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EC number: 205-016-3 | CAS number: 131-17-9
- 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
Information is only available for repeated oral dose toxicity. No data is available for dermal toxicity or toxicity through inhalation.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 8 - 21 September 1976
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study is well documented and reliable but exposure duration is 14 days instead of 28 days as required by the REACH regulation.
- Reason / purpose for cross-reference:
- reference to same study
- Principles of method if other than guideline:
- No specific guidelines followed, study was a preliminary study for the 13 week study (see cross reference).
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Frederick Cancer Research Center (Frederick, MD)
- Acclimation period: 18 d
- Age at study initiation: 10 wk
- Method of Identification: Ear tag
- Housing: 2-3 per cage, Polycarbonate (Lab Same as single- Products. Garfield, NJ. administration studies and Hazleton Systems, Aberdeen, MD)
- Bedding:Ab-sorb-dri ( Lab Products; Garfield, NJ)
- Diet: Purina Lab Chow@ (ground); provided ad libitum
- Water (e.g. ad libitum): Tap water in bottles, acidified to pH 2.5 with HCl; provided ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23 ± 1;
- Humidity (%):30-70;
- Air changes (per hr): 12-15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: necropsy date: 22 September 1976 - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- Dosing solution: 50 mg/ml. Different volumes were administered to achieve the various doses; vehicle controls received the same dose volume as did the 600 mg/kg animals.
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 14 d.
- Frequency of treatment:
- Once daily.
- Remarks:
- Doses / Concentrations:
0,50,100,200,400, 600 mg/kg bw
Basis:
actual ingested - No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control:
- Not applicable
- Observations and examinations performed and frequency:
- - Type and Frequency of Observation: Observed once daily for mortality; weighed on d 0,7,14.
- Necropsy of survivors performed: yes. - Sacrifice and pathology:
- No pathology performed.
- Other examinations:
- No tissues examined microscopically.
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- All the rats died at 600 mg/kg bw and 3/5 males and 1/5 females died at 400 mg/kg bw. Clinical effects were limited to inactivity occasionally occurring at 100 and 600 mg/kg bw. No clinical signs were observed in other dose groups.
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- All the rats died at 600 mg/kg bw and 3/5 males and 1/5 females died at 400 mg/kg bw. Clinical effects were limited to inactivity occasionally occurring at 100 and 600 mg/kg bw. No clinical signs were observed in other dose groups.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Males initially lost weight at 400 mg/kg bw; mean body weight gains for males at 200 or 400 mg/kg bw and for females at 400 mg/kg bw appeared to be lower than those of the vehicle controls.
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Dark, mottled lungs and distended stomachs males and females at >= 400 mg/kg bw. Enlarged cecums and spleen in both sexes at 200 mg/kg and enlarged cecums in males at 50 and 100 mg/kg. Abnormalities of liver in both sexes >=50 mg/kg bw.
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Dose descriptor:
- other: LC50
- Effect level:
- 350 mg/kg bw (total dose)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: See attached figure presenting the dose-response relation for estimation of the LC50.
- Dose descriptor:
- other: LC0
- Effect level:
- 200 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Dose descriptor:
- LOEL
- Remarks:
- Abnormalities in liver
- Effect level:
- 50 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Critical effects observed:
- not specified
- Conclusions:
- The liver appeared to be the main target organ of diallyl phthalate exposure in rats. Gross examination showed visible effects on the liver even at the lowest dose of 50 mg/kg bw tested (LOEC). Other organs affected were spleen (>= 200 mg/kg bw) and lungs (>= 400 mg/kg bw). No dose related mortality was observed at and below 200 mg/kg bw (LC0).
Reference
TABLE: Survival and mean body weights of rats in the fourteen-day repeated-administration gavage studies of diallylphthalate
Dose |
Survival |
Mean body weights (grams) |
|||
Initial |
Interim |
Final |
Change |
||
MALE |
|||||
0 |
5/5 |
128 |
161 |
191 |
63 |
50 |
5/5 |
128 |
169 |
186 |
58 |
100 |
5/5 |
128 |
161 |
182 |
54 |
200 |
5/5 |
128 |
169 |
169 |
41 |
400 |
2/5 |
128 |
112 |
124 |
-4 |
600 |
0/5 |
128 |
(d) |
(d) |
- |
FEMALE |
|||||
0 |
5/5 |
103 |
119 |
134 |
31 |
60 |
5/5 |
103 |
121 |
131 |
28 |
100 |
5/5 |
103 |
121 |
136 |
33 |
200 |
5/5 |
103 |
121 |
133 |
30 |
400 |
4/5 |
103 |
97 |
111 |
8 |
600 |
0/5 |
103 |
(d) |
(d) |
- |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 50 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- Klimisch 2
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Evaluation of the key value for repeated oral dose toxicity is based on a series of studies in rats. Studies with mice have also been added, but these show a higher tolerance for oral DAP exposure compared to rats. In rats, the liver appeared to be the primary target organ with changes observed at and above 50 mg/kg/day for males and 100 mg/kg/day for females in the 90-day study. However, the features identified in the subchronic oral rat study at 50 mg/kg/day were termed "hepatocellular alterations characterised by hepatocellular basophillia, cellular and nuclear hypertrophy and nuclear hyperchromatism". There were only mild alterations at 100 mg/kg/day and the 25 mg/kg/day histopathological examination was not performed because of the "absence (or presence of only minimal) hepatic changes at 50 mg/kg/day". The description in the study report of a low incidence of minimal (or absent) hepatic changes confirms the identification of the NOAEL at 50 mg/kg/day.
Repeated dose toxicity: via oral route - systemic effects
(target organ) digestive: liver
Justification for classification or non-classification
Specific Target Organ Toxicity: Repeated. STOT-RE is assigned on the basis of findings of ‘significant’ or ‘severe’ toxicity. In this context ‘significant’ (Category 2) means changes which clearly indicate functional disturbance or morphological changes which are toxicologically relevant. ‘Severe’ (Category 1) effects are generally more profound or serious than ‘significant’ effects and are of a considerably adverse nature which significantly impact on health. Both factors have to be evaluated by weight of evidence and expert judgement. Classification in Category 2 is applicable when significant toxic effects observed in a 90-day repeated-dose study conducted in experimental animals are seen to occur within guidance value ranges which are presented in the "Guidance on the Application of the CLP Criteria" Page 482 (noting that these are guidance values intended for guidance purposes). For a 90 day study significant effects are seen at dose levels between 10 and 100 mg/kg/day. In the results of the key study, described above, an NOAEL of 50 mg/kg/day has been selected (on the basis of the absence of or minimal hepatic changes) and the alterations at 100 mg/kg/day are described as mild. Consequently, the changes described are not considered to be significant (changes which clearly indicate functional disturbance or morphological changes which are toxicologically relevant) and therefore a classification of STOT Repeated Exposure Category 1 or 2 is not justified.
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