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EC number: - | 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

Repeated dose toxicity: oral
Administrative data
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- August 13 - October 09, 2007
- Reliability:
- 1 (reliable without restriction)
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Deviations:
- yes
- Remarks:
- see field below
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.7 (Repeated Dose (28 Days) Toxicity (Oral))
- Deviations:
- yes
- Remarks:
- see field below
- Principles of method if other than guideline:
- Functional observation results of males at 50 mg/kg/day (animal numbers 11-15) were not recorded. However, sufficient functional observation results were available for evaluation and the study integrity was not adversely affected.
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Strontium 4-chloro-2-[2-hydroxy-6-sulfonatonaphthalen-1-yl)diazenyl]benzoate
- Cas Number:
- 474814-88-5
- Molecular formula:
- C17H9ClN2O6SSr
- IUPAC Name:
- Strontium 4-chloro-2-[2-hydroxy-6-sulfonatonaphthalen-1-yl)diazenyl]benzoate
- Test material form:
- solid: nanoform, no surface treatment
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- according to guideline
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- oral via gavage
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The concentrations analysed in the formulations of Group 2 (50 mg/kg bw/d), Group 3 (250 mg/kg bw/d) and Group 4 (1000 mg/kg bw/d) were in agreement with target concentrations (i.e. mean accuracies between 85% and 115%).
No test substance was detected in the Group 1 formulation (vehicle control).
The formulations of Group 2 and Group 4 were homogeneous (i.e. coefficient of variation ≤ 10%) (not determined for Group 3). - Duration of treatment / exposure:
- 28 days.
- Frequency of treatment:
- Once daily, 7 days per week, approximately the same time each day with a maximum of 4 hours difference between the earliest and latest dose.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
50 mg/kg bw/d
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
250 mg/kg bw/d
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
1000 mg/kg bw/d
Basis:
actual ingested
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Doses are based on dose-range-finding
Examinations
- Sacrifice and pathology:
- Necropsy:
ORGAN WEIGHTS: Yes: Adrenal glands, Brain, Epididymides, Heart, Kidneys, Liver, Ovaries, Spleen, Testes, Thymus
Histopathology: yes
Gross Pathology: yes - Statistics:
- - If the variables could be assumed to follow a normal distribution, the Dunnett-test1 (many-to-one t-test) based on a pooled variance estimate was applied for the comparison of the treated groups and the control groups for each sex.
- The Steel-test2 (many-to-one rank test) was applied when the data could not be assumed to follow a normal distribution.
- The exact Fisher-test3 was applied to frequency data.
All tests were two-sided and in all cases p < 0.05 was accepted as the lowest level of significance.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Sex:
- male/female
- Basis for effect level:
- other: no effects at highest tested dose level
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Treatment up to 1000 mg/kg/day was well tolerated; no toxicologically relevant changes in clinical signs or functional observations were noted, and body weight and food intake appeared unaffected by treatment. Blood analyses revealed a few changes which were considered not to represent an adverse effect on organ function, taking into account their slight nature and the absence of corroborative morphological changes. At the end of the treatment period, these changes included lower relative lymphocyte counts and lower prothrombine time (PT), higher relative L- reticulocyte counts and mean corpuscular haemoglobin concentration (MCHC), in males at 50 and/or 250 mg/kg/day, and lower methaemoglobin levels in females at 1000 mg/kg/day. At the end of the recovery period, these changes consisted of lower relative L-reticulocyte counts, and higher relative M-reticulocyte counts and relative monocyte counts in males at 1000 mg/kg/day.
No treatment-related toxicologically significant changes were noted in any of the remaining parameters investigated in this study (i.e. macroscopic examination, organ weights, and microscopic examination).
NOAEL = 1000 mg/kg/day.
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