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EC number: 308-208-6 | CAS number: 97925-95-6
- 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 water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- from 31 October 2001 to 2 January 2002
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- other: ISO 14593 (Water quality – Evaluation of the ultimate aerobic biodegradability of organic compounds in an aqueous medium – Method by analysis of inorganic carbon in sealed vessels)
- Deviations:
- yes
- Remarks:
- : temperature was below 22 (± 2) °C specified in the guideline on day 0 (19.5 °C) and day 4 (19.7 °C)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EPA OPPTS 835.3120 (Sealed Vessel Carbon Dioxide Production Test)
- Principles of method if other than guideline:
- Conditions employed (mineral medium composition, activated sludge inoculum density and test substance concentration) are equivalent to those represented by the OECD 301 series (ready biodegradability). The test is equivalent to the OECD 301 B test.
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Burley Menston sewage treatment works (Yorkshire Water)
- Suspended solids concentration: 5.632 g solids/L - Duration of test (contact time):
- 28 d
- Initial conc.:
- 10 mg/L
- Based on:
- other: TOC
- Parameter followed for biodegradation estimation:
- inorg. C analysis
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Synthetic mineral salts medium containing 10 mL/L of solution a) and 1 mL/L each of solutions b), c) and d):
a) KH2PO4 (8.5 g/L), K2HPO4 (21.7 g/L), Na2HPO4.2(H2O) (33.4 g/L), NH4Cl (0.5 g/L)
b) CaCl2.2H2O (36.4 g/L)
c) MgSO4.7H2O (22.5 g/L)
d) FeCl3.6H2O (0.2 g/L)
- Test temperature: 20.9 - 22.2 °C (apart from the first day (19.5 °C) and fourth day (19.7 °C)); measured continuously
- pH: no data
- Suspended solids concentration: 4 mg/L (3 L medium inoculated with 2.13 mL activated sludge)
- Continuously shaking (135 rpm)
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: 160 mL glass bottles
- Volume of test medium: 107 mL
- Liquid : headspace ratio: 2:1
- Number of culture flasks/concentration: 5 bottles/concentration
- Test performed in closed vessels: prevent absorbing/measuring of atmospheric CO2
SAMPLING
- Sampling frequency: once at the last day of the experiment (day 28) after adding NaHO solution
- Sampling method: 1000 µL samples (in triplicate) were taken from each vessel through the butyl rubber plugs using a gas-tight syringe; samples were directly injected to a Rosemount Dohrmann DC-80 TOC analyser
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes (test medium + activated sludge) => 5 replicates (like test and reference substance)
- Abiotic sterile control: no
- Toxicity control: no - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- initial concentration based on TOC: 15 mg/L
- Parameter:
- % degradation (inorg. C analysis)
- Value:
- 37
- Sampling time:
- 28 d
- Results with reference substance:
- The mean final degradation of the reference substance sodium benzoate was 96%.
- Interpretation of results:
- other: Significant mineralisation occurred but degradation did not reach 60% and thus Atmer 163 would not qualify for classification as readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Validated QSAR model. Calculation for main component of Ethanol, 2,2'-iminobis-, N-(C13-15-branched and linear alkyl) derivs., CAS 97925-95-6. The substance/component is in the applicability domain of the model. All relevant related fragments show experimentally ready biodegradability. Thus the prediction is considered as valid.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Principles of method if other than guideline:
- Calculation based on BIOWIN v4.10, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on results:
- For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables".
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Validated QSAR model: Calculation for main component of Ethanol, 2,2'-iminobis-, N-(C13-15-branched and linear alkyl) derivs., CAS 97925-95-6. The substance/component is in the applicability domain of the models. Thus the prediction is considered as valid.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Principles of method if other than guideline:
- Calculation based on VegaNIC version 1.0.8 using Ready biodegradability model (version 1.0.8)
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Validated QSAR model: Calculation for main component of Ethanol, 2,2'-iminobis-, N-(C13-15-branched and linear alkyl) derivs., CAS 97925-95-6. The substance/component is in the applicability domain of the models. Thus the prediction is considered as valid.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Principles of method if other than guideline:
- Calculation based on BIOWIN v4.10, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on results:
- For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables".
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Validated QSAR model. Calculation for main component of Ethanol, 2,2'-iminobis-, N-(C13-15-branched and linear alkyl) derivs., CAS 97925-95-6. The substance/component is in the applicability domain of the model. All relevant related fragments show experimentally ready biodegradability. Thus the prediction is considered as valid.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Principles of method if other than guideline:
- Calculation based on VegaNIC version 1.0.8 using Ready biodegradability model (version 1.0.8)
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Interpretation of results:
- readily biodegradable
Referenceopen allclose all
The test substance was degraded to 37% after 28 days. Thus, the substance is not readily biodegradable according to the OECD testing scheme. ISO does not recognise the concept of "ready" biodegradability, or the notion passing or failing a biodegradability assessment. However, the conditions employed are equivalent to those represented by the OECD 301 series ready biodegradability test methods.
Table 1: Biodegradation of Atmer 163 at day 28 as Percentage Theoretical IC Yield
Atmer 163 |
Reference substance: sodium benzoate |
42% |
97% |
42% |
95% |
34% |
95% |
29% |
95% |
38% |
96% |
mean: 37% |
mean: 96% |
Table: Ready biodegradability prediction using BIOWIN v4.1
Biowin1 (Linear Model Prediction) |
0.8313 |
biodegrades fast |
Biowin2 (Non-Linear Model Prediction): |
0.6863 |
biodegrades fast |
Biowin3 (Ultimate Biodegradation Timeframe): |
2.9273 |
weeks |
Biowin4 (Primary Biodegradation Timeframe): |
3.6729 |
days-weeks |
Biowin5 (MITI Linear Model Prediction) : |
0.8854 |
biodegrades fast |
Biowin6 (MITI Non-Linear Model Prediction): |
0.9077 |
biodegrades fast |
Biowin7 (Anaerobic Model Prediction): |
0.0453 |
does not biodegrade fast |
Ready Biodegradability Prediction: |
|
yes |
Compound SMILES: CCCCCCCCCCCCCN(CCO)(CCO)
Experimental value: -Prediction: possible Ready Biodegradable
Structural Alerts: Bb9 (tridecane); Bb16 (propan-1-amine); Bb18 (heptanes); Bb20 (butane)
No. Specific Non-Biodegradable SAs: 0
No. Balanced Non-Biodegradable SAs: 0
No. Specific Biodegradable SAs: 0
No. Balanced Biodegradable SAs: 4
Reliability: Compound is in model Applicability Domain
Remarks for the prediction: none
Global AD Index
AD Index = 0.964
Explanation: predicted substance is into the Applicability Domain of the model.
Similar molecules with known experimental value
Similarity index = 0.928
Explanation: strongly similar compounds with known experimental value in the training set have been found.
Concordance for similar molecules
Concordance index = 1
Explanation: similar molecules found in the training set have experimental values that agree with the predicted value.
Accuracy of prediction for similar molecules
Accuracy index = 1
Explanation: accuracy of prediction for similar molecules found in the training set is good.
Atom Centered Fragments similarity check
ACF matching index = 1
Explanation: all atom centered fragment of the compound have been found in the compounds of the training set.
Table: Ready biodegradability prediction using BIOWIN v4.1
Biowin1 (Linear Model Prediction) |
0.8180 |
biodegrades fast |
Biowin2 (Non-Linear Model Prediction): |
0.5949 |
biodegrades fast |
Biowin3 (Ultimate Biodegradation Timeframe): |
2.8653 |
weeks |
Biowin4 (Primary Biodegradation Timeframe): |
3.6325 |
days-weeks |
Biowin5 (MITI Linear Model Prediction) : |
0.9007 |
biodegrades fast |
Biowin6 (MITI Non-Linear Model Prediction): |
0.9118 |
biodegrades fast |
Biowin7 (Anaerobic Model Prediction): |
0.0973 |
does not biodegrade fast |
Ready Biodegradability Prediction: |
|
yes |
Compound SMILES: OCCN(CCO)CCCCCCCCCCCCCCC
Experimental value: -
Prediction: possible Ready Biodegradable
Structural Alerts: Bb9 (tridecane); Bb16 (propan-1-amine); Bb18 (heptanes); Bb20 (butane)
No. Specific Non-Biodegradable SAs: 0
No. Balanced Non-Biodegradable SAs: 0
No. Specific Biodegradable SAs: 0
No. Balanced Biodegradable SAs: 4
Reliability: Compound is in model Applicability Domain
Remarks for the prediction: none
Global AD Index
AD Index = 0.965
Explanation: predicted substance is into the Applicability Domain of the model.
Similar molecules with known experimental value
Similarity index = 0.931
Explanation: strongly similar compounds with known experimental value in the training set have been found.
Concordance for similar molecules
Concordance index = 1
Explanation: similar molecules found in the training set have experimental values that agree with the predicted value.
Accuracy of prediction for similar molecules
Accuracy index = 1
Explanation: accuracy of prediction for similar molecules found in the training set is good.
Atom Centered Fragments similarity check
ACF matching index = 1
Explanation: all atom centered fragment of the compound have been found in the compounds of the training set.
Description of key information
Atmer 163 is not readily biodegradable (37% after 28 days), but will be moderately biodegraded. This is supported by a (Q)SAR calculation using BIOWIN v4.10 and Vega Ready biodegradability model v1.0.8.
Key value for chemical safety assessment
Additional information
The ultimate biodegradability of Atmer 163 (CAS No. 97925-95-6) was assessed by Bealing (2002). The testing procedure was based on the ISO Standard 14593. The conditions employed are equivalent to those represented by the OECD 301 series ready biodegradability test methods.
Non adapted activated sludge from a STP treating predominantly domestic sewage was used as inoculum. At the end of the incubation (28 days), the test vessels contents were rendered alkaline to fix inorganic carbonates and to absorb CO2 from the headspace into the test medium. The inorganic carbon (IC) yield in each vessel was then determined by injecting measured volumes of the liquid phase into a carbon analyser. The mean final IC yield for Atmer 163 was 37% of the organic carbon dosed to the test system, indicating that significant, but incomplete mineralisation had occurred. As degradation did not reach 60% Atmer 163 does not qualify for classification as readily biodegradable, but will be moderately biodegraded and is not persistent in the environment.
This is supported by additional QSAR calculations using different models (BIOWIN 1 -6 v4.10; and VEGA Ready biodegradability model v1.0.8). Calculations were performed on main components of Atmer 163. Both components fit into the applicability domain of the models. The results show that the components of Atmer 163 are readily biodegradable, thus underlining the assessment that Atmer 163 is not persistent in the environment.
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