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EC number: 203-872-2 | CAS number: 111-46-6
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
From the available test data in combination with the QSAR calculation it can be concluded, that the test substance shows a very low long-term toxicity to fish.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- NOEC
- Effect concentration:
- > 40 mg/L
Additional information
Within the category of 'ethylene glycol and higher glycols'data on long-term effects to fish are available only for triethylene glycol (CAS 112-27-6, Montgomery et al., 1985). Therefore, the read-across approach was performed in order to assess the long-term toxicity of diethalene glycol to fish.
The early life stage test was conducted with triethylene glycol according to the standard of ASTM (E-47.01, Draft No. 3, 1980 - Standard for Toxicity Tests With the Early Life Stages of Fisheries). In this study survival, hatching and growth (weight) of embryos from the saltwater species Menidia peninsulae were monitored. The test organisms were exposed under flow-through conditions for 28 days. Statistically significant differences were found in weight and survival at the highest test concentrations (230 and 1500 mg/L, measured). Nevertheless, since the survival of the embryos was significantly different from the control at 230 mg/L but not at 1500 mg/L, the effect observed was not concentration dependent. Hence, it have to be expected that the effect in the 230 mg/L treatment may not be caused by toxicity of the test item. However, the key NOEC of > 40 mg/L (measured, based on weight and mortality) was used as the key value as the worst-case consideration.
Additionaly, for the test substance itself and for the each structurally similar substance long-term toxicity to fish was determined using a valid QSAR model (ECOSAR v2.0; BASF SE, 2022). The model predicts the chronic value ChV, which is defined as the geometric mean of the no-observed-effect concentration (NOEC) and the lowest-observed-effect concentration (LOEC). The ChV for the test substance was predicted to be 20734 mg/L. The substance is within the applicability domain of the model. The estimated chronic values are presented in the table 1.
Table 1. Overview of the estimated ChVs for the substance and its structurally similar substance.
CAS Nr. | ChV (mg/L) | Applicability Domain |
107 -21 -1 | 913.9 | in AD |
111 -46 -6 | 20734 | in AD |
112 -27 -6 | 18640 | in AD |
112 -60 -7 | 41268 | in AD |
4792 -15 -8 | 86666 | in AD |
Overall, experimental and estimated chronic values are clearly greater than 1 mg/L with regard to classification limits and also greater than 10 mg/L, which the limit concentration in long-term toxicity testing; therefore, long-term effects on fish are not to be expected.
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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