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EC number: 403-730-1 | CAS number: 2687-96-9
- 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
Repeated dose oral:
A 28-day oral toxicity study (Smith, 1989) was available which is key study. This study showed that No Observed Adverse Effect Level (NOAEL) for the test substance is 100 mg/kg/day.
A 90-day oral (capsule) toxicity study with dog (Liao, 1991) which run on analog substance N-(n-octyl)-2-pyrrolidinone (2687-94-7) is available which is key study. The NOAEL was 30 mg/kg bw/day.
Repeated dose inhalation:
Endpoint waived as the substance is corrosive to the skin.
Repeated dose dermal:
A repeated dose dermal study (Busch, 1987) used 2% w/v suspension in distilled water was available which is supporting study. This study showed that a mean comedogenic grade of ≥ 2.0 in rabbits.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 38 mg/kg bw/day
- Study duration:
- subacute
- Species:
- dog
- Quality of whole database:
- The No Observed Adverse Effect Level (NOAEL) for the analogue was 30 mg/kg bw/day, corrected for the molecular weight of N-(n-dodecyl)pyrrolidinone the NOAEL is 38 mg/kg bw/day.
Additional information
Repeated dose oral:
A 28 -day oral toxicity study had no guideline using rat (Smith, 1989). Key study.
This study showed that No Observed Adverse Effect Level (NOAEL) for the test substance is 100 mg/kg/day.
A 90-day oral (capsule) toxicity studies with dog (Liao, 1991) which run on analog substance N-(n-octyl)-2-pyrrolidinone (2687-94-7) was conducted according to EPA OPP 82-1 (90-Day Oral Toxicity). Key study. This study showed that No Observed Adverse Effect Level (NOAEL) for the test substance is 30 mg/kg bw/day for N-(n-octyl)-2-pyrrolidinone corresponding to 38 mg/kg bw/day for N-(n-dodecyl)-2-pyrrolidinone. The Lowest Observed Adverse Effect Level (LOAEL) in dogs is 90 mg/kg bw/day for N-(n-octyl)-2-pyrrolidinone corresponding to 115 mg/kg bw/day for N-(n-dodecyl)-2-pyrrolidinone.
The table below summarizes the repeated dose oral toxicity studies performed with either of the two molecules. Taking note of the direct comparison of the 28-day toxicity studies in rat (100 mg/kg bw/d for N-(n-dodecyl)pyrrolidinone and 55 mg/kg bw/d for N-(n-octyl)-2-pyrrolidinone) and furthermore making allowance for the difference in duration between 28-day and 90-day studies, the NOAELs are considered to be broadly comparable. In fact, the toxic potency of N-(n-octyl)-2-pyrrolidinone appears to be higher than that of N-(n-dodecyl)pyrrolidinone. This supports the assumption that read across from the first to the second molecule is overprotective. The final No Observed Adverse Effect Level (NOAEL) for N-(n-octyl)-2-pyrrolidinone of 30 mg/kg bw/day was based on the 90-day study in dogs. Corrected for the molecular weight of N-(n-dodecyl)pyrrolidinone the extrapolated NOAEL is 38 mg/kg bw/day.
Existing repeat dose toxicity studies are available on both substances:
Substance |
N-(n-dodecyl)pyrrolidinone |
N-(n-octyl)-2-pyrrolidinone |
||
Duration |
28 day |
90 day |
28 day |
90 day |
Route |
Oral gavage |
Oral capsule |
Oral gavage |
Dietary |
Species |
Rat |
Dog |
Rat |
Rat |
NOAEL (mg/kg bw/d) |
100 |
30 |
55 |
33 – 69 |
Reference |
Smith, 1989a |
Liao, 1991b |
Smith, 1989b |
Liao, 1991a |
Reapeated dose inhalation:
According to REACH Annex VIII column 2 this endpoint is waived as: the substance is classified as corrosive to the skin and the vapour pressure of the test substance has been determined as: 0.00204 Pa at 25℃.
Repeated dose dermal:
This endpoint waived due to positive skin corrosion classification.
A repeated dose dermal study was conducted according to 21 CFR Part 58 (Busch, 1987). Supporting study.
This study is primarily a Comedogenic study and so is conducted at low doses and investigations focussed on dermal reactions. While well run is not considered suitable to address this endpoint in isolation. It showed that a mean comedogenic grade of ≥ 2.0 in rabbits.
Justification for classification or non-classification
Repeated dose toxicity: Oral. The NOEL for the 28-day study with N-(n-dodecyl)-2-pyrrolidinone in rats was 100 mg/kg/day, while the LOEL was 1000 mg/kg/day. In addition, the 90 -day NOEL for rats was > 10 mg/kg/day and the LOEL calculated for dogs was > 100 mg/kg/day, both based on the studies with the analog N-(n-octyl)-2-pyrrolidinone. Application of the CLP Criteria (version 4.0, 2013) "STOT-RE clasification is assigned on the basis of findings of ‘significant’ or ‘severe’ toxicity. In this context ‘significant’ means changes which clearly indicate functional disturbance or morphological changes which are toxicologically relevant." Hence, these data were not considered as sufficient evidence for a STOT-RE classification in Category 2.
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