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EC number: 273-224-1 | CAS number: 68953-70-8 The complex combination of alkanolamines from the distillation of reaction products of ammonia and oxirane. It consists predominantly of triethanolamine, diethanolamine and higher amines from the reaction of triethanolamine and oxirane.
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
Description of key information
Based on the main components, it is expected that the mixture does not significantly accumulate in aquatic organisms.
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 labelling and/or risk assessment and (4) adequate and reliable documentation of the applied method is provided.
For the assessment of "oxirane, reaction products with ammonia, distn. residues" (CAS 68953-70-8) (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
Since "oxirane, reaction products with ammonia, distn. residues" (CAS 68953-70-8) is a mixture consisting of a variety of components a single bioconcentration factor or log Kow cannot be calculated. Therefore, the bioaccumulation potential was assessed based on a weight-of-evidence approach including the available experimental and estimated BCF and log Kow values of the main components of AMIX TE which are covering more than 90% of the UVCB.
The log Kow values range from -1.62 (CAS 122-96-6) to 1.34 (CAS 102-71-6). In accordance with column 2 of REACH Annex IX, a bioaccumulation study need not be conducted since the main components of the mixture have a log Kow less than 3. Based on the log Kow of less than 3 bioaccumulation is not to be expected in aquatic organisms.
Regarding BCF data, there is one experimental result available for the main component 2,2’,2’’-Nitrilotriethanol (CAS 102-71-6; typical concentration of AMIX TE: 86%). The study was conducted according to the OECD test guideline 305 was performed.Cyprinus carpiowas used as test species. The maximum BCF determined in this study was < 3.9 (MITI 1992). No further experimental data are available.
In addition BCF values for the three main constituents were estimated using several QSAR models: EPI Suite v4.11: BCFBAF v3.01; VEGA v1.1.1/v1.1.3: CAESAR v2.1.14, Meylan v1.0.3, KNN/Read-Across v1.1.0; T.E.S.T. v4.2.1; OASIS Catalogic v5.11.17/v5.11.19: BCF baseline model v02.09. The table below lists the applied models and the resulting BCF values as well as information on the applicability domain (AD). Detailed information on the model’s results and the AD are given in the endpoint study records of IUCLID Chapter 5.3.1. The selected models comply with the OECD principles for (Q)SAR models. All BCF values indicate that significant bioaccumulation in organisms is not to be expected. The maximum BCF value is 19.1 without considering any mitigating factors, which could be reduced to 6.8 after considering mitigating factors like water solubility, metabolism and molecular size. Detailed results of the BCF models are listed in the table below. It can be concluded that significant bioaccumulation of AMIX TE is not to be expected.
Chemical name |
Oxirane, reaction products with ammonia, distn. residues |
2,2’,2’’-Nitrilotriethanol |
2,2’-[[2-(2-Hydroxyethoxy)ethyl]imino] bisethanol |
N,N,N',N'-Tetra-(2-hydroxyethyl)-bis 2,2'-aminoethylether |
CAS no. |
68953-70-8 |
102-71-6 |
17626-34-5 |
55468 -09 -2 |
BIOACCUMULATION (BCF, L/kg): |
||||
Exp. data |
no data |
MITI (1992):Cyprinus carpio: BCF < 3.9 L/kg |
no data |
no data |
Calc. data |
||||
BCFBAF v3.01(EPI Suite v4.11): Meylan et al.(1997/1999) |
no data |
3.6* |
3.2* |
3.2* |
CAESAR v2.1.14 (VEGA v1.1.3) |
no data |
3.0* |
1.0* |
1.0# |
Meylan v1.0.3 (VEGA v1.1.3) |
no data |
3.0# |
3.0# |
3.2# |
KNN/Read-Across v1.1.0 (VEGA v1.1.3) |
no data |
1.26* |
0.91# |
0.5# |
T.E.S.T. v4.2.1 (US EPA, 2012) |
no data |
0.46* |
0.76* |
0.36* |
BCF baseline-model v02.09 (OASIS Catalogic v5.11.19) 1) including mitigating factors |
no data |
6.76* |
2.34* |
2.34* |
2) without mitigating factors |
no data |
19.14* |
9.16* |
9.14* |
Octanol-water partition coefficient (log Kow, 25 °C) 1) Exp. data (see IUCLID Ch. 4.7) |
no data |
-2.3 at pH 7.1 1.34 at pH 9.5 |
no data |
-1.62 at pH 9.4-9.7 |
2) KOWWIN v1.68 (EPI Suite v4.11) |
no data |
-2.48* |
-2.75* |
-1.92* |
Conclusion |
Significant accumulation in organisms is not expected based on measured and estimated BCF data (max. BCF = 19, est.) as well as log Kow values < 3 (measured and estimated; see IUCLID Ch. 4.7) for the main constituents which represent ca. 90% of the UVCB. |
The substance does not significantly accumulate in organisms. |
Significant accumulation in organisms is not expected. |
Significant accumulation in organisms is not expected. |
Legend:
*: The substance is within the applicability domain of the model.
#: The substance is not within the applicability domain of the model.
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