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EC number: 600-736-8 | CAS number: 106276-80-6
- 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
Biodegradation in soil
Administrative data
- Endpoint:
- biodegradation in soil: simulation testing
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- see attached justification
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- additional information on environmental fate and behaviour
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 318
- Executive summary:
At any of the time points mentioned in the TG-318, the influence of Ca is critical. Regardless of pH, the pigment is least stable in 10 mM Ca, representing high water hardness.
After 6h, the samples showed high dispersion stability in 0 mM Ca and intermediate stability at all other conditions.
After 24 hours the stability in 0 mM Ca at pH 4 remained high. The stability in 0 mM Ca at pH 9 became intermediate. For the samples at all other conditions the stability was low.
At any of the time points mentioned in the TG-318, the influence of Ca is critical. Regardless of pH, the pigment is least stable in 10 mM Ca, representing high water hardness.
After 6h, the samples showed high dispersion stability in 0 mM Ca and intermediate stability at all other conditions.
After 24 hours the stability in 0 mM Ca at pH 4 remained high. The stability in 0 mM Ca at pH 9 became intermediate. For the samples at all other conditions the stability was low.
Full results of the dispersion stability in the presence of NOM | |||||||
Ca(NO3)2 | Stability after 6h | Standard deviation | Stability after 15h | Standard deviation | Stability after 24h | Standard deviation | |
[mM] | [%] | [%] | [%] | [%] | [%] | [%] | |
pH 4 | 0 | 96.8 | 0.6 | 94.9 | 0.1 | 92.8 | 0.3 |
pH 4 | 1 | 75.3 | 0.9 | 22.2 | 1.0 | 10.2 | 1.5 |
pH 4 | 10 | 14.5 | 1.5 | 6.6 | 0.6 | 2.9 | 0.4 |
. | |||||||
pH 7 | 0 | 98.4 | 0.1 | 66.2 | 11.1 | 6.8 | 2.3 |
pH 7 | 1 | 38.9 | 0.3 | 10.8 | 0.3 | 5.0 | 0.2 |
pH 7 | 10 | 10.3 | 0.7 | 4.4 | 0.3 | 1.9 | 0.1 |
. | |||||||
pH 9 | 0 | 89.8 | 0.7 | 83.9 | 0.3 | 78.2 | 1.5 |
pH 9 | 1 | 22.0 | 3.2 | 7.7 | 0.7 | 3.9 | 0.7 |
pH 9 | 10 | 14.6 | 1.1 | 0.0. | 0.6 | 19.4 | 2.0 |
To rationalize the observed dispersion stability, we finally checked the particle size distribution directly in the environmental medium. We applied the NanoDefine method of Analytical Ultracentrifugation (SOP AUC-RI, published by 3). The centrifugation parameters are given in the methods section.
As required by TG318, paragraph 31, the tested nanomaterial was pre-wetted in ultrapure water and left in the form of wet-paste for 24 h. The TG318 requires this step “to insure the proper interaction of nanomaterial surface with ultrapure water.” We visually observed incomplete wetting, and so any ensuing measurement would have been incorrect. In accord with the NanoGenoTox dispersion protocol, a drop of ethanol was added, successfully transferred the powder into a paste, which was then further diluted as specified in the TG318
The observed size distributions confirm the moderate agglomeration at 1 mM Ca, pH7, with NOM (Figure 4). If the particles would have been significantly dissolved, no size distribution would be observable at all by this method, which relies on the detection of the movement of particles during centrifugal separation.
Additionally, the centrifugation methods include a determination of the remaining absorption after centrifugation, fully consistent with the conventional determination of the dissolved fraction after centrifugation as recommended by the TG-318. The remaining absorption was measured at ca. 0.01. This is a fraction of 1% of the initial absorption, but actually is close to the LOD of the built-in UV/Vis detector. Considering the LOD, between 0% and 1% of the sample may have been dissolved.
All evidence combined, the results after centrifugation confirm that at least 99% of the observed dispersion stability has to be attributed to the particles, not to dissolution.
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- biodegradation in water: ready biodegradability
- 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, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Remarks:
- Parameter ranges: In domain; Structural domain: Out of domain (Correct fragments: 95.24%; Incorrect fragments: 0%; Unknown fragments: 4.76%);
- Justification for type of information:
- 1. SOFTWARE
OASIS Catalogic v5.13.1.156
2. MODEL (incl. version number)
CATALOGIC 301C v.11.15
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
See section 'Test Material'.
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See attached QMRF.
5. APPLICABILITY DOMAIN
See attached QPRF.
6. ADEQUACY OF THE RESULT
- The model is scientifically valid (see attached QMRF).
- The model estimates the biodegradability of a substance Screening information on the ready biodegradability is required for substances manufactured or imported in quantities of 1 t/y or more. Depending on the results, further information may be required for substances manufactured or imported in quantities of 100 t/y or more (simulation testing on ultimate degradation in surface water/soil/sediment). Column 2 of REACH Annex VII provides exemptions for conducting the study. It does not need to be conducted if the substance is inorganic. According to column 2 of REACH Annex IX, testing is not required if the substance is highly insoluble in water, or the substance is readily biodegradable.
- See attached QPRF for reliability assessment. - Principles of method if other than guideline:
- Estimation of ready biodegradation in water using CATALOGIC v5.13.1.156 BOD 28 days MITI (OECD 301C) v11.15
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: model calculation
- Duration of test (contact time):
- 28 d
- Parameter followed for biodegradation estimation:
- O2 consumption
- Parameter:
- % degradation (O2 consumption)
- Value:
- 5
- Sampling time:
- 28 d
- Remarks on result:
- other: The octachloro derivative is not completely within the applicability domain of the model due to 4.76% unknown fragments in the training set.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 10
- Sampling time:
- 28 d
- Remarks on result:
- other: The monomethoxy-heptachloro derivative is not completely within the applicability domain of the model due to 13.64% unknown fragments in the training set.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 14
- Sampling time:
- 28 d
- Remarks on result:
- other: The bismethoxy-hexachloro derivative is not completely within the applicability domain of the model due to 21.74% unknown fragments in the training set.
- Interpretation of results:
- not readily biodegradable
- Remarks:
- according to OECD criteria
Octachloro derivative:
-Concomitant predictions:
Not ready degradable
Primary Half Life = 9.97 days
Ultimate Half Life = 11m 17d
- Predicted value (model result): O2 -consumption (BOD) = 0.05 ± 0.0178
Metabolite predition:
The model Catalogic 301 C v11.15 (OASIS Catalogic v5.13.1.156) calculated 125 metabolites (see octachloro document attached under "attached background material") identifying 48 metabolites as relevant degradation products in terms of PBT/vPvB assessment, with an estimated quantity of ≥ 0.1%.
All metabolites identified as relevant degradation products were calculated to be not readily biodegradable. Individual biodegradation of these metabolites was estimated to be 0% to 10% after 28 days (based on BOD).
Monomethoxy-heptachloro derivative:
-Concomitant predictions:
Not ready degradable
Primary Half Life = 5.33 days
Ultimate Half Life = 6m 4d
- Predicted value (model result): O2 -consumption (BOD) = 0.10 ± 0.0148
Metabolite predition:
The model Catalogic 301 C v11.15 (OASIS Catalogic v5.13.1.156) calculated 175 metabolites (see monomethoxy-heptachloro document attached under "attached background material") identifying 58 metabolites as relevant degradation products in terms of PBT/vPvB assessment, with an estimated quantity of≥ 0.1%.
All metabolites identified as relevant degradation products were calculated to be not readily biodegradable. Individual biodegradation of these metabolites was estimated to be 1% to 11% after 28 days (based on BOD). Only one metabolites was identified as biodegradable (100%) based on BOD. Since the quantity is only 0.14% the overall conclusion will not be affected.
Bismethoxy-hexachloro derivative:
-Concomitant predictions:
Not ready degradable
Primary Half Life = 3.64 days
Ultimate Half Life = 4m 7d
- Predicted value (model result): O2 -consumption (BOD) = 0.14 ± 0.0181
Metabolite predition:
The model Catalogic 301 C v11.15 (OASIS Catalogic v5.13.1.156) calculated 45 metabolites (see bismethoxy-hexachloro document attached under "attached background material") identifying 24 metabolites as relevant degradation products in terms of PBT/vPvB assessment, with an estimated quantity of≥ 0.1%.
All metabolites identified as relevant degradation products were calculated to be not readily biodegradable. Individual biodegradation of these metabolites was estimated to be 3% to 13% after 28 days (based on BOD).
Only one metabolites was identified as biodegradable (100%) based on BOD. Since the quantity is only 0.25% the overall conclusion will not be affected.
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- biodegradation in water: ready biodegradability
- 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, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Prediction of ready biodegradability based on EPI Suite v4.10 BIOWIN v4.10.
- GLP compliance:
- no
- Remarks on result:
- other: Ready biodegradability prediction: Substance is not readily biodegradable.
- Remarks:
- It is true for the three derivatives
- Interpretation of results:
- not readily biodegradable
Results octachloro derivative:
Biowin1 (Linear Model Prediction) : Does Not Biodegrade Fast
Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin3 (Ultimate Biodegradation Timeframe): Recalcitrant
Biowin4 (Primary Biodegradation Timeframe): Months
Biowin5 (MITI Linear Model Prediction) : Does Not Biodegrade Fast
Biowin6 (MITI Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast
Ready Biodegradability Prediction: NO
TYPE |
NUM |
Biowin1 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2102 |
0.4203 |
Frag |
8 |
Aromatic chloride [-CL] |
-0.1824 |
-1.4594 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.3056 |
Const |
* |
Equation Constant |
|
0.7475 |
RESULT |
Biowin1 (Linear Biodeg Probability) |
|
-0.5971 |
TYPE |
NUM |
Biowin2 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
2.6913 |
5.3826 |
Frag |
8 |
Aromatic chloride [-CL] |
-2.0155 |
-16.1240 |
MolWt |
* |
Molecular Weight Parameter |
|
-9.1156 |
RESULT |
Biowin2 (Non-Linear Biodeg Probability) |
|
0.0000 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
TYPE |
NUM |
Biowin3 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.0542 |
-0.1084 |
Frag |
8 |
Aromatic chloride [-CL] |
-0.2066 |
-1.6528 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.4186 |
Const |
* |
Equation Constant |
|
3.1992 |
RESULT |
Biowin3 (Survey Model - Ultimate Biodeg) |
|
0.0193 |
TYPE |
NUM |
Biowin4 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2054 |
0.4109 |
Frag |
8 |
Aromatic chloride [-CL] |
-0.1653 |
-1.3227 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.9262 |
Const |
* |
Equation Constant |
|
3.8477 |
RESULT |
Biowin4 (Survey Model - Primary Biodeg) |
|
2.0097 |
Result Classification: 5.00 -> hours 4.00 -> days 3.00 -> weeks
(Primary & Ultimate) 2.00 -> months 1.00 -> longer
TYPE |
NUM |
Biowin5 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.1266 |
0.2533 |
Frag |
8 |
Aromatic chloride [-CL] |
0.0062 |
0.0494 |
Frag |
4 |
Aromatic-H |
0.0082 |
0.0329 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.9098 |
Const |
* |
Equation Constant |
|
0.7121 |
RESULT |
Biowin5 (MITI Linear Biodeg Probability) |
|
-0.8621 |
TYPE |
NUM |
Biowin6 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.8859 |
1.7717 |
Frag |
8 |
Aromatic chloride [-CL] |
-0.2191 |
-1.7532 |
Frag |
4 |
Aromatic-H |
0.1201 |
0.4806 |
MolWt |
* |
Molecular Weight Parameter |
|
-18.5321 |
RESULT |
Biowin6 (MITI Non-Linear Biodeg Probability) |
|
0.0000 |
A Probability Greater Than or Equal to 0.5 indicates --> Readily Degradable
A Probability Less Than 0.5 indicates --> NOT Readily Degradable
TYPE |
NUM |
Biowin7 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.5679 |
-1.1358 |
Frag |
8 |
Aromatic chloride [-CL] |
-0.4023 |
-3.2182 |
Frag |
4 |
Aromatic-H |
-0.0954 |
-0.3817 |
Const |
* |
Equation Constant |
|
0.8361 |
RESULT |
Biowin7 (Anaerobic Linear Biodeg Prob) |
|
-3.8996 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
Ready Biodegradability Prediction: (YES or NO)
----------------------------------------------
Criteria for the YES or NO prediction: If the Biowin3 (ultimate survey model) result is "weeks" or faster (i.e. "days", "days to weeks", or "weeks" AND the Biowin5 (MITI linear model) probability is >= 0.5, then the prediction is YES (readily biodegradable). If this condition is not satisfied, the prediction is NO (not readily biodegradable). This method is based on application of Bayesian analysis to ready biodegradation data (see Help). Biowin5 and 6 also predict ready biodegradability, but for degradation in the OECD301C test only; using data from the Chemicals Evaluation and Research Institute Japan (CERIJ) database.
Results monomethoxy-heptachloro derivative:
Biowin1 (Linear Model Prediction) : Does Not Biodegrade Fast
Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin3 (Ultimate Biodegradation Timeframe): Recalcitrant
Biowin4 (Primary Biodegradation Timeframe): Weeks-Months
Biowin5 (MITI Linear Model Prediction) : Does Not Biodegrade Fast
Biowin6 (MITI Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast
Ready Biodegradability Prediction: NO
TYPE |
NUM |
Biowin1 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2102 |
0.4203 |
Frag |
7 |
Aromatic chloride [-CL] |
-0.1824 |
-1.2769 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
0.1319 |
0.1319 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.3035 |
Const |
* |
Equation Constant |
|
0.7475 |
RESULT |
Biowin1 (Linear Biodeg Probability) |
|
-0.2807 |
TYPE |
NUM |
Biowin2 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
2.6913 |
5.3826 |
Frag |
7 |
Aromatic chloride [-CL] |
-2.0155 |
-14.1085 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
2.2483 |
2.2483 |
MolWt |
* |
Molecular Weight Parameter |
|
-9.0528 |
RESULT |
Biowin2 (Non-Linear Biodeg Probability) |
|
0.0000 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
TYPE |
NUM |
Biowin3 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.0542 |
-0.1084 |
Frag |
7 |
Aromatic chloride [-CL] |
-0.2066 |
-1.4462 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
-0.0581 |
-0.0581 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.4088 |
Const |
* |
Equation Constant |
|
3.1992 |
RESULT |
Biowin3 (Survey Model - Ultimate Biodeg) |
|
0.1776 |
TYPE |
NUM |
Biowin4 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2054 |
0.4109 |
Frag |
7 |
Aromatic chloride [-CL] |
-0.1653 |
-1.1574 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
0.0771 |
0.0771 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.9198 |
Const |
* |
Equation Constant |
|
3.8477 |
RESULT |
Biowin4 (Survey Model - Primary Biodeg) |
|
2.2585 |
Result Classification: 5.00 -> hours 4.00 -> days 3.00 -> weeks
(Primary & Ultimate) 2.00 -> months 1.00 -> longer
TYPE |
NUM |
Biowin5 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.1266 |
0.2533 |
Frag |
7 |
Aromatic chloride [-CL] |
0.0062 |
0.0432 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
0.1952 |
0.1952 |
Frag |
4 |
Aromatic-H |
0.0082 |
0.0329 |
Frag |
1 |
Methyl [-CH3] |
0.0004 |
0.0004 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.8966 |
Const |
* |
Equation Constant |
|
0.7121 |
RESULT |
Biowin5 (MITI Linear Biodeg Probability) |
|
-0.6595 |
TYPE |
NUM |
Biowin6 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.8859 |
1.7717 |
Frag |
7 |
Aromatic chloride [-CL] |
-0.2191 |
-1.5340 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
1.3227 |
1.3227 |
Frag |
4 |
Aromatic-H |
0.1201 |
0.4806 |
Frag |
1 |
Methyl [-CH3] |
0.0194 |
0.0194 |
MolWt |
* |
Molecular Weight Parameter |
|
-18.4045 |
RESULT |
Biowin6 (MITI Non-Linear Biodeg Probability) |
|
0.0000 |
A Probability Greater Than or Equal to 0.5 indicates --> Readily Degradable
A Probability Less Than 0.5 indicates --> NOT Readily Degradable
TYPE |
NUM |
Biowin7 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.5679 |
-1.1358 |
Frag |
7 |
Aromatic chloride [-CL] |
-0.4023 |
-2.8159 |
Frag |
1 |
Aromatic ether [-O-aromatic carbon] |
0.1780 |
0.1780 |
Frag |
4 |
Aromatic-H |
-0.0954 |
-0.3817 |
Frag |
1 |
Methyl [-CH3] |
-0.0796 |
-0.0796 |
Const |
* |
Equation Constant |
|
0.8361 |
RESULT |
Biowin7 (Anaerobic Linear Biodeg Prob) |
|
-3.3988 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
Ready Biodegradability Prediction: (YES or NO)
----------------------------------------------
Criteria for the YES or NO prediction: If the Biowin3 (ultimate survey model) result is "weeks" or faster (i.e. "days", "days to weeks", or "weeks" AND the Biowin5 (MITI linear model) probability is >= 0.5, then the prediction is YES (readily biodegradable). If this condition is not satisfied, the prediction is NO (not readily biodegradable). This method is based on application of Bayesian analysis to ready biodegradation data (see Help). Biowin5 and 6 also predict ready biodegradability, but for degradation in the OECD301C test only; using data from the Chemicals Evaluation and Research Institute Japan (CERIJ) database.
Results bismethoxy-hexachloro derivative:
Biowin1 (Linear Model Prediction) : Does Not Biodegrade Fast
Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin3 (Ultimate Biodegradation Timeframe): Recalcitrant
Biowin4 (Primary Biodegradation Timeframe): Weeks-Months
Biowin5 (MITI Linear Model Prediction) : Does Not Biodegrade Fast
Biowin6 (MITI Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast
Ready Biodegradability Prediction: NO
TYPE |
NUM |
Biowin1 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2102 |
0.4203 |
Frag |
6 |
Aromatic chloride [-CL] |
-0.1824 |
-1.0945 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
0.1319 |
0.2638 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.3014 |
Const |
* |
Equation Constant |
|
0.7475 |
RESULT |
Biowin1 (Linear Biodeg Probability) |
|
0.0357 |
TYPE |
NUM |
Biowin2 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
2.6913 |
5.3826 |
Frag |
6 |
Aromatic chloride [-CL] |
-2.0155 |
-12.0930 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
2.2483 |
4.4966 |
MolWt |
* |
Molecular Weight Parameter |
|
-8.9901 |
RESULT |
Biowin2 (Non-Linear Biodeg Probability) |
|
0.0003 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
TYPE |
NUM |
Biowin3 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.0542 |
-0.1084 |
Frag |
6 |
Aromatic chloride [-CL] |
-0.2066 |
-1.2396 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
-0.0581 |
-0.1162 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.3991 |
Const |
* |
Equation Constant |
|
3.1992 |
RESULT |
Biowin3 (Survey Model - Ultimate Biodeg) |
|
0.3358 |
TYPE |
NUM |
Biowin4 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2054 |
0.4109 |
Frag |
6 |
Aromatic chloride [-CL] |
-0.1653 |
-0.9920 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
0.0771 |
0.1542 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.9134 |
Const |
* |
Equation Constant |
|
3.8477 |
RESULT |
Biowin4 (Survey Model - Primary Biodeg) |
|
2.5074 |
Result Classification: 5.00 -> hours 4.00 -> days 3.00 -> weeks
(Primary & Ultimate) 2.00 -> months 1.00 -> longer
TYPE |
NUM |
Biowin5 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.1266 |
0.2533 |
Frag |
6 |
Aromatic chloride [-CL] |
0.0062 |
0.0370 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
0.1952 |
0.3905 |
Frag |
4 |
Aromatic-H |
0.0082 |
0.0329 |
Frag |
2 |
Methyl [-CH3] |
0.0004 |
0.0008 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.8835 |
Const |
* |
Equation Constant |
|
0.7121 |
RESULT |
Biowin5 (MITI Linear Biodeg Probability) |
|
-0.4569 |
TYPE |
NUM |
Biowin6 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.8859 |
1.7717 |
Frag |
6 |
Aromatic chloride [-CL] |
-0.2191 |
-1.3149 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
1.3227 |
2.6454 |
Frag |
4 |
Aromatic-H |
0.1201 |
0.4806 |
Frag |
2 |
Methyl [-CH3] |
0.0194 |
0.0389 |
MolWt |
* |
Molecular Weight Parameter |
|
-18.2769 |
RESULT |
Biowin6 (MITI Non-Linear Biodeg Probability) |
|
0.0000 |
A Probability Greater Than or Equal to 0.5 indicates --> Readily Degradable
A Probability Less Than 0.5 indicates --> NOT Readily Degradable
TYPE |
NUM |
Biowin7 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.5679 |
-1.1358 |
Frag |
6 |
Aromatic chloride [-CL] |
-0.4023 |
-2.4136 |
Frag |
2 |
Aromatic ether [-O-aromatic carbon] |
0.1780 |
0.3560 |
Frag |
4 |
Aromatic-H |
-0.0954 |
-0.3817 |
Frag |
2 |
Methyl [-CH3] |
-0.0796 |
-0.1591 |
Const |
* |
Equation Constant |
|
0.8361 |
RESULT |
Biowin7 (Anaerobic Linear Biodeg Prob) |
|
-2.8981 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
Ready Biodegradability Prediction: (YES or NO)
----------------------------------------------
Criteria for the YES or NO prediction: If the Biowin3 (ultimate survey model) result is "weeks" or faster (i.e. "days", "days to weeks", or "weeks" AND the Biowin5 (MITI linear model) probability is >= 0.5, then the prediction is YES (readily biodegradable). If this condition is not satisfied, the prediction is NO (not readily biodegradable). This method is based on application of Bayesian analysis to ready biodegradation data (see Help). Biowin5 and 6 also predict ready biodegradability, but for degradation in the OECD301C test only; using data from the Chemicals Evaluation and Research Institute Japan (CERIJ) database.
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- biodegradation in water: ready biodegradability
- 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, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- The model is based on the OECD TG 301C - modified MITI -I test data and provides a qualitative evaluation (binary classification) of ready biodegradability properties. It has been developed using Sarpy software, by Istituto di Ricerche Farmacologiche Mario Negri and Politecnico di Milano.
The applicability domain of predictions is assessed using an Applicability Domain Index (ADI) that has values from 0 (worst case) to 1 (best case). The ADI is calculated by grouping several other indices, each one taking into account a particular issue of the applicability domain. Most of the indices are based on the calculation of the most similar compounds found in the training and test set of the model, calculated by a similarity index that consider molecule's fingerprint and structural aspects (count of atoms, rings and relevant fragments). - GLP compliance:
- no
- Remarks on result:
- other: Result: The substance is not readily biodegradable. It is out of the Applicability Domain of the model according to the AD index. This state ment is true for all three derivates.
- Interpretation of results:
- not readily biodegradable
Model output octachloro derivative:
Compound: Molecule 0
Compound SMILES: O=C4NC(=Nc3ccc(N=C1NC(=O)c2c1c(c(c(c2Cl)Cl)Cl)Cl)cc3)c5c4c(c(c(c5Cl)Cl)Cl)Cl
Experimental value: -
Predicted RB activity: NON Readily Biodegradable
No. alerts for non RB: 3
No. alerts for possible non RB: 3
No. alerts for RB: 0
No. alerts for possible RB: 0
Structural alerts: Non RB alert no. 1 (1,2-dichlorobenzene); Non RB alert no. 21 (methanimine); Non RB alert no. 25 (2-chlorobenzaldehyde); Possible non RB alert no. 2 (1-chloro-2-methylbenzene); Possible non RB alert no. 7 (chlorobenzene); Possible non RB alert no. 11 (halogenated ring structure)
Reliability: the predicted compound is outside the Applicability Domain of the model
Remarks: none
Model output monomethoxy-heptachloro derivative:
Compound: Molecule 0
Compound SMILES: O=C4NC(=Nc3ccc(N=C1NC(=O)c2c1c(c(c(c2Cl)Cl)Cl)Cl)cc3)c5c4c(c(OC)c(c5Cl)Cl)Cl
Experimental value: -
Predicted RB activity: NON Readily Biodegradable
No. alerts for non RB: 4
No. alerts for possible non RB: 3
No. alerts for RB: 0
No. alerts for possible RB: 1
Structural alerts: Non RB alert no. 1 (1,2-dichlorobenzene); Non RB alert no. 10 (3-chlorophenol); Non RB alert no. 21 (methanimine); Non RB alert no. 25 (2-chlorobenzaldehyde); Possible non RB alert no. 2 (1-chloro-2-methylbenzene); Possible non RB alert no. 7 (chlorobenzene); Possible non RB alert no. 11 (halogenated ring structure); Possible RB alert no. 19 (anisole)
Reliability: the predicted compound is outside the Applicability Domain of the model
Remarks: none
Model output bismethoxy-hexaachloro derivative:
Compound: Molecule 0
Compound SMILES: O=C4NC(=Nc3ccc(N=C1NC(=O)c2c1c(c(c(OC)c2Cl)Cl)Cl)cc3)c5c4c(c(OC)c(c5Cl)Cl)Cl
Experimental value: -
Predicted RB activity: NON Readily Biodegradable
No. alerts for non RB: 4
No. alerts for possible non RB: 3
No. alerts for RB: 0
No. alerts for possible RB: 1
Structural alerts: Non RB alert no. 1 (1,2-dichlorobenzene); Non RB alert no. 10 (3-chlorophenol); Non RB alert no. 21 (methanimine); Non RB alert no. 25 (2-chlorobenzaldehyde); Possible non RB alert no. 2 (1-chloro-2-methylbenzene); Possible non RB alert no. 7 (chlorobenzene); Possible non RB alert no. 11 (halogenated ring structure); Possible RB alert no. 19 (anisole)
Reliability: the predicted compound is outside the Applicability Domain of the model
Remarks: none
Data source
Materials and methods
Results and discussion
Applicant's summary and conclusion
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