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EC number: 249-707-8 | CAS number: 29590-42-9
- 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
Key value for chemical safety assessment
Effects on developmental toxicity
Description of key information
Three studies have been conducted relating to reproductive and developmental effects:
-Teratology Screen in Rats: No definitive indication of teratogenic effects were noted in the fetuses.
-Combined Repeat Dose and Reproductive/Developmental
Toxicity Screening Study: NOAEL for Reproductive Effects was a 20% solution applied dermally. This was the highest concentration tested.
-Repeat Dose 90-Day Oral Study in Rats. NOAEL was 600 mg/kg. There were no effects noted on reproductive organs.
Additional information
Teratology Screen
In the Teratology Screen, pregnant female rats were exposed to IOA at 1000 mg/kg from days 6 to days 15 gestation in a limit test. Clear signs of maternal toxicity were noted as evidenced by effects of body weight, clinical signs and gross pathology. Apparent effects on food and water water consumption were also noted. No definitive indication of teratogenic effects were noted in the fetuses. Any effects observed in the developing fetuses were believed attributable to the maternal toxicity.
Reproductive Screen
The reproduction screen was a dermal application to the backs of male and female rats. The animals were dosed for two weeks prior to mating, through mating until sacrifice. The animals were dosed at levels of 0%, 1%, 7.5%, 5%, 15% and 25% in acetone. The 25% dose was lowered to 20% after one week due to severe irritation. There were no test material-related significant differences observed for mating or female fertility indices, mean days to mate, or length of gestation. There were no test material-related differences for male fertility based on the percent of pregnant females. There were no test material-related effects seen in the offspring. This includes viability, clinical signs, body weight, sexual maturation, gross pathology, histopathology,
When IOA was administered dermally to rats in concentrations of 1%, 7.5%, 15%, and 20%, the NOEL for effects on reproductive performance and growth and development of offspring was 20%. There was no overt material toxicity at the highest dose level tested (20% IOA).
90-Day Study
The toxicity potential of IOA was evaluated in a 90-day repeat dose study in male and female Crl:WI(Han) rats. The study was conducted under GLP conditions. The test method was based on OECD 408 (1998). The test material was diluted in corn oil (vehicle) to the appropriate dose concentrations. Male and Female rats (10/sex/group) received 0 (vehicle), 40, 150, or 600 mg/kg/day of the test article via oral gavage for 90 days. Clinical observations (daily), body weight (weekly), food consumption (weekly), functional tests (week 12), ophthalmoscopic examination (pretest and week 13), haematology (prior to necropsy), clinical chemistry (prior to necropsy), urinalysis (at end of treatment), gross pathology (at necropsy), histopathology (at necropsy) and immunohistochemistry (at necropsy) were each examined.
Adrenal glands
Spleen
Brain
Testes
Epididymides
Thymus
Heart Uterus (including cervix)
Kidneys
Prostate1
Liver
Seminal vesicles including coagulating glands 1
Ovaries
Thyroid including parathyroid
No effects were noted in any of the reproductive organs. The NOAEL for human risk assessment is 600 mg/kg.
Justification for classification or non-classification
Based on these data, IOA does not meet the criteria for classification as a reproductive/developmental toxic substance per the DPD or CLP.
Additional information
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