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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Toxicological information

Basic toxicokinetics

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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:
2010

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

Constituent 1
Chemical structure
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.

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.