Registration Dossier
Registration Dossier
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: 205-565-9 | CAS number: 142-84-7
- 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
Acute Toxicity:
- oral: LD50: 495 mg/kg bw (rat);
- dermal: 925 mg/kg bw (rat);
- inhalation: 4.4 mg/L air (rat);
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 495 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- LC50
- Value:
- 4 400 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 925 mg/kg bw
Additional information
Oral:
In a study which was in large parts equivalent to methods described in OECD guideline 401, the LD50 for oral acute toxicity in rats was calculated as 495 mg/kg bw (BASF AG, 1969; Val. 2). Doses of 290, 370, 474 and 592 mg/kg bw of an 4% aqueous solution were applied by gavage followed by a post dose period of 7 days. Main clinical signs observed were intermittent respiration, dyspnoe, ruffled fur, squatting posture, trembling gait and watery mouth discharge. At necropsy no abnormalities were noted.
In a further acute toxicology study dose levels of 125, 250, 500, 1000, 2000 mg/kg bw were administered to 4 female animals and a similar result was obtained (LD50 = 500 mg/kg bw; Dow Chemical 1973; Val 2). A slightly lower LD50 of 300 mg/kg bw was found in a study where only female animals were tested (Eli Lilly, 1980; Val. 2). Additionally the results of the study indicated that dipropylamine may cause CNS effects such as hyperactivity and leg weakness. When tested as a 5% solution a LD50 of 933 mg/kg bw and at necropsy congestion of internal organs was observed (Union Carbide, 1980; Val. 2). In the same report it is mentioned that dipropylamine was found to be more toxic undiluted as rats were killed by a dosage of only 125 ml/kg bw. As it is usual with corrosive materials, apparent toxicity is less upon dilution.
Acute systemic toxicity was evaluated in groups of 5 mice administered a gavaged oral dose of 10% dipropylamine in corn oil at doses ranging from 100-1600 mg/kg bw. The LD50 was 800-1600 mg/kg bw with time to death of a solitary high-dose mouse occurring at 13 minutes post-gavage. Symptoms of toxicity exhibited during 2 weeks post-treatment observation included weakness, ataxia, and convulsions at the highest dosage (Eastman Kodak, 1955; Val. 2).
Inhalation:
In an acute inhalation toxicity study after 1 h of exposure no mortality occurred and the LC50 was set to be over the calculated dose of 8.22 mg/L air (Eli Lilly, 1979; Val. 2). The animals were ataxic and hypoactive the first hour following exposure and several animals exhibited tremors. Other observations included bloody nasal discharge, labored respiration and wheezing. A LC50 of 4.4 mg/L air (4h) is stated in a Russian study from 1982 with unclear validity (Izmerov, Val. 4).
Additional data were available from an inhalation risk test (IRT) which meets generally accepted scientific principles (BASF AG, 1969; reliability score 2). The inhalation of a saturated vapor-air mixture for 3 minutes caused mortality. Clinical signs were escape attempts, dyspnoea, trembling, anaemia. At necropsy, distended lungs were observed. A second IRT study was conducted with 4 Sprague-Dawley rats receiving whole body exposure to a saturated atmosphere of dipropylamine in a gas environment chamber for 15 minutes. Ten to twelve minutes into the exposure, all rats were observed with labored breathing to the point of gasping, loss of equilibrium, and forced movements. After 15 minutes of exposure, some of the animals became prostrate and the exposure was terminated. All animals survived the exposure and subsequent 14 day observation period. Necropsy did not revealed any gross alterations (DOW, 1973; Val. 2). In a third IRT no mortality occurred after a 15 min exposure of concentrated vapor (Union Carbide, 1957; Val. 2).
Dermal:
In an acute dermal toxicity study the LD50 was found to be 925 mg/kg bw (Union Carbide, 1957, Val. 2.). Dipropylamine was applied to the skin of groups of 4 male rats at doses of 462.5, 925 and 1850 mg/kg bw for 24 hours. Following treatment, rats were observed daily and a gross necropsy examination was performed at the time of scheduled euthanasia (day 14). Necrosis of the skin resulted from the covered application. Internal organs of victims appeared pale or opaque and the lung among the 6 animals that died had hemorrhaged. In a second report with very limited data only a LD50 of 3700-7400 mg/kg bw is stated (East Kodak, 1980; Val. 4)
Justification for classification or non-classification
EU classification according to Annex I of Directive 67/548/EEC: Xn, R22
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.
