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EC number: 604-314-4 | CAS number: 142844-00-6
- 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
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- Nanomaterial radical formation potential
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- 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

Epidemiological data
Administrative data
- Endpoint:
- epidemiological data
- Type of information:
- other: Epidemiological survey of exposure and health
- Adequacy of study:
- supporting study
- Study period:
- 1994-1998
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study done to the highest standards by independent institute with international colaboration
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 999
- Report date:
- 1999
Materials and methods
- Study type:
- cross sectional study
- Endpoint addressed:
- repeated dose toxicity: inhalation
Test guideline
- Qualifier:
- no guideline required
Test material
- Reference substance name:
- oxo[(oxoalumanyl)oxy]alumane; silanedione
- EC Number:
- 604-314-4
- Cas Number:
- 142844-00-6
- Molecular formula:
- amorphous glass Si(n)O(3n+1) polymeric anions bonded to Zr and Al(3+)
- IUPAC Name:
- oxo[(oxoalumanyl)oxy]alumane; silanedione
- Details on test material:
- - Name of test material (as cited in study report):RCF
Constituent 1
Method
- Type of population:
- occupational
- Ethical approval:
- confirmed and informed consent free of coercion received
- Details on study design:
METHOD OF DATA COLLECTION
- Type: Questionnaire, Work history and Clinical tests.
- Details: Target population comprised all current workers associated with RCF production plus others, who had left the industry (774 workers 90% of current workers and 37% of leavers). Information was collected on personal characteristcs, chest radiographs, lung function, respiratory symptoms, smoking, and full occupational history. Regression analysis was used to study relations between indices of health and cumulative exposure to airborne dust and fibres and likely past exposure to asbestos.
STUDY PERIOD:1994-1998- Exposure assessment:
- measured
- Details on exposure:
- TYPE OF EXPOSURE: airbourne dust
TYPE OF EXPOSURE MEASUREMENT: Personal sampling for fibre concentration and total inhalable and total respirable dust (including silica) and fibres.
Results Fibres : <0.1 f/ml up to 0.4 f/ml depending on occupational groups and plant. Secondary conversion and finishing gave higher concentrations with results ranging from 0.3 f/ml up to 1.25 f/ml. Total inhalable dust was low when compared to current occupational hygiene standards. Respirable quartz was seldom detected, the highest recorded result from 200 samples was only 0.015 mg/m3, consequently no further action was taken on quartz measurements.
EXPOSURE PERIOD: 1995-1996
POSTEXPOSURE PERIOD:varies by worker but was documented - ongoing programme of sampling to same standards - Statistical methods:
- Regression analysis
Results and discussion
- Results:
- The individual cumulative exposure was calculated for each worker and regressed against clinical results.
Radiology: Prevalence of small opacities -760 individuals provided x-rays for this survey it was difficult to find any coherent pattern in the results. Small opacities of profusion 1/0+ were not associated to life time accumulated exposures to fibres and dust however a positive association was suggested with exposures up to 1971. There was little or no evidence of a positive association with later exposures.
Pleural changes of any kind were seen on 11% of radiographs with pleural plaques on 5% . Pleural plaques and pleural changes more generally were both associated with age and exposure to asbestos there was no evidence that exposure to RCF was additionally associated with pleural changes on the chest radiographs.
Lung function : There was no association between cumulative exposure to respirable fibres and lung function in the study population overall. Among men FEV1 and FVC decreased with increased exposure but only in current smokers .On average the effect on male smokers was mild (100ml for average life time exposure to RCF).
Respiratory symptoms- Breathlessness did not show any association with exposure but reports of recurrent chest illness were associated with cumulative exposure to both fibres and dust.
Summary
The authors concluded that it was premature to speculate on the nature of any response if indeed there is any adverse effect of RCF. - Confounding factors:
- Asbestos and smoking were the major confounding factors.
- Strengths and weaknesses:
- The study population represents most of the wokers exposed but this is still a small population and exposures are low.
Any other information on results incl. tables
The full report may be down loaded form the Institute of Occupational Medicine (IOM) web site (www.iom-world.org)
Cowie et al (2001) Epidemiological Research in the European Ceramic Fibre Industry 1994 -1998 A study of the respiratory Health of Workers in the European RCF Industry; Occupational and Environmental medicine,Volume 58, pages 800 -810
Applicant's summary and conclusion
- Conclusions:
- If there is any adverse effect of RCF it will only become apparent after further cross sectional studies on workers who have been exposed for longer.
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