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EC number: 233-297-2 | CAS number: 10108-73-3
- 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
Toxicity to birds
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to birds
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Endpoint:
- short-term toxicity to birds: dietary toxicity test
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- As the systemic toxicity of cerium compounds is mainly determined by the extent to which the compound gives rise to bioavailable cerium for uptake in the body, and equally water soluble cerium compounds can be expected to give rise to similar levels of bioavailable cerium under similar conditions, results on systemic toxicity obtained with water soluble cerium compounds can be lumped for hazard assessment purposes. In the case of cerium trinitrate, a study on the toxicity of cerium citrate to birds (Zohravi, 2006) was therefore included in this dossier. The results of this study are however only considered as supporting information because of the mixed exposure conditions during the test and because only an unbound NOEC at relatively low dose was obtained. The full read across justification is attached to IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Duration (if not single dose):
- 4 wk
- Dose descriptor:
- NOEC
- Effect level:
- >= 140 mg/kg diet
- Conc. / dose based on:
- element
- Remarks:
- Ce
- Basis for effect:
- other: mortality and growth
- Remarks on result:
- other: only used as supporting information
- Endpoint:
- short-term toxicity to birds: dietary toxicity test
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Mixed exposure.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- One day old Japanese quails were allotted to a basal diet with several concentrations of REE-citrate (containing Ce, La, and Pr). The experiments lasted four weeks, feed and water were supplied ad libitum. Growth, mortality, and several physiological parameters were monitored throughout the study. Three experiments were conducted. Experiment 1 and 3 were similar concerning the REE-citrate treatments used. Experiment 2 is not discussed because only one low exposure level of REE-citrate was used, not yielding any relevant results.
- GLP compliance:
- not specified
- Dose method:
- feed
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on preparation and analysis of diet:
- The basal diet was formulated according to NRC nutrient requirements of poultry 1994.
The control diet was the basal diet with no additives and the treatment diets were basal diet plus test substance. The test substance with mineral and vitamin supplements was added and mixed with diet at the end of making ration. - Test organisms (species):
- Coturnix coturnix japonica
- Details on test organisms:
- TEST ORGANISM
- Common name: Japanese quails
- Source: institute of animal physiology and nutrition of Munich University
- Age at test initiation (mean and range, SD): one day old
- Weight at test initiation (mean and range, SD): 8.34 g +/- 0.39 g (experiment 1) / 8.10 g +/- 0.49 g (experiment 3)
- Sexes used: no data - Limit test:
- no
- Total exposure duration (if not single dose):
- 4 wk
- No. of animals per sex per dose and/or stage:
- 24 (experiment 1), 45 (experiment 3) (no data about sex)
- Control animals:
- yes, plain diet
- Nominal and measured doses / concentrations:
- Both experiments: Control + 50, 100, 400, 800 mg/kg (test substance in food)
- Details on test conditions:
- ACCLIMATION
- Acclimation period: first day after eclosion
- Acclimation conditions (same as test or not): the new born quails were transferred to brooder house and were put in three or four plastic boxes until the next day when experiment started
- Feeding: corn meal
- Health (any disease or mortality observed): no data
- Fasting period before study: no
PEN SIZE AND CONSTRUCTION MATERIALS
- Description: plastic reticular boxes with the size of 60 × 80 cm
- Floor covering: no information
- Caging: group
NO. OF BIRDS PER REPLICATE
- For control: 12 (Exp. 1), 15 (Exp. 3)
- For treated: 12 (Exp. 1), 15 (Exp. 3)
NO. OF REPLICATES PER GROUP
- For control: 2 (Exp. 1), 3 (Exp. 3)
- For treated: 2 (Exp. 1), 3 (Exp. 3)
TEST CONDITIONS (range, mean, SD as applicable)
- Temperature: The temperature in house was set at 38 °C at the first day and was decreased by 2°C every two days during the first week. Then the temperature was weekly decreased by 4°C to reach the room temperature (22 ±2 °C) by the end of the fourth week.
- Relative humidity (%): no data
- Photoperiod: Light was provided for 24 hours per day
- Ventilation: air circulation was provided by ventilators
- Details on examinations and observations:
- MORTALITY / CLINICAL SIGNS
- Time schedule for examinations: every day the boxes were checked for dead or sick quails
- Remarks: Until the 3rd day of each experiment, the dead quails were replaced with new quails. After the third day the dead quails were removed without replacement and the remaining feed in the feeder was measured.
BODY WEIGHT
- Time schedule for examinations: at initiation, then every week
FOOD CONSUMPTION (if feeding study)
- Time schedule for examinations: every week the amount of feed consumption in each group was calculated by subtraction of the sum of added feed to feeder from the remaining feed in feeder.
WATER CONSUMPTION (if drinking water study): not observed
PATHOLOGY: not observed
ORGAN WEIGHTS: not observed
REGURGITATION: not observed
OTHER:
At the end of each experiment four Japanese quails (two male and two female) were randomly chosen from each box (replicate) and slaughtered by cervical dislocation. Tibia bones, breast and liver were taken from each slaughtered bird. Also a blood sample was taken from each quail during cutting the neck. In blood samples (serum) and tibia bones Calcium, Phosphorus and Magnesium content were measured. The liver and breast samples were taken for measuring the test substance content (with the addition: "if it was necessary"). - Duration (if not single dose):
- 4 wk
- Dose descriptor:
- NOEC
- Effect level:
- >= 140 mg/kg diet
- Conc. / dose based on:
- element
- Remarks:
- cerium
- Basis for effect:
- other: mortality and growth
- Remarks on result:
- other: based on 17.5% Ce present in the REE-citrate mixture at 800 mg/kg diet
- Mortality and sub-lethal effects:
- MORTALITY
The average percentage of mortality (dead and eliminated animals) during the whole period of experiment was 2.7% in Exp. 1 and 1.3% in Exp. 3. The weak quails which had much lower weight than the average weight of replicate were eliminated. The rate of mortality in Japanese quails was higher during the first week of experiment (3.7%). As there was no special disease during the experiment, the number of dead or eliminated quails significantly dropped to 0.6% (Exp. 1) and 0.5% (Exp. 3) after first week of trial.
CLINICAL SIGNS: no data
ABNORMAL BEHAVIOUR: no data
BODY WEIGHT and WEIGHT GAIN
- Results Exp. 1: Birds receiving REE-citrate had significantly higher body weight than the control group during the first three weeks of Exp. 1. After 4 weeks, the difference was not significant anymore. Similar results were obtained for weight gain. Therefore, for these endpoints, the 28-d NOEC is >= 800 mg REE-citrate/kg food.
- Results Exp. 3: After 28 days, the quails in the highest dose (800 mg/kg) had a slightly but significantly lower body weight than the birds in the control group. However, weight gain was not significantly lower after 4 weeks. Body weight was significantly higher than in the control in the 100 and 400 mg/kg treatments. Here too, no significant differences were observed on weight gain. Therefore, the 28-d NOEC of the first experiment was confirmed.
FOOD CONSUMPTION (if feeding study)
- Results Exp. 1: No significant differences in feed consumption were observed throughout the study.
- Results Exp. 3: No significant differences were observed throughout the study.
WATER CONSUMPTION (if drinking water study): no data
PATHOLOGY: no data
ORGAN WEIGHTS: no data
HISTOPATHOLOGY: no data - Conclusions:
- In this study, one-day old Japanese quails were exposed to REE-citrate in which La (5.5%), Ce (17.5%) and Pr (3.28%) were present. The REE-citrate was added to the diet of the quails for 4 weeks. No significant decrease of growth or increase of mortality was observed during the test compared to the control treatment. The NOECs for both mortality and growth were therefore >= 140 mg Ce/kg diet.
Referenceopen allclose all
Description of key information
Only supporting information was identified (Zohravi, 2006) from a study in which a mixture of rare earth elements (Pr, Ce, La) were added to the food of birds. This information is not sufficient to cover this endpoint. However, because toxicity to birds is an Annex X endpoint and therefore not mandatory for this dossier, no further testing is required.
Key value for chemical safety assessment
Additional information
A single reliable study was identified on the toxicity of cerium to birds. In this study (Zohravi, 2006), one-day old Japanese quails were exposed to REE-citrate in which La (5.5%), Ce (17.5%) and Pr (3.28%) were present. The REE-citrate was added to the diet of the quails for 4 weeks. No significant decrease of growth or increase of mortality was observed during the test compared to the control treatment. The NOECs for both mortality and growth were therefore >= 140 mg Ce/kg diet. However, since the birds were exposed to a mixture of three different rare earth elements, the results of this study are not sufficient to cover this endpoint.
However, being an Annex X endpoint, toxicity to birds is not a mandatory endpoint for this dossier. Therefore, no further testings is required.
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.
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