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Diss Factsheets
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EC number: 203-962-1 | CAS number: 112-35-6
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
Substance: 2-(2-(2-methoxyethoxy)ethoxy)ethanol:
Leuciscus idus: 96hr LC0>10000mg/l
Danio rerio: 96hr LC0>5000mg/l
P promelas, 96hr LC50>10000mg/l
Danio rerio, 96hr NOEC (fish embryo test)>820mg/L
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 10 000 mg/L
Additional information
Conventional guideline acute toxicity studies are available for 2 -(2 -(2 -methoxyethoxy)ethoxy)ethanol across two different fish species. Studies consistently show that the substance is effectively non toxic to fish with LC0 values between 5000 -10000mg/l and LC50 values in excess of 10000mg/l. There is no data available on marine fish.
2-(2 -(2 -methoxyethoxy)ethoxy) ethanol (TEGME) and its main metabolite (2 -(2 -methoxyethoxy)ethoxy) acetic acid (TEGMEA) were evaluated using the zebrafish embryotoxicity test (ZET). The morphological characteristics of each embryo were assessed at 72 and 96 hours post fertilization (hpf) following exposure to the test substance at various concentrations up to a maximum tolerated dose ascertained by a dose range finder study. At 72 hpf, the embryos were evaluated for dead or alive. At 96 hpf, the embryos and larvae were evaluated for a wide series of normal or anomalous developmental characteristics substance at various concentrations up to a maximum tolerated dose ascertained by a dose range finder study, which in the case of TEGME was 10mM and TEGMEAA 5mM. The lower figure was used for the main study for both substances.
Both substances were found to cause some isolated effects across all doses in both the range finder and main study. There was no dose response or consistency in the findings with the highest doses showing the least effects. The findings were interpreted as random and not treatment related. The positive controls (ethanol and methoxyacetic acid) used exhibited a wider range of developmental effects (growth retardation and malformations). Both substances were considered as negative by the study authors in this assay. The NOAEL was 5.0mM (820mg/L) for TEGME and 5mM (890mg/L) for TEGMEA, the maximum tested doses.
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