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EC number: 268-071-2 | CAS number: 68002-58-4 This substance is identified by SDA Substance Name: C14-C18 dialkyl dimethyl ammonium methyl sulfate and SDA Reporting Number: 17-049-00.
- 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:
- (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 limited documentation / justification
- Justification for type of information:
- 1. SOFTWARE
EPISUITE v4.11
2. MODEL (incl. version number)
BIOWIN v4.10
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
Dimethyl-dihexadecyl ammonium (C34) [Cl-].CCCCCCCCCCCCCCCC[N+](C)(C)CCCCCCCCCCCCCCCC
Dimethyl-hexadecyl-heptadecyl ammonium (C35) [Cl-].CCCCCCCCCCCCCCCC[N+](C)(C)CCCCCCCCCCCCCCCCC
Dimethyl-diheptadecyl ammonium (C 36) [Cl-].CCCCCCCCCCCCCCCCC[N+](C)(C)CCCCCCCCCCCCCCCCC
Dimethyl-heptadecyl-octadecyl ammonium (C37) [Cl-].CCCCCCCCCCCCCCCCC[N+](C)(C)CCCCCCCCCCCCCCCCCC
Dimethyl-dioctadecyl ammonium (C 38) [Cl-].CCCCCCCCCCCCCCCCCC[N+](C)(C)CCCCCCCCCCCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
- Defined endpoint:
Aerobic and anaerobic biodegradation
for further details see attached information
5. APPLICABILITY DOMAIN
- Descriptor domain:
Molecular weight, structural features
- Similarity with analogues in the training set:
When a structure contained none of the fragments occurring in the training or validation sets of the 7 used models, for which coefficients were developed, the program could not estimate the probability. With the inclusion of the molecular weight parameter, estimates are possible for all structures. Thus, exceeding molecular weight reveales unreliable predictions. Since the substance contains fragments which are included in either the training set or the validation set predictions are considered to be reliable.
6. ADEQUACY OF THE RESULT
The substance falls within the range of reliable predictivity (molecular weight of the constituents ranging from 229.45 to 790.54 g/mol, weighted mean ca. 467 g/mol). Quaternary amines are contained in the trainign set. Therefore, the result of the estimation is considered to be sufficient to fulfil the information requirements. - Principles of method if other than guideline:
- prediction of biodegradation using Episuite v4.11, BioWin v4.10
- GLP compliance:
- no
- Oxygen conditions:
- aerobic/anaerobic
- Key result
- Remarks on result:
- not readily biodegradable based on QSAR/QSPR prediction
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- Di-C14-18 alkyldimethyl ammonium methosulfate is predicted to be not readily biodegradable (Episuite v4.11, BioWin v4.10).
- Endpoint:
- biodegradation in water: screening test, other
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
This read-across is based on the hypothesis that source and target substances have similar toxicological properties because
• they are manufactured from similar or identical precursors under similar conditions
• they share structural similarities with common functional groups: quaternary ammonium and saturated or unsaturated alkyl chains with comparable length (corresponding to scenario 2 of the read-across assessment framework)
The read-across hypothesis is based on structural similarity of target and source substances. Based on available experimental data, including key physicochemical properties and data from acute toxicity, irritation, sensitization (human) and genotoxicity studies, the read-across strategy is supported by a quite similar toxicological profile of all substances.
Therefore, read-across from the existing ecotoxicity, environmental fate and toxicity studies conducted with the source substances is considered as an appropriate adaptation to the standard information requirements of the REACH Regulation for the target substance, in accordance with the provisions of Annex XI, 1.5 of the REACH Regulation.
A justification for read-across is attached to IUCLID section 13.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
See justification for read-across attached to IUCLID section 13.
3. ANALOGUE APPROACH JUSTIFICATION
See justification for read-across attached to IUCLID section 13.
4. DATA MATRIX
See justification for read-across attached to IUCLID section 13. - Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across: supporting information
- Oxygen conditions:
- aerobic
- Key result
- Remarks on result:
- other: not readily biodegradable
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- Di-C14-18 alkyldimethyl ammonium methosulfate is considered to be not readily biodegradable based on reliable data from a structurally closely related substance.
Referenceopen allclose all
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.
Summary:
|
Results of single models |
Ready Biodegradability Prediction: |
Dimethyl-dihexadecyl ammonium (C34) |
Biowin1 (Linear Model Prediction) : Biodegrades Fast Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast Biowin3 (Ultimate Biodegradation Timeframe): Weeks-Months Biowin4 (Primary Biodegradation Timeframe): Days-Weeks Biowin5 (MITI Linear Model Prediction) : Readily Degradable Biowin6 (MITI Non-Linear Model Prediction): Readily Degradable Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast |
NO |
Dimethyl-hexadecyl-heptadecyl ammonium (C35) |
Biowin1 (Linear Model Prediction) : Biodegrades Fast Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast Biowin3 (Ultimate Biodegradation Timeframe): Weeks-Months Biowin4 (Primary Biodegradation Timeframe): Days-Weeks Biowin5 (MITI Linear Model Prediction) : Readily Degradable Biowin6 (MITI Non-Linear Model Prediction): Readily Degradable Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast |
NO |
Dimethyl-diheptadecyl ammonium (C 36) |
Biowin1 (Linear Model Prediction) : Biodegrades Fast Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast Biowin3 (Ultimate Biodegradation Timeframe): Weeks-Months Biowin4 (Primary Biodegradation Timeframe): Days-Weeks Biowin5 (MITI Linear Model Prediction) : Readily Degradable Biowin6 (MITI Non-Linear Model Prediction): Readily Degradable Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast |
NO |
Dimethyl-heptadecyl-octadecyl ammonium (C37) |
Biowin1 (Linear Model Prediction) : Biodegrades Fast Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast Biowin3 (Ultimate Biodegradation Timeframe): Weeks-Months Biowin4 (Primary Biodegradation Timeframe): Days-Weeks Biowin5 (MITI Linear Model Prediction) : Readily Degradable Biowin6 (MITI Non-Linear Model Prediction): Readily Degradable Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast |
NO |
Dimethyl-dioctadecyl ammonium (C 38) |
Biowin1 (Linear Model Prediction) : Biodegrades Fast Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast Biowin3 (Ultimate Biodegradation Timeframe): Weeks-Months Biowin4 (Primary Biodegradation Timeframe): Days-Weeks Biowin5 (MITI Linear Model Prediction) : Readily Degradable Biowin6 (MITI Non-Linear Model Prediction): Readily Degradable Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast |
NO |
Description of key information
not readily biodegradable (Episuite v4.11, BioWin v4.10)
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
Di-C14-18 alkyldimethyl ammonium methosulfate is predicted to be not readily biodegradable (Episuite v4.11, BioWin v4.10).
Supporting data are available for a structurally closely related substance. A justification for read-across is attached to IUCLID section 13.
Results on biodegradation of DODMAC are summarised in EU RAR, 2002 "It is shown in several tests that DODMAC/DHTDMAC are not readily biodegradable and there is no standard guideline test from which inherent biodegradability could be concluded.
Adaptation seems to be necessary for significant degradation but even then mineralisation is very slow. In river water tests with adapted inocula degradation is occurring with a half-life in the range of several weeks. In two cases degradation discontinued after 63 days reaching approx. 10% at a lower and 20% at a higher DODMAC concentration. In another study a degradation half-life of approx. 80 days could be derived. Based on these results a degradation constant kbiowater = 0.0047 d-1 can be extrapolated for surface water, which would correspond to inherently biodegradable substances (DT50 = 150 days). With this value it is taken into account that the lower DODMAC concentrations in surface waters are degraded slower than in the cited tests probably. DT50-values of <80 days from river water tests with added adapted sediment reveal situations where the concentration of biodegrading microorganisms is increased over the normal level. Therefore these results can not be used for the derivation of the degradation rate constant in surface waters. Most of the data referring to the elimination in wastewater treatment plants do not distinguish between biodegradation and adsorption."
Elimination ranged from 70 to 95% in different tests; the elimination is mainly attributable to adsorption.
[Type of water: freshwater]
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