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EC number: 445-710-5 | CAS number: 108313-21-9
- 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
Link to relevant study record(s)
- Endpoint:
- partition coefficient
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- 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:
- The octanol/water partition coefficient of TBPAAQ could not be determined by the shake flask method due to the low solubility of the test substance in both octanol and water. Therefore this endpoint was assessed using QSAR:
SOFTWARE : QSAR model KOWWIN (v1.69, U.S. EPA 2015) which uses a “fragment constant” methodology to predict Log KOW.
MODEL (incl. version number) : QSAR model KOWWIN (v1.69, U.S. EPA 2015) which uses a “fragment constant” methodology to predict Log KOW.
SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : SMILES code for TBPAAQ:CCCCc1ccc(cc1)Nc2c3c(c(cc2)Nc4ccc(cc4)CCCC)C(=O)c5c(ccc(c5C3(=O))Nc6ccc(cc6)CCCC)Nc7ccc(cc7)CCCC
General Information:
Date of QPRF: September 27, 2019
Purpose: The n-octanol/water partition coefficient of TBPAAQ was estimated in this work using a quantitative structure-activity relationship (QSAR) model
(KOWWIN v1.69, US Environmental Protection Agency, 2015). KOWWIN was chosen due to its estimation accuracy and the transparency of the model and training
set. The compound for which KOW was estimated (i.e., target compound) was TBPAAQ
with a molecular weight of 797 g/mol.
Prediction:
Endpoint (OECD Principle 1):
a. Endpoint: n-octanol/water partition coefficient (POW or KOW)
b. Dependent variable: Log KOW (or Log POW)
Algorithm (OECD Principle 2):
a. Model or submodel name: KOWWIN for n-octanol/water partition
coefficient
b. Model version: v1.69, U.S. EPA, 2015
c. Reference to QMRF: N/A
d. Predicted value (comments): The above predictions are in logarithm units (Log KOW). The corresponding n-octanol/water partition coefficient (Log KOW) for TBPAAQ is 19.9.
Applicability domain (OECD principle 3):
a. Domains:
i. Descriptor domain: N/A
ii. Structural fragment domain: in domain
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. The target compound is within the domain of KOWWIN (v1.69). The functional groups or other structural features of the target compound are all represented in the training set.
iii. Mechanism domain: in domain.
KOWWIN model is developed based on the assumption that the phase transfer enthalpy of a molecule (for hydrophobic molecules this is largely the negative of the solvation enthalpy) is the sum of the phase transfer enthalpies of its fragments. The enthalpy for a list of fragments is estimated from a database of n-octanol/water partitioning coefficient for molecules containing these fragments. Predictions can be made for molecules that contain these fragments. The approach is described in more details by Meylan and Howard (1995) for deriving n-octanol/water partitioning fragment contribution. The target compound is within the domain of KOWWIN (v1.69).
iv. Metabolic domain: not relevant
b. Structural analogues: The training dataset and the validation dataset have been searched for analogues using a sub-structural search for relevant fragments present in the target compound. Examples of structural analogues are evaluated for the model performance. A comparison of the experimental and predicted values is shown in Table 1.
c. Considerations on structural analogues:
Estimated Log KOW values for the analogues using KOWWIN are consistent with the experimental data. As the prediction is based on the contribution of the structural fragments, the prediction for the target compound is considered reliable.
The uncertainty of the prediction (OECD principle 4):
The predictions are considered reliable because the estimated log KOW values for the analogues are consistent with the experimental data. In addition, KOWWIN is considered reliable within the domain based on the correlation between the experimental and KOWWIN estimated Log KOW values presented by the developers. See Table 2.
The chemical and biological mechanisms according to the model underpinning
the predicted result (OECD principle 5):
The KOWWIN model estimates Log KOW based on the assumption that the phase transfer enthalpy of a molecule (for hydrophobic molecules this is largely the
negative of the solvation enthalpy) is the sum of the phase transfer enthalpies of its fragments. The enthalpy for a list of fragments is estimated from a database of noctanol/water partitioning coefficient for molecules containing these fragments. Predictions can be made for molecules that contain these fragments. The approach is described in more details by Meylan and Howard (1995) for deriving noctanol/ water partitioning fragment contribution. - Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- QSAR assessment
- Type:
- log Pow
- Partition coefficient:
- 19.9
- Remarks on result:
- other: QSAR used to predict Log Kow Value.
- Conclusions:
- The estimated Log KOW value for TBPAAQ was 19.9. The estimation by KOWWIN is deemed reliable with high confidence because TBPAAQ is within the estimation domain of the model, and estimated Log KOW values of structural analogues of TBPAAQ agree well with existing experimental data.
- Executive summary:
The n-octanol/water partition coefficient (POW or KOW) of 1,4,5,8-tetrakis[(4-butylphenyl)amino]-9,10-dihydroanthracene-9,10-dione (TBPAAQ, CAS number:108313-21-9) was estimated using quantitative structure-activity relationship (QSAR). The compound for which KOW was estimated was TBPAAQ with a molecular weight of 797 g/mol. The logarithm of KOW (Log KOW or Log POW) was calculated for TBPAAQ using QSAR model KOWWIN (v1.69, U.S. EPA 2015) which 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 was chosen due to its estimation accuracy and its transparency of the model and training set. Simplified molecular input line entry system (SMILES) code for TBPAAQ was used as the input for the KOWWIN model.
The estimated Log KOW value for TBPAAQ was 19.9. The estimation by KOWWIN is deemed reliable with high confidence because TBPAAQ is within the estimation domain of the model, and estimated Log KOW values of structural analogues of TBPAAQ agree well with existing experimental data.
Reference
Description of key information
The estimated Log Kow value for TBPAAQ was 19.9.The estimated Log KOWvalue for TBPAAQ was 19.9. The estimation by KOWWIN is deemed reliable with high confidence because TBPAAQ is within the estimation domain of the model, and estimated Log KOWvalues of structural analogues of TBPAAQ agree well with existing experimental data.
The n-octanol/water partition coefficient (POW or KOW) of 1,4,5,8-tetrakis[(4-butylphenyl)amino]-9,10-
dihydroanthracene-9,10-dione (TBPAAQ, CAS number: 108313-21-9) was estimated using quantitative
structure-activity relationship (QSAR). The compound for which KOW was estimated was TBPAAQ with
a molecular weight of 797 g/mol. The logarithm of KOW (Log KOW or Log POW) was calculated for
TBPAAQ using QSAR model KOWWIN (v1.69, U.S. EPA 2015) which uses a “fragment constant”
methodology to predict Log KOW.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 19.9
Additional information
The n-octanol/water partition coefficient (POW or KOW) of 1,4,5,8-tetrakis[(4-butylphenyl)amino]-9,10-
dihydroanthracene-9,10-dione (TBPAAQ, CAS number: 108313-21-9) was estimated using quantitative
structure-activity relationship (QSAR). The compound for which KOW was estimated was TBPAAQ with
a molecular weight of 797 g/mol. The logarithm of KOW (Log KOW or Log POW) was calculated for
TBPAAQ using QSAR model KOWWIN (v1.69, U.S. EPA 2015) which 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 was chosen due to its estimation accuracy and its transparency
of the model and training set. Simplified molecular input line entry system (SMILES) code for TBPAAQ
was used as the input for the KOWWIN model.
The estimated Log KOW value for TBPAAQ was 19.9. The estimation by KOWWIN is deemed reliable
with high confidence because TBPAAQ is within the estimation domain of the model, and estimated Log
KOW values of structural analogues of TBPAAQ agree well with existing experimental data.
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