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EC number: 241-420-6 | CAS number: 17392-83-5
- 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
Inhalation is the only relevant exposure pathway for methyl lactate under REACH.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Dose descriptor:
- NOAEC
- 200 mg/m³
- Study duration:
- subacute
- Species:
- rat
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Dose descriptor:
- LOAEC
- 150 mg/m³
- Study duration:
- subchronic
- Species:
- rat
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
In a subchronic inhalation toxicity study ethyl lactate was administered to 5 male and 5 female Wistar rats/concentration by whole body exposure at concentrations of 0, 0.025, 0.075 and 0.2 mg/L (0, 25, 75 and 200 mg/m³) for 6 hours per day, 5 days/week for a total of 28 days. Two additional (recovery) groups of 5 male and 5 female Wistar rats exposed to 0 or 0.2 mg/ were kept untreated for 28 post-exposure days. Clinical observations, growth, macroscopical observations at autopsy and microscopical examinations of the nose were used as criteria for disclosing possible harmful effects.
There were no compound related effects in mortality, clinical signs, body weight or gross and histological pathology. Microscopic examination revealed minimal changes (nest-like infolds, slight hypertrophy, and slight hyperplasia) in the nasal respiratory epithelium of animals in all groups, the control group included. Type and incidence of the changes were similar in the various groups, or the changes occurred in a single animal only. These changes were not ascribed to treatment. The NOAEL is 200 mg/m³.
In contrast to a previous study (TNO report V 90.322), in which rats were exposed to 150, 600 or 2500 mg ethyl lactate per m³ for 28 days, the results of the last study show that rats exposed to 25, 75 or 200 mg ethyl lactate per m³ for the same period did not develop compound-related histopatholocial changes in the nose. The histopathological changes observed at an exposure concentration of 150 mg/m³ (TNO report V 90.322), viz. replacement of olfactory epithelium by respiratory epithelium, goblet cell hypertrophy and moderate goblet cell hyperplasia, were considered to be in line with the changes observed at concentration-response relationshop including the response seen at the 150 mg/m³ exposure concentration. The minimal changes observed in the present study consisting of nest-like infolds and slight hypertrophy and hyperplasia are fully comparable to the minimal changes observed at the 150 mg/m³ level of the previous study. However, since in the present study these minimal changes were observed in all groups, controls included, and their incidences in treatment groups were not different from those in the control group, or the changes occurred in a single animal only, these minimal alterations were not ascribed to treatment. Therefore, it is concluded that the no-adverse-effect level of ethyl lactate in the present study is 200 mg/m³, indicating that the level of 150 mg/m³ used in the previous study (TNO report V 90.322), should be considered a no-adverse-effect level as well.
The exposure to ethyl lactate at levels up to 2500 mg/m³ resulted in concentration-related adverse effects in the nose of all test groups and in growth retardation and decreased food consumption in rats exposed to 2500 mg ethyl lactate/ m³ air. Growth retardation might be explained by the impaired ability to smell and taste as a result of severe damage to the olfactory epithelium. The increased blood glucose value in males exposed to 2500 mg/m³ is considered an isolated finding unrelated to treatment. Further all observed effects can be explained from the reduced food intake and subsequent growth retardation.
Justification for selection of repeated dose toxicity inhalation - systemic effects endpoint:
Inhalation toxicity information is available for ethyl lactate and ethylhexyl lactate. There is a definitive but not very steep correlation between no-effect levels and alkyl chain length with longer alkyl chain lactates being more toxic. As such methyl lactate will be less toxic than ethyl lactate, and the NOAEC can be set at the NOAEC for ethyl lactate.
Justification for selection of repeated dose toxicity inhalation - local effects endpoint:
Ethyl lactate is irritating to the lung epithelium; irritation is caused by enzymatic hydrolysis to lactic acid. With a lower molecular weight and faster hydrolysis rate, methyl lactate will also be iriitating to the lung epithelium
Justification for classification or non-classification
No compound related effect in mortality, clinical signs, body weight or gross and histological pathology were observed at concentrations up to 200 mg/m³.
Microscopic examination revealed minimal changes (nest-like infolds, slight hypertrophy, and slight hyperplasia) in the nasal respiratory epithelium of animals in all groups, the control group included. Type and incidence of the changes were similar in the various groups, or the changes occurred in a single animal only. These changes were not ascribed to treatment. The NOAEL is 200 mg/m³.
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