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EC number: 809-920-4 | CAS number: 1047637-37-5
- 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
Two key studies for the evaluation of repeated dose toxicity of the substance are available. A 28-day oral gavage study in rats according to OECD guidlines 407 and 424 and an oral dietary 2-generation study in rats according to OECD guideline 416. In the latter study histopathology of the target organs of the 28-day study was additionally performed.
In the 28-day study groups of 5 male and 5 female Spraque-Dawley rats received daily doses of 0, 15, 150 and 600 mg of the test substance/kg bw in olive oil by gavage. Treatment related effects in this study were a significantly increased blood cholesterol level in males and females of the high dose group compared to controls, singificantly increased absolute and relative liver weights in females of the 150 mg/kg bw/day group (35% and 30% respectively), females of the 600 mg/kg bw/day group (78% and 73% respectively) and in males of the high dose group (52% absolute and 68% relative). An increase in absolute and relative thyroid weight was observed in high dose animals. The absolute thyroid weights were increased by 36% and 58% and the relative weights by 48 and 54% in males and females respectively. A slight hepatocellular hypertrophy was observed in 3 of 5 female rats of the 150 mg/kg bw dose group and findings of slight to marked hepatocellular hypertrophy were reported in all males and females of the high dose group. There was no evidence of nuclear or cytoplasmic degenerative or necrotic changes. Thyroid microscopy revealed follicular cell hypertrophy, decreased diameter of follicular lumen and decreased eosinophilic colloidal contents in all animals of the high dose group. These changes are indicative of an increased thyroid activity. This is frequently observed after liver enzyme induction due to increased thyroid hormone turnover in the liver and can thus be secondary to the liver hypertrophy. A NOAEL of 15 mg/kg bw per day was derived from this study based on liver weight changes and liver histopathology ...
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 15 mg/kg bw/day
Additional information
Based on Read-Across with 2,2-Bis(chloromethyl)trimethylene bis[bis(2-chloroethyl)phophate
In a 28-day study oral (gavage) study in Sprague-Dawley rats, significantly greater absolute and relative liver weights were noted in females from the mid dose of 150 mg/kg/day and in males at the highest dose (600 mg/kg/day). A significantly higher mean cholesterol level was detected in the high dose animals. A significant increase in absolute and relative thyroid weight was also noted in the high dose group. The higher liver and thyroid weights were considered treatment-related and correlated with histopathological changes observed in these organs among these animals. A NOAEL of 15 mg/kg/day can be determined from this study based on the absolute and relative liver weight changes and the correlated liver histopathology. The effects in the mid dose group where however mild and can be viewed as adaptive rather than adverse effects. It is noted that the dose spacing in this study was large (10 fold) and therefore, the true NOAEL may actually be higher than 15 mg/kg. The target organs identified in the 28 -day and the 2 -generation study are the same, the doses at which the effects were observed in the target organs and the severity of the effects are comparable between the two studies. Therefore, the NOAEL of 15 mg/kg bw/day from the 28-day study, while conservative, can be considered to be relatively robust and an increase in the duration of exposure (to sub-chronic exposure) does not increase the severity of the effect observed. No data are available on inhalation and dermal repeated dose toxicity.
Repeated dose toxicity: via oral route - systemic effects (target organ) digestive: liver; glandular: thyroids
Justification for classification or non-classification
Due to the slight rather adaptive than adverse effects observed in the mid dose groups of both the 28 -day and the 2 -generation study in rats that do not represent a significant toxic effect according to Regulation (EC) No 1272/2008 and EC Dir 67/548 and adaptations. A significant toxic effect or target organ toxicity was not observed at dose levels below 300 mg/kg bw per day in the 28 -day study or 100 mg/kg bw per day in the 2 -generation study. Therefore no classification for specific target organ toxicity after repeated exposure is warranted.
Reference:
European Union Risk Assessment Report "2,2-Bis(chloromethyl)trimethylene bis[bis(2-chloroethyl)phophate]" (V6), CAS 38051-10-4, May 2008
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