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Diss Factsheets
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EC number: 915-069-0 | 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: accepted QSAR method
Data source
Reference
- Reference Type:
- other: Model calculation
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
- Objective of study:
- distribution
- Principles of method if other than guideline:
- The Multiple-Path Particle Dosimetry Model (MPPD, v2.11; CIIT, 2013, available via Internet http://www.ara.com/products/mppd.htm) was used to predict this fractional deposition behaviour in the human respiratory tract.
- GLP compliance:
- no
Test material
- Reference substance name:
- dialuminium(3+) tetracalcium hexaoxidandiide phosphonate
- EC Number:
- 915-069-0
- Molecular formula:
- not applicable
- IUPAC Name:
- dialuminium(3+) tetracalcium hexaoxidandiide phosphonate
Constituent 1
Results and discussion
Main ADME results
- Type:
- other: fractional deposition in respiratory tract of total dustiness (119.32 mg/g (11.93 % of total substance mass))
- Results:
- naso-pharyngeal (head) region: 89.1 %; tracheobronchial region: 1.4 %; pulmonary (alveolar) region: 4.3 %
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- not determined
- Details on distribution in tissues:
- not determined
- Details on excretion:
- not determined
Metabolite characterisation studies
- Metabolites identified:
- no
- Details on metabolites:
- not determined
Any other information on results incl. tables
Particle size distribution of measured total dustiness (119.32 mg/g) was determined in study DMT 2013 (see Technical Dossier Section 4.5, endpoint study record: key_Particle size distribution (Granulometry) DMT GS 3 – 00 005 13rev1) and the calculated MMAD and GSD values were used as input parameters for the prediction of the inhalable amount (94.8% of total dustiness) and its fractional deposition behaviour in the respiratory tract applying the Multiple Path Particle model (MPPD)(ver.2.11).
Only very few amounts of the total dustiness fraction (4.3 %) will reach the pulmonary (alveolar) region. The vast majority of inhaled dust will be withheld in the naso-pharyngeal (head) region (89.1 %) and minor amounts in the tracheobronchial region (1.4 %). Deposits in the alveolar region would not get directly absorbed as the substance is an poorly soluble dust. The alveolar dust deposits would mainly be engulfed by alveolar macrophages. The macrophages will then either translocate particles to the ciliated airways or carry particles into the pulmonary interstitium and lymphoid tissues. Poorly water-soluble dusts depositing in the nasopharyngeal region could be coughed or sneezed out of the body or swallowed. Dusts depositing in the tracheo-bronchial region would mainly be cleared from the lungs by the mucocilliary mechanism and swallowed (c.f. ECHA TGD R7a, R.7.12.2.1).
Thus, direct inhalative systemic bioavailability is highly unlikeley due to the deposition behaviour, crystalline structure and limited solubility.
Applicant's summary and conclusion
- Conclusions:
- Direct inhalative systemic bioavailability is unlikely due to the deposition behaviour, crystalline structure and limited solubility
- Executive summary:
Prediction of respiratory deposition patterns using the MPPD model
MMAD (9.9 µm) and GDS (3.6) were used as distribution parameter for the MPPD model enabling an estimation of deposited dust fractions in the human respiratory tract: Using the derived particle size distribution parameters, it is possible to quantify the deposited fractions of the airborne dust in the human respiratory tract. The Multiple-Path Particle Dosimetry Model (MPPD, v2.11; CIIT, 2013) was used to predict this fractional deposition behaviour for workers.
Particle size distribution of measured total dustiness (119.32 mg/g) was determined in study DMT 2013 (see Technical Dossier Section 4.5, endpoint study record: key_Particle size distribution (Granulometry) DMT GS 3 – 00 005 13rev1) and the calculated MMAD and GSD values were used as input parameters for the prediction of the inhalable amount (94.8% of total dustiness) and its fractional deposition behaviour in the respiratory tract.
Only very few amounts of the total dustiness fraction (4.3%) will reach the pulmonary (alveolar) region. The vast majority of inhaled dust will be withheld in the naso-pharyngeal (head) region (89.1%) and minor amounts in the tracheobronchial region (1.4%). Deposits in the alveolar region would not get directly absorbed as the substance is an poorly soluble dust. The alveolar dust deposits would mainly be engulfed by alveolar macrophages. The macrophages will then either translocate particles to the ciliated airways or carry particles into the pulmonary interstitium and lymphoid tissues. Poorly water-soluble dusts depositing in the nasopharyngeal region could be coughed or sneezed out of the body or swallowed. Dusts depositing in the tracheo-bronchial region would mainly be cleared from the lungs by the mucocilliary mechanism and swallowed (c.f. ECHA TGD R7a, R.7.12.2.1).
Thus, direct inhalative systemic bioavailability is unlikely due to the deposition behaviour, crystalline structure and limited solubility.
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