |
S.D. |
1.6 |
0.6 |
0.8 |
0.8 |
Foetal resorptions |
1 |
4 |
3 |
5 |
% of implantation sites |
0.3 |
1.2 |
0.9 |
1.5 |
Mean |
0.0 |
0.2 |
0.1 |
0.2 |
S.D. |
0.2 |
0.4 |
0.3 |
0.4 |
Foetuses |
|
|
|
|
No. of dams |
23 |
23 |
23 |
22 |
Total foetuses |
294 |
329 # |
321 ## |
314 # |
% of implantation sites |
89.4 |
95.1 |
95.8 |
94.3 |
Mean |
12.8 |
14.3 |
13.9 |
14.3 |
S.D. |
2.6 |
2.1 |
2.2 |
1.9 |
Live foetuses |
294 |
329 |
319 |
314 |
Dead foetuses |
0 |
0 |
2 |
0 |
Malformed foetuses |
1 |
0 |
2 |
0 |
% of foetuses |
0.3 |
0.0 |
0.6 |
0.0 |
Mean |
0.0 |
0.0 |
0.1 |
0.0 |
S.D. |
0.2 |
0.0 |
0.3 |
0.0 |
Sex of foetuses |
|
|
|
|
Total males |
132 |
146 |
154 |
154 |
% of foetuses |
44.9 |
44.4 |
48.0 |
49.0 |
Mean |
5.7 |
6.3 |
6.7 |
7.0 |
S.D. |
2.1 |
2.7 |
2.2 |
1.9 |
Total females |
162 |
183 |
165 |
160 |
% of foetuses |
55.1 |
55.6 |
51.4 |
51.0 |
Mean |
7.0 |
8.0 |
7.2 |
7.3 |
S.D. |
1.5 |
2.8 |
1.8 |
2.2 |
Weights of live foetuses (litter basis) |
|
|
|
|
Males and females |
|
|
|
|
N (litters) |
23 |
23 |
22 |
22 |
Mean |
4.1 |
4.2 |
4.6 |
4.4 |
S.D. |
0.7 |
0.8 |
0.9 |
0.8 |
Runts |
|
|
|
|
N (litters) |
3 |
1 |
2 |
2 |
Mean |
1.0 |
1.0 |
1.0 |
1.0 |
S.D. |
0.0 |
0.0 |
0.0 |
0.0 |
Males |
|
|
|
|
N (litters) |
23 |
23 |
23 |
22 |
Mean |
4.2 |
4.3 |
4.7 |
4.5 |
S.D. |
0.7 |
0.8 |
1.0 |
0.8 |
Runts |
|
|
|
|
N (litters) |
2 |
0 |
1 |
0 |
Mean |
1.0 |
0.0 |
1.0 |
0.0 |
S.D. |
0.0 |
0.0 |
0.0 |
0.0 |
Females |
|
|
|
|
N (litters) |
23 |
23 |
23 |
22 |
Mean |
4.1 |
4.1 |
4.5 |
4.3 |
S.D. |
0.7 |
0.7 |
0.9 |
0.7 |
Runts |
|
|
|
|
N (litters) |
1 |
1 |
1 |
2 |
Mean |
1.0 |
1.0 |
1.0 |
1.0 |
S.D. |
0.0 |
0.0 |
0.0 |
0.0 |
Weights of placenta (litter basis) |
|
|
|
|
Males and females |
|
|
|
|
N (litters) |
23 |
23 |
23 |
22 |
Mean |
0.6 |
0.6 |
0.6 |
0.6 |
S.D. |
0.1 |
0.1 |
0.1 |
0.1 |
Weights of uteri (dam basis) |
|
|
|
|
N (dams) |
23 |
23 |
23 |
22 |
Mean |
78.2 |
89.2 * |
91.6 * |
90.7 * |
S.D. |
16.2 |
11.7 |
18.4 |
14.1 |
# Fisher's Exact test (Bonferroni-Holm-corrected) significant at level 5% (#), 1% (##)
* Dunnett test based on pooled variance significant at level 1%
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the test, the repeat oral administration of the test material to pregnant rats showed no symptoms of cumulative toxicity or any embryotoxic or teratogenic potential up to 360 mg/kg bw/day.
- Executive summary:
The test material was tested at dose levels of 0 (group 1), 40 (group 2), 120 (group 3) and 360 (group 4) mg/kg bw. Each group consisted of at least 24 female rats (pregnant rats: 23 in groups 1 to 3 and 22 in group 4). The test material was administered orally by gavage daily from days 6 to 15 of gestation. A standard dose volume of 5 mL/kg bw was used. Control animals were dosed with the vehicle alone over the same period.
Clinical conditions and reactions to treatment were recorded at least once daily. Body weights were recorded for days 0, 6, 16 and 20 of gestation. All surviving females were sacrificed on day 20 of gestation and the foetuses were removed by caesarean section. At necropsy, the females were examined macroscopically and live foetuses were weighed, sexed and examined for visceral and skeletal abnormalities.
No mortality was observed at any of the dose levels tested. No compound-related symptoms were observed in all treatment groups. Maternal body weight gain was not affected by treatment. No treatment-related abnormalities were found at necroscopy of the females. All females had viable foetuses. Pre-implantation loss, post-implantation loss, mean numbers of resorptions, embryonic deaths and total foetuses were not affected by treatment.
Mean foetal placental and uterus weights were not affected by treatment; foetal sex ratio was comparable in all group. No treatment-related foetal abnormalities were found at necroscopy; there were no treatment-related effects in the reproduction data. The examined foetuses showed no treatment-related malformations. The number of skeletal variations showed no treatment-related deviations. The number of skeletal ossifications in both the test groups and the control group were considered to be similar. The number of visceral variations in both the test groups and the control group were considered to be similar.
The results of the study show that repeat oral administration of the test material (days 6 - 15 post coitum) to pregnant rats caused no symptoms of cumulative toxicity up to 360 mg/kg bw/day. The test material reveals no embryotoxic or teratogenic potential at dose levels up to 360 mg/kg bw/day.
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