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EC number: 915-048-6 | 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
Acute Toxicity: oral
Administrative data
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- From 18 August 1998 to 11 September 1998
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 798.1175 (Acute Oral Toxicity)
- Deviations:
- no
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- yes
Test material
- Reference substance name:
- Dicerium trisulphide
- EC Number:
- 234-603-7
- EC Name:
- Dicerium trisulphide
- Cas Number:
- 12014-93-6
- Molecular formula:
- Ce2S3
- IUPAC Name:
- Dicerium trisulphide
- Test material form:
- solid: particulate/powder
- Remarks:
- powder
- Details on test material:
- - Name of test material (as cited in study report): Cerium sulphide
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan U.K. Ltd, Bicester, Oxon, England
- Age at study initiation: 8-10 weeks
- Weight at study initiation: 0.222-0.273 kg
- Fasting period before study: overnight
- Housing: Rats were allocated without conscious bias to cages within the treatment group and housed in groups of five rats of the same sex in metal cages with wire mesh floors in Building Rl4 Room 7
- Diet (ad libitum): standard laboratory rodent diet (Special Diet Services RM1(E) SQC expanded pellet). The batch of diet used for the study was analysed for certain nutrients, possible contaminants and micro-organisms.
Access to diet was prevented for 4 hours after dosing.
- Water (ad libitum): Results of routine physical and chemical examination of drinking water, as conducted by the supplier, are made available to the testing laboratory as quarterly summaries.
Access to water was prevented for 4 hours after dosing.
- Acclimation period: 8 days
Each animal was identified by cage number and ear punching. Each cage was identified by a coloured label displaying the dose level, study schedule number, animal mark and the initiais of the Study Director and Home Office licensee.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-23.5
- Humidity (%): 41-61
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light):12/12 (0700-1900 hours)
A permanent daily recordings of the environmental condition parameters was made and archived with other Department raw data.
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- PRELIMINARY STUDY:
In the absence of precise toxicological information, a group of two rats (one male and one female) was dosed at 2000 mg/kg bodyweight.
VEHICLE
- Concentration in vehicle: 50% w/v
- Amount of vehicle (if gavage): 10 ml/kg bw
- Justification for choice of vehicle: no data
-Lot/ batch (if required): no data
- Purity: no data
MAXIMUM DOSE VOLUME APPLIED: 10 ml/kg bw
DOSAGE PREPARATION (if unusual): not applicable
CLASS METHOD (if applicable)
- Rationale for the selection of the starting dose: not applicable - Doses:
- Males and females: 5000 mg/kg bw
- No. of animals per sex per dose:
- Males: 5 per dose
Females: 5 per dose - Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: The body weight of each rat was recorded on Days 1 (prior to dosing), 8 and 15, or at death. Individual weekly bodyweight changes and group mean body weights were calculated.
Cages of rats were checked at least twice daily for any mortalities.
Animals were observed soon after dosing and at frequent intervals for the remainder of Day 1. On subsequent days, surviving animals were observed once in the morning and again at the end of the experimental day (with the exception of Day 15- morning only). The nature and severity of the clinical signs and time were recorded at each observation. All surviving animals were observed for 14 days after dosing.
All surviving animals were killed on Day 15 by carbon dioxide.
- Necropsy of survivors performed: yes. All animals were subjected to a macroscopic examination which consisted of opening the cranial, thoracic and abdominal cavities.The macroscopic appearance of all examined orgnas was recorded.
- Other examinations performed: no further examinations - Statistics:
- Not applicable
Results and discussion
- Preliminary study:
- The dose of the main study was selected based on results of a preliminary study. As no precise toxicological information was available, a group of two rats (one male and one female) was dosed at 2000 mg/kg body weight.
There were no deaths. Clinical signs were confined to piloerection and hunched posture with waddling/unsteady gait also seen in the female. Bodyweight gain was considered satisfactory. No macroscopic abnormalities were recorded at the terminal necropsy on Day 8.
Based on these results, 5000 mg/kg was selected as a suitable dose leve for the main study
Effect levels
- Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 5 000 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: Only one animal died. However, this death was due to intubation error during dosing, and was not considered to be related to the toxicity of the test material.
- Mortality:
- One male died within approximately 9 minutes of dosing. Macroscopic examination of this animal revealed congestive changes (characterised by dark tissue) in the bram, heart, liver and spleen. ln addition, congestion with red fluid contents was seen in the lungs and thoracic cavity, with red fluid contents also seen in the stomach. These findings were considered to indicate the death of this animal was due to intubation error during dosing, rather than to be related to the toxicity of the test material.
- Clinical signs:
- other: Piloerection was observed in all surviving rats soon after dosing. This sign persisted and was accompanied in surviving animals later during the study by hunched posture, waddling/unsteady gait, abnormal faeces and ungroomed appearance. ln addition, dark
- Gross pathology:
- No macroscopic abnormalities were observed for animals killed at study termination on Day 15.
- Other findings:
- No other findings were reported.
Applicant's summary and conclusion
- Interpretation of results:
- not classified
- Remarks:
- Criteria used for interpretation of results: EU
- Conclusions:
- Under the conditions of this study, the acute oral LD50 of Dicerium trisulphide is greater than 5000 mg/kg bw in male and female rats.
According to the criteria specified by Directive 67/548/EEC and subsequent regulations, the test item is not classified as acute toxic via the oral route.
According to the EC Regulation No. 1272/2008 and subsequent regulations, the test item is not classified as acute toxic via the oral route. - Executive summary:
This study was performed to assess the acute oral toxicity of Dicerium trisulphide to the rat.
Methods
The method followed was that described in:
- EPA Health Effects Testing Guidelines, Subpart B - General Toxicity Testing § 798.1175 Acute oral toxicity, September 27, 1985 (described in Federal Register VoL 50, No. 188) and subsequent revisions. Subpart B provides detailed information relating to data requirements of 40 CFR Part
798 and supports the Toxic Substances Control Act (TSCA).
- EPA Pesticide Assessment Guidelines, Subdivision F. Hazard Evaluation: Human and Domestic Animais 81-1 (Revised Edition November 1984). Subdivision F provides detailed information relating to data requirements of 40 CFR Part 158 and supports the Federal Insecticide, Fungicide
and Rodenticide Act (FIFRA).
- Japanese Ministry of Agriculture, Forestry and Fisheries, Requirements for Safety Evaluation of Agricultural Chemicals and Testing Guidelines for Toxicology Studies, Acute Oral Toxicity Study, 59 NohSan No. 4200, Agricultural Production Bureau, January 28, 1985.
A group of ten fasted rats (five males and five females) received a single oral gavage dose of the test substance, formulated in corn oil and administered at a dose level of 5000 mg/kg body weight. This dosage was selected on the basis of results from a preliminary investigation. All surviving animals were killed and examined macroscopically on Day 15, the end of the observation period.
Results
One male died within approximately 9 minutes of dosing. Macroscopic examination of this animal revealed congestive changes in sorne tissues and congestion and red fluid contents in the lungs. Necropsy findings were considered to indicate the death of this animal was a result of intubation error during dosing and not related to the toxicity of the test material.
Clinical signs of reaction to treatment included piloerection, hunched posture, waddling/unsteady gait, abnormal faeces, ungroomed appearance and dark colouring to eyes, seen in both males and females. In addition, lethargy, abnormal respiration, pallid extremities, walking on toes, increased sensitivity to touch, thin appearance and prostration were seen in females only, with protruding eyes noted in one male only. Recovery of surviving rats was complete in all animals by Day 8.
All animals were considered to have achieved satisfactory bodyweight gains throughout the study. No macroscopic abnormalities were observed for animals killed at study termination on Day 15.
Conclusion
The acute median lethal oral dose (LD50) to rats of Dicerium trisulphide was demonstrated to be greater than 5000 mg/kg bodyweight.
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