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Diss Factsheets
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EC number: 203-870-1 | CAS number: 111-44-4
- 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Acute/short term exposure
DNEL related information
Local effects
Acute/short term exposure
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Acute/short term exposure
DNEL related information
Workers - Hazard for the eyes
Additional information - workers
General Population - Hazard via inhalation route
Systemic effects
Acute/short term exposure
DNEL related information
Local effects
Acute/short term exposure
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Acute/short term exposure
DNEL related information
General Population - Hazard via oral route
Systemic effects
Acute/short term exposure
DNEL related information
General Population - Hazard for the eyes
Additional information - General Population
BCEE is metabolized within the body and has only a low risk for bioaccumulation.
The acute oral LD50 for rat is 75 mg/kg bw, the dermal LD50 is 9 mg/kg bw (assuming that the information was based on test material and not ai) and the inhalation LC50 is 0.33 mg/L. A 13 hr inhalation period with rat resulted in an NOAEL of 205 mg/m³.
Within a period of 130 days, an air concentration of 420 mg/m³, inhaled by rats and guinea pigs 7 hours daily, 5 days per week, led to delayed weight gain of the male animals as opposed to the untreated control animals. The quality of this information is unclear since no further information was provided.
Volunteers inhalatively exposed to concentrations of about 550 ppm were reported to have suffered after a short time period from unbearable severe irritation to the eyes and nose combined with cough, gag reflex and nausea. The irritation was still noticeable at 260 and 100 ppm but no longer at 35 ppm. The odor, characterized as repugnant, was still distinguished even at 35 ppm.
This strong irritation reaction is considered a good warning system against poisoning.
The ATSDR report concludes:
"The principal reason for concern with BCEE is its apparent carcinogenic potential. The most direct evidence indicating that BCEE is carcinogenic is the increased incidence of hepatomas in two strains of mice dosed orally for 80 weeks (Innes et al. 1969). This is supported by limited data indicating that BCEE is mutagenic in some bacterial test systems, although several studies have yielded negative results. On the other hand, increased incidence of mouse liver hepatomas has been questioned as a reliable indication of true carcinogenic potential (Maronpot et al. 1987), and BCEE was not observed to cause a significant increase in tumors in a chronic feeding study in rats (Weisburger et al. 1981) or in parenteral exposure studies in mice (Theiss et al. 1977; Van Duuren et al. 1972) and rats (Norpoth et al. 1986). Also, no binding of BCEE to DNA and no foci of ATPase-deficient cells (a sign of pre-neoplastic effects) were detected in liver of rats exposed to BCEE (Gwinner et al. 1983), and no evidence of heritable chromosome damage was detected in a preliminary study in mice (Jorgenson et al. 1978). Consequently, while the positive carcinogenicity findings in mice are adequate to conclude that BCEE may be a human carcinogen, the evidence on this point is limited."
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