Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 911-254-5 | CAS number: -
- 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
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
Key study: Read-across from experimental results on the substance 6-tert-Butyl-2,4-xylenol: Test according to OECD guideline 422. GLP study.
NOAELs for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.
Data waiving: In accordance with column 1 of REACH Annex IX, a extended one-generation reproductive toxicity study does not need to be conducted since the repeated dose toxicity study does not indicate adverse effects on reproductive organs or tissues.
Link to relevant study records
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
The substance CAS No. 1879-09-0 is one of the main components of the reaction mass of 2-tertbutyl-4,6-dimethylphenol and 4-tert-butyl-2,5-dimethylphenol and it is present in a concentration of more than 70%. Therefore, the results obtained with the substance CAS No. 1879-09-0 can be used for the read-across approach.
See attached the reporting format. - Reason / purpose for cross-reference:
- read-across source
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 150 mg/kg bw/day (actual dose received)
- Based on:
- other: Read-across from an analogue
- Sex:
- male
- Basis for effect level:
- reproductive performance
- Remarks on result:
- other: read-across from an analogue for which NOEL = 150 mg/kg bw/day
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 30 mg/kg bw/day (actual dose received)
- Based on:
- other: read-across from an analogue
- Sex:
- female
- Basis for effect level:
- reproductive performance
- Remarks on result:
- other: read-across from an analogue for which NOEL = 30 mg/kg bw/day
- Key result
- Critical effects observed:
- no
- Key result
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 30 mg/kg bw/day (actual dose received)
- Based on:
- other: Read-across from an analogue
- Sex:
- male/female
- Basis for effect level:
- viability
- Remarks on result:
- other: read-across from an analogue for which NOEL = 30 mg/kg bw/day
- Key result
- Critical effects observed:
- no
- Reproductive effects observed:
- not specified
- Conclusions:
- Based on read-across approach from experimental data on analogue substance 6-tert-butyl-2,4-xylenol (CAS 1879-09-0), the NOAELs of the reaction mass of 2-tert-butyl-4,6-dimethylphenol and 4-tert-butyl-2,5-dimethylphenol for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.
- Executive summary:
6-tert-Butyl-2,4-xylenol was studied in an OECD combined repeat dose and reproductive/developmental toxicity screening test (OECD Guideline 422) at doses of 0, 6, 30 and 150 mg/kg/day.The compound showed no effects on mating, fertility and oestrous cycle. In terms of reproductive/developmental toxicity, one female given 150 mg/kg died during the delivery. With three females in the same treatment group all pups died during the lactation period. A tendency to decrease of viability index of pups at Day 4 after birth was observed in 150 mg/kg group. The NOELs for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively. Based on these results, the NOAELs of the read-across approach was applied and the reaction mass of 2-tert-butyl-4,6-dimethylphenol and 4-tert-butyl-2,5-dimethylphenol for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Remarks:
- Meets the requirements of GLP. There are no deviations from the recommended guideline.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Crj: CD(SD)
- Sex:
- male/female
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Duration of treatment / exposure:
- Males: 45 days including 14 days before mating
Females: from 14 days before mating to day 3 of lactation - Frequency of treatment:
- Daily
- Dose / conc.:
- 0 mg/kg bw/day (actual dose received)
- Remarks:
- (Vehicle)
- Dose / conc.:
- 6 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 30 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 150 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- Males,12; females, 12/group
- Control animals:
- yes, concurrent vehicle
- Parental animals: Observations and examinations:
- DETAILED CLINICAL OBSERVATIONS: Yes
BODY WEIGHT: Yes
FOOD CONSUMPTION: Yes - Litter observations:
- - No. of total live pups born
- Sex ratio
- No. of live pups on Day 4
- No. of dead pups born - Postmortem examinations (parental animals):
- GROSS PATHOLOGY: Yes
ORGAN WEIGHTS: Yes
HISTOPATHOLOGY: Yes - Reproductive indices:
- - Gestation index
- Implantation index
- Delivery index
- Live birth index - Offspring viability indices:
- - Viability index on Day 4
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- There were no clinical abnormal signs attributable to the administration of the test substance. However, two female animals given 150 mg/kg died at the end of gestation period (one of them during the delivery). In addition with three females of the same treatment group all pups died during the lactation period. A tendency for decrease in the viability index of the pups at Day 4 after birth was also observed in this group.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- Two female animals given 150 mg/kg died at the end of gestation period (one of them during the delivery)
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The body weight gain of females given 150 mg/kg was lower than that of the controls during the gestation period. However, body weights of males did not demonstrate any effects attributable to the administration of test substance.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Food consumption of both males and females did not demonstrate any effects attributable to the administration of test substance.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Histopathological examination revealed swelling of centrilobular hepatocytes in males given 150 mg/kg and swelling and necrosis of centrilobular hepatocytes, and single cell necrosis in females given 150 mg/kg. The dead females and females with pups which all died showed increased incidences of parakeratosis of the tongue, esophageal swelling and necrosis of centrilobular hepatocytes, as well as a variety of degenerative charges, single cell necrosis and mitosis in the liver. Degeneration and protein cast in the proximal tubules and PAS positive granules deposited in the renal papilla, were observed in the kidneys of females given 150 mg/kg.
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not examined
- Reproductive function: oestrous cycle:
- no effects observed
- Description (incidence and severity):
- The compound showed no effects on estrous cycle.
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- The compound showed no effects on mating and fertility.
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 150 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- reproductive performance
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 30 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- reproductive performance
- Key result
- Critical effects observed:
- no
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- A tendency for decrease in the viability index of the pups at Day 4 after birth was also observed in the group of females given 150 mg/kg bw.
Viability index on day 4 (%, mean ± SD) for males: from 95.5 ± 15.1 (non parametric analysis) (0 mg/kg) to 71.4 ± 42.9 (150 mg/kg)
Viability index on day 4 (% mean ± SD) for females: from 95.5 ± 15.1 (non parametric analysis) (0 mg/kg) to 69.7 ± 44.0 (150 mg/kg)
In 3 females of the same treatment group all pups died during the lactation period. - Dermal irritation (if dermal study):
- not examined
- Mortality / viability:
- mortality observed, treatment-related
- Description (incidence and severity):
- A tendency for decrease in the viability index of the pups at Day 4 after birth was also observed in the group of females given 150 mg/kg bw.
Viability index on day 4 (%, mean ± SD) for males: from 95.5 ± 15.1 (non parametric analysis) (0 mg/kg) to 71.4 ± 42.9 (150 mg/kg)
Viability index on day 4 (% mean ± SD) for females: from 95.5 ± 15.1 (non parametric analysis) (0 mg/kg) to 69.7 ± 44.0 (150 mg/kg)
In 3 females of the same treatment group all pups died during the lactation period. - Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not examined
- 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
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings:
- not specified
- Other effects:
- not examined
- Behaviour (functional findings):
- not examined
- Developmental immunotoxicity:
- not examined
- Key result
- Dose descriptor:
- NOEL
- Generation:
- F1
- Effect level:
- 30 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- viability
- Key result
- Critical effects observed:
- no
- Reproductive effects observed:
- not specified
- Conclusions:
- NOELs for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.
- Executive summary:
6-tert-Butyl-2,4-xylenol was studied in an OECD combined repeat dose and reproductive/developmental toxicity screening test (OECD Guideline 422) at doses of 0, 6, 30 and 150 mg/kg/day.The compound showed no effects on mating, fertility and oestrous cycle. In terms of reproductive/developmental toxicity, one female given 150 mg/kg died during the delivery. With three females in the same treatment group all pups died during the lactation period. A tendency to decrease of viability index of pups at Day 4 after birth was observed in 150 mg/kg group. The NOELs for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.
- Endpoint:
- extended one-generation reproductive toxicity - basic test design (Cohorts 1A, and 1B without extension)
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the extended one-generation reproductive toxicity study does not need to be conducted because there are no results from available repeated dose toxicity studies that indicate adverse effects on reproductive organs or tissues, or reveal other concerns in relation with reproductive toxicity
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
In accordance with column 1 of REACH Annex IX, a extended one-generation reproductive toxicity study does not need to be conducted since the repeated dose toxicity study does not indicate adverse effects on reproductive organs or tissues. - Reproductive effects observed:
- not specified
Referenceopen allclose all
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 30 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Klimisch 1. This study was carried out in accordance with internationally valid GLP principles.
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Key study: 6-tert-Butyl-2,4-xylenol was studied in an OECD combined repeat dose and reproductive/developmental toxicity screening test (OECD Guideline 422) at doses of 0, 6, 30 and 150 mg/kg/day.The compound showed no effects on mating, fertility and oestrous cycle. In terms of reproductive/developmental toxicity, one female given 150 mg/kg died during the delivery. With three females in the same treatment group all pups died during the lactation period. A tendency to decrease of viability index of pups at Day 4 after birth was observed in 150 mg/kg group. The NOELs for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.Based on these results, the NOAELs of the read-across approach was applied and the reaction mass of 2-tert-butyl-4,6-dimethylphenol and 4-tert-butyl-2,5-dimethylphenol for reproductive performance of males and for that of females and pup development are considered to be 150 mg/kg/day and 30 mg/kg/day, respectively.
Data waiving: In accordance with column 1 of REACH Annex IX, a extended one-generation reproductive toxicity study does not need to be conducted since the repeated dose toxicity study does not indicate adverse effects on reproductive organs or tissues.
Justification for selection of Effect on fertility via oral route:
Only one study available.
Effects on developmental toxicity
Description of key information
Key study: OECD guideline 414 and EU method B.31. GLP study.
The NOAEL for both maternal toxicity and developmental toxicity was determined to be 50 mg/kg bw/day.
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Meets the requirements of GLP. There are no deviations from the recommended guideline.
- 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 (incl. QA statement)
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Experimental Medicine Centre at the Medical University in Białystok
- Age at study initiation: 13 weeks old
- Weight at study initiation: Average body weight of females of control group and treated groups: 232.5 g.
- Housing: Animals were kept in plastic cages with metal wire lid and dimensions: 37 x 22 x 15 cm (lenght x width x height) on UV sterilized bedding. At mating one female was placed in one cage with one male. At pregnancy the females were housed individually.
- Diet (e.g. ad libitum): “Murigran” standard laboratory fodder, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: Minimum 3 weeks.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-23 ºC
- Humidity (%): 30-80%
- Air changes (per hr): about 16 times/hour
- Photoperiod (hrs dark / hrs light): 12 hours light/12 hours dark - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test item was diluted in corn oil directly before administration, in concentration correct for each dose.
A constant volume of solution (0.4mL of solution / 100 g bw) was used at every level of dosage. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- In order to confirm correct preparation of the test item, each of three doses was analyzed during the whole administration period using a liquid chromatographic method. The linearity of response of the analytical method, its specificity, precision, recovery, limit of quantification and detection were assessed in the process of the analytical method validation.
- Details on mating procedure:
- - If cohoused: The females were mated with not related males. The males came from the same husbandry and stock and were at a similar age.
- M/F ratio per cage: One male was used to mate with maximally three females.
- Length of cohabitation: from 1 to 4 days. In case of unsuccessful pairing the first male was replaced by a second one (4 cases), a third one (2 cases) or a fourth male (1 case).
- Proof of pregnancy: For each mating one female was placed in a cage with one male. Everyday in the morning, vaginal smears were taken from females. The sperm-positive females were accepted as mated and the day of observation of sperm in the smear was accepted as 0 day of gestation. - Duration of treatment / exposure:
- The test item in treated groups and the corn oil in control group were given to pregnant females by gavage daily from 0 to 19th day of gestation.
- Frequency of treatment:
- Daily
- Duration of test:
- On day 20 of gestation (one day prior to the expected day of delivery), females were euthanised by intraperitoneal administration of morbital and subjected to caesarean section.
- Dose / conc.:
- 8.3 mg/kg bw/day (actual dose received)
- Remarks:
- Group 1
- Dose / conc.:
- 50 mg/kg bw/day (actual dose received)
- Remarks:
- Group 2
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Remarks:
- Group 3
- No. of animals per sex per dose:
- 25 females per group
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
Sighting range-finding study:
Three different doses of the test item (10, 50 and 250 mg/kg bw) were administered orally to three groups of pregnant females. A concurrent control group of pregnant females was not given the test item. Seven pregnant females were used per group.
The doses were selected on the grounds of the LD50 value which is about 500 mg/kg bw (300 mg/kg bw: no mortality occurred; 2000 mg/kg bw: three animals died). The highest dose should be between 1/2-1/5 of the LD50, the medium dose should be between 1/10-1/20 of the LD50 and the lowest dose should be between 1/50-1/100 of the LD50.
The test item in the used doses administered from 5th to 19th gestation day, did not indicate any toxic influence on pregnant females, except for the decrease of food consumption from 5th to 8th in group 3. A statistically significant reduction on the weight of placenta was observed in the treated groups. No embryotoxicity, no fetotoxicity and no teratogenic effects were stated in the examined fetuses. - Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: The evaluation of general condition of the animals, i.e. the observation of all animals for morbidity and mortality was performed twice a day during labour week and once a day on days off.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: The detailed clinical observations were performed for all females on day of beginning of experiment (day 0) and then on 2nd, 5th, 8th, 11th, 14th, 17th and 20th day of gestation. The observations comprised: skin changes, coat changes, changes in eyes and mucous membranes, respiratory system, circulatory system, autonomous and central nervous system, somatic activity and behavior.
BODY WEIGHT: Yes
- Time schedule for examinations: Body weights of the females were determined on days 0, 2, 5, 8, 11, 14, 17, and 20 of gestation.
FOOD CONSUMPTION: Yes
- Time schedule for examinations: Days 0, 2, 5, 8, 11, 14, 17, and 20 of gestation.
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 20
- Organs examined: At necropsy, females were examined macroscopically for any abnormalities in body structure or pathological changes which could have influenced gestation. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes.
After caesarean section, uterus from each female with fetuses was dissected. After removing of fetuses left and right uteri horn were examined. Number of viable and dead fetuses as well as number of resorptions was determined in each horn. Each pregnant uterus after removing of fetuses was weighed. Uteri of non pregnant females and non pregnant horns of uteri were fixed between two glass plates and overexposed by electric lamp to confirm the non-pregnant status. Then these uteri were stained using ammonium sulphide and then again overexpose with light by electric lamp in order to confirm the non-pregnant status. At the necropsy ovaries from each pregnant female were collected and fixed in 10% solution of formalin in order to determine number of corpora lutea.
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. Sex of each fetus, body weight, length with tail and without tail was determined. Weight of fetuses with placenta and fetal membranes was determined first and then weight of fetuses without placenta and fetal membranes as well as weight of placenta were measured. After removal of fetal membranes each fetus was measured with tail and without tail, and detailed gross evaluation was performed.
During the gross evaluation attention was paid to:
- reactions to tactile impulses
- formation of body coverings
- formation of limbs
- number of fingers and toes
- shape of head
- formation of auricular conchas
- presence of nasal apertures
- formation of oral cavity
- presence of anus and tail
- Skeletal examinations: Yes. In every group, half of fetuses of each litter was subjected to evaluation of skeleton. The fetuses were fixed in 95% ethanol then overexposed in 1% KOH and stained with alizarin S, decolorized in Moll solution and moved to glycerine. The stained fetuses were examined and formation of skull bones, back-bone, ribs, acromial and pelvic girdles with limbs was evaluated. Points of ossification in sternum, metacarpus of fore limbs and metatarsus of hind limbs were counted during evaluation.
- Soft tissue examinations: Yes. The remaining fetuses from each litter were fixed in 10% solution of formalin, then cut in sagittal plane. Formation of particular cavities and presence of internal organs was evaluated.
- Head examinations: Yes. - Statistics:
- Evaluation of the study was performed for pregnant females from which fetuses were obtained at necropsy. The obtained results (body weight of pregnant females, food consumption of pregnant females, number of corpora lutea, number of fetuses in litter, number of males and females in litter, weight of uteri, weight of fetuses, length of fetuses, number of ossification points in sternum and limbs) were elaborated statistically with the use of t-Student test with p ≤ 0.05.
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Coat thinning in one female of group 1 and in one female of group 3 should not be connected with the test item. This sign occurred also in three females in control group and should be connected rather with hormonal changes during gestation. Clinical signs on the last day of experiment observed in one female of group 3 were connected with death of fetuses at the last period of gestation. No other clinical signs were stated in the females.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Description (incidence):
- All females survived during the period of experiment.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- No statistically significant changes were observed in the mean body weights of the treated groups when compared to the control group at the end of the study period.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Statistically significantly lower food consumption in group 3 from 0 to 5th day of experiment was reflected in statistically significant lower body weight of females on 2nd and 5th day of gestation. Statistically significant greater food consumption from 8th to 11th day and from 14th to 20th day of experiment caused compensation of the low body weight of females at the initial period of experiment.
- 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 specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
- Number of abortions:
- not specified
- Pre- and post-implantation loss:
- effects observed, treatment-related
- Description (incidence and severity):
- In group 3, in one female fifteen implantation sites and lack of fetuses were stated in uterus.
- Total litter losses by resorption:
- effects observed, treatment-related
- Description (incidence and severity):
- In group 3, two resorptions in two females in group 3 were observed.
- Early or late resorptions:
- not specified
- Dead fetuses:
- effects observed, treatment-related
- Description (incidence and severity):
- One dead fetus in group 1 should not be connected with test item and should be considered as incidental.
In group 3 in one female, in which on day of dissection some clinical signs were observed, only dead fetuses were stated. - Changes in pregnancy duration:
- not specified
- Changes in number of pregnant:
- not specified
- Other effects:
- not specified
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (actual dose received)
- Basis for effect level:
- other: maternal toxicity
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (actual dose received)
- Basis for effect level:
- other: developmental toxicity
- Key result
- Abnormalities:
- no effects observed
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Differences on average body weight of fetuses in treated groups compared to control group were observed but there is no relationship between the dose and the effect. Decreased body weight of fetuses without placenta was observed in group 1 and group 3. However, increased body weight of fetuses without placenta was observed in group 2. The lowest weight of fetuses without placenta was observed in group 3. Average weight of fetuses in control group, group 1 and group 2 are within the range from literature data, while average weight of fetuses without placenta in group 3 – 3.338 g is below the lower range (3.35 g to 3.85 g).
The length of fetuses with tail and without tail was lower in group 3. It may confirm delay of the growth of fetuses in group 3 considering the changes in body weight and length of fetuses. - Reduction in number of live offspring:
- effects observed, treatment-related
- Description (incidence and severity):
- One dead fetus in group 1 should not be connected with test item and should be considered as incidental.
In group 3 in one female, in which on day of dissection some clinical signs were observed, only dead fetuses were stated. - Changes in sex ratio:
- not specified
- Changes in litter size and weights:
- not specified
- Changes in postnatal survival:
- not examined
- External malformations:
- no effects observed
- Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Dislocation of sternum ossification points and ribs attachment in one fetuses in group 1 should not be connected with test item. This case was noticed only in one fetus and similar changes in ribs and sternum were observed in fetuses of control groups in other prenatal developmental toxicity studies performed at the testing facility. Therefore, this change should be considered as a spontaneous disorder.
Decrease in number of ossification points is considered as a change associated with delayed development due to toxicity which does not influence postnatal development and is later compensated. A statistically significant lower number of ossification points of metacarpus in group 1 results from greater percentage of fetuses with 3 ossification points of metacarpus in group 1, whereas lower number of ossification points of metatarsus in group 3 results from the fact that in one female of this group 4 fetuses had 3 ossification points of metatarsus and 1 fetus had no ossification points of metatarsus. All other fetuses in group 3 had 4 ossification points of metatarsus. Additionally, in control group, which treated groups are compared to, average number of ossification points of metatarsus was above 4, because 7 fetuses from one female in control group had 5 ossification points of metacarpus (likewise in group 2). - Visceral malformations:
- no effects observed
- Other effects:
- no effects observed
- Description (incidence and severity):
- In each of the treated groups one case of conjoined placenta was stated. This finding is not considered to be treatment related. Subcutaneous blood hemorrhages observed in fetuses in different parts of the body occurred in control group and in treated groups and should not be connected with the test item. Subcutaneous blood hemorrhages were observed often in fetuses in other prenatal developmental toxicity studies performed in the testing facility and they should be considered as typical disturbances in fetuses.
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- reduction in number of live offspring
- fetal/pup body weight changes
- Key result
- Abnormalities:
- no effects observed
- Developmental effects observed:
- not specified
- Conclusions:
- The NOAEL for both maternal toxicity and developmental toxicity was determined to be 50 mg/kg bw/day.
- Executive summary:
A prenatal developmental toxicity study on rats was performed according to OECD guideline 414 and EU method B.31 in order to determine test item influence and possible toxic effects to pregnant females and their fetuses due to treatment during period of gestation. The study was conducted on 100 females divided into four experimental groups: three treated groups and one control group. Every group was consisted of 25 females. From day 0 to 19th of gestation the females of treated group were given by gavage the test item dissolved in corn oil. The following doses of the test item were used: in group 1 – 8.3 mg/kg bw/day, in group 2 – 50 mg/kg bw/day and in group 3 – 300 mg/kg bw/day. Females of the control group (group 0) were given corn oil. During the study, clinical observations for mortality and signs of toxic influence of the test item were performed in females. Body weight and food consumption were recorded. On Day 20 of gestation, the females were killed and caesarean section with gross examination was performed in each female. The following endpoints were determined in each pregnant females in the sighting study and the main study: number of alive and dead fetuses, number of resorptions. After the removing of fetuses each uterus was weighed. The non-gravid uteri and non-gravid horns were overexposed by electric lamp and were stained using ammonium sulphide in order to confirm the non-pregnant status. In the main study the number of corpora lutea was determined in fixed ovaries. The following endpoints were determined in all fetuses: sex, body weight with and without placenta, weight of placenta, body length with and without tail. Each fetus was subjected to gross examination. Half of fetuses from each litter was stained with alizarin and subjected to evaluation of skeleton. The rest of them was fixed in 10% solution of formalin and evaluated for formation of body cavities and internal organs. Based on the results, the dose levels 8.3 and 50 mg/kg bw /day did not indicate any toxic influence on pregnant females. The dose level of 300 mg/kg bw/day caused increased intrauterine mortality and reduction of body weight and body length in fetuses. The dose levels 8.3, 50 and 300 mg/kg bw/day did not cause morphological changes in fetuses of treated females.
Reference
Table 1 - Results of mating - main study
Parameter |
Number of females |
|||
Group 0 |
Group 1 |
Group 2 |
Group 3 |
|
Number of females per group |
25 |
25 |
25 |
25 |
Number of pregnant females |
21 |
23 |
22 |
20 |
Number of not pregnant females |
4 |
2 |
3 |
5 |
Females with all dead fetuses |
- |
- |
- |
1 |
Females with implantations and without fetuses |
- |
- |
- |
1 |
Females with resorptions |
6 [1,10,17,18, 19(2),20] |
3 [2,11,24] |
4 [3,7,24(4),25] |
2 [8,21] |
Number of females for evaluation |
21 |
23 |
22 |
18 |
[ ] computer numbers of females
( ) number of resorptions
Table 2 - Body weights of females (g) - main study
Day of gestation |
Group |
|||
0 |
1 |
2 |
3 |
|
0 |
233.71 ± 20.83 |
235.13 ± 20.47 |
230.23 ± 15.38 |
230.61 ± 15.44 |
2 |
237.48 ± 20.52 |
237.30 ± 23.32 |
232.05 ± 16.27 |
219.83 ± 14.26* |
5 |
244.67 ± 20.29 |
248.13 ± 21.41 |
245.77 ± 15.78 |
228.67 ± 21.77* |
8 |
253.14 ± 21.77 |
254.00 ± 21.68 |
252.18 ± 18.22 |
243.06 ± 20.82 |
11 |
264.90 ± 19.68 |
267.13 ± 23.76 |
265.95 ± 17.66 |
258.44 ± 25.22 |
14 |
275.29 ± 20.12 |
277.04 ± 22.44 |
278.45 ± 17.22 |
274.94 ± 20.76 |
17 |
300.57 ± 22.66 |
301.57 ± 23.53 |
304.14 ± 20.99 |
300.67 ± 23.53 |
20 |
335.81 ± 24.24 |
340.70 ± 25.87 |
340.64 ± 25.65 |
339.78 ± 30.57 |
* statistically significant difference with p ≤ 0.05
Table 3 - Food consumption (g/100 g bw/day) - main study
Day of gestation |
Group |
|||
0 |
1 |
2 |
3 |
|
0 – 2 |
5.7 ± 1.84 |
5.1 ± 1.38 |
4.8 ± 1.08 |
2.2 ± 1.13 * |
2 – 5 |
7.2 ± 1.29 |
7.0 ± 0.86 |
7.2 ± 0.93 |
4.7 ± 1.91 * |
5 – 8 |
7.1 ± 0.98 |
7.0 ± 1.01 |
7.2 ± 0.84 |
7.3 ± 1.26 |
8 – 11 |
6.8 ± 0.85 |
6.9 ± 1.02 |
6.9 ± 0.79 |
7.8 ± 1.12 * |
11 – 14 |
6.9 ± 0.93 |
6.7 ± 0.88 |
6.7 ± 0.81 |
7.4 ± 1.52 |
14 – 17 |
6.7 ± 1.06 |
6.6 ± 0.79 |
6.8 ± 0.84 |
7.6 ± 0.67 * |
17 – 20 |
6.4 ± 0.64 |
6.6 ± 0.68 |
6.6 ± 0.59 |
6.9 ± 0.85 * |
* statistically significant difference with p ≤ 0.05
Table 4 - Average weight of uterus of pregnant females - main study
Group |
Number of pregnant females |
Weight of uterus |
|
0 |
21 |
5.19 ± 0.84 |
|
1 |
23 |
5.51 ± 0.75 |
|
2 |
22 |
5.12 ± 1.14 |
|
3 |
18 |
5.08 ± 1.31 |
|
Table 5 - Number of fetuses - main study
Group |
Number of pregnant females |
Number of fetuses |
|||||
Total
|
in litters min. – max. |
average in litter in 1 female |
females |
males |
dead |
||
0 |
21 |
247 |
2 – 16 |
11.76 ± 2.91 |
5.76 ± 2.28 |
6.00 ± 2.17 |
0 |
1 |
23 |
270 |
6 – 15 |
11.74 ± 1.94 |
6.22 ± 2.00 |
5.52 ± 1.86 |
1 |
2 |
22 |
244 |
5 – 14 |
11.09 ± 2.39 |
6.45 ± 2.09 |
4.64 ± 1.94 |
0 |
3 |
18 |
199 |
1 – 15 |
11.06 ± 3.69 |
5.39 ± 1.91 |
6.38 ± 1.41 |
13* |
*- all fetuses dead from one female (female not accounted in statistical evaluation)
Table 6 - Number of implantations and number or resorptions - main study
Group |
Number of pregnant females |
Average number of corpora lutea per one female |
Number of implantations |
Number of resorptions |
||
total |
in females min - max |
average in one female |
||||
0 |
21 |
13.00 ± 1.61 |
0 |
7 |
0 – 2 |
0.33 ± 0.58 |
1 |
23 |
12.57 ± 1.62 |
0 |
3 |
0 – 1 |
0.13 ± 0.34 |
2 |
22 |
12.55 ± 1.63 |
0 |
7 |
0 – 4 |
0.32 ± 0.89 |
3 |
18 |
13.11 ± 1.91 |
15* |
2 |
0 – 1 |
0.11 ± 0.32 |
*- all implantations from one female (female not accounted in statistical evaluation)
Table 7 - Average weight of fetuses and placenta (g) - main study
Group |
Number of examined fetuses |
Weight of fetuses |
Weight of placenta |
|
with placenta (x) |
without placenta |
|||
0 |
247 |
4.706 ± 0.607 |
3.431 ± 0.535 |
0.535 ± 0.098 |
1 |
270 |
4.627 ± 0.364 |
3.354 ± 0.307 * |
0.535 ± 0.086 |
2 |
244 |
4.884 ± 0.437 * |
3.467 ± 0.442 * |
0.555 ± 0.115 * |
3 |
199 |
4.809 ± 0.604 |
3.338 ± 0.512 * |
0.557 ± 0.180 |
*statistically significant difference with p ≤ 0.05
(x) with placenta and fetal membranes
Table 8 - Average length of fetuses and placenta (cm) - main study
Group |
Number of examined fetuses |
Length of fetuses |
|
with tail |
without tail |
||
0 |
247 |
5,32 ± 0,24 |
3,75 ± 0,20 |
1 |
270 |
5,28 ± 0,23 |
3,74 ± 0,17 |
2 |
244 |
5,30 ± 0,27 |
3,78 ± 0,21 |
3 |
199 |
5,18 ± 0,34 * |
3,69 ± 0,26 * |
* statistically significant difference with p ≤ 0.05
Table 9 - Pathological changes in fetuses - main study
Pathological changes |
Number of fetuses |
|||
Group 0 |
Group 1 |
Group 2 |
Group 3 |
|
Total number of fetuses |
247 |
271 |
244 |
212 |
Number of alive fetuses |
247 |
270 |
244 |
199 |
Number of dead fetuses |
0 |
1[7] |
0 |
13*[3] |
Number of blood hemorrhage |
6 |
6 |
5 |
3 |
Blood hemorrhage on back |
1 [5] |
3 [4, 6, 17] |
5 [3, 6(2), 10(2)] |
3 [6 (3)] |
Blood hemorrhage on metatarsus |
1 [4] |
- |
- |
- |
Blood hemorrhage on thigh |
- |
3 [2(2), 6] |
- |
- |
Blood hemorrhage on shank |
1 [8] |
- |
- |
- |
Blood hemorrhage on arm |
1 [6] |
- |
- |
- |
Blood hemorrhage on forearm |
1 [6] |
- |
- |
- |
Blood hemorrhage on tail |
1 [4] |
- |
- |
- |
Conjoined placenta |
- |
1 [7] ♀** i ♂ |
1 [10] ♂ i ♂ |
1 [22] ♀ i ♂ |
*–all fetuses dead from one female (female not accounted in statistical evaluation)
**– dead fetuses
[ ] –computer numbers of females
( )–number of fetuses in a given female, if more than 1
Table 10 - Pathological changes in skeletal system - main study
Pathological changes
|
Number of fetuses |
|||
Group 0 |
Group 1 |
Group 2 |
Group 3 |
|
No ossification points of sternum |
- |
- |
- |
1 [10] |
1 ossification point of sternum |
- |
- |
- |
2 [10(2)] |
2 ossification points of sternum |
- |
- |
- |
2 [10(2)] |
3 ossification points of sternum |
5 [10(3),14,16] |
1 [21] |
2 [16(2)] |
3 [8(2),12] |
Dislocation of sternum ossification points and rib attachment |
- |
1 [10] |
- |
- |
No ossification points of metatarsus |
- |
- |
- |
1 [10] |
3 ossification points of metatarsus |
- |
- |
- |
4 [10] |
1 ossification point of metacarpus |
- |
- |
- |
1 [10] |
5 ossification points of metatarsus |
7 [25(7)] |
- |
7 [17(7)] |
- |
Total number of all pathological changes (Table 22 and 23) |
18 |
9 |
15 |
18 |
[ ] computer numbers of females
( ) number of fetuses in a given female, if more than 1
Table 11 - Percentage of fetuses with a given number of ossification points of sternum (%) - main study
Group |
Number of examined fetuses |
Number of ossification points |
|||||||
0 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
||
0 |
129 |
0.0 |
0.0 |
0.0 |
3.88 |
14.73 |
40.31 |
41.08 |
0,0 |
1 |
141 |
0.0 |
0.0 |
0.0 |
0.71 |
14.89 |
54.61 |
29.79 |
0,0 |
2 |
129 |
0.0 |
0.0 |
0.0 |
1.55 |
13.95 |
41.86 |
42.64 |
0,0 |
3 |
105 |
0.95 |
1.90 |
1.90 |
2.86 |
12.38 |
35.24 |
44.77 |
0,0 |
Table 12 - Percentage of fetuses with a given number of ossification points of limbs (%) - main study
Group |
Number of examined fetuses |
Fore limbs Number of ossification points |
Hind limbs Number of ossification points |
||||||||||||
0 |
1 |
2 |
3 |
4 |
5 |
0 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
||
0 |
129 |
0.0 |
0.0 |
0.0 |
39.53 |
60.47 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
94.57 |
5.43 |
0.0 |
0.0 |
1 |
141 |
0.0 |
0.0 |
0.0 |
58.87 |
41.13 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
100,0 |
0.0 |
0.0 |
0.0 |
2 |
129 |
0.0 |
0.0 |
0.0 |
47.29 |
52.71 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
94.57 |
5.43 |
0.0 |
0.0 |
3 |
105 |
0.0 |
0.95 |
0.0 |
39.05 |
60.00 |
0.0 |
0.95 |
0.0 |
0.0 |
3.81 |
95.24 |
0.0 |
0.0 |
0.0 |
Table 13 - Average number of ossification points of sternum and limbs - main study
Group |
Number of examined fetuses |
Sternum |
Metacarpus of fore limbs |
Metatarsus of hind limbs |
0 |
129 |
5.19 ± 0.83 |
3.60 ± 0.49 |
4.05 ± 0.23 |
1 |
141 |
5.13 ± 0.68 |
3.41 ± 0.49 * |
4,00 ± 0,00 |
2 |
129 |
5.26 ± 0.75 |
3.53 ± 0.50 |
4.05 ± 0.23 |
3 |
105 |
5.09 ± 1.19 |
3.58 ± 0.55 |
3.92 ± 0.43 * |
* statistically significant difference with p ≤ 0.05
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 50 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Klimisch 1. This study was carried out in accordance with internationally valid GLP principles.
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Key study: OECD guideline 414 and EU method B.31. GLP study.
The NOAEL for both maternal toxicity and developmental toxicity was determined to be 50 mg/kg bw/day.
Justification for selection of Effect on developmental toxicity: via oral route:
Only one study available
Justification for classification or non-classification
Based on the available data, the substance is not classified as toxic for reproduction.
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.