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EC number: 265-057-8 | CAS number: 64741-56-6 A complex residuum from the vacuum distillation of the residuum from atmospheric distillation of crude oil. It consists of hydrocarbons having carbon numbers predominantly greater than C34 and boiling above approximately 495°C (923°F).
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
This information was not available. Testing proposal for extendended one-generation study has been submitted.
Effect on fertility: via oral route
- Endpoint conclusion:
- no study available
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available (further information necessary)
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
No reproductive study on bitumen has been performed. However, based on the results from repeated-dose toxicity studies, dermal exposure to bitumen at doses up to 2000 mg/kg did not show any treatment related effects on reproductive organ weights and histopathology.
Table 1. Summaries of data on reproductive organs from subchronic studies with bitumen (Robust study summaries are provided in Section 7.5 Repeated Dose Toxicity) |
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Test Material |
Route, Species, Doses, Exposure Regimen |
Endpoints |
Results |
Reference |
Vacuum residuum (API 81-13) |
Dermal. Rabbit. 0, 200, 1000, 2000 mg/kg, applied on a gauze pad and wrapped for 6 hr, 3 d/wk for 4 wk |
Weights of testes and ovaries. Histopathology of seminal vesicles, testes, epididymides, prostate, ovaries, uterus, and vagina |
No treatment-related effect on reproductive organs noted. |
API, 1983a |
Vacuum residuum (API 81-14) |
Dermal. Rabbit. 0, 200, 1000, 2000 mg/kg, applied on a gauze pad and wrapped for 6 hr, 3 d/wk for 4 wk |
Weights of testes and ovaries. Histopathology of seminal vesicles, testes, epididymides, prostate, ovaries, uterus, and vagina |
No treatment-related effect on reproductive organs noted. |
API, 1983b |
The need for an extended one-generation reproductive toxicity study with bitumen is considered questionable based on the following observations.
1) No effects were seen in weights of testes or ovaries or in the histopathology of seminal vesicles, testes, epididymides, prostate, ovaries, uterus, or vagina in two 4-week dermal studies in rabbits with bitumen at doses up to 2000 mg/kg.
2) Additional supporting evidence comes from separate dermal screening-level fertility studies of syntower bottoms in males and females. The NOAEL was = 250 mg/kg/day. Although not in the bitumen category, this test substance contains significantly higher levels of PACs than bitumen and is one of the more toxic petroleum streams.
Nonetheless, there is a clear data gap with respect to the REACH Annex X testing requirements for an extended one-generation reproductive toxicity study. Therefore an OECD guideline 443 study is proposed.
Short description of key information:
No reproductive study on bitumen has been performed. However, some indication of the likely effect of a test substance on reproductive organs can be gained from the results of repeated-dose toxicity studies where the weights and histopathology of reproductive organs were not affected following dermal exposure to bitumen at doses up to 2000 mg/kg.
Effects on developmental toxicity
Description of key information
Note on choice of exposure route:
A developmental inhalation study on bitumen has been performed. Bitumen is a (semi) solid material, therefore it is considered that any potential exposure is solely to the fumes that may arise during occupational handling of the material at elevated temperatures. This study was therefore performed via the inhalation route as this is considered the only relevant route of human exposure, which means that sufficient Bitumen and OA fumes, collected as condensates, were generated before the studies can be conducted.
An additional complexity with applying this approach is that the composition of the condensate is influenced by the occupational conditions, mainly the temperature at which the Bitumen is heated when applied. Thus, Concawe has validated the composition of the condensate collected at the manufacturing site against actual workplace fume samples through a workplace monitoring campaign to ensure that the tested material is representative of real-life exposures.
Full reports of fume collection and validation, as well as workplace monitoring campaigns and fume condensate comparisons, are available from Concawe upon request.
Brief summary of results:
The maternal NOAEL was determined to be the low dose group, 50 mg/m³. Observations at 500 mg/m³ included effects on body weight, food consumption, lung weight and histopathological changes in the lung and larynx. At 150 mg/m³ observations were restricted to histopathological changes in the larynx.
The developmental NOAEL was the medium dose group, 150 mg/m³, due to reduced fetal weight at 500 mg/m³.
Importantly, nose-only exposure to bitumen fumes in concentrations up to 500 mg/m³ from p.c days 1 to 19, did not induce any fetal anomalies.
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEC
- 150 mg/m³
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- A single study study was conducted on a worst case test sample representing the category members. This category approach is further supported with additional historical data on the substances (available in this IUCLID dossier and the Category Justification Document), as well as ongoing mechanistic work to further support the worst case approach (see mechanism of action field below)
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Mode of Action Analysis / Human Relevance Framework
Concawe initiated a multi-year research project in 2015 to generate further proof for the mechanistic basis underpinning the hypothesis that developmental toxicity is related to (3-7 ring) PAHs, supporting selection of the test sample with highest PAH content as a worst case representative and further supporting read across between the substances in the Concawe Bitumen category. Initial results are presented in the publication: Prenatal developmental toxicity testing of petroleum substances: Application of the mouse embryonic stem cell test (EST) to compare in vitro potencies with potencies observed in vivo; Lenny Kamelia, Jochem Louisse, Laura de Haan, Ivonne M.C.M. Rietjens, Peter J. Boogaard; To appear in: Toxicology in Vitro; Accepted date: 19 July 2017.
Justification for classification or non-classification
Currently available data do not raise concern with regard to classification of bitumen as toxic for reproduction or development under CLP Regulation, (EC)1272/2008.
Additional information
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.
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