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EC number: 266-007-8 | CAS number: 65996-74-9 The oxidized surface of steel produced during reheating, conditioning, hot rolling, and hot forming operations. This substance is usually removed by process waters used for descaling, roll and material cooling, and other purposes. It is subsequently recovered by gravity separation techniques. Composed primarily of high-purity iron oxides. May contain varying amounts of other oxides, elements, and trace compounds.
- 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: inhalation
Administrative data
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Remarks:
- The deficits of the study were that details on inhalation exposure missing, the exposure duration was too short, one low concentration only (200 mg/m³) was tested, analytical concentration was missing, the test material was insufficiently characterised (source, purity, impurities), observation periods were too short (<=24h), an uncommon species (rabbit) was used and only lungs were investigated, clinical signs, bodyweight and mortality was missing.
Data source
Reference
- Reference Type:
- publication
- Title:
- Lysosomal enzyme activities in pulmonary macrophages from rabbits breathing iron oxide.
- Author:
- Grant MM, Sorokin SP, and Brain JD.
- Year:
- 1 979
- Bibliographic source:
- American Review of Respiratory disease, 120: 1003-1012
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The aim of the study was to investigate the in vivo pulmonary macrophage response to iron oxide particle (Fe2O3, 200 mg/m³ air) in male New Zealand White rabbits, after 3h of exposure via inhalation. A bronchoalveolar lavage was performed at time points 0, 12, 18 and 24 h after termination of the exposure, for different groups of animals. The lysosomal acid hydrolase activities in the pulmonary macrophages were examined with biochemical and histochemical techniques.
- GLP compliance:
- not specified
- Test type:
- other: Inhalation study aimed at the observation of effects on macrophages in the lungs by means of several biochemical and histochemical techniques.
- Limit test:
- no
Test material
- Test material form:
- solid
- Details on test material:
- - Name of test material (as cited in study report): iron oxide
- Molecular formula (if other than submission substance): Fe2O3
No further details available in the publication.
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Weight at study initiation: 3 to 4 kg
- Diet: ad libitum
- Water: ad libitum
Administration / exposure
- Route of administration:
- inhalation: dust
- Type of inhalation exposure:
- head only
- Vehicle:
- air
- Mass median aerodynamic diameter (MMAD):
- >= 0.17 - <= 0.31 µm
- Geometric standard deviation (GSD):
- 1.61
- Details on inhalation exposure:
- TEST ATMOSPHERE
- Generation: according to Brain et al. (1974)
- Particle size distribution: determined with an aerosol spectrometer of the Tillery (1974) design - Analytical verification of test atmosphere concentrations:
- not specified
- Duration of exposure:
- 3 h
- Remarks on duration:
- once
- Concentrations:
- 200 mg/m3 (nominal); actual range 186 to 222 mg/m³
- No. of animals per sex per dose:
- See below 'details on study design'.
- Control animals:
- yes
- Details on study design:
- Groups of animals were killed immediately after termination of the exposure (0 h-8 animals) and 12 h (12 animals), 18 h (10 animals), and 24 h (8 animals) thereafter. Pulmonary macrophages were obtained by multiple lung lavages (10 washes of 50 ml) with Dulbecco's Ca+2 and Mg+2 free balanced salt solution warmed at 37°C. Macrophages from 2 animals were pooled for each enzyme analysis. The cell numbers were measured with an American Optical hemocytometer and thereafter, homogenates were prepared and centrifuged at 600 g. The 600 g supernatant was either applied to a sucrose density gradient or centifuged further at 15000g for 15 min to obtain a 15000g supernatant and pellet.
Sucrose density gradient centrifugation: performed in order to examine the density distribution of lysosomes from pulmonary macrophages.
Protein and enzyme analysis: enzymes measured and conditions of the assays are summarized in Table 1 below in section 'any other information on materials and methods incl. tables'.
Histochemical examinations: the cell pellets were used for measurements of acid phosphatase according to Barka and Anderson (1963). Staining with Perl's Prussian was also performed.
After BAL the lungs were dissected and examined for any gross pathologic lesions - Statistics:
- not specified
Results and discussion
- Preliminary study:
- not specified
Effect levels
- Dose descriptor:
- other: no LC50 established
- Remarks on result:
- not measured/tested
- Remarks:
- The study was not aimed at the observation of the endpoints that are typically studied in a standard acute inhalation toxicity study. Mortality rates were not reported and observation periods were too short in the publication and hence, an LC50 value could not be established.
- Mortality:
- Although the presentation of the results does not explicitly states anything about mortality, the exposure for 3 h up to 200 mg/m³ and the reported results indicates that no treatment-related mortality occurred within the 24 hours post exposure.
- Clinical signs:
- other: not specified
- Body weight:
- not specified
- Gross pathology:
- No gross pathologic lesions in the lung were found in the animals exposed to ferric oxide. However, lesions were observed in three of the control animals, that were for this reason eliminated from the study.
- Other findings:
- The total cell count increased significantly with time (at 12, 18 and 24 h), after exposure to the aerosol. The protein level in the 600 g- supernatant, did not increase, when expressed per 10^8 cells, whilst the amount of protein recovered after 18 and 24 h after exposure decreased significantly. Macrophages lavaged reacted histochemically for acid-phosphatase and showed increased staining and redestribution of the enzyme within the cytoplasm.
No significant changes on the specific lysosomal enzymic activities, of animals sacrified 0 and 8 h after exposure, were observed in comparison to the controls in the 600g supernatant, except for catepsin D (Table 4, attachment). The activity of β-glycerol-phosphatase and catepsin D did not show any significant changes (expressed per 10^8 cells) in the animals killed at all time points, except for time point 12h, where β-glycerol-phosphatase's activity was decreased. Similarly, catepsin's D activity decreased slightly at 18 h, but not to a statistically significant extent (Table 3, see attachment).
The specific activities of catepsin D and β- glycerol-phosphatase (Fig.1, attachment) remained unchanged or decreased (catepsin D at 18 h), in the 600g supernatant and 15000g pellet fractions of macrophages. On the contrary, in the 15000 g supernatant, the specific activitites were significantly greater than in the controls, suggesting a possible disruption of cells (macrophages).
Any other information on results incl. tables
The study was not aimed at the observation of the endpoints that are typically studied in a standard acute inhalation toxicity study. Mortality rates were not reported in the publication and hence, an LC50 value could not be established.
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Although the presentation of the results does not explicitly states anything about mortality, the presentation of the results indicates that no treatment-related mortality occurred. Therefore this study indicates that 3 h exposure to 200 mg/m³ respirable ferric oxide (Fe2O3) particles does not result in mortality within 24 hours post exposure.
Exposure to ferric oxide particles has lead to little effect on the average activities of lysosomal hydrolases in pulmonary macrophages, to an increased lysosomal heterogeneity and redistribution of enzymic activity within the cell cytoplasm. - Executive summary:
Male white New Zeland rabbits were exposed to an iron(III) oxide (Fe2O3) aerosol with an MMAD of 0.17 to 0.31 μm (GSD 1.61) head-only for 3 h, at a concentration of 200 mg/m3. The aim of the study was to investigate the in vivo pulmonary macrophage response after exposure to this aerosol. A bronchoalveolar lavage was performed at time points 0, 12, 18 and 24 h after termination of the exposure, for different groups of animals. The lysosomal acid hydrolase activities in the pulmonary macrophages were examined with biochemical and histochemical techniques. The results suggest that exposure to Fe2O3 may have little effects on the average activities of lysosomal hydrolases of the pulmonary macrophages, although it indeed stimulates their recruitment in the lung, leading to an increase of the total enzyme in the BAL fluid. An increased lysosomal heterogeneity and redistribution of enzymic activity within the cell cytoplasm of the macrophages was observed.
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