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EC number: 297-648-1 | CAS number: 93685-99-5 Oil shale waste is produced by thermal processing in a fluidized bed process at 800°C from mining exhausted oil shale. Oil shale waste consists essentially of Al2O3, CaO, CaSO4, Fe2O3 and SiO2.
- 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

Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.233 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 3
- Dose descriptor:
- LOAEC
- AF for dose response relationship:
- 3
- Justification:
- Extrapolation from LOAEC to NAEC
- AF for differences in duration of exposure:
- 1
- AF for interspecies differences (allometric scaling):
- 1
- AF for other interspecies differences:
- 1
- AF for intraspecies differences:
- 1
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - workers
For the alveolar fraction (aerodynamic diameter <5 µm) of crystalline silica, epidemiological data indicate that the LOAEC (human) for silicosis is 0.05 mg/m³. Applying an assessment factor 3 to account for extrapolation from a LOAEC to a NAEC, results in a DNEL for the alveolar crystalline silica fraction of 0.017 mg/m³ [(0.05 mg/m³)/3]. No further assessment factors for workers are required as the LOAEC was determined from data of subjects occupationally exposed (8-10 h/day for a working lifetime) to respirable silica particles.
Comparable results are obtained from animal data. The lowest published toxic concentration for chronic inhalation exposure in rats is 0.74 mg/m³ (Muhle et al., 1991; NTP, 2009). Rats were exposed to crystalline silica particles (MMAD 1.4 µm) at that analytic concentration for 6 h/day, 5 days/week for 24 months.
A DNEL value for the alveolar fraction of crystalline silica is derived by applying the following corrections and assessment factors:
Step 1) Relevant dose descriptor |
LOAECrat= 0.74 mg/m³ |
Step 2) Modification of starting point Correction differences between experimental and human exposure conditions Correction for differences in 8-h inhalative volumes between workers in rest and workers under light activity |
(6 h/day)/(8 h/day)
6.7 m³/10 m³ |
Step 3) Assessment factors Interspecies Intraspecies Exposure duration Dose response Quality of data base |
2.5 5 1 3 1 |
DNEL value for the alveolar crystalline silica fraction |
0.01 mg/m³ (0.74 x [6/8] x [6.7/10] x [1/(2.5 x 5 x 3)]) |
Rather than the value based on rat data, the value of 0.017 mg/m³ obtained from human data is used as DNEL for the alveolar fraction of crystalline silica particles.
As the above mentioned DNEL values applies for the alveolar fraction of crystalline silica particles, DNEL values for burnt oil shale, total dust, are derived taking into account the content of respirable particles (≤4 µm) as well as the total quartz contents.
Chemical composition, granulometry and crystallinity data are available for 2 burnt oil shale samples:
Sample |
P.1034 |
P.1082 |
Quartz content |
22% |
17% |
Particles ≤4 µm (alveolar fraction) |
33.4% |
39.1% |
Overall alveolar quartz fraction (assuming homogeneous distribution of quartz throughout all particle size fractions) |
0.22×0.334= 0.073 |
0.17×0.391= 0.066 |
DNEL for alveolar crystalline silica (mg/m³) |
0.017 |
0.017 |
DNEL for burnt oil shale, total dust (mg/m³) |
0.233 |
0.258 |
The lower DNEL value of 0.233 mg/m³ is used for burnt oil shale, total dust.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.233 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 3
- Dose descriptor starting point:
- LOAEC
- AF for dose response relationship:
- 3
- Justification:
- Extrapolation from LOAEC to NAEC
- AF for interspecies differences (allometric scaling):
- 1
- AF for other interspecies differences:
- 1
- AF for intraspecies differences:
- 1
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Oral
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - General Population
The general public can be exposed to burnt oil shale in cement. The use of cement by the general population is infrequent and short-term/acute. Individuals using cement are healthy adults so that the intraspecies factor of 5 for workers can be adopted. Additional safety is introduced by using long-term epidemiological data as point of departure. Thus, the long-term inhalation DNEL for workers is adopted for the general population.
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