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EC number: 609-256-3 | CAS number: 365400-11-9
- Life Cycle description
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- Endpoint summary
- Appearance / physical state / colour
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- 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
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- Exposure related observations in humans
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- Additional toxicological data

Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 08 Oct 2003 - 30 Jan 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- adopted in 2001
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.31 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- adopted in 1992
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3700 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- adopted in 1998
- Qualifier:
- according to guideline
- Guideline:
- other: M.A.F.F. in Japan, notification 12 Nousan N°8147 guideline
- Version / remarks:
- adopted in 2000
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Groupe Interministeriel des Produits Chimiques, Paris, France
- Limit test:
- no
Test material
- Reference substance name:
- (5-hydroxy-1,3-dimethyl-1H-pyrazol-4-yl)[2-(methylsulfonyl)-4-(trifluoromethyl)phenyl]methanone
- EC Number:
- 609-256-3
- Cas Number:
- 365400-11-9
- Molecular formula:
- C14H13F3N2O4S
- IUPAC Name:
- (5-hydroxy-1,3-dimethyl-1H-pyrazol-4-yl)[2-(methylsulfonyl)-4-(trifluoromethyl)phenyl]methanone
Constituent 1
- Specific details on test material used for the study:
- STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Solubility and stability of the test substance in the solvent/vehicle: analytically demonstrated
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Remarks:
- Crl: CD (SD)
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, St Germain-sur-l'Arbresle, France
- Weight at study initiation: 226 - 308 g
- Fasting period before study: no
- Housing: individually in suspended, stainless steel, wire mesh cages
- Diet: certified rodent pelleted and irradiated diet A04C-10 from S.A.F.E. (Scientific Animal Food and Engineering, Epinay-sur-Orge, France, ad libitum
- Water: municipal water, ad libitum
- Acclimation period: 19 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 40 - 70
- Air changes (per hr): target of 15 (not monitored)
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 28 Oct 2003 To: 18 Nov 2003
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: 0.5% aqueous solution of methylcellulose 400 (Fluka, Mulhouse, France)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Formulations were prepared twice during the study and stored at approximately 5°C (± 3°C).
The suspensions were mixed continuously before and during treatment with an electromagnetic stirrer.
VEHICLE
- Amount of vehicle (if gavage): 10 mL/kg bw - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis of dose formulations was performed using High Performance Liquid Chromatography (HPLC) with UV detection.
Homogeneity of the suspensions was checked on the first formulation (F1) for the lowest and the highest concentrations (1 and 30 g/L). In addition, the intermediate concentration of the first formulation (F1) and all concentrations of the second formulation (F2) were checked. Stability of the test substance in suspension in the vehicle at concentrations of 0.1 and 250 g/L was determined in a previous range-finding study, and was found to be stable for 29 days under similar conditions to those of the current study.
Homogeneity and concentration checks of dosing suspensions were between 91 and 104% of nominal values, which is within the in-house target range of 90 to 110% of nominal. - Details on mating procedure:
- - Impregnation procedure: cohoused with stock males of the same strain and same supplier
- M/F ratio per cage: 1/1
- Verification of same strain and source of both sexes: yes
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 0 of pregnancy - Duration of treatment / exposure:
- Gestation day (GD) 6 to 20
- Frequency of treatment:
- once daily
- Duration of test:
- 15 days of treatment
Doses / concentrationsopen allclose all
- Dose / conc.:
- 10 mg/kg bw/day
- Dose / conc.:
- 100 mg/kg bw/day
- Dose / conc.:
- 300 mg/kg bw/day
- No. of animals per sex per dose:
- 25 females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The range of doses was selected in agreement with the Sponsor Representative and based on results obtained in a range-finding study, where pregnant rats received 0, 25, 75, 250, 500 or 800 mg/kg bw/day. The high dose of 300 mg/kg bw/day was expected to cause slight maternal toxicity and possibly slight developmental toxicity, but not exceed a Maximum Tolerated Dose (MTD). The mid dose of 100 mg/kg bw/day was considered to be a suitable intermediate dose, should the high dose prove to be too high. The low dose of 10 mg/kg bw/day was expected to be a clear No Observed Effect Level (NOEL) for both maternal and developmental toxicity.
- Rationale for animal assignment (if not random): The females were assigned to control and treated groups using a body weight procedure for each day of pairing. Body weight means were checked after the mating period to ensure similar means among all groups.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: All animals were examined from GD 0 through GD 21. All cages were checked for dead or moribund animals twice daily, once in the morning and again in the afternoon (except at weekends and public holidays when checking was carried out once daily). Clinical signs were recorded once daily.
DETAILED CLINICAL OBSERVATIONS: No
BODY WEIGHT: Yes
- Time schedule for examinations: GD 0, 6, 8, 10, 12, 14, 16, 18 and 21.
FOOD CONSUMPTION: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/animal/day: Yes
WATER CONSUMPTION: No
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 21
- Organs examined: visceral organs, the number of ribs recorded and the kidney and urinary bladder examined for the presence of gritty material
OTHER:
- Liver weights were recorded and the liver was preserved in 10% neutral buffered formalin, but apparently no histopathological examination was conducted - 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
- Other: Uterine horn(s) without visible implantations were immersed in a 10% solution of ammonium sulfide according to the SALEWSKI method in order to visualize any sites which were not apparent - 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:
- Bartlett test was performed to compare the homogeneity of group variances. If the Bartlett test was not significant (p > 0.05), means were compared using the analysis of variance (ANOVA). If the ANOVA was not significant (p > 0.05), the group means were considered homogeneous and no further analysis was performed. If the ANOVA was significant (p ≤ 0.05), a Dunnett test (2-sided) was performed. If the Bartlett test was significant (p ≤ 0.05) for body weight change and corrected body weight change, a Kruskal-Wallis test was performed. If the Kruskal-Wallis test was not significant (p > 0.05), group means were considered homogeneous and no further analysis was performed. If the Kruskal-Wallis test was significant (p ≤ 0.05), means of exposed groups were compared to the mean of the control group using the Dunn test (2-sided).
If the Bartlett test was significant (p ≤ 0.05) for food consumption or for liver weight, a log transformation of the data was performed.
-If the Bartlett test on log transformed data was not significant (p > 0.05), means were compared using the ANOVA on log transformed data. If the ANOVA was not significant (p > 0.05), the group means were considered homogeneous and no further analysis was performed. If the ANOVA was significant (p ≤ 0.05), a Dunnett test (2-sided) on log transformed data was performed.
- If the Bartlett test on log transformed data was significant even after transformation (p ≤ 0.05), group means were compared using the non-parametric Kruskal-Wallis test. If the Kruskal-Wallis test was not significant (p > 0.05), the group means were considered homogeneous and no further analysis was performed. If the Kruskal-Wallis test was significant (p ≤ 0.05), means of exposed groups were compared to the mean of the control group using the Dunn test (2-sided).
For fetal sex and fetal death status, groups were compared using the Chi-square test for fetal sex parameter, using the Fisher Exact test (2-sided) for fetal death status parameter. - Indices:
- - Pre-implantation loss
- Post-implantation loss
- Number of live fetuses
- Number of dead fetuses
- Percentage of dead fetuses per litter
- Percentage of male fetuses per litter
- Mean fetal body weight per litter
- Mean fetal body weight per group
- Mean fetal body weight per sex
- Percentage of fetuses affected per litter
- Mean percentage of fetuses affected per group - Historical control data:
- Historical control data for six studies conducted in the laboratory in Sprague-Dawley CD rats are available and presented in the report.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- In the high dose group, all females had increased salivation, 7/25 had intense yellow urine, 5/25 had vaginal discharge and 8/25 anogenital soiling, on one or more occasions. In the mid dose group, 7/25 females had increased salivation and 1/25 females had brown soiling around the anogenital region, on at least one occasion. No treatment-related signs were observed at the low dose.
All other clinical signs were considered to be incidental and not related to treatment. - Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One control female was killed in a moribund condition on GD 17 due to accidental trauma.
There were no other mortalities during the course of the study. - Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Body weight gain was reduced by 84% (p ≤ 0.01) at 300 mg/kg bw/day and by 53% (p ≤ 0.05) at 100 mg/kg bw/day between GD 6 to 8, when compared with the controls. Thereafter, body weight gain between each interval phase was essentially comparable between the groups, though the initially observed reduction in absolute body weight observed at the two highest dose levels was maintained throughout treatment.
No effect on body weighs was observed at 10 mg/kg bw/day.
Maternal corrected body weight gain was 16% less (p ≤ 0.05) at 300 mg/kg bw/day than in the control group, but was unaffected by treatment at the lower two dose levels. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Food consumption was reduced between GD 6 and 16 at 300 mg/kg bw/day, compared with controls. The effect was most pronounced between GD 6 to 8, when there was a 15% reduction (p ≤ 0.01) and GD 8 to 10 when the reduction was 7% (p ≤ 0.05).
At 100 and 10 mg/kg bw/day, food consumption was comparable with the controls throughout treatment. - 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):
- There was a minimal increase in liver weight of 6% (p ≤ 0.05) at 300 mg/kg bw/day and a trend towards increased liver weight (+5%, not statistically significant) at 100 mg/kg bw/day.
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- One high dose female had yellow sediment in the kidney with a gritty content found in the urinary bladder.
The few other macroscopic findings were considered to be incidental as they did not occur in a dose-related manner and are common findings in this age and strain of rat. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
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
- Changes in pregnancy duration:
- not examined
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Effects on pregnancy duration" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsMaternalAnimals.MaternalDevelopmentalToxicity.EffectsOnPregnancyDuration): not examined - Changes in number of pregnant:
- no effects observed
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- Grossly enlarged placentas were observed for two and four fetuses from the same litter in the mid and high dose, respectively.
Effect levels (maternal animals)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 10 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: no adverse effects observed at 10 mg/kg bw/day
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- 100 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- clinical signs
- food consumption and compound intake
Maternal abnormalities
- Abnormalities:
- no effects observed
- Description (incidence and severity):
- No organ changes were noted.
Results (fetuses)
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Mean fetal body weights (calculated by sex and combined sex) were reduced by 5 - 6% at 300 mg/kg bw/day. The change was statistically significant (p ≤ 0.01) for each parameter. At 100 mg/kg bw/day, there was 2% reduction for each parameter compared with controls, the effect being statistically significant (p ≤ 0.05) for male body weights.
Mean fetal body weights were unaffected by treatment at 10 mg/kg bw/day.
Migrated Data from removed field(s)
Field "Fetal/pup body weight changes" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.FetalPupBodyWeightChanges): not examined - Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- At 300 mg/kg bw/day, there were four fetuses from two different litters (3 fetuses from one litter and 1 fetus from a second litter), with the malformation hindpaw polydactyly. The three fetuses from the same litter at 300 mg/kg/day with hindpaw polydactyly also had an anomaly consisting of a combination of forelimb hyperflexion, digits on forepaws misshapen and digits on both forepaws and hindpaws malpositioned. The low incidence of this finding, the lack of other related findings in either forepaws or hindpaws in further fetuses, and the lack of ossification of the extra phalanges in the 2 fetuses of these 4 which were examined by skeletal staining suggest that this malformation was due to chance and was not an indication of a teratogenic potential of the test substance.
The only other malformation observed was a single fetus with an umbilical hernia at the low dose, which was therefore considered to be incidental. - Skeletal malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- The only malformations observed were in two fetuses from the same litter at 300 mg/kg bw/day, which consisted of a combination of short tibia and femur, supernumerary cartilaginous phalanges, fused cartilage for a number of metatarsals and phalanges, and unossified 5th metatarsal. These two fetuses were two of the four fetuses which had the external observations hindpaw polydactyly. At such a low incidence these findings are considered to be incidental.
The number of other anomalies noted was few and either occurred in a non dose-related manner, in isolation or were inside the in-house historical control range and are therefore considered to be chance findings.
At 300 mg/kg bw/day, the following variants occurred at a higher incidence than in the controls: enlarged fontanelle, 5th or 6th sternebra unossified, extra ossification point on the 14th thoracic vertebra, and incomplete ossification of the 5th metacarpal. At both 300 and 100 mg/kg bw/day, the following variants occurred with a higher frequency than in controls and in a dose-related manner: incompletely ossified or bipartite 5th and/or 6th sternebra, 3rd and/or 4th proximal phalanges of the forepaw unossified, and short 14th thoracic rib. At all three dose levels tested the following variants were increased in a dose-related manner, though the effects at 10 mg/kg bw/day were slight: 7th cervical centrum unossified, 1st metatarsal unossified, and less than 9 sacrocaudal vertebrae ossified.
No other variants were considered to be related to treatment as they occurred at a similar frequency in the control group, did not occur in a dose-related manner or were within in-house historical control ranges. - Visceral malformations:
- no effects observed
- Other effects:
- no effects observed
Effect levels (fetuses)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 10 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: no adverse effects were noted at 10 mg/kg bw/day
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- 100 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- fetal/pup body weight changes
- skeletal malformations
Fetal abnormalities
- Key result
- Abnormalities:
- no effects observed
- Description (incidence and severity):
- No treatment-related fetal malformations were noted.
Overall developmental toxicity
- Key result
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 100 mg/kg bw/day
- Treatment related:
- yes
- Relation to maternal toxicity:
- developmental effects as a secondary non-specific consequence of maternal toxicity effects
- Dose response relationship:
- yes
Applicant's summary and conclusion
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