Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 203-149-1 | CAS number: 103-83-3
- 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
Different doses of undiluted test substance given per gavage to male rats resulted in LD50 oral: 0.65 ml (579 mg/kg bw);
Different doses applied to the dorsal skin of male rabbits resulted in LD50 dermal: 1.66 ml/kg (1477 mg/kg bw);
Whole body exposure of male and femle rats to different vapour concentrations for 4 hours resulted in LC50 inhal: 373 ppm (2052 mg/m³).
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 579 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- LC50
- Value:
- 2 052 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 1 477 mg/kg bw
Additional information
ACUTE ORAL TOXICITY
In an acute oral toxicity study undiluted test material was administered by gavage to groups of 5 male Wistar-derived rats of 90-120 g and 3-4 weeks of age. Following doses were tested: 0.5 , 1.0, 2.0 ml/kg bw (445, 890, 1780 mg/kg bw) Animals were observed daily for signs of toxicity over a 14-day postdosing period, at the end they were subjected to gross pathological examination. All animals died at a dose of 2.0 and 1.0 ml/kg bw, but only 1 of 5 at 0.5 ml/kg, indicating a steep slope to the response. Deaths occurred within 10 to 90 minutes after dosing, with the latency increasing as dosage decreased. Signs of toxicity included tremors and salivation which were seen within a few minutes after dosing. Autopsy examination of dead animals showed congestion and hemorrhages of the stomach, and intestinal congestion. Survivors of the 0.5 ml/kg bw group, sacrificed at the end of the 14 -day postdosing observation period, showed no gross abnormalities at autopsy. The LD50 was 0.65 ml/kg bw (resp. 579 mg/kg bw, Ballantyne1985).
ACUTE INHALATION TOXICITY
The acute inhalation toxicity of the test substance was studied in groups of 6 male and 6 female F344 rats per concentration
by 4-hours exposures to 25, 150, 277, 500 ppm (133, 769, 1532, 2771 mg/m³). A control group (2/sex) was exposed to filtered air only. Mortalities occurred at the highest concentration only, with all animals dying within 2 to 2.5 hours from the start of the exposure. Signs of toxicity included irritation, salivation labored breathing and urogenital wetness. During the 14 day postexposure, periorbital and perinasal red encrustations were observed and pathological changes determined in lungs and the upper respiratory tract at 500 and 277 ppm.
The LC50 was determined to be 373 ppm/4h (2052 mg/m³/4h, Ballantyne 1985)
ACUTE DERMAL TOXICITY
In an acute dermal toxicity study the undiluted test substance was applied to the clipped dorsal skin of groups containing 4 male rabbits/group at doses of 0.5, 1.0, 1.4, 2.0 ml/kg bw. The test material was maintained in contact with the skin by a polythene sheet held in place with an adhesive dressing. Animals were immobilized during a 24-hr occlusion period. At the end of the contact period the polythene sheeting was removed, the skin gently wiped clean, and the area inspected for signs of local inflamation. Animals were observed daily over a 14-day postapplication period for signs of toxicity. At the end of this time the survivors were sacrificed and subjected to autopsy examination. All animals died at the highest dose of 2.0 ml/kg bw, with a latency of up to 2 days. Signs of toxicity included tremors and hyperactivity. No signs of systemic toxicity were seen in animals following the application of 1.4 ml/kg bw and lower. On removal of the occlusive dressing, edema and necrosis were seen at the site of application of undiluted test substance to skin. This progressed to scab formation over the ensuing 14 days. Autopsy examination of the animals that died revealed a red mottled appearance to the liver and kidneys, but otherwise there were no abnormalities. The LD50 was determined to be 1.66 ml/kg bw (ca1477 mg/kg bw).
Justification for classification or non-classification
According to Regulation (EC) 1272/2008 (CLP/GHS) N,N-Dimethylbenzylamine is already classified
acute oral toxicity: category 4 (H302); acute dermal toxicty: category 4 (H312); acute inhalation toxicity: category 4 (H332).
However, based on the available data on acute inhalation toxicity, regarding Regulation (EC) 1272/2008 (CLP/GHS), classification in category 3 (acute inhalation toxicity) and labelling with H331 is required.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.