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EC number: 500-029-3 | CAS number: 9049-71-2 1 - 16.5 moles propoxylated
- 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
Endpoint summary
Administrative data
Description of key information
NOAEL (28 days repeated dose, Wistar): ≥ 1000 mg/kg bw.
Key value for chemical safety assessment
Additional information
Results 'read across' from study on 2, 2', 2''-nitrilotriethanol, propoxylated, as permitted by Annex XI paragraph 1.5, based on the justification in the report by Paul Illing Consultancy Services Ltd and Marlin Consultancy (Illing and Barratt, 2007). The report identifies that 2, 2', 2''-nitrilotriethanol, propoxylated is the most bioavailable of the NLP polyols linked by an ether group, and the lack of toxicity seen for it and for both components (sucrose and -propane-1,2-diol) of sucrose, propoxylated should be considered representative of of the lack of toxicity of the ether linked polyol. Thus, on animal welfare grounds this test should not be undertaken on sucrose, propoxylated. For further details concerning the grouping, consult Illing and Barratt, 2007.
In a repeated dose oral toxicity study in rats (Wistar, OECD TG 407), 2,2',2" -Nitrilotriethanol, propoxylated was adimistered via gavage to 5 rats/sex/dose at 0, 100, 300, 1000 mg/kg bw for 4 weeks.. No death was observed in either sex. No clinical effects were observed in both sex of all dose groups.There was no effect observed upon haematological, clinical biochemistry or macroscopic examination at any dose. Based on these results the NOAEL was considered to be ≥ 1000 mg/kg bw/day. If at all the slight changes in thyroids of females at 1000 mg/kg were related to the treatment, they are regarded as an indirect and adaptive effect.
The need for further testing for individual NLP polyols under the REACH Regulation can be significantly modified if arrangements for grouping into categories and ‘read across’, based on the principles in Annex XI can be used. The justifications and the proposed categories are set out in Part 1 of Barratt and Illing (2007). 'Read across' based on (a) the same bond linking the core moiety and the repeating unit moiety (b) molecular weight distributions. Sucrose is listed in Annex 4 of the regulation. Experimental data on core substances, repeating units, selected polyols within the category and 'read across' based on bioavailabilities indicates that the propoxylated substances in this category are not classifiable in respect of their repeated dose toxicity.This categorisation for read across has also been used to justify read across for tests required by Annex VII and VIII. There is sufficient available information for an adequate hazard characterisation and a chemical safety assessment. In view of this ‘weight of evidence’ approach and the need to consider animal welfare, no further testing is proposed (Illing and Barratt, 2009)
Justification for classification or non-classification
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