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EC number: 219-536-3 | CAS number: 2457-02-5
- 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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- disregarded due to major methodological deficiencies
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The documentation of the experimental conditions insufficient for an assessment. The test item is a mixture of a large number of different metals, thus a test-item effect correlation cannot be made. Consequently, the references is considered not relevant for the safety assessment of strontium neodecanoate.
Data source
Reference
- Reference Type:
- publication
- Title:
- Distribution of metals of inhaled fly ash in various organs of rats at various periods after exposure.
- Author:
- Srivastava, V.K., et al.
- Year:
- 1 984
- Bibliographic source:
- J. Environ. Sci. Health, A19, 663-677
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- 24 male rats were exposed to coal fly ash (0.2-0.4 mg/L) on 6h/d for 15 consecutive days. 24 control rats were kept in a dust-free room. Records of their body weights were maintained. 6 rats of control and 6 rats of the experimental group were sacrificed by decapitation 1, 7, 15 and 30 days after the last inhalation exposure. Before sacrifice, blood was collected from the jugular vein. After sacrifice, lung, liver, heart, kidney, and small intestine was collected, cleaned, wiped, weighed and processed for quantification of metals by atomic absorption spectrophotometry. Serum was also processed likewise. The distribution of metal ions (Na, K, Fe, Ca, Mg, Pb, Zn, Cu, Co, Ni, Cr, Mn, and Sr) in lung, liver, kidney, heart, small intestine and serum on 1, 7, 15 and 30 days after the last inhalation exposure was determined.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Fly ash (containing different metals such as strontium)
- IUPAC Name:
- Fly ash (containing different metals such as strontium)
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
- Details on test material:
- - Name of test material (as cited in study report): Fly ash
- Other: low sulfur pulverized coal, containing diffferent metal ions (Na, K, Fe, Ca, Mg, Pb, Zn, Cu, Co, Ni, Cr, Mn, and Sr)
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: from the Institute maintained colony (Department of Biochemistry, V.P. Chest Institute, University of Delhi, Delhi-110007, India)
- Weight at study initiation: 150-175 g
- Fasting period before study: no
- Housing: no data
- Diet (ad libitum): Hind lever diet (Hindustan lever Ltd, Bombay)
- Water (ad libitum): free access before and after exposure
- Acclimation period: no data
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- not specified
- Vehicle:
- not specified
- Remarks:
- no vehicle
- Remarks on MMAD:
- MMAD / GSD: no data
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Preparation of the fly ash samples: low sulfur pulverized coal was operated by an electrostatic precipitator (IP Thermal power Plant, New Delhi). Afterwards the bulk was collected and sieved through 400 mesh sieve (37 µm) to remove coarser particles.
- Exposure apparatus: The fly ash aerosol was generated by a Wright dust generator, the dust cloud passed through a large glass vessel, before entering the inhalation chamber
- Inhalation chamber: 624 L capacity
- Dust concentration: 0.2 - 0.4 mg fly ash / L
- Method of particle size determination: light microscope fitted with an eyepiece graticule
- control rats were kept in a dust free room.
TEST ATMOSPHERE
- Samples taken from breathing zone: no data - Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- The quantification of metals in the tissues and blood serum was estimated by Perkin Elmer Atomic Absorption spectrophotometer (Model 2380)
- Duration of treatment / exposure:
- 15 days
- Frequency of treatment:
- 6 hrs/d on 15 consecutive days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0.2-0.4 mg Fly ash/ L
Basis:
no data
- No. of animals per sex per dose:
- 6 male animals in each group (control and test group) and period (1, 7, 15 and 30 days after last inhalation exposure)
- Control animals:
- yes
- Details on study design:
- no data
- Positive control:
- no
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: animals were sacrificed on days 1, 7, 15 and 30 after the last inhalation exposure. Before sacrifice, blood was collected from the jugular vein for serum preparation. After sacrifice, lung, liver, heart, kidney and small intestine (upper 30cm) was collected, cleaned, wiped, weighed and processed for quantification of metals By Perkin Elmer Atomic Absorption spectrophotometer. serum was also processed likewise.
BODY WEIGHT: Yes
- Time schedule for examinations: records of their body weights were maintained
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No data
WATER CONSUMPTION: No data
OPHTHALMOSCOPIC EXAMINATION: No data
HAEMATOLOGY: No data
CLINICAL CHEMISTRY: No data
URINALYSIS: No data
NEUROBEHAVIOURAL EXAMINATION: No data - Sacrifice and pathology:
- GROSS PATHOLOGY: No data
HISTOPATHOLOGY: No data
Animals were sacrificed by decapitation on 1, 7, 15 and 30 days after the last inhalation exposure. - Other examinations:
- no data
- Statistics:
- no data
Results and discussion
Results of examinations
- Clinical signs:
- not specified
- Mortality:
- not specified
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Records of body weights were maintained but not reported
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- metal ion concentration was detected in several tissues and blood serum
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- organs were weight after cleaning and wiping. No results were reported
- Gross pathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Details on results:
- - The results showed a profound increase in the concentration of Na, K, Fe, Ca, Mg, Pb, Zn, Cu, Co, Ni, Cr, Mn and Sr in all the tissues and serum of rats after the inhalation exposure to fly ash.
- The increased levels of the metals were highest one day after the last exposure and at later periods their concentration declined which varied from metal to metal and from organ to organ.
- The Sr concentrations were the lowest of all metals in all animals (controls and test animals) at all time points. After one day the Sr concentration was raised in the lung (1.0 µg/g wet tissue), heart (0.5 µg/g wet tissue) and kidney (0.4 µg/g wet tissue) in comparison to the control value (0.3 µg/g wet tissue). The highest concentration was found in the lung (1.1 µg/g wet tissue) and liver (0.6 µg/g wet tissue) after 7 days, which reduced to control value after 30 days in lung and 15 days in liver. The Sr concentration in the kidneys did not change until the end of the test (15 days after last inhalation exposure). The Sr concentration in the small intestine was the same as the control value (0.3 µg/g wet tissue).
Effect levels
- Dose descriptor:
- NOAEC
- Remarks on result:
- not determinable
- Remarks:
- no NOAEC identified
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Concentration of Sr in tissues after different recovery periods
Days after last inhalation exposure | Control[µg Sr/g wet tissue] | Lung[µg Sr/g wet tissue] | Liver[µg Sr/g wet tissue] | Heart[µg Sr/g wet tissue] | Kidney[µg Sr/g wet tissue] | Small intestine [µg Sr/g wet tissue] |
1 | 0.3 ± 0.1 | 1.0 ± 0.1 | 0.3 ± 0.1 | 0.5 ± 0.1 | 0.4 ± 0.1 | 0.3 ± 0.1 |
7 | 0.3 ± 0.1 | 1.1 ± 0.1 | 0.6 ± 0.1 | 0.3 ± 0.1 | 0.4 ± 0.1 | 0.3 ± 0.1 |
15 | 0.3 ± 0.1 | 0.6 ± 0.1 | 0.3 ± 0.1 | 0.2 ± 0.1 | 0.4 ± 0.1 | 0.3 ± 0.1 |
30 | 0.3 ± 0.1 | 0.3 ± 0.1 | 0.3 ± 0.1 | 0.2 ± 0.1 | - | - |
Applicant's summary and conclusion
- Conclusions:
- These results show the translocation of inhaled fly ash metals to extrapulmonary organs. No further conclusions can be drawn from this publication.
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