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EC number: 231-843-4 | CAS number: 7758-94-3
- 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 reproduction: other studies
Administrative data
- Endpoint:
- toxicity to reproduction: other studies
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Research paper study well documented meeting generally accepted scientific principles.
Data source
Reference
- Reference Type:
- publication
- Title:
- Genome-linked toxic responses to dietary iron overload
- Author:
- Whittaker P, Dunkel VC, Bucci TJ et al.
- Year:
- 1 997
- Bibliographic source:
- Toxicol Pathol 25:556-64
Materials and methods
- Principles of method if other than guideline:
- This study was undertaken to evaluate genome-related differences to iron overload between and within rodent species.
- GLP compliance:
- not specified
- Type of method:
- in vivo
Test material
- Reference substance name:
- Iron
- EC Number:
- 231-096-4
- EC Name:
- Iron
- Cas Number:
- 7439-89-6
- IUPAC Name:
- iron(2+)
- Details on test material:
- carbonyl iron
Constituent 1
Test animals
- Species:
- other: Fischer 344 rats, B6C3F1 mice and yellow and black C5YS F1 mice.
- Strain:
- other:
- Sex:
- male
Administration / exposure
- Route of administration:
- oral: feed
- Duration of treatment / exposure:
- 12 weeks
- Frequency of treatment:
- ad lib
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1500; 3500; 5000; 10000 µg iron/g diet
Basis:
- Control animals:
- other: Yes, 35 µg carbonyl iron/g diet
- Details on study design:
- Groups of 12 male Fischer 344 rats were housed in pairs and groups of 12 male B6C3F1 (strain B) mice and yellow and black C5YS F1 (strain C) mice were housed 4/cage. All groups received food and water ad lib for a 12 week period The test materials were incorporated into the diet as follows: Controls: diet +35 ug iron/g diet, treatment groups: diet + 1,500 ug iron/g diet, diet + 3,500 ug iron/g diet, diet + 5,000 ug iron /g diet and diet + 10,000 ug iron/g diet. Final body weight and food consumption were recorded.
At the end of the test period the animals were fasted for 15 hours and a complete necroscopy was performed at sacrifice. Organ weights were determined. Tissues were fixed in 10% neutral formalin, and sections divided into two sets. One set was stained with haematoxylin and eosin (H&E), and another set was reacted with Perl's Prussian blue for Fe. Non-haem iron was determined by the bathophenanthroline reaction. Cell proliferation indices in the liver were determined by immunohistochemical localisation of proliferation cell nuclear antigen (PGNE). Effects of Fe on the pancreas were determined by immunohistochemical identification and determination of the numbers of alpha, beta and delta cells in the islets of Langerhans in the control and the 10,000 ug/g groups of mice and the 5,000 ug/g rat group.
Statistical significance was determined by one-way ANOVA or regression analysis using the ABstat general linear model program. Duncan multiple comparison method was used to differentiate among means for variables significantly affected by treatment. Significance was at p<0.05.Correlation coefficients were determined using Pearson's product moment correlation matrix. Mean organ:brain weight ratios were compared using Student's t-tests. Immunohistochemical assays and pancreas morphology data were compared by ANOVA with Holm's correction.
Results and discussion
Effect levels
- Dose descriptor:
- NOAEC
- Effect level:
- 5 mg/kg diet
- Based on:
- test mat.
- Remarks:
- carbonyl iron
Observed effects
All animals showed a dose-related increase in liver non-haem Fe, and the Fe was stored in hepatocytes, principally in the periportal region. Significant hypertropy of the hepatocytes was observed in B6C3F1 mice and F344 rats at the highest dose.
The PCNA assays showed stimulation of hepatocyte proliferation in the F344 rats and the strain C mice at the highest dose. (In comparison with control; not determined at lower doses).
In the rat there was pancreatic atrophy with loss of endocrine and exocrine tissue at the 3,500 ug/g dose.
Beta cells in the pancreas were reduced in strain B and yellow strain C mice, but not in black strain C mice. Islet numbers and total and mean islet areas were reduced in yellow strain C mice at the highest dose. (In comparison with control; not determined at lower doses).
Rats showed exacerbated dose-dependent nephropathy and changes in glomerular and tubular epithelium associated with Fe accumulation at the highest dose. Degeneration of the germinal epithelium of the testis, formation of multinucleated giant cells and lack of mature sperm were observed in rats at the highest dose.
Applicant's summary and conclusion
- Conclusions:
- The results suggest absorbable iron complexes can adversely affect the male reproductive system under conditions of iron overload. Mortality was observed in 75% of rats at the highest dose, at which effects in the testes were observed.
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