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EC number: 216-940-1 | CAS number: 1704-62-7
- 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
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Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
Description of key information
Significant accumulation in organisms is not to be expected.
Key value for chemical safety assessment
Additional information
QSAR-disclaimer:
In Article 13 of Regulation (EC) No 1907/2006, it is laid down that information on intrinsic properties of substances may be generated by means other than tests, provided that the conditions set out in Annex XI (of the same Regulation) are met.
Furthermore, according to Article 25 of the same Regulation testing on vertebrate animals shall be undertaken only as a last resort.
According to Annex XI of Regulation (EC) No 1907/2006 (Q)SAR results can be used if (1) the scientific validity of the (Q)SAR model has been established, (2) the substance falls within the applicability domain of the (Q)SAR model, (3) the results are adequate for the purpose of classification and labeling and/or risk assessment and (4) adequate and reliable documentation of the applied method is provided.
For the assessment of 2-[2-(dimethylamino)ethoxy]ethanol (DMEE) (CAS 1704-62-7) (Q)SAR results were used for aquatic bioaccumulation. The criteria listed in Annex XI of Regulation (EC) No 1907/2006 are considered to be adequately fulfilled and therefore the endpoint(s) sufficiently covered and suitable for risk assessment.
Therefore, and for reasons of animal welfare, further experimental studies on aquatic bioaccumulation are not provided.
Assessment:
In accordance with column 2 of REACH Annex IX section 9.3.2 the study does not need to be conducted if the substance has a log Kow less or equal than 3. DMEE (CAS 1704-62-7) has an experimental log Kow value of -0.78 (pH 5-9, Harlan, 2012, study rep.: 41202877)
In order to assess the bioaccumulation potential of the substance, the BCF was calculated with several estimation models. Considering all models applied for the test substance, the estimated BCF values range from 0.9 to 9.42 L/kg. The substance was within the applicability domain of all estimation models except of the two VEGA submodels: Meylan v1.0.3 and CAESAR v2.1.14.
- BCF base-line model v03.10 (OASIS Catalogic v5.13.1): The model estimated a BCF of 9.42 L/kg without considering mitigation factors. But, water solubility and, for a minor part, metabolism and molecular size reduce the log BCF to 2.45 L/kg as estimated by the model. The test substance is within the applicability of the structural domain of the model (BASF SE, 2018).
- BCFBAF v3.01 (EPI Suite v4.11): Based on the estimated log Kow of -0.78 (pH 5-9, Harlan, 2012), a BCF value of 3.2 L/kg was estimated with the submodel Meylan et al. (1997/1999). This BCF estimate can be regarded as accurate as the compound was within the applicability of the model, indicating that significant bioaccumulation in organisms is not to be expected. Using the Arnot &Gobas (2003) submodel with included biotransformation rate estimates, the BCF was calculated to be 0.91 L/kg (BASF SE, 2018). The substance was not within the applicability domain of this submodel; the estimation may be less accurate due to the substance's property to appreciably ionize at physiological pH.
- T.E.S.T. v4.2.1 (US EPA, 2016): The model is validated using statistical external validation using separate training and test data sets. The Consensus method averages the reasonable results from all applicable methods of T.E.S.T.: hierarchical clustering, single model, group contribution, FDA, and nearest neighbor, resulting in a BCF of 1.27 (BASF SE, 2019). The confidence in the results is high and the substance is within the applicability domain of the model.
- VEGA v1.1.3: The KNN/Read-Across submodel v1.1.0 estimated a BCF of 1.513 L/kg (log BCF = 0.18); the substance was within the model's applicability domain.
Assessment of relevant metabolites
The model Catalogic 301 C v11.15 (OASIS Catalogic v5.13.1) calculated 19 metabolites of DMEE, identifying 8 metabolites as relevant degradation products, with an estimated quantity of ≥ 0.1% (for details see ‘Attached background material’ of the respective Endpoint Study Record in IUCLID chapter 5.2.1). Overall, the 19 modelled degradation products of DMEE were estimated to exhibit log Kow values in a range of -5.65 to 0.35, which is ≤3. Therefore, significant accumulation in organisms is not to be expected.
An overview of the predicted metabolites is given in the table below:
Table: QSAR prediction for CAS-#1704-62-7 (DMEE) using CATALOGIC 301C v11.15 – July 2018 (OASIS CATALOGIC v5.13.1.156; metabolites with a quantity > 0.001 mol/mol parent after 28 d are highlighted by grey background and bold type; metabolite no: according to (Q)SAR model Catalogic v11.15 – July 2018 (OASIS CATALOGIC v5.13.156); P.= parent, pred.= predicted)
# | Metab. | Smiles | Name and CAS no. | Quantity (mol/mol parent) | Log Kow | BOD (% after 28d, pred.) | PBT-Assessment: |
P. | 1 | CN(C)CCOCCO | 2-[2-(Dimethylamino)ethoxy]ethanol (DMEE) (CAS no. 1704-62-7) | 1.00E-05 | -1.21 | 78 | not PBT/vPvB |
1 | 2 | CN(C)CCOCC=O | 2-[2-(Dimethylamino)ethoxy]acetaldehyde (CAS no. 1407486-83-2) | 1.00E-05 | -1.23 | 78 | not found, |
2 | 3 | CN(C)CCOCC(O)=O | [2-(Dimethylamino)ethoxy] acetic acid (CAS no. 98278-28-5) | 8.26E-02 | -4.18 | 76 | not found, |
3 | 11 | C=O | Formaldehyde (CAS no. 50-00-0) | 1.28E-05 | 0.35 | 100 | not PBT/vPvB |
4 | 4 | CN(C)CC=O | 2-(Dimethylamino)acetaldehyde (CAS no. 52334-92-6) | 7.63E-06 | -0.96 | 81 | not found, |
5 | 16 | OCC(O)=O | Glycollic acid (CAS no. 79-14-1) | 9.02E-06 | -1.07 | 100 | not PBT/vPvB |
6 | 17 | CNCCOCC(O)=O | [2-(Methylamino)ethoxy] acetic acid (CAS no. 98137-58-7) | 9.23E-03 | -4.39 | 77 | not found, |
7 | 19 | CN(CCOCC(O)=O)CO | {2-[(Hydroxymethyl)(methyl)amino]ethoxy} acetic acid (CAS no. -) | 6.25E-03 | -5.65 | 41 | not found, |
8 | 6 | OC(=O)C=O | Glyoxylic acid (CAS no. 298-12-4) | 1.71E-05 | -1.40 | 100 | not PBT/vPvB |
9 | 12 | OC=O | Formic acid (CAS no. 64-18-6) | 1.28E-05 | -0.46 | 100 | not PBT/vPvB |
10 | 5 | CN(C)CC(O)=O | N,N-Dimethylglycine (CAS no. 1118-68-9) | 4.85E-03 | -2.73 | 79 | not PBT/vPvB |
11 | 18 | CNCC=O | 2-(Methylamino)acetaldehyde (CAS no. 145757-95-5) | 8.31E-07 | -1.17 | 83 | not found, |
12 | 20 | CN(CC=O)CO | N-(2-Hydroxyethyl)-N-methylformamide (CAS no. 1590-50-7) | 5.63E-07 | -2.42 | 20 | not registered |
13 | 7 | OC(=O)C(O)=O | Oxalic acid (CAS no. 144-62-7) | 1.71E-05 | -1.74 | 100 | not PBT/vPvB |
14 | 10 | CNC | Dimethylamine (CAS no. 124-40-3) | 5.33E-02 | -0.17 | 71 | not PBT/vPvB |
15 | 15 | CNCC(O)=O | Sarcosine (CAS no. 107-97-1) | 3.68E-02 | -2.94 | 81 | registered, but no relevant data |
16 | 21 | CN(CC(O)=O)CO | N-(Hydroxymethyl)sarcosine (CAS no. 15826-50-3) | 5.02E-02 | -3.20 | 11 | not registered |
17 | 13 | CN | Methylamine (CAS no. 74-89-5) | 2.82E-01 | -0.64 | 64 | not PBT/vPvB |
18 | 22 | OCNCC(O)=O | Glycine, N-(hydroxymethyl)- (CAS no. 15874-34-7) | 4.89E-04 | -3.41 | 92 | not found, |
19 | 23 | NCO | Methanol, amino- (CAS no. 3088-27-5) | 5.65E-08 | -2.10 | 100 | not found, |
Conclusion:
Based on the experimental data for the log Kow and supported by a weight-of-evidence approach from calculated BCF data DMEE (CAS 1704-62-7) is concluded to not significantly accumulate in organisms.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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