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EC number: 485-390-4 | 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
Toxicity to reproduction
Administrative data
- Endpoint:
- toxicity to reproduction
- Remarks:
- other: extended subchronic study
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2006-03-10 to 2006-11-03
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD test guideline
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 408 including additional reproductive endpoints
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Crj: CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories Germany GmbH, Sulzfeld/Germany
- Age at study initiation: 36-37 days
- Weight at study initiation: Males: 72.9 - 84.9 g
Females: 70.2 - 80.9 g
- Fasting period before study: no
- Housing: MAKROLON cages (type III) with a basal surface
of approx. 39 x 23 cm and a height of approx. 15 cm
- Diet (e.g. ad libitum): ssniff® R/M-H V1530 ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 9 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22°C ± 3°C
- Humidity: 55% ± 15%
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- soya oil
- Details on exposure:
- VEHICLE
- Amount of vehicle: 5 mL/kg bw/day (administration volume)
- Details on mating procedure:
- no mating
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- For each test or reference item that was mixed with a vehicle, tests by appropriate analytical methods were conducted to determine the concentration, stability and homogeneity of the test or reference item in the solution. For the analysis of the test item-vehicle mixtures, samples of approximately 10 mL were taken at the following times and stored at -20°C or colder until analysis.
At study initiation:
- Analysis of stability and concentration
Immediately after preparation of the mixtures as well as 8 and 24 hours after storage of the test item preparations at room temperature (3 samples/dose level group). Total number of samples: 9
- Homogeneity
At the start of administration, during (middle) administration and before administration to the last animal of each dose level group (3 samples/
dose level group). Total number of samples: 9
At study termination:
- Analysis of concentration
During treatment with the test item always before administration to the last animal/dose level group (1 sample/dose level group)
Total number of samples: 3
The samples were labelled with study number, species, type of sample, concentration, test day, sampling time and date.
The samples were analysed according to a spectrophotometer method revalidated by LPT.
The following parameters were determined during re-validation:
- linearity
- accuracy
- precision
- sensitivity
- specificity
The results of the validation revealed that the method used was reproducible and led to reliable results. - Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
100, 300, 1000 mg/kg bw/d
Basis:
actual ingested
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- The dose levels were selected based on available toxicological data.
- Positive control:
- none
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least once daily
- Parameters examined: skin/fur, eyes, mucous membranes, respiratory and circulatory systems, somatomotor activity and behaviour patterns
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once before adminsitration and weekly thereafter
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD and DRINKING WATER CONSUMPTION
The quantity of food left by individual animals was recorded on a weekly basis throughout the experimental period. Food intake per rat (g/rat/week) was calculated using the total amount of food given to and left by each rat in each group on completion of a treatment week. Drinking water consumption was monitored daily by visual appraisal throughout the study.
OTHER: see examinations related to other systemic effects under section 7.5.1 - Oestrous cyclicity (parental animals):
- OESTRUS CYCLE
At the end of the study (weeks 12 and 13), vaginal lavages were taken daily from all female animals for periods of 2 weeks each. The stages of the oestrus cycles observed in each vaginal lavage were recorded. - Sperm parameters (parental animals):
- SPERM COUNT, VIABILITY, MOTILITY:
From one testicle and epididymis a sperm count was carried out, the sperm viability was determined and the sperm morphology was examined for the control and treated animals. - Litter observations:
- no litter
- Postmortem examinations (parental animals):
- SACRIFICE:
Starting on test day 91 (one day after the last administration) the animals were dissected following a randomisation scheme. Animals not dissected on test day 91 were dosed again until one day before sacrifice. The animals were sacrificed under ether anaesthesia by cutting the aorta abdominalis,
exsanguinated, weighed, dissected and inspected macroscopically under the direction of a pathologist.
PATHOLOGY:
All superficial tissues were examined visually and by palpation and the cranial roof removed to allow observation of the brain, pituitary gland and cranial nerves. After ventral midline incision and skin reflection, all subcutaneous tissues were examined. The condition of the thoracic viscera was noted with due attention to the thymus, lymph nodes and heart. The abdominal viscera were examined before and after removal; the urinary bladder was examined externally and by palpation. The gastro-intestinal tract was examined as a whole and the stomach and caecum were incised and examined. The lungs were removed and all pleural surfaces examined. Any abnormalities in the appearance and size of the gonads, adrenals, uterus, intra-abdominal lymph nodes and accessory reproductive organs were recorded.
The weights of the following organs of all animals were determined before fixation:
adrenal gland (2), heart, ovary (2), thymus,brain, kidney (2), spleen, uterus, epididymis (1), liver, testicle (1)
The following organs or parts of organs of all animals (including deceased or sacrificedanimals) were fixed in 7% buffered formalin. The eyes were preserved in Davidson's solution.
adrenal (2)
aorta abdominalis
bone marrow (os femoris)
brain (3 levels: cerebrum, cerebellum, medulla/pons)
epididymis (1)
eye with optic nerve (2)
gross lesions observed
heart (3 levels: right and left ventricle, septum)
intestine, large (colon, rectum)
intestine, small (duodenum, jejunum,
ileum, incl. Peyer's patches, Swiss roll method)
kidney and ureter (2)
liver
lungs (with mainstem bronchi and bronchioles [preserved by inflation with fixative and then immersion])
lymph node (cervical) (1)
lymph node (mesenteric) (1)
mammary gland
nerve (sciatic)
oesophagus
ovary (2)
pancreas
pituitary
prostate
salivary glands (mandibular, parotid and sublingual gland)
skin (left flank)
spinal cord (3 levels: cervical, mid-thoracic, lumbar)
spleen
stomach
testicle (1)
thymus
thyroid (2) (incl. parathyroids)
tissue masses or tumours (including regional lymph nodes)
trachea (incl. larynx)
urinary bladder
uterus (incl. cervix and oviducts)
vagina
The afore-listed organs of all animals of groups 1 and 4 were examined histologically after preparation of paraffin sections and haematoxylin-eosin staining. In addition, frozen sections of the heart, liver and one kidney were made and stained with scarlet R.
Parathyroids cannot always be identified macroscopically. They were examined microscopically if in the plan of section and in all cases where they were noted as grossly enlarged. - Postmortem examinations (offspring):
- no offsprings
- Statistics:
- Student's t-test
ANOVA with Dunnett's post-hoc test
Fisher's exact test
Results and discussion
Results: P0 (first parental generation)
Details on results (P0)
Treatment with 1000 mg/kg bw/day caused an increase in the absolute and relative liver weights (both sexes). The increase is considered to be a non-specific adaptive change to the high work load of the liver caused by a dose level of 1000 mg/kg bw/day.
OESTRUS CYLE:
No test item-related changes in the oestrus cycle were found in the evaluated females at any dose during the observation periods (test week 12 + 13).
SPERM COUNT, VIABILITY, MOTILITY:
The number of ultrasound-resistant spermatids per gram of testicular tissue was not influenced by any dose.
No test item-related changes were noted in the numbers of motile spermatozoa in the cauda epididymis for the male animals treated with
100, 300 or 1000 mg test substance/kg bw/day.
The male animals treated with 100, 300 or 1000 mg/kg bw/day showed 99.9 to 100 % morphologically normal spermatids.
Effect levels (P0)
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No effects observed
Results: F1 generation
Details on results (F1)
ORGAN WEIGHTS
Treatment with 1000 mg/kg bw/day caused an increase in the absolute and relative liver weights (both sexes). The increase is considered to be a non-specific adaptive change to the high work load of the liver caused by a dose level of 1000 mg/kg bw/day.
OESTRUS CYLE:
No test item-related changes in the oestrus cycle were found in the evaluated females at any dose during the observation periods (test week 12 + 13).
SPERM COUNT, VIABILITY, MOTILITY:
The number of ultrasound-resistant spermatids per gram of testicular tissue was not influenced by any dose.
No test item-related changes were noted in the numbers of motile spermatozoa in the cauda epididymis for the male animals treated with
100, 300 or 1000 mg test substance/kg bw/day.
The male animals treated with 100, 300 or 1000 mg/kg bw/day showed 99.9 to 100 % morphologically normal spermatids.
Effect levels (F1)
- Key result
- Dose descriptor:
- NOEL
- Generation:
- other: effects on parenteral animals
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: no effects
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Applicant's summary and conclusion
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.
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