Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 231-850-2 | CAS number: 7759-02-6
- 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:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Reasonably well-documented paper. However, study results are not relevant since the Sr speciation (important in read-acrossability) is not given. Also competitive metals as calcium, magnesium were present. The concentrations in Sr in the fly-ash were not determined.
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:
- The rats were exposed daily to fly ash in an inhalation chamber for 6 hours/d continuously for 15 days. The dust concentration in the chamber was maintained between 0.2 to 0.4 mg/L. Control rats were kept in a dust-free room. Records of their body weights were maintained. Rats of control and experimental groups were sacrificed by decapitation on 1, 7, 15 and 30 days after the last 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.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Strontium (fly ash)
- IUPAC Name:
- Strontium (fly ash)
- Test material form:
- not specified
- Details on test material:
- - Name of test material (as cited in study report): Strontium (fly ash)
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 maintaine dcolony (Department of Biochemistry, V.P. Chest Institute, Univercity of Delhi)
- Weight at study initiation: 170-175 g bw
- Diet (ad libitum): Hind Lever diet (Hindustan Lever Ltd., Bombay)
- Water (ad libitum): free access before and after exposure
No further information given.
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- not specified
- Vehicle:
- other: unchanged (no vehicle)
- Details on inhalation exposure:
- - rats were exposed in an inhalation chamber (624 liters capacity)
- The fly ash was collected from electrostatic precipitator of the IP Thermal power Plant New Dehli, using low sulfur pulverized coal during its operation.
- To remove coarser particles fly ash sample was sieved through 400 mesh sieve and this sieved material was used for inhalation studies.
- The approximate particle size of fly ash was determined using a light microscope fitted with an eyepiece graticule. This method could give an over estimate of particle size.
- The fly ash aerosol was generated by a Wright dust geneator and the dust cloud passed through alarge glass vessel, before entering the inhalation chamber.
- The dust concentration in the chamber was maintained between 0.2 to 0.4 mg/liter.
- Control rats were kept in a dust free room.
No further information given. - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 15 days
- Frequency of treatment:
- 6 hours/d , daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
between 0.2 - 0.4 mg/L
Basis:
no data
- No. of animals per sex per dose:
- 6 rats in each group analysed at each sacrifice period
- Control animals:
- yes
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: Records of the 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
OTHER:
- Before sacrifice, blood was collected from the jugular vein for serum preparation. serum was processed for quantification of metals by atomic absorption spectrophotometry.
- After sacrifice, lung, liver, heart, kidney, and small intestine was collected, cleaned, wiped, weighed and processed for quantification of metals by atomic absorption spectrophotometry.
-The following metals of fly ash were analyzed: Na, K, Fe, Ca, Mg, Pb, Zn, Cu, Co, Ni, Cr, Mn and Sr.
- Their distribution in lung, liver, heart, kidney, small intestine and serum was studied. - Sacrifice and pathology:
- - Rats of control and experimental groups were sacrificed by decapitation on 1, 7, 15 and 30 days after the last exposure.
GROSS PATHOLOGY: No data
HISTOPATHOLOGY: No data
Results and discussion
Results of examinations
- Details on results:
- OTHER FINDINGS
- 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 serum of rats which inhaled fly ash.
- 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 tissues of rats which inhaled 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 contents in all tissues were the lowest of all metals studied (0.2±0.1 to 0.3±0.1 µg/g wet tissue).
- The values tended to be higher at 1, 7 and 15 days.
- After 30 days, the fly ash Sr load from lung, liver, heart, kidney and small intestine was cleared to values of the control group.
Effect levels
- Dose descriptor:
- NOAEC
- Remarks on result:
- not determinable
- Remarks:
- no NOAEC identified
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- The results show the translocation of inhaled fly ash metals including Sr to extra-pulmonary organs. The study is not appropriate for derivation of a NOAEL.
- Executive summary:
Wistar rats (170-175 g body weight) were exposed daily to fly ash in an inhalation chamber for 6 hours/d continuously for 15 days. The dust concentration in the chamber was maintained between 0.2 to 0.4 mg/L. The following metals of fly ash were analyzed: Na, K, Fe, Ca, Mg, Pb, Zn, Cu, Co, Ni, Cr, Mn and Sr. Their distribution in lung, liver, heart, kidney, small intestine and serum was studied. The strontium contents in all tissues were the lowest of all metals studied. The values tended to be higher at 1, 7 and 15 days. After 30 days, the fly ash strontium load from lung, liver, heart, kidney and small intestine was cleared. The results showed the translocation of inhaled fly ash metals including strontium to extra-pulmonary organs. However, this study is not considered to be of any relevance for risk assessment purposes.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.