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EC number: 225-716-2 | CAS number: 5026-74-4
- 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
In the first acute oral toxicity test conducted according to OECD 401 guideline and without GLP principles, the test substance is slightly toxic in Chinese hamster and the LD50 was determined to be 2739 mg/kg bw.
In the second acute oral toxicity test conducted according to OECD 401 guideline and without GLP principles, the test substance is harmful in Mouse and the LD50 was determined to be 1413 mg/kg bw.
In the third acute oral toxicity test conducted according to OECD 401 guideline and without GLP principles, the test substance is slightly toxic in rats and the LD50 was determined to be 1037 mg/kg bw.
In the acute dermal toxicity test conducted according to OECD 402 guideline and without GLP principles, the test substance is practically nontoxic in rats and the LD50 was determined to be greater tahn 4000 mg/kg bw.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- April 9 - April 30, 1980
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well-documented pre-guideline study without GLP, testing protocol similar to OECD 401
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- yes
- Remarks:
- Pre-guideline and pre-GLP study.
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: T1f: RAIf (SPF)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Healthy random bred rats of 7-8 weeks age were raised on the premises and kept at room temperature of 22 + 2 deg. C, at relatie humidity of 55 + 10% and on a 10 hour light cylce day. They received ad libitum rat food (supplier: NAFAG, Gossau, Switzerland) and water.
They were adapted to the laboratory for a minimum of 4 days before treatment. During treatment and observation period the animals were housed in groups of 5 animals in Macrolon cages type 3. Animals were individually marked with picric acid. - Route of administration:
- oral: gavage
- Vehicle:
- polyethylene glycol
- Remarks:
- PEG 400, Fluka AG, Art. 81170
- Details on oral exposure:
- Animals fasted overnight were treated by single oral intubation.
- Doses:
- 400 - 1000 - 2000 - 3000 mg/kg bw
- No. of animals per sex per dose:
- 5 males and 5 females
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Observations: 1 / hour for the first 5 hours, thereafter at least 1 / day. Body weight determination 1 / week
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight - Statistics:
- LD50 including 95% confidence intervals were calculated by the logit model
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- ca. 1 037 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- > 668 - < 1 403
- Mortality:
- Males: 3000 mg/kg 2 (3 hours), 1 (5 hours), 2 (24 hours) : 5/5
Males: 2000 mg/kg 1 (24 hours), 1 (day 2), 1 (day 4), 1 (day 6) : 4/5
Males: 1000 mg/kg 2 (24 hours): 2/5
Males: 400 mg/kg : 0/5
Females: 3000 mg/kg 1 (2 hours), 3 (5 hours), 1 ( 24 hours) : 5/5
Females: 2000 mg/kg 1 (24 hours), 1 (day 3), 1 (day 4), 1 (day 6) : 4/5
Females: 1000 mg/kg 3 (24 hours), 1 (day 6) : 4/5
Females: 400 mg/kg : 0/5 - Clinical signs:
- other: Animals treated with 3000 mg/kg bw showed a moderate effect on ruffled fur for the first 5days and slight effects as sedation, dyspnea, exophthalmos, diarrhea and curved body position (all on on the first 5 hours). Animals treated with 2000 mg/kg bw show
- Interpretation of results:
- sligthly toxic
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The acute toxicity is similar for males and females. The LD50 is 1037 (668-1403) mg/kg bw.
- Executive summary:
The acute toxicity has been investiagated in a pre-guideline and pre-GLP study performed and recorded similarly to the later standards. The doses selected were 3000 -2000 -1000 and 400 mg/kg bw. Each 5 male and 5 female animals were treated by gavage application with the test substance suspended in PEG 400. Mortality was 100% at the top dose in both sexes. Mortality at the lower dose was 80% in both sexes, 40% in males and 80% in females at 1000 mg/kg bw. The low dose was without mortality in both sexes. At all doses there were the usual clinical symptoms in animals of both sexes. Mortality occurred within 6 days after treatment. The LD50 calculated is 1037 mg/kg bw (95% confidence limits are 668 -1403 mg/kg).
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 1 037 mg/kg bw
- Quality of whole database:
- Data from rat, mouse and chinese hamster are available. The rat is the most sensitive species.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- May 21 - June 10, 1980
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well-documented pre-guideline study without GLP, testing protocol similar to OECD 402
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Deviations:
- yes
- Remarks:
- pre-guideline and pre-GLP study
- Principles of method if other than guideline:
- According to: Noakes, D.N. and Sanderson, D.M. (1969). A method for determining the dermal toxicity of pesticides. Brit. J. Indust. Med. 26, pp 59-64.
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Tif:RAIf (SPF)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Healthy random bred Rats of 8-9 weeks age were raised on the premises and kept at room temperature of 22 + 2 deg. C, at relatie humidity of 55 +/- 10% and on a 10 hour light cylce day. They received ad libitum rat food (supplier: NAFAG, Gossau, Switzerland) and water. They were adapted to the laboratory for a minimum of 4 days before treatment. During treatment and observation period the animals were housed individually in Macrolon cages type 2.
- Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- Approximately 24 hours before treatement an area of approximately 60 square centimeters was shaved with an electric clipper. For the treatment the test material was evenly dispersed on the skin with a syringe and was covered with an occlusive dressing which was fastened around the trunk with an adhesive elastic bandage. After 24 hours the dressing was removed, the skin was cleaned with lukewarm water and the reaction of the skin was appraised.
- Duration of exposure:
- 24 hours
- Doses:
- 0 - 3000 - 3500 - 4000 mg/kg bw Treatment with higher doses was not possible
- No. of animals per sex per dose:
- 5 males and 5 females
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Observations: 1 / hour for the first 5 hours, thereafter at least 1 / day. Body weight determination 1 / week
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight - Statistics:
- not required
- Sex:
- male/female
- Dose descriptor:
- LD0
- Effect level:
- > 4 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- no mortality observed during the observation period of 14 days following treatment
- Clinical signs:
- other: Animals treated with 4000 mg/kg bw showed a moderate skin erithema (days 2-8) and a slight skin erythema on day 9. Slight effects recorded are sedation (days 1-5), dyspnea (days 1-6), exophthalmos (days 1-7), ruffled fur (days 1-8) and curved body positi
- Gross pathology:
- No substance related gross organ changes were seen.
- Interpretation of results:
- practically nontoxic
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The acute toxicity is similar for males and females. The acute dermal toxicity is >4000 mg/kg bw.
- Executive summary:
The acute dermal toxicity has been investigated in a pre-guideline and pre-GLP study performed and recorded similarly to the later standards. The doses selected were 4000, 3500 and 3000 mg/kg bw. Each 5 male and 5 female animals were treated on the shaved skin (60 cm2) and received an occlusive patch . There was no mortality in all dose groups. At all doses there were the usual clinical symptoms in animals of both sexes. The LD50 derived is >4000 mg/kg.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 4 000 mg/kg bw
Additional information
Oral:
The acute toxicity of p-(2,3-epoxypropoxy)-N,N-bis(2,3-epoxypropyl)aniline was assessed on three different species: Chinese hamster, mouse and rats which is the most sensitive species.
In the first experiment, in Chinese hamsters, the acute oral LD50 of the test material was determined in both sexes and animals were
observed over a period of 14 days. The LD50 is found to be 2739 (2276-3429) mg/kg. The test material has therefore a slight acute toxicity to Chinese hamsters by this route of administration.
In the second experiment, the acute toxicity has been investigated in mouse. Each 5 male and 5 female were trated by gavage application with the test substance suspended in PEG 400 at doses seleceted: 3000 -2500 -1500 -1000 and 600 mg/kg bw.
Mortality was 100% at the top dose in females and 80% in the top dose in males. Mortality at the lower dose was 80% in both sexes, 80% in males and 60% in females of the middle group. Mortality was 20% in males and 0% in females at 1000 mg/kg bw. The low dose was without mortality in males and 20% in females. At all doses there were the usual clinical symptoms in animals of both sexes. Mortality occurred within 4 days after treatment. The LD50 calculated is 1413 mg/kg bw (95% confidence limits are 1024 -1873 mg/kg).
In the third experiment which is the Key study, the acute toxicity has been investigated in rats, 5 male and 5 female were used in each group. The doses selected were 3000 -2000 -1000 and 400 mg/kg bw. The test system was supsended in PEG 400.
Mortality was 100% at the top dose in both sexes. Mortality at the lower dose was 80% in both sexes, 40% in males and 80% in females at 1000 mg/kg bw. The low dose was without mortality in both sexes. At all doses there were the usual clinical symptoms in animals of both sexes. Mortality occurred within 6 days after treatment. The LD50 calculated is 1037 mg/kg bw (95% confidence limits are 668 -1403 mg/kg).
Dermal:
The acute dermal toxicity has been investigated in rats. The doses selected were 4000, 3500 and 3000 mg/kg bw. Each 5 male and 5 female animals were treated on the shaved skin (60 cm2) and received an occlusive patch . There was no mortality in all dose groups. At all doses there were the usual clinical symptoms in animals of both sexes. The LD50 derived is >4000 mg/kg.
Justification for selection of acute toxicity – dermal endpoint
The acute dermal toxicity has been investigated in a pre-guideline and pre-GLP study performed and recorded similarly to the later standards. The doses selected were 4000, 3500 and 3000 mg/kg bw. Each 5 male and 5 female animals were treated on the shaved skin (60 cm2) and received an occlusive patch . There was no mortality in all dose groups. At all doses there were the usual clinical symptoms in animals of both sexes. The LD50 derived is >4000 mg/kg.
Justification for classification or non-classification
According to Regulation (EC) No 1272/2008 on classification, labelling and packaging of substances and mixtures, p-(2,3-epoxypropoxy)-N,N-bis(2,3-epoxypropyl)aniline should be classified for acute oral toxicity as Category 4 and should be labeled as H302: Harmful if swallowed.
p-(2,3-epoxypropoxy)-N,N-bis(2,3-epoxypropyl)aniline does not have to be classified for acute dermal toxicity to Regulation (EC) No 1272/2008.
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