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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
Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2010-03-05 - 2010-04-22
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP - Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5100 - Bacterial Reverse Mutation Test (August 1998)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Oil shale, thermal processing residue
- IUPAC Name:
- Oil shale, thermal processing residue
- Reference substance name:
- Oil shale, thermal processing waste
- EC Number:
- 297-648-1
- EC Name:
- Oil shale, thermal processing waste
- Cas Number:
- 93685-99-5
- Molecular formula:
- Not applicable (UVCB substance)
- IUPAC Name:
- tricalcium oxo[(oxoalumanyl)oxy]alumane oxo[(oxoferrio)oxy]iron silanedione carbonate oxidandiide sulfate
- Details on test material:
- - Name of test material (as cited in study report): Burnt Oil shale (BOS)
- Physical state: greish-reddish fine powder
- Analytical purity: no data
- Lot/batch No.: P.1082
- Expiration date of the lot/batch: not applicable
- Storage condition of test material: room temperature, avoid moisture
- Density: ca. 2.8 [g/m³]
Constituent 1
Constituent 2
Method
- Target gene:
- his-operon
Species / strain
- Species / strain / cell type:
- S. typhimurium, other: TA 1535, TA 1537, TA 98, TA 100 and TA 102
- Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- rat liver S9-mix (phenobarbital and β-naphthoflavone induced)
- Test concentrations with justification for top dose:
- 0 (solvent control), 31.6, 100, 316, 1000, 2500 and 5000 µg/plate
- Vehicle / solvent:
- Aqua dest.
Controls
- Untreated negative controls:
- not specified
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- not specified
- Positive controls:
- yes
- Positive control substance:
- other: -S9: 4-nitroquinoline-N-oxide (10 µg/plate for TA 98, 40 µg/plate for Ta 1537), sodium azide (10 µg/plate), methylmethanesulfonate (1 µl/plate), +S9: 2-aminoanthracene (2.5 µg/plate; 10 µg/plate for TA 102)
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: Two experiments were performed: in agar (plate incorporation) (experiment 1) and preincubation (Experiment 2)
DURATION
- Preincubation period: 60 min (experiment 1)
- Exposure duration: 48 hours
NUMBER OF REPLICATIONS: triplicates
DETERMINATION OF CYTOTOXICITY
- Method: background lawn or reduction in the number of revertants - Evaluation criteria:
- Evaluation of cytotoxicity:
Cytotoxicity can be detected bay a clearing or rather diminution of the background lawn or a reduction in the number of revertants down to a mutation factor of approximately ≤ 0.5 to the solvent control.
Evaluation of mutagenicity:
The mutation factor is calculated by dividing the mean value of the revertant counts through the mean values of the solvent control.
A test item is considered as mutagenic if:
- a clear and dose-related increase in the number of revertants occurs and/or
- a biologically relevant positive response for at least one of the dose groups occurs in at least one tester strain with or without metabolic activation.
A biologically relevant increase is described as follows:
- if a tester strains TA 100 and TA 102 the number of reversions is at least twice as high
- if in tester strains TA 98, TA 1535 and TA 1537 the number of reversions is at least three times higher than the reversion rate of the solvent control. - Statistics:
- No data
Results and discussion
Test results
- Species / strain:
- S. typhimurium, other:
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Remarks on result:
- other: strain/cell type:
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Table 1: Ames Test Results - Experiment 1
With or without S9-Mix |
Test substance concentration (μg/plate) |
Mean number of revertant colonies per plate |
||||
Base-pair substitution type |
Frameshift type |
|||||
TA 98 |
TA 100 |
TA 1535 |
TA 1537 |
TA 102 |
||
- |
Neg. control (a. dest.) |
22 |
115 |
17 |
11 |
301 |
- |
31.6 |
21 |
98 |
14 |
14 |
290 |
- |
100 |
20 |
95 |
11 |
9 |
288 |
- |
316 |
23 |
111 |
16 |
12 |
367 |
- |
1000 |
20 |
117 |
17 |
12 |
372 |
- |
2500 |
27 |
138 |
14 |
15 |
396 |
- |
5000 |
27 |
134 |
12 |
12 |
380 |
Positive controls - S9 |
Name |
4-NOPD |
NaN3 |
NaN3 |
4-NOPD |
MMS |
Concentrations (μg/plate) |
10 |
10 |
10 |
40 |
1 µl/plate |
|
Number of colonies/plate |
418 |
815 |
921 |
206 |
1666 |
|
|
TA 98 |
TA 100 |
TA 1535 |
TA 1537 |
TA 102 |
|
+ |
Neg. control (a. dest.) |
28 |
131 |
10 |
9 |
204 |
+ |
31.6 |
35 |
124 |
10 |
18 |
212 |
+ |
100 |
29 |
117 |
10 |
13 |
211 |
+ |
316 |
30 |
125 |
10 |
11 |
176 |
+ |
1000 |
35 |
122 |
8 |
14 |
203 |
+ |
2500 |
28 |
141 |
11 |
13 |
250 |
+ |
5000 |
23 |
134 |
6 |
17 |
213 |
Positive controls + S9 |
Name |
2-AA |
2-AA |
2-AA |
2-AA |
2-AA |
Concentrations (μg/plate) |
2.5 |
2.5 |
2.5 |
2.5 |
10 |
|
Number of colonies/plate |
2484 |
2251 |
201 |
439 |
1692 |
Table 2: Ames Test Results - Experiment 2
With or without S9-Mix |
Test substance concentration (μg/plate) |
Mean number of revertant colonies per plate |
||||
Base-pair substitution type |
Frameshift type |
|||||
TA 98 |
TA 100 |
TA 1535 |
TA 1537 |
TA 102 |
||
- |
Neg. control (a. dest.) |
19 |
117 |
10 |
6 |
325 |
- |
31.6 |
26 |
128 |
11 |
7 |
331 |
- |
100 |
31 |
138 |
12 |
12 |
348 |
- |
316 |
32 |
137 |
12 |
5 |
354 |
- |
1000 |
36 |
153 |
10 |
11 |
362 |
- |
2500 |
27 |
152 |
7 |
12 |
407 |
- |
5000 |
28 |
128 |
10 |
11 |
452 |
Positive controls - S9 |
Name |
4-NOPD |
NaN3 |
NaN3 |
4-NOPD |
MMS |
Concentrations (μg/plate) |
10 |
10 |
10 |
40 |
1 µl/plate |
|
Number of colonies/plate |
578 |
994 |
989 |
134 |
1678 |
|
|
TA 98 |
TA 100 |
TA 1535 |
TA 1537 |
TA 102 |
|
+ |
Neg. control (a. dest.) |
37 |
115 |
8 |
7 |
290 |
+ |
31.6 |
31 |
117 |
6 |
10 |
280 |
+ |
100 |
28 |
120 |
13 |
11 |
310 |
+ |
316 |
35 |
116 |
8 |
11 |
268 |
+ |
1000 |
26 |
114 |
8 |
12 |
323 |
+ |
2500 |
33 |
113 |
7 |
9 |
326 |
+ |
5000 |
34 |
139 |
10 |
14 |
305 |
Positive controls + S9 |
Name |
2-AA |
2-AA |
2-AA |
2-AA |
2-AA |
Concentrations (μg/plate) |
2.5 |
2.5 |
2.5 |
2.5 |
10 |
|
Number of colonies/plate |
2432 |
1411 |
95 |
207 |
1079 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
Under the experimental conditions, Oil shale, thermal processing waste did not cause gene mutations by base pair changes or frameshifts in the genome of the tester strains used. Therfore, Oil shale, thermal processing waste is considered to be non-mutagenic in this bacterial reverse mutation assay. - Executive summary:
In order to investigate the potential of Oil shale, thermal processing waste for its ability to induce gene mutations the plate incorporation test (experiment 1) and the pre-incubation test (experiment 2) were performed with Salmonella typhimurium strains TA 98, TA 100, TA 1535, TA 1537 and TA 102. In 2 independent experiments several concentrations of the test item were used. Each assay was conducted with and without metabolic activation. The concentrations, including the controls, were tested in triplicate. The following concentrations of the test item were prepared and used in the experiments: 31.6, 100, 316, 1000, 2500 and 5000 µg/plate. Precipitation of the test item was observed in all tester strains used in experiment 1 and 2 (with and without metabolic activation).
No toxic effect of the test item were noted in any of the 5 tester strains used up to the highest dose group evaluated in both experiments with the exception of a toxic effect noted in strain TA 100 at a concentration of 5000 µg/plate in experiment 2.
No biologically relevant increases in revertant colony numbers of any of the 5 tester strains were observed following treatment with Oil shale, thermal processing waste at any concentration level, neither in the presence nor absence of metabolic activation.
The reference mutagens induced a distinct increase of revertant colonies indicating the validity of the experiment.
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