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EC number: 227-579-4 | CAS number: 5895-46-5
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 16 July 2007 to 31 October 2008
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted to GLP 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. These data have been read-across from a structurally similar compound.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 422 (combined repeated dose toxicity study with the reprduction/develpmental toxicity screenign test
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Dicerium tricarbonate
- EC Number:
- 208-655-6
- EC Name:
- Dicerium tricarbonate
- Cas Number:
- 537-01-9
- IUPAC Name:
- dicerium tricarbonate
- Details on test material:
- dicerium tricarbonate
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Janvier, Le Genest-Saint-Isle, France
- Age at study initiation: approximately 10 weeks old at the beginning of the treatment period
- Weight at study initiation: at the beginning of the treatment period, the animals had a mean body weight of 419g (range: 392g to 442g) for the males and 263g (range: 239g to 283g) for the females
- Fasting period before study: no
- Housing: The males were individually housed, except during pairing, in wire-mesh cages (43.0 x 21.5 x 18.0 cm). The females were individually housed, except during pairing, until late gestation in wire-mesh cages (43.0 x 21.5 x 18.0 cm). The females were individually housed from late gestation, and with their litter during lactation, in polycarbonate cages (43.0 x 21.5 x 20.0 cm).
- Diet: free access to SSNIFF R/M-H pelleted maintenance diet
- Water: free access to bottles containing tap water (filtered with a 0.22 µm filter)
- Acclimation period: the animals were acclimated to the study conditions for a period of 7 days before the beginning of the treatment period.
ENVIRONMENTAL CONDITIONS
- Temperature: 22 +/- 2°C
- Humidity: 50 +/- 20%
- Air changes: about 12 cycles/hour of filtered, non-recycled air
- Photoperiod: 12 hrs dark / 12 hrs light
IN-LIFE DATES: From 14-AUG-2007 to 10-OCT-2007
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: 0.5% aqueous methylcellulose solution
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test item was administered as a suspension in the vehicle. The test item was ground to fine powder using a mortar and pestle, suspended in the vehicle in order to achieve the concentrations of 30, 90 and 200 mg/mL and then homogenized using a magnetic stirrer. The test item dosage forms were prepared at a frequency based on stability data (up to 9 days) and were stored at +4°C, protected from light, prior to use.
VEHICLE
- Justification for use and choice of vehicle (if other than water): aqueous suspension for a poorly hydrosoluble test substance, as recommended in the guideline
- Concentration in vehicle: 30, 90 and 200 mg/mL
- Amount of vehicle (if gavage): a constant volume of 5 mL/kg/day was used
- Lot/batch no. (if required): methylcellulose batch No. 017K0052, supplied by Sigma
- Purity: data not available - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- During a pre-study period, the homogeneity, stability and concentration of two dosage forms prepared at the lowest and highest concentrations of the present study (30 and 200 mg/mL) were checked using ICP-OES (Inductively Coupled Plasma/Optical Emission Spectrometry) after validation of the analytical method. The results showed acceptable homogeneity and stability of both concentrations over 9 days at +4°C.
During the study, the concentration of the test item and homogeneity of the dosage forms was determined in samples of each control and test item dosage form prepared for use in weeks 1, 3 and 6. The results showed acceptable homogeneity and concentration of all dosage forms analyzed. Precision (RSD =< 10%) and accuracy (100 +/- 10%) of the method were found to be satisfactory. - Duration of treatment / exposure:
- - In males: 15 days before mating, during the mating period (up to 3 weeks), until sacrifice (i.e. at least 4 weeks in total)
- In females: 15 days before mating, during the mating period (up to 3 weeks), during pregnancy, during lactation until day 5 post-partum inclusive - Frequency of treatment:
- Each animal was given the appropriate dosage form once a day, at approximately the same time each day, 7 days a week.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 150, 450 and 1000 mg/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- 10/sex/group
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: on the basis of a previous 14-day toxicity study in the rat in which the dose-levels of 150, 450 and 1000 mg/kg/day elicited no significant treatment-related effects.
- Rationale for animal assignment: during the pre-treatment period, the required number of animals (40 males and 40 females) was selected according to body weight and clinical condition and allocated to the groups (by sex), according to a computerized stratification procedure, so that the average body weight of each group was similar.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: From arrival, the animals were observed once a day as part of routine examinations. From the start of treatment period, each animal was observed once a day, at approximately the same time for the recording of clinical signs.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: on all animals outside the home cage, in a standard arena, once before the beginning of the treatment period and then once a week until the end of the study.
Observations included (but were not limited to) changes in the skin, fur, eyes, mucous membranes, occurrence of secretions and excretions and autonomic activity (e.g. lachrymation, piloerection, pupil size, unusual respiratory pattern). Changes in gait, posture and response to handling as well as the presence of clonic or tonic movements, stereotypes (e.g. excessive grooming, repetitive circling) or bizarre behavior (e.g. self-mutilation, walking backwards) were also recorded.
BODY WEIGHT: Yes
- Time schedule for examinations: the body weight of each male was recorded on the first day of treatment (day 1), then once a week until sacrifice. The body weight of each female was recorded on the first day of treatment (day 1), then once a week until mated (or until sacrifice) and on days 0, 7, 14 and 20 post-coitum and days 1 and 5 post-partum.
FOOD CONSUMPTION: Yes
The quantity of food consumed by each male was recorded once a week, over a 7 day period, from the first day of treatment until sacrifice. The quantity of food consumed by each female was recorded once a week, over a 7 day period, from the first day of treatment through gestation (days 0-7, 7-14 and 14-20 post-coitum intervals) and lactation (days 1-5 post-partum intervals) until sacrifice. During the pairing period, food consumption was not recorded for males or females.
WATER CONSUMPTION: No
OTHER:
MORTALITY AND MORBIDITY: each animal was checked for mortality or signs of morbidity at least twice a day during the treatment period.
Functional Observation Battery (FOB): on the first five males and the first five females, once at the end of the treatment period. This included a detailed clinical examination, measurement of reactivity to manipulation or to different stimuli and motor activity.
HEMATOLOGY: peripheral blood
The following parameters were determined for the last five males and females of each group on the day of sacrifice: Erythrocytes, Hemoglobin, Mean cell volume, Packed cell volum, Mean cell hemoglobin concentration, Mean cell hemoglobin, Thrombocytes, Leucocytes, Differential white cell count with cell morphology (neutrophils, eosinophils, basophils, lymphocytes and Large Unstained Cells), Monocytes, Reticulocytes, Prothrombin time, Activated partial thromboplastin time, Fibrinogen.
BLOOD BIOCHEMISTRY:
The following parameters were determined for the last five males and females of each group on the day of sacrifice: Sodium, Potassium, Chloride, Calcium, Inorganic phosphorus, Glucose, Urea, Creatinine, Total bilirubin, Total proteins, Albumin, Albumin/globulin ratio, Total cholesterol, Triglycerides, Alkaline phosphatase, Aspartate aminotransferase, Alanine aminotransferase, Lactate dehydrogenase, Bile acids. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes / No / No data
Examinations included:
- Gravid uterus weight: No (pups were born
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: No
- Number of late resorptions: No
- Other: Ovaries and uterus were preserved and microscopic examination were evaluated. - Fetal examinations:
- Pups found dead, prematurely sacrificed and pups sacrificed on day 5 post-partum were carefully examined externally for gross external abnormalities and a macroscopic examination was performed. There was no preservation of tissues.
- External examinations: Yes: all per litter
- Soft tissue examinations: No
- Skeletal examinations: No data
- Head examinations: No data - Statistics:
- Mean values were compared by one-way variance analysis and Dunnett test, (mean values being considered as normally distributed, variances being considered as homogeneous). Percentage values were compared by Fisher exact probability test.
- Indices:
- Reproductive indices
The following parameters were evaluated:
- Pre-implantation loss,
- Post-implantation loss,
- Mating index,
- Fertility index,
- Gestation index,
- Number of corpora lutea,
- Number of implantations,
- Number of pups delivered
Offspring viability indices
The following parameters were evaluated:
- Live birth index,
- Viability index on day 4 post-partum,
- Mean litter size,
- Pup sex ratios
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOEL
- Remarks:
- for reproductive performance (mating and fertility)
- Effect level:
- 1 000 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: other:
- Dose descriptor:
- NOEL
- Remarks:
- for toxic effects on progeny
- Effect level:
- 1 000 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: other:
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No effects on viability
No clinical signs
No effects on body weight
No gross pathological efffects
There were no effects on pup survival after birth or on pup sex. Mean pup body weight was higher at all dose-levels but the mean body weight gain was comparable to controls. There were no relevant macroscopic findings at pup necropsy.
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Table 2: Summary of reproductive data
( ): female with no evidence of mating
Table 3 : Summary of delivery data
Table 4: Reproductive and litter data
Statistical key: d=ANOVA + Dunnett-test f =Fishers exact test N= number of animals |
Applicant's summary and conclusion
- Conclusions:
- Based on the experimental conditions of this study, the NOEL for reproductive performance (mating and fertility) was considered to be 1000 mg/kg/day and the NOEL for toxic effects on progeny was 1000 mg/kg/day.
- Executive summary:
The test item, Cerium carbonate, was administered daily by oral gavage to male and female Sprague-Dawley rats, for 2 weeks before mating, during mating, gestation and until day 5 post-partum, at dose-levels of 150, 450 or 1000 mg/kg/day. There were no adverse effects of treatment at any dose-level on mortality, clinical signs, body weight or food consumption. Animals treated at 1000 mg/kg/day had lower white blood cell counts and females in this group had lower chloride concentration and higher glucose, potassium, inorganic phosphorus and urea levels. There were no effects in any group on mating, fertility or delivery and no treatment-related effects on the mean numbers of corpora lutea, implantations or pups. There were no effects on mean pup body weight, survival or sex. There were no treatment-related organ weights and macroscopic changes in rats treated at 1000 mg/kg/day. At 450 or 150 mg/kg/day, there were no treatment-related organ weights and macroscopic changes. There were microscopic treatment related findings in the stomach that consisted of increased incidence and/or severity of submucosal eosinophil infiltration and pyloric gland hyperplasia in rats from both sexes treated at 1000 mg/kg/day and males at 450 mg/kg/kg. No microscopic treatment related changes were observed in the testes and ovaries.
Based on the experimental conditions of this study, the No Observed Effect Level (NOEL) for parental toxicity was considered to be 150 mg/kg/day in female and male rats. The NOEL for reproductive performance (mating and fertility) was considered to be 1000 mg/kg/day and the NOEL for toxic effects on progeny was 1000 mg/kg/day.
These data have been read-across from a structurally similar compound.
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