Benzo[rst]phenanthro[10,1,2-cde]pentaphene-9,18-dione, reaction products with 1-chlorododecane

Adsorption / desorption

Link to relevant study record(s)

Reference

Endpoint:

adsorption / desorption: screening

Type of information:

(Q)SAR

Adequacy of study:

key study

Study period:

April 28, 2017

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

accepted calculation method

Justification for type of information:

1. SOFTWARE: EPI Suite (U.S. Environmental Protection Agency, 2012)

2. MODEL (incl. version number): KOCWIN (a module of EPI Suite (U.S. Environmental Protection Agency, 2012)) for soil adsorption coefficient v2.00, U.S. EPA, 2010

3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL: CCCCCCCCCCCCc1cc-2c3c(ccc4c3c1c5ccc6c7c5c4ccc7c8ccccc8C6=O)C(=O)c9c2cccc9

4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL

- Defined endpoint: Soil adsorption coefficient (KOC). The KOC describes the partitioning equilibrium for a substance between water and the organic carbon contained in soil or sediment.

- Unambiguous algorithm: MCI Method: The molecular connectivity index (MCI) derived for the molecular structure and a series of correction factor for structural fragments. If no fragment is defined ('non-polar' molecules), no correction is applied. Log KOC = 0.5213 MCI + 0.60 + ΣPfN where ΣPfN is the summation of the products of all applicable correction factor coefficients multiplied by the number of times (N) that factor is counted for the structure.

KOW Method: Log KOW and a series of correction factor for structural fragments. If no fragment is defined ('non-polar' molecules), no correction is applied. Log KOC = 0.55313 Log KOW + 0.9251 + ΣPfN where ΣPfN is the summation of the products of all applicable correction factor coefficients multiplied by the number of times (N) that factor is counted for the structure.

- Defined domain of applicability: KOCWIN does not provide explicit information about applicability domain of the model. The applicability domain can be derived from the training data set and the fragments with correction. If a given target consist of fragments that are not aliphatic or aromatic and do not have a correction factor listed they have to be considered out of domain.

- Appropriate measures of goodness-of-fit and robustness and predictivity: The predications are considered reliable because the estimated KOC values for the analogues are consistent with the experimental data. In addition, KOCWIN is considered reliable based on the correlation between the experimental and KOCWIN estimated log KOC values presented by the developers. Based on data presented by the developers, approx. 95% of all predictions of Log KOC for the training set falls within the range of ±0.7 of the experimental value. This can be used to define the 95% confidence interval for the KOC of the target. The major contribution of the uncertainty is likely to come from the variability in the soil and sediment matrixes that were used for determining experimental data of the training set. This level of uncertainty of the KOCWIN estimation indicates that the uncertainty of the QSAR method is similar to the uncertainty often associated with experimental measurements.

- Mechanistic interpretation: The dominant driving force for partitioning into soil organic carbon of the molecules in the training set is hydrophobicity. Likewise, partitioning of the target is driven by hydrophobicity.

5. APPLICABILITY DOMAIN

i. Descriptor domain: In domain. Not specified by developer. For both MCI and KOW methods, the minimum to maximum of molecular mass in the training data: 32 < MW < 665 [g/mol]. The MW of the target is 624.8 [g/mol].

ii. Structural fragment domain: In domain. The model does not specify structural fragment domain. Assessed as all molecules with either aliphatic structural fragment or with a fragment with a correction factor. Fragments of the target: ketone are represented by structural fragments in the model training set.

iii. Mechanism domain: In domain. The model does not define a mechanism of partitioning. However, the dominant driving force for partitioning into soil organic carbon of the molecules in the training set is hydrophobicity. Likewise, partitioning of the target is driven by hydrophobicity.

iv. Metabolic domain: Not Relevant.

Structural analogues: Analogues were identified using a sub-structural search for relevant fragments present in the target. The substructure that was searched was ketone, aromatic rings. Examples of structural analogues are evaluated for the model performance. KOCWIN estimated Log KOC values for the analogues are consistent with the experimental data. As the prediction is based on the contribution of the structural fragments, the prediction for the target is considered reliable. For these analogues, the predictions by both methods are very close to the experimental value. The Log KOC values estimated by MCI method are slightly closer to the experimental values than those by KOW method. Based on this finding, preference is given to the MCI method for estimating the target

6. ADEQUACY OF THE RESULT
The predications are considered reliable because the estimated KOC values for the analogues are consistent with the experimental data. In addition, KOCWIN is considered reliable based on the correlation between the experimental and KOCWIN estimated log
KOC values presented by the developers.

Principles of method if other than guideline:

The soil adsorption coefficient (KOC) of C.I. Solvent Red 175 (CAS: 68411-75-6) was estimated using quantitative structure-activity relationship (QSAR) algorithm implemented in KOCWIN v2.00 which is a module of the Estimation Program Interface Suite program (EPI Suite, v4.1, U.S. Environmental Protection Agency, 2012). The material estimated was C.I. Solvent Red 175 with a molecular weight of 624.8 g/mol. KOCWIN was chosen due to its estimation accuracy and the transparency of the model and training set.

GLP compliance:

no

Type of method:

other: QSAR estimation

Media:

other: QSAR estimation

Specific details on test material used for the study:

CAS number: 68411-75-6
Chemical Name: C.I. Solvent Red 175
Molecular Weight: 624.8
SMILES code: CCCCCCCCCCCCc1cc-2c3c(ccc4c3c1c5ccc6c7c5c4ccc7c8ccccc8C6=O)C(=O)c9c2cccc9

Radiolabelling:

no

Key result

Type:

log Koc

Remarks:

Based on Molecular Connectivity Index

Value:

10.7

Key result

Type:

Koc

Remarks:

Based on Molecular Connectivity Index

Value:

47 900 000 000 L/kg

Type:

log Koc

Remarks:

Based on Log Kow

Value:

9.7

Type:

Koc

Remarks:

Based on Log Kow

Value:

5 097 000 000 L/kg

Koc Estimate from MCI	C.I. Solvent Red 175
First Order Molecular Connectivity Index	23.669
Non-Corrected Log Koc (0.5213 MCI + 0.60)	12.9385
Fragment Corrections: 2 Ketone (-C-CO-C-)	-2.2581
Corrected Log Koc	10.6804
Estimated Koc (L/kg)	4.79 x 10^10

Koc Estimate from Log Kow	C.I. Solvent Red
Log Kow (Kowwin estimate)	15.17
Non-Corrected Log Koc (0.55313 log Kow + 0.9251)	9.3161
Fragment Corrections: 2 Ketone (-C-CO-C-)	0.3912
Corrected Log Koc	9.7073
Estimated Koc (L/kg)	5.097 x 10^9

Structural analogues: Analogues were identified using a sub-structural search for relevant fragments present in the target. The substructure that was searched was ketone, aromatic rings. Examples of structural analogues are evaluated for the model performance. A comparison of the experimental and predicted values is shown in the table below.

CAS	Name	Log Koc (Experimental)	Log Koc Estimated (MCI)	Log Koc Estimated (Log Kow)
84 -75 -3	dihexyl phthalate	4.72	4.11	4.57
84-65-1	anthraquinone	3.7	3.70	3.70
1468-95-7	9-(hydroxymethyl)anthracene	3.61	3.4	2.20
723-62-6	9-anthracenecarboxylic acid	2.74	3.29	2.29
112 -53 -8	1-dodecanol	3.52	2.63	3.35
194 -59 -2	H-Dibenzo[c,g]carbazole	6.03	6.03	5.55

Validity criteria fulfilled:

yes

Conclusions:

It is with high confidence to conclude that the Log KOC of C.I. Solvent Red 175 is estimated to be 10.7.

Executive summary:

The soil adsorption coefficient (KOC) of C.I. Solvent Red 175 (CAS: 68411-75-6) was estimate using quantitative structure-activity relationship (QSAR) algorithm implemented in KOCWIN v2.00 which is a module of the Estimation Program Interface Suite program (EPI Suite, v4.1, U.S.Environmental Protection Agency, 2012). The material estimated was C.I. Solvent Red 175 with a molecular weight of 624.8 g/mol. KOCWIN was chosen due to its estimation accuracy and the transparency of the model and training set.

The KOCWIN model estimates KOC either from the octanol-water coefficient (KOW) or from a first-order molecular connectivity index (MCI). Structural analogues as identified in the training set have been processed parallel to the target. The model does not define parametric or structural domain. However, the analogues identified from within the training set suggest coverage of relevant substructures present in the target (ketone, aromatic rings). A comparison of experimental and predicted values for structural analogues was performed to decide on the preferred model for the prediction. Confidence intervals of the estimation are derived based on the error histogram provided by the model developer indicating that 95% of the substances in the training dataset are predicted within ±0.7 log units of the experimental value.

Simplified molecular input line entry system (SMILES) codes for the molecule was used as the input for the KOCWIN model. Preference is given to the MCI method because the Log KOC values for structural analogues estimated by MCI method are slightly closer to the experimental values than those by KOW method. The estimation by KOCWIN MCI method is deemed reliable because the estimated KOC values of structural analogues agree well with existing experimental data. It is with high confidence to conclude that the Log KOC of C.I. Solvent Red 175 is estimated to be 10.7.

Description of key information

The soil adsorption coefficient (KOC) of C.I. Solvent Red 175 (CAS: 68411-75-6) was estimated using quantitative structure-activity relationship (QSAR) algorithm implemented in KOCWIN v2.00 which is a module of the Estimation Program Interface Suite program (EPI Suite, v4.1, U.S. Environmental Protection Agency, 2012). Simplified molecular input line entry system (SMILES) codes for the molecule was used as the input for the KOCWIN model. It is with high confidence to conclude that the Log Koc of C.I. Solvent Red 175 is estimated to be 10.7 based on the prediction from the molecular connectivity index approach.

Key value for chemical safety assessment

Koc at 20 °C:

47 900 000 000

Additional information

U.S. EPA. 2012. Estimation Program Interface (EPI) Suite (v4.1): KOCWIN (v2.0). United States Environmental Protection Agency, Washington, DC, USA.

[LogKoc: 10.7]