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EC number: 215-266-5 | CAS number: 1317-35-7
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: A non-GLP study conducted to sound scientific principles with a sufficient level of detail to assess the quality of the relevant results.
Data source
Reference
- Reference Type:
- publication
- Title:
- Pulmonary clearance of manganese phosphate, manganese sulfate, and manganese tetraoxide by CD rats following intratracheal instillation.
- Author:
- Vitarella D, Moss O and Dorman DC
- Year:
- 2 000
- Bibliographic source:
- Inhal Toxicol 12:941-957.
Materials and methods
- Objective of study:
- other: Pulmonary clearance rates in respect to particle dissolution
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Determination of the contribution of particle dissolution on pulmonary clearance rates of Mn sulphate (MnSO4, Mn phosphate, and Mn3O4) in CD rats following an intratracheal instillation exposure. In addition, brain (striatal) Mn concentrations were evaluated following exposure.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Manganese (II) sulphate
- IUPAC Name:
- Manganese (II) sulphate
- Reference substance name:
- Manganese (II) phosphate
- IUPAC Name:
- Manganese (II) phosphate
- Reference substance name:
- Manganese tetroxide
- IUPAC Name:
- Manganese tetroxide
- Details on test material:
- - Name of test materials (as cited in study report): Manganese(II) sulphate [MnSO4 .H2O], Manganese(II) phosphate [Mn5(PO4)2(PO3(OH)2.4H2O] Manganese tetroxide Mn3O4
Constituent 1
Constituent 2
Constituent 3
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- other: CD
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Inc. (Raleigh, NC)
- Weight at study initiation: Average weight 300 g
- Housing: Animals were individually housed in humidityand temperature-controlled, HEPA-filtered, mass air-displacement rooms in an animal facility accredited by the American Association for the Accreditation of Laboratory Animal Care (AAALAC).
- Diet: NIH-07 rodent feed containing approximately 100 ppm Mn.
- Water: Deionized, filtered tap water ad libitum.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): Maintained at approximately 18.5–21.5°C
- Humidity (%): Relative humidity of approximately 40–60%.
- Photoperiod (hrs dark / hrs light): Fluorescent lighting was kept on a 12-h light–dark cycle.
Administration / exposure
- Route of administration:
- intratracheal
- Vehicle:
- other: 300 μl sterile Dulbecco’s phosphate-buffered saline solution at room temperature.
- Details on exposure:
- - MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): The mass median diameter and geometric standard deviation (MMD, GSD) were estimated to be 4.9 μm and 2.0 for MnSO4, 66% at 1.67 μm and 2.3 and 34% at 15.5 μm and 2.1 for Mn phosphate, and 0.73 μm and 1.75 for Mn3O4 based on densities of 2.9, 2.8, and 4.85 g/ml, respectively. The Mn phosphate was a mixture of two different size distributions. Specific surface area by nitrogen absorption measurement was 0.29, 2.76, and 9.91 m2/g, respectively.
- Duration and frequency of treatment / exposure:
- A single exposure
Doses / concentrationsopen allclose all
- Dose / conc.:
- 40 other: μg Mn/kg
- Dose / conc.:
- 80 other: μg Mn/kg
- Dose / conc.:
- 160 other: μg Mn/kg
- No. of animals per sex per dose / concentration:
- 6 animals per dose
- Control animals:
- yes
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Pulmonary clearance, dissolution)
- Tissues and body fluids sampled: Lungs and brain
- Time and frequency of sampling: Tissues taken at 0, 1, 3 or 14 days post instillation. - Statistics:
- To use data from the in vitro dissolution to interpret in vivo Mn clearance from the lungs, the following approach was taken. The time course of current (m, particle mass at time t) to initial (Mo, initial particle mass) particle-associated Mn (m/Mo) in the lung fluid simulant was fit with a simple exponential in order to approximate the dissolution rate under conditions of concentration dependent readsorption. Equations for the dissolution of a polydisperse distribution of particles were applied to the size distribution associated with each compound and fit to the initial slope of the in vitro dissolution curve for concentrations less than 20% of the equilibrium concentration. The curve fit was accomplished by iteratively estimating values for the dissolution rate constant (g/cm2/day) in Mercer’s (1967) equations. The highest estimated value of the dissolution rate constant for each compound was used to compare absorptive clearance to the observed (in vivo) lung clearance. The curve predicting Mn clearance due to the dissolution of particles was adjusted to fit the lung clearance data by including a single exponential function representing clearance due to mechanical transport mechanisms.
Results and discussion
Any other information on results incl. tables
All pulmonary clearance half-times were less than 0.5 day. At the concentrations used, striatal Mn levels were unaffected, and lung pathology was unremarkable. The dissolution rate constant of the Mn particles was determined in vitro using lung simulant fluids. The solubility of the Mn compounds was in general 20 to 40 times greater in Hatch artificial lung lining fluid than in Gamble lung simulant fluid. The dissolution rate constant of the water-soluble MnSO(4) particles in Hatch artificial lung fluid containing protein was 7.5 x 10(-4) g (Mn)/cm(2)/day, which was 54 times that of relatively water-insoluble Mn phosphate and 3600 times that of Mn(3)O(4). The dissolution rate constants for these compounds were sevenfold slower in Gamble lung fluid simulant. For both solutions, the time for half the material to go into solution differed only by factors of 1/83 to 1/17 to 1 for MnSO(4), Mn phosphate, and Mn(3)O(4), respectively, consistent with measured differences in size distribution, specific surface, and dissolution rate constant. These data suggest that dissolution mechanisms only played a role in the pulmonary clearance of MnSO(4), while nonabsorptive (e.g., mechanical transport) mechanisms predominate for the less soluble phosphate and oxide forms of Mn.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: bioaccumulation potential cannot be judged based on study results
In conclusion, the data suggest that absorptive (e.g., dissolution) mechanisms are likely to predominate in the pulmonary clearance of MnSO4, given the rapid rate of dissolution of this compound in lung simulant fluids. Non-absorptive (e.g., mechanical transport) mechanisms are likely to be the dominant mechanisms for the pulmonary clearance of both the tetraoxide and phosphate forms of Mn, given the slow rate of dissolution. In all cases mechanical clearance appears to have a half-life of approximately 0.5 days. Brain levels of Mn were not increased following instillation of either the MnSO4, phosphate, or Mn3O4, and significant pulmonary pathology did not occur post-instillation.
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