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EC number: 248-698-8 | CAS number: 27859-58-1
- 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
Acute Toxicity: oral
Administrative data
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 01 June 1988 to 28 June 1988
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1989
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- no
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- no
Test material
- Reference substance name:
- (tetrapropenyl)succinic acid
- EC Number:
- 248-698-8
- EC Name:
- (tetrapropenyl)succinic acid
- Cas Number:
- 27859-58-1
- Molecular formula:
- C16H28O4
- IUPAC Name:
- 2-(C12-rich-branched olefins from propene oligomerization)-1,4-butanedioic acid
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- - Appearance: Brown liquid
- Storage conditions of test material: Ambient conditions
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Strain: Sprague-Dawley Crl:CD®BR
- Age at study initiation: Young adults. Males were 63 and 70 days old; females were 70 and 77 days old.
- Weight at study initiation: Males weighed between 272 and 353 g; females weighed between 186 and 217 g.
- Fasting period before study: Yes. Overnight prior to dosing.
- Housing: The animals were individually housed in stainless-steel wire-bottom cages in an air conditioned room.
- Diet: ad libitum access to certified rodent feed
- Water: ad libitum
- Acclimation period: 14 days for males, 21 days for females
ENVIRONMENTAL CONDITIONS
- Temperature: 20.2 to 20.6 °C
- Humidity: 47.9 to 76.4 % (relative)
- Photoperiod: 12-hour light/dark cycle
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- MAXIMUM DOSE VOLUME APPLIED: No data on dose volume
The mean (± SD) weight of the test material administered was 0.57 to 0.87 (± 0.001 to 0.002) g/kg for the males and 0.27 to 0.59 (± 0.01 to 0.02) g/kg for the females. - Doses:
- 2.0, 2.5 and 3.0 g/kg for males and 1.3, 2.0 and 3.0 g/kg for females
- No. of animals per sex per dose:
- 5 animals per sex per dose
- Control animals:
- yes
- Remarks:
- Five fasted un-dosed animals of each sex served as the controls for the 2.0 and 3.0 g/kg animals; however, in order to conserve additional animals, controls were not used for the 1.3 g/kg females and 2.5 g/kg males
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Animals were observed frequently on the day of dosing for any physiological or behavioural abnormalities and at least once each day for 14 days after treatment. The animals were weighed immediately before dosing and at 2, 7, and 14 days after treatment.
- Necropsy of survivors performed: Yes. A necropsy was performed on all animals. This included an examination of the external body surface, all orifices, the thoracic and abdominal cavities, and the contents of these cavities. The animals were sacrificed by carbon dioxide.
- Other examinations performed: Histopathology. Abnormal tissues and necessary comparison tissues were collected and fixed in 10 % neutral buffered formalin by immersion. Tissues were trimmed and embedded in paraffin, sectioned and stained with haematoxylin and eosin. Glandular stomach, non-glandular stomach and thymus gland were examined from the control animals (5 males, 5 females). Tissues with abnormal macroscopic findings were examined from all animals, including the controls. - Statistics:
- The LD50, slope, and 95 % confidence limits were determined using the method of Berkson.
Mean body weights of the 3.0 and 2.0 g/kg dose groups were compared to concurrent controls using one way analysis of variance (ANOVA) when there were three or more survivors per dose group.
Results and discussion
Effect levelsopen allclose all
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 2 100 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- >= 1 100 - <= 3 400
- Key result
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 2 700 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- >= 2 300 - <= 3 500
- Mortality:
- No animals died in the control group or the 1.3 g/kg female dose group and the 2.0 g/kg male dose group.
For the females, 2 animals died in the 2.0 g/kg dose group on days 1 to 2 and all 5 animals died in the 3.0 g/kg dose group on days 1 to 3.
For the males, 1 animal died in the 2.5 g/kg dose group on day 2 and 4 animals died in the 3.0 g/kg dose group on days 2 to 3. - Clinical signs:
- other: Salivation, anogenital, nasal and ocular discharge, decreased motor activity, soft faeces and reduced food consumption were frequently observed signs of toxicity. Signs of toxicity observed infrequently included: collapse, closed eyes, decreased body temp
- Gross pathology:
- MACROSCOPIC PATHOLOGY
The following macroscopic findings were observed in the tissues of animals in this study: red discoloration or foci in the thymus, red discoloration of the glandular or non-glandular stomach, friable areas in the non-glandular stomach, tan foci in the liver, degeneration in a testicle, an enlarged mandibular lymph node and alopecia.
MICROSCOPIC PATHOLOGY
The most common findings were congestion and/or haemorrhage in the thymus gland, and congestion in the stomach (glandular and non-glandular portions). Autolysis was common in animals dying during the study period.
In one animal of the 2.5 g/kg dose group and one from the 3.0 g/kg dose group, there was epithelial necrosis in the glandular portion of the stomach. Oedema, inflammation, ulceration, and haemorrhage were present in the non-glandular portion of the stomach of one animal from the 3.0 g/kg dose group.
Ulceration and inflammation of the non-glandular stomach also occurred in the animal from the 2.5 g/kg dose group that exhibited epithelial necrosis.
The gastric necrosis (in both glandular and non-glandular portions) was considered to be related to the oral exposure to the compound. The other findings were likely secondary lesions associated with the loss of integrity in the gastric mucosa or secondary to vascular shock associated with an agonal death.
Any other information on results incl. tables
Table 1: Mean Body Weights
Sex |
Dose (g/kg) |
|
Weight (g) |
|||
Day 0 |
Day 2 |
Day 7 |
Day 14 |
|||
M |
0 |
Mean N |
287 ± 9 5 |
322 ± 12 5 |
357 ± 14 5 |
397 ± 15 5 |
2.0 |
Mean N |
286 ± 10 5 |
260 ± 23** 5 |
312 ± 18** 5 |
369 ± 19* 5 |
|
2.5 |
Mean N |
335 ± 11 5 |
288 ± 3 5 |
335 ± 19 4 |
395 ± 22 5 |
|
3.0 |
Mean N |
289 ± 3 5 |
239 ± 2 2 |
284† 1 |
356† 1 |
|
F |
0 |
Mean N |
199 ± 8 5 |
214 ± 9 5 |
228 ± 9 5 |
240 ± 10 5 |
1.3 |
Mean N |
206 ± 9 5 |
201 ± 18 5 |
227 ± 13 5 |
244 ± 16 5 |
|
2.0 |
Mean N |
198 ± 7 5 |
171 ± 15** 3 |
217 ± 1 3 |
246 ± 10 3 |
|
3.0 |
Mean N |
197 ± 6 5 |
161† 1 |
- |
- |
†Not statistically analysed
- = Complete mortality
*Significantly less than the controls at p=0.05
**Significantly less than the controls at p=0.01
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Remarks:
- Not classified in accordance with EU criteria
- Conclusions:
- Under the conditions of the study, the LD50 and 95 % confidence limits were determined to be 2700 (2300 to 3500) mg/kg for males and 2100 (1100 to 3400) mg/kg for females.
- Executive summary:
A study was conducted to determine the acute oral toxicity potential of the test material under GLP conditions using methodology equivalent to the standardised guideline OECD 401.
Single doses of the undiluted test material were administered via gavage to fasted male and female Sprague-Dawley rats. Doses administered were 2.0, 2.5 and 3.0 g/kg for males and 1.3, 2.0 and 3.0 g/kg for females. Animals were observed frequently on the day of dosing for any physiological or behavioural abnormalities and at least once each day for 14 days after treatment. The animals were weighed immediately before dosing and at 2, 7, and 14 days after treatment. A necropsy was performed on all animals and any abnormal tissues and necessary comparison tissues were collected, fixed and processed.
No animals died in the control group or the 1.3 g/kg female dose group and the 2.0 g/kg male dose group. For the females, 2 animals died in the 2.0 g/kg dose group on days 1 to 2 and all 5 animals died in the 3.0 g/kg dose group on days 1 to 3. For the males, 1 animal died in the 2.5 g/kg dose group on day 2 and 4 animals died in the 3.0 g/kg dose group on days 2 to 3.
Salivation, anogenital, nasal and ocular discharge, decreased motor activity, soft faeces and reduced food consumption were frequently observed signs of toxicity. Signs of toxicity observed infrequently included: collapse, closed eyes, decreased body temperature, oral discharge, unkempt appearance, and abnormal respiration. No signs of toxicity were evident in surviving animals after Day 5. Other clinical observations were not considered to be signs of toxicity.
Mean body weights were significantly less than controls in males at 2.0 g/kg through Day 14 and females at 2.0 g/kg on Day 2. Depressed body weights were observed in 2.5 g/kg males through Day 7 and in 1.3 g/kg females on Day 2. Test material-related pathological changes were observed in the stomach.
Under the conditions of the study, the LD50 and 95 % confidence limits were determined to be 2700 (2300 to 3500) mg/kg for males and 2100 (1100 to 3400) mg/kg for females.
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