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EC number: 212-215-9 | CAS number: 769-92-6
- 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:
- key study
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
EPIWIN software by US-EPA
2. MODEL (incl. version number)
KOWWIN v1.68
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
c1cc(N)ccc1C(C)(C)C
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
- The model and the training and validation sets are published by US Environmental Protection Agency (USA).
The experimental Log Kow values in the training set and validation set were measured using one or more methods equivalent or similar to the following guidelines:
- Shake Flask method (OECD TG 107)
- HPLC method (OECD TG 117)
- Slow Stirring method (OECD TG 123)
Plus relevant EU (1992 as amended) and US EPA OPPTS (1982 as amended) and ASTM (1993) methods may be also used where appropriate.
A full list of experimental Log Kow reference citations is provided in the KOWWIN help menu with additional reference citations.
5. APPLICABILITY DOMAIN
The intended application domain is organic chemicals. Inorganic and organometallic chemicals generally are outside the domain.
The minimum and maximum values for molecular weight are the following:
Training Set Molecular Weights:
Minimum MW: 18.02
Maximum MW: 719.92
Average MW: 199.98
Validation Molecular Weights:
Minimum MW: 27.03
Maximum MW: 991.15
Average MW: 258.98
Currently there is no universally accepted definition of model domain. However, users may wish to consider the possibility that log P estimates are less accurate for compounds outside the MW range of the training set compounds, and/or that have more instances of a given fragment than the maximum for all training set compounds. It is also possible that a compound may have a functional group(s) or other structural features not represented in the training set, and for which no fragment coefficient was developed. These points should be taken into consideration when interpreting model results.
6. ADEQUACY OF THE RESULT
The organic substance p-tert-butyaniline lies within the applicability domain with a molecular weight of 149.23 and not having more instances of a given fragment than the maximum for all training set compounds. Further, an experimental log Pow (similar to the estimated one) is available in the experimental database of the program; due to this and the suitable training set the result is considered as adequate.
Data source
Reference
- Title:
- EPI Suite Version 4.10
- Year:
- 2 012
- Bibliographic source:
- KOWWIN - Meylan and Howard (1995)
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: REACH guidance on QSARs Chapter R.6
- Version / remarks:
- May 2008
- Principles of method if other than guideline:
- Meylan, W.M. and P.H. Howard. 1995. Atom/fragment contribution method for estimating octanol-water partition coefficients. J. Pharm. Sci. 84: 83-92
- GLP compliance:
- no
- Type of method:
- calculation method (fragments)
- Partition coefficient type:
- octanol-water
Test material
- Reference substance name:
- p-tert-butylaniline
- EC Number:
- 212-215-9
- EC Name:
- p-tert-butylaniline
- Cas Number:
- 769-92-6
- Molecular formula:
- C10H15N
- IUPAC Name:
- 4-tert-butylaniline
Constituent 1
- Specific details on test material used for the study:
- SMILES: c1cc(N)ccc1C(C)(C)C
Results and discussion
Partition coefficientopen allclose all
- Type:
- log Pow
- Partition coefficient:
- 2.99
- Remarks on result:
- other: QSAR predicted value
- Key result
- Type:
- log Pow
- Partition coefficient:
- 2.7
- Remarks on result:
- other: Result from Experimental Database Structure Match for CAS 769-92-6 (Hansch, C et al., 1995)
Any other information on results incl. tables
KOWWIN predicted that the substance has a log Kow = 2.99
Result from Experimental Database Structure Match for CAS 769-92-6: log Kow = 2.70 (Hansch, C et al., 1995)
Applicant's summary and conclusion
- Conclusions:
- The study report describes a scientifically accepted calculation method for the partition coefficient using the US-EPA software KOWWIN v1.68. No GLP criteria are applicable for the usage of this tool and the QSAR estimation is easily repeatable. The result is adequate for the regulatory purpose; further, an experimental log Pow is available in the experimental database of the program.
- Executive summary:
The partition coefficient of the substance p-tert-butylaniline was determined by the computer program KOWWIN v1.68 (EPIWIN software) by US-EPA (2012). The program uses the chemical structure of a compound to predict the logarithmic octanol water partition coefficient (logPow). The structure is denoted in its SMILES notation. As first step the software determines the logPow contributions from individual molecular fragments. Afterwards these fragments are summed up to gain the logPow for the whole molecule. In this case a logPow of 2.99 was determined as result. Further, an experimental log Pow of 2.70 (Hansch, C. et al., 1995) is available in the experimental database of the program.
Adequacy of the QSAR:
- QSAR model is scientifically valid.
- The substance falls within the applicability domain of the QSAR model.
- The prediction is fit for regulatory purpose.
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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