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EC number: 211-330-1 | CAS number: 638-29-9
- 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
Partition coefficient
Administrative data
- Endpoint:
- partition coefficient
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- 1. SOFTWARE
The Estimation Programs Interface (EPI) SuiteTM was developed by the US Environmental Protection Agency's Office of Pollution Prevention
and Toxics and Syracuse Research Corporation (SRC). It is a screening-level tool, intended for use in applications such as to quickly screen
chemicals for release potential and "bin" chemicals by priority for future work. Estimated values should not be used when experimental
(measured) values are available.
2. MODEL (incl. version number)
EPI SUMMARY (v4.11), Log Kow(version 1.68 estimate)
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
O=C(CCCC)CL
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
QMRF: Estimation of Octanol-Water Partition Coefficient using KOWWIN v1.68 (EPI Suite v4.11)
1.0 QSAR identifier
1.1 QSAR identifier (title)
Estimation of Octanol-Water Partition Coefficient using KOWWIN v1.68 (EPI Suite v4.11)
1.2 Other related models
-
1.3 Software coding the model
KOWWIN v1.68 (EPI Suite v4.11)
2.0 General information
2.1 Date of QMRF
01 Nov. 2013
2.2 QMRF author and contact details
BASF SE, Department of Product Safety, Ludwigshafen, Germany
2.3 Date of QMRF update(s)
-
2.4 QMRF update(s)
-
2.5 Model developer(s) and contact details
WM Meylan and PH Howard, US EPA
2.6 Date of model development and/or publication
Publication of first model: 1995
2.7 References to main scientific papers and/or software package
Meylan, W.M. and P.H. Howard. 1995. Atom/fragment contribution method for estimating octanol-water partition coefficients. J. Pharm. Sci. 84: 83-92
2.8 Availability of information about the model
The model is non-proprietary and can be downloaded freely from US EPA.
2.9 Availability of another QMRF for exactly the same model
No (http://qsardb.jrc.it/qmrf/).
3.0 Defining the endpoint
3.1 Species
3.2 Endpoint
Log Kow at 25 °C
3.3 Comment on the endpoint
Regulation (EC) No 1907/2006 [REACH], Annex VII, 7.8 Partition coefficient octanol/water
3.4 Endpoint units
mg/L
3.5 Dependent variable
log S (mol/L)
3.6 Experimental protocol
The log Kow of a substance can be determined according to OECD guideline 107 or OECD guideline 117.
3.7 Endpoint data quality
4.0 Defining the algorithm
4.1 Type of model
QSAR (QSPR)
4.2 Explicit algorithm
KOWWIN uses a "fragment constant" methodology to predict log Kow. In a "fragment constant" method, a structure is divided into fragments (atom or larger functional groups) and coefficient values of each fragment or group are summed together to yield the log Kow estimate. KOWWIN’s methodology is known as an Atom/Fragment Contribution (AFC) method. Coefficients for individual fragments and groups were derived by multiple regression of 2447 reliably measured log Kow values. Correction factors were developed to be able to consider larger or more complex substructures than the fragments (“atoms”).
log Kow =Σ(fini)+Σ(cjnj)+0.229
(num = 2447, r2= 0.982, std dev = 0.217, mean error = 0.159)
Where:
1)Σ(fini) is the summation offi(the coefficient for each atom/fragment) timesni(the number of times the atom/fragment occurs in the structure)
2)Σ(cjnj) is the summation ofcj(the coefficient for each correction factor) timesnj(the number of times the correction factor occurs (or is applied) in the molecule).
4.3 Descriptors in the model
SMILES: structure of the compound as SMILES notation; The chemical structure (as SMILES) is the only required descriptor for estimating the water solubility. All other descriptors can be derived from the chemical structure.
Fragments: The structure is divided into fragments (atom or larger functional groups).
Correction factors: The correction factors were derived from a multiple linear regression that correlated differences between the experimental log Kow and the log Kow estimated by the initial equation [log Kow = Σ(fini) + b; where b is the linear equation constant] with the correction factor descriptors.
4.4 Descriptor selection
Coefficients for individual fragments and groups were derived by multiple regression of 2447 reliably measured log Kow values. Correction factors were derived from differences between initially estimated log Kow values and the experimental data.
4.5 Algorithm and descriptor generation
SMILES: user entered (required for estimation)
Fragments and correction factors:taken from database
4.6 Software name and version for descriptor generation
KOWWIN v1.68 (EPI Suite v4.11)
4.7 Descriptor/Chemicals ratio
Training dataset: 2447 compounds with reliably measured data for log Kow
Descriptors:2 (Fragments and correction factors derived from chemical structure)
5.0 Defining the applicability domain
5.1 Description of the applicability domain of the model
The applicability domain is described by the range of the molecular weight of the training set as well as the identification and number of instances of a given fragment. The number of instances of a given fragment is compared to the maximum for all training set compounds. If this number exceeds the maximum number or a fragment is not identified, the estimate of a substance is regarded to be less accurate.
5.2 Method used to assess the applicability domain
The applicability is assessed by comparing the molecular weight and the given fragments of a compound with the corresponding values of the training set.
5.3 Software name and version for applicability domain assessment
-
5.4 Limits of applicability
Range of Molecular Weights in the Training set:
- Minimum = 18.02 g/mol
- Maximum = 719.92 g/mol
- Average = 199.98 g/mol
Structural features:
- See 6.1
6.0 Defining goodness-of-fit and robustness
6.1 Availability of the training set
The KOWWIN training and validation datasets can be downloaded from the Internet at:http://esc.syrres.com/interkow/KowwinData.htm.
Substructure searchable formats of the data can be downloaded at:http://esc.syrres.com/interkow/EpiSuiteData_ISIS_SDF.htm.
6.2 Available information for the training set
- CAS number
- Chemical name
- Molecular formula
- Data set (training set, validation set, diverse subsets)
- Measured log Kow
- Estimated log Kow (KOWWIN)
- Residual
- Reference for experimental data
6.3 Data for each descriptor variable for the training set
Descriptors derived from chemical structure, therefore not listed in database
6.4 Data for the dependent variable (response) for the training set
-
6.5 Other information about the training set
-
6.6 Pre-processing of data before modelling
-
6.7 Statistics for goodness-of-fit
Total Training Set Statistics:
- number in dataset = 2447
- correlation coefficient (r2) = 0.982
- standard deviation = 0.217
- absolute deviation = 0.159
- average molecular weight = 199.98
7.0 Defining predictivity
7.1 Availability of the external validation set
See 6.1
7.2 Available information for the external validation set
See 6.2
7.3 Data for each descriptor variable for external validation set
See 6.3
7.4 Data for the dependent variable for the external validation set
See 6.4
7.5 Other information about the external validation set
-
7.6 Experimental design of test set
References to data given
7.7
Total Validation Set Statistics:
- number in dataset = 10946
- correlation coefficient (r2) = 0.943
- standard deviation = 0.479
- absolute deviation = 0.356
- average Molecular Weight = 258.98
The external validation set of 10946 compounds contains 372 compounds that exceed the domain of instances of a given fragment or correction factor maximum for all training set compounds. The estimation accuracy for these compounds is:
Exceed Fragment Instance Domain - Accuracy Statistics:
- number in dataset = 372
- correlation coefficient (r2) = 0.939
- standard deviation = 0.731
- absolute deviation = 0.564
- average Molecular Weight = 460.0
Exceed Molecular Weight Domain - Accuracy Statistics:
- number in dataset = 103
- correlation coefficient (r2) = 0.879
- standard deviation = 0.815
- absolute deviation = 0.619
- average Molecular Weight = 802.16
Exceed BOTH Fragment & MW Domain - Accuracy Statistics:
- number in dataset = 75
- correlation coefficient (r2) = 0.879
- standard deviation = 0.905
- absolute deviation = 0.706
- average Molecular Weight = 812.70
Appendix F of the User’s Guide lists the 75 compounds that exceed both the fragment instance domain and molecular limit domain.
7.8 Predictivity - Assessment of the external validation set
-
8.0 Providing a mechanistic interpretation
8.1 Mechanistic basis of the model
The octanol-water partition coefficient is a physical property used extensively to describe a chemical's lipophilic or hydrophobic properties.KOWWIN uses a "fragment constant" methodology to predict log P. In a "fragment constant" method, a structure is divided into fragments (atom or larger functional groups) and coefficient values of each fragment or group are summed together to yield the log P estimate. KOWWIN’s methodology is known as an Atom/Fragment Contribution (AFC) method.
9.0 Miscellaneous information
9.1 Comments
-
9.2 Bibliography
- Meylan, W.M. and P.H. Howard. 1995. Atom/fragment contribution method for estimating octanol-water partition coefficients. J. Pharm. Sci. 84: 83-92
- US EPA (2012). On-Line KOWWIN User’s Guide.
5. APPLICABILITY DOMAIN
1. Substance
See “Test material identity”
2. General information
2.1 Date of QPRF
See “Data Source (Reference)”
2.2 QPRF author and contact details
See “Data Source (Reference)”
3. Prediction
3.1 Endpoint (OECD Principle 1)
Endpoint: Octanol-water partition coefficient (log Kow)
Dependent variable. Octanol-water partition coefficient (log Kow)
3.2 Algorithm (OECD Principle 2)
Model or submodel name. KOWWIN
Model version: v. 1.68
Reference to QMRF: QMRF: Estimation of Octanol-Water Partition Coefficient
using KOWWIN v1.68 (EPI Suite v4.11)
Predicted value (model result): See “Results and discussion”
Input for prediction: Chemical structure via CAS number or SMILES
Descriptor values: - Chemical structure
- Fragments
- Correction factors
3.3 Applicability domain (OECD principle 3)
Domains:
1) Molecular weight (range of test data set: 18.02 to 719.92 g/mol; On-Line KOWWIN User’s Guide, Ch. 6.2.3 Estimation Domain)
Substance (not) within range (120.58 g/mol)
2) Fragments: Number of instances of the identified fragments does not exceed the maximum number as listed in Appendix D (On-Line KOWWIN User’s Guide)
fulfilled.
3) Fragments: Substance has a functional group(s) or other structural features not represented in the training set, and for which no fragment coefficient was developed (Appendix D, On-Line KOWWIN User’s Guide)
applicable.
4) Correction factors: Number of instances of the identified correction factor does not exceed the maximum number as listed in Appendix D (On-Line KOWWIN User’s Guide)
fulfilled.
3.4 The uncertainty of the prediction (OECD principle 4)
According to REACH Guidance Document R.7a, (Nov. 2012), solubility in water is difficult to model accurately. For this reason, as well as the fact that the experimental error on solubility measurements can be quite high (generally reckoned to be about 0.5 log unit), the prediction of aqueous solubility is not as accurate as is the prediction of octanol/water partitioning.
3.5 The chemical mechanisms according to the model underpinning the predicted result (OECD principle 5)
The water solubility of a substance depends on its affinity for water as well as its affinity for its own crystal structure. In general, substances with high melting points have poor solubility in any solvent.
References
- US EPA (2012). On-Line KOWWIN User’s Guide.
Data source
Referenceopen allclose all
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 2 020
- Report date:
- 2020
- Reference Type:
- other: Estimation software
- Title:
- Estimation Programs Interface Suite for Microsoft Windows, v4.11
- Author:
- US-EPA
- Year:
- 2 012
- Bibliographic source:
- United States Environmental Protection Agency, Washington, DC, USA
Materials and methods
Test guideline
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Estimation of log Kow using KOWWIN v1.68
- GLP compliance:
- no
- Type of method:
- calculation method (fragments)
- Partition coefficient type:
- octanol-water
Test material
- Reference substance name:
- Valeryl chloride
- EC Number:
- 211-330-1
- EC Name:
- Valeryl chloride
- Cas Number:
- 638-29-9
- Molecular formula:
- C5H9ClO
- IUPAC Name:
- pentanoyl chloride
- Test material form:
- liquid
Constituent 1
Results and discussion
Partition coefficient
- Type:
- log Pow
- Partition coefficient:
- 1
- Temp.:
- 25 °C
- Remarks on result:
- other: The substance is within the applicability domain of the model.
Any other information on results incl. tables
SMILES : O=C(CCCC)CL
CHEM : Pentanoyl chloride
MOL FOR: C5 H9 CL1 O1
MOL WT : 120.58
-------+-----+--------------------------------------------+---------+--------
TYPE | NUM | LOGKOW FRAGMENT DESCRIPTION | COEFF | VALUE
-------+-----+--------------------------------------------+---------+--------
Frag | 1 | -CH3 [aliphatic carbon] | 0.5473 | 0.5473
Frag | 3 | -CH2- [aliphatic carbon] | 0.4911 | 1.4733
Frag | 1 | -CL [chlorine, aliphatic attach] | 0.3102 | 0.3102
Frag | 1 | -C(=O)- [carbonyl, aliphatic attach] |-1.5586 | -1.5586
Const | | Equation Constant | | 0.2290
-------+-----+--------------------------------------------+---------+--------
NOTE | | Acetyl halides hydrolyze....estimate questionable! |
-------+-----+--------------------------------------------+---------+--------
Log Kow = 1.0012
Applicant's summary and conclusion
- Executive summary:
QPRF: KOWWIN v1.68 (01 Nov. 2013)
1.
Substance
See “Test material identity”
2.
General information
2.1
Date of QPRF
See “Data Source (Reference)”
2.2
QPRF author and contact details
See “Data Source (Reference)”
3.
Prediction
3.1
Endpoint
(OECD Principle 1)Endpoint
Octanol-water partition coefficient (log Kow)
Dependent variable
Octanol-water partition coefficient (log Kow)
3.2
Algorithm
(OECD Principle 2)Model or submodel name
KOWWIN
Model version
v. 1.68
Reference to QMRF
QMRF: Estimation of Octanol-Water Partition Coefficient using KOWWIN v1.68 (EPI Suite v4.11)
Predicted value (model result)
See “Results and discussion”
Input for prediction
Chemical structure via CAS number or SMILES
Descriptor values
- Chemical structure
- Fragments
- Correction factors
3.3
Applicability domain
(OECD principle 3)Domains:
1) Molecular weight
(range of test data set: 18.02 to 719.92 g/mol; On-Line KOWWIN User’s Guide, Ch. 6.2.3 Estimation Domain)Substance (not) within range (120.58 g/mol)
2) Fragments: Number of instances of the identified fragments does not exceed the maximum number as listed in Appendix D (On-Line KOWWIN User’s Guide)
fulfilled.
3) Fragments: Substance has a functional group(s) or other structural features not represented in the training set, and for which no fragment coefficient was developed (Appendix D, On-Line KOWWIN User’s Guide)
applicable.
4) Correction factors: Number of instances of the identified correction factor does not exceed the maximum number as listed in Appendix D (On-Line KOWWIN User’s Guide)
fulfilled.
3.4
The uncertainty of the prediction
(OECD principle 4)According to REACH Guidance Document R.7a, (Nov. 2012), solubility in water is difficult to model accurately. For this reason, as well as the fact that the experimental error on solubility measurements can be quite high (generally reckoned to be about 0.5 log unit), the prediction of aqueous solubility is not as accurate as is the prediction of octanol/water partitioning.
3.5
The chemical mechanisms according to the model underpinning the predicted result
(OECD principle 5)The water solubility of a substance depends on its affinity for water as well as its affinity for its own crystal structure. In general, substances with high melting points have poor solubility in any solvent.
References
- US EPA (2012). On-Line KOWWIN User’s Guide.
Assessment of estimation domain (molecular weight, fragments, correction factors):
SMILES : O=C(CCCC)CL
CHEM : Pentanoyl chloride
MOL FOR: C5 H9 CL1 O1
MOL WT : 120.58
-------+-----+--------------------------------------------+---------+--------
TYPE | NUM | LOGKOW FRAGMENT DESCRIPTION | COEFF | VALUE
-------+-----+--------------------------------------------+---------+--------
Frag | 1 | -CH3 [aliphatic carbon] | 0.5473 | 0.5473
Frag | 3 | -CH2- [aliphatic carbon] | 0.4911 | 1.4733
Frag | 1 | -CL [chlorine, aliphatic attach] | 0.3102 | 0.3102
Frag | 1 | -C(=O)- [carbonyl, aliphatic attach] |-1.5586 | -1.5586
Const | | Equation Constant | | 0.2290
-------+-----+--------------------------------------------+---------+--------
NOTE | | Acetyl halides hydrolyze....estimate questionable! |
-------+-----+--------------------------------------------+---------+--------
Log Kow = 1.0012
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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