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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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
The substance is not readily biodegradable.
Key value for chemical safety assessment
Additional information
Parent compound:
The biodegradation potential of DMEE (CAS 1704-62-7) was assessed in a Zahn-Wellens test according to OECD TG 302B using activated sludge from a biological treatment plant receiving primarily industrial wastewater as inoculum. DMEE was poorly eliminated from water. The removal was determined to be 17% after 28 days based on DOC removal (BASF AG, 1987, report no. 01.82).
Further experimental data are available via read-across to the structurally similar substance 2-(2-dimethylaminoethyloxy)-N,N-dimethylethanamine (BDMAEE, CAS no. 3033-62-3) from another Zahn-Wellens test (OECD TG 302B) using activated sludge from an industrial source as inoculum. Based on a DOC removal of less than 10%, it was concluded that the substance is not inherently biodegradable (BASF AG, 1987, report no. 01.79).
In a ready biodegradability study according to OECD TG 301F, BDMAEE was determined to be not readily biodegradable. The removal was only 2% after 28 d (CENOX/Huntsman, 1996, report no. 1928).
According to the screening criteria for persistence as listed in the REACH Guidance document Part C (v3.0, June 2017: Table C.4-1), DMEE is potentially P or vP as the substance has a low removal in the available tests on ready and inherent biodegradability (e.g. < 60% removal in OECD TG 301F and < 70% DOC removal in OECD TG 302B). The substance is to be considered as potentially P or vP according to the screening criteria for persistence as laid down in Section 3.1.1 of REACH Annex XIII.
Metabolites:
In addition, the model CATALOGIC 301C v11.15 (OASIS Catalogic v5.13.1) was used to predict potential metabolites of DMEE. In contrast to the experimental data, the model predicted the substance to be readily biodegradable (78% removal in 28 d, based on BOD). The substance was within the applicability domain of the model. The model predicted 19 metabolites, identifying 8 metabolites as relevant degradation products in terms of PBT/vPvB assessment, with an estimated quantity of ≥ 0.1% (for details see ‘Attached background material’ of the respective Endpoint Study Record). Two of the 8 relevant metabolites were calculated to be not readily biodegradable (between 11 and 41% after 28 days, based on BOD). The other relevant metabolites were estimated to be readily biodegradable (≥ 60% after 28 days, based on BOD). In conclusion, the majority of the predicted metabolites present in a concentration of ≥ 0.1% are estimated to be readily biodegradable.
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:
Summing up the available experimental and calculated data, DMEE (CAS 1704-62-7) is concluded to be not readily biodegradable from a precautionary point of view.
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