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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
Carcinogenicity
Administrative data
Description of key information
The 2 year carcinogenicity study in rats (NTP, 1985) did provide evidence of an increased incidence of mononuclear cell leukaemia associated with DAP administration but it was confined to high dose female rats (100 mg/kg/day) and is commonly found in control rats. The authors concluded the study provided only equivocal evidence of carcinogenicity. In a 2 year oral study (NTP, 1983) in B6C3F1 mice there was evidence of chronic inflammatory and hyperplastic responses of the forestomach leading to squamous cell papillomas which may have been associated with DAP administration. An increased incidence of lymphomas in male mice (100 mg/kg) was observed that was considered to be only equivocally related to DAP treatment. The equivocal or negative carcinogenicity data in rats and mice are considered to be of limited relevance to human exposure at the high doses
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study with acceptable restrictions: 2 instead of 3 dose levels, detailed observation not made
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 451 (Carcinogenicity Studies)
- Deviations:
- yes
- Principles of method if other than guideline:
- Diallyl phthtalate was administered by oral gavage to Fisher rats for 103 weeks in order to determine the carcinogenic potential of the substance
- GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories (Portage, MI)
- Age at study initiation: 6 wk old
- Housing: 5 animals per cage; cages Polycarbonate (Lab Products. Garfield, NJ, and Hazleton Systems, Aberdeen, MD)
- Diet: Pellets (Ralston Purina Co., St. Louis, MO); provided ad libitum
- Water (e.g. ad libitum): Tap water in bottles, acidified to pH 2.5 with HCl; provided ad libitum
- Acclimation period: 2 wks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 24
- Humidity (%): 30-70
- Air changes (per hr): 12-15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: necropsy date: 02-22-1982 - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 103 wks
- Frequency of treatment:
- 5 times/wk
- Remarks:
- Doses / Concentrations:
0, 50 & 100 mg/kg
Basis:
actual ingested - No. of animals per sex per dose:
- 50 rats/sex/dose
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Dose volume: 3.33 mg/ml
- Observations and examinations performed and frequency:
- DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly for the initial 12 weeks of the studies and once every 4 weeks thereafter
BODY WEIGHT: Yes
- Time schedule for examinations: weekly for the initial 12 weeks of the studies and once every 4 weeks thereafter
HAEMATOLOGY: Yes - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- HAEMATOLOGY
Mononuclear cell leukemia in female rats, significantly greater incidence in the high dose group: diffuse infiltration of atypical mononuclear white blood cells into the liver sinusoids and the interfollicular pulp of the spleen
HISTOPATHOLOGY: NON-NEOPLASTIC
Chronic liver injury characterized by periportal necrosis and fibrosis, pigment accumulation in periportal histiocytes and excessive bile duct hyperplasia; effects more severe in the high dose group - Relevance of carcinogenic effects / potential:
- Supporting evidence:
The apparent increase in mononuclear cell leukemia was statistically significant by both trend tests and pairwise comparisons.
The occurrence of mononuclear cell leukemia in vehicle control female rats in this study was within the range observed for historical controls.
Mitigating evidence:
There was no evidence for a diallylphthalaterelated increased occurrence of mononuclear cell leukemia in male rats or in the lower dose female rats.
Mononuclear cell leukemia is a rapidly progressing disease in Fischer 344 rats and can be difficult to diagnose in a definitive fashion.
The relatively high and variable spontaneous occurrence of mononuclear cell leukemia in aged Fischer 344 rats confounds the interpretation of an increased occurrence of this tumor type in dosed animals as evidence of a carcinogenic response.
No other chemically related increased incidences of neoplasia were observed in rats. - Conclusions:
- Because of the variability in incidence of this neoplasm in aged Fischer 344 rats and the difficulty in definitively diagnosing this lesion in Fischer 344 rats, this increase was considered to be equivocal evidence of carcinogenicity of diallylphthalate in female rats. There was no evidence of carcinogenicity in male rats.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
DAP is not classified for carcinogenicity, because data of the animal studies were insufficient to indicate a clear cause and effect between DAP administration and the observed neo-plasmic symptoms, and the tumour types observed were of no or limited significance to humans.
Additional information
In the two chronic studies in mice and rats, the evidence of DAP induced carcinogenicity is equivocal and the tumour types described were of limited significance to humans.
Justification for selection of carcinogenicity via oral route
endpoint:
These
are studies of high quality, although carried out some time ago, are
considered adequate for assessing the carcinogenicity endpoint .
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.
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