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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Endpoint:
adsorption / desorption
Remarks:
other: (Q)SAR
Type of information:
(Q)SAR
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Accepted (Q)SAR method
Justification for type of information:
QSAR prediction: migrated from IUCLID 5.6

Data source

Reference
Reference Type:
publication
Title:
KOCWIN 2.00, included in EPI Suite 4.00
Author:
EPA's Office of Pollution Prevention Toxics and Syracuse Research Corporation (SRC)
Year:
2008
Bibliographic source:
U.S. Environmental Protection Agency 2000-2008 (http://www.epa.gov/oppt/exposure/pubs/episuite.htm)

Materials and methods

Test guideline
Guideline:
other: REACH guidance on QSARs R.6, May 2008
Principles of method if other than guideline:
Model for predicting the soil-sorption coefficient (Koc) for nonpolar organics.
GLP compliance:
not specified

Test material

Constituent 1
Chemical structure
Reference substance name:
Crotonaldehyde
EC Number:
224-030-0
EC Name:
Crotonaldehyde
Cas Number:
4170-30-3
Molecular formula:
C4H6O
IUPAC Name:
but-2-enal
Details on test material:
SMILES: O=CC=CC
log Kow value of 0.6 was used for the model.

Study design

Batch equilibrium or other method

Computational methods:
- Adsorption coefficient per organic carbon (Koc): KOCWIN 2.00

Results and discussion

Adsorption coefficientopen allclose all
Type:
Koc
Value:
10.66
Type:
log Koc
Value:
1.028

Results: HPLC method

Details on results (HPLC method):
Validity of model:
1. Defined endpoint: Soil sorption coefficient Koc
2. Unambiguous algorithm: Linear regression QSAR;  log Koc  =  0.55313 Log Kow  +  0.9251 + SPfN; where SPfN is the sum of all correction factors applicable for the substance. In case of crotonaldehyde the following correction factor applied:
Miscellaneous (C=O) group (aliphatic attachment): -0.2293
3. Applicability domain: Currently, there is no universally accepted definition of a model domain. The molecular weights of the chemicals used for the regression are within the range from 32.04 to 665.02. Using this QSAR for estimating a Koc outside this range is not recommended.
4. Statistical characteristics: N = 447; Coefficient of Determination (r²) = 0.855
5. Adequacy of prediction: The molecular weight of crotonaldehyde of 70.09 is within the range recommended for the model. Therefore, a sufficient adequacy of the model for predicting the soil sorption coefficient for the test substance is given.

Applicant's summary and conclusion

Conclusions:
The substance crotonaldehyde was predicted to have a soil sorption coefficient (Koc) of 10.66 L/kg, corresponding to a log Koc of 1.0277.