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Diss Factsheets
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EC number: 701-338-8 | CAS number: -
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- other: expert statement
- Title:
- No information
- Author:
- Dollenmeier P
- Year:
- 2 010
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: ECHA REACH Guidance R.7.12
- Principles of method if other than guideline:
- Paper based review of toxicokinetics
- GLP compliance:
- no
Test material
- Reference substance name:
- 2,5-Furandione, dihydro-, mono-C15-20-alkenyl derivs.
- EC Number:
- 272-221-2
- EC Name:
- 2,5-Furandione, dihydro-, mono-C15-20-alkenyl derivs.
- Cas Number:
- 68784-12-3
- Molecular formula:
- Due to a mixture of numerous isomers a specific molecular formular cannot be provided ( UVCB-substance) .
- IUPAC Name:
- 2,5-Furandione, dihydro-, mono-C15-20-alkenyl derivs.
Constituent 1
Results and discussion
Any other information on results incl. tables
Non-human information
An experimental study on the toxicokinetics of ASA is not available.
Because ASA is an UVCB substance, model calculations have been done with an idealized molecule (ASA1, structure inserted, Smiles: C1(C(C=CCCCCC)CCCCCC)CC(=O)OC1=O) ) , which may be a component of ASA:
ASA1 as well as the other components of ASA is highly lipophilic. Calculation of the water solubility and the partition coefficient of ASA1, by EPISuite 4.0, results in a water solubility of 7.4 µg/L and a log Powof 7.32.
Absorption
Skin absorption
According to the skin permeability model of Fitzpatrick et. al. (2004) the model substance ASA1 is able to penetrate the skin. The result of the model calculation is confirmed with the observation of a skin sensitizing potential of ASA in the study according to Magnusson-Kligman (OECD 406).
Skin permeability according to Fitzpatrick et al. (2004) |
Values |
|
Chemical |
|
ASA |
Molecular weight of chemical |
Mw (Da) |
294.44 |
Logarithm octanol/water partition coefficient |
logKow |
7.32 |
Logarithm skin permeation coefficient |
logKp |
0.236594 |
|
|
|
Interpretation: |
|
permeable |
non-permeable |
< -10 |
|
marginally permeable |
< -06 >= -10 |
|
slightly permeable |
< -03 >= -06 |
|
moderately permeable |
< -01 >= -03 |
|
permeable |
> = -01 |
|
Oral absorption
The combined repeated dose / reproductive toxicity study in the rat (OECD 422) showed in the top dose of 1000 mg/kg bw/day elevated levels of liver-derived enzymes in the plasma and at the top and lower doses signs of reduced maternal care. It is therefore concluded that ASA is absorbed and enters circulation following oral exposure.
Metabolism
An experimental study on the metabolism of ASA is not available.
It is considered that enzymatic hydrolysis of ASA is an early step in metabolism. Hydrolases (EC 3.6) are known to be present in the cells of the intestinal tract, in the plasma, the liver and other organs. The resulting alkenylated succinic acid is similar to (rare) naturally occurring fatty acids, alkylitaconates, which are known to be degraded in the liver (Ref [1]).
It is considered that the metabolic breakdown of alkenylated succinic acid occurs by the binding of CoA and subsequent release of Acetyl-CoA, which is used in many metabolic steps (e.g. fatty acid synthesis) or degradation in the citric acid cycle. The other resulting molecule is an unsaturated fatty acid, which in turn is degraded similar to natural fatty acids.
Human information
No human information is available.
Summary and discussion of toxicokinetics
Experimental data on the toxicokinetics of ASA are not available. Based on observations made in repeated dose toxicity studies it is considered ASA is absorbed following oral exposure. Model calculation show that the substance is also absorbed following dermal exposure.
It is considered that ASA is metabolized and degraded similarly to fatty acids.
References
Fitzpatrick, D., Corish, J., Hayes, B. (2004). Modelling skin permeability in risk assessment – the future. Chemosphere 55 , 1309 –1314.
Adler, J. Shu-Fang Wang, AND Henry A. Lardy (1957): The metabolism of itaconic acid by liver mitochondria. .J Biol Chem.1957 Dec;229(2):865-79. Available from:www.jbc.org/content/229/2/865.full.pdf
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): low bioaccumulation potential based on study results
Based on observations made in repeated dose toxicity studies, it is considered that the substance is absorbed following oral exposure. Model calculations show that the substance is also absorbed following dermal exposure. It is considered that ASA is metabolized and degraded similarly to fatty acids.
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