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EC number: 940-783-4 | CAS number: -
- 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
Link to relevant study record(s)
Description of key information
There is no information available for the multiconsituent substance itself. For one of the of the two major consituents, 40% is bis(2-chloroethoxy)methane CAS 111 -91 -1 + homologues, adme has been has been studied. These data are included here. Bis(2-chloroethoxy)methaneis rapidly absorbed, distributed and excreted after oral, dermal and IV exposure (Black 2007). Therfore 100% absorprion is assumed as the worst case.
The test substance is not readily biodegradable in the closed bottle test. 111-91-1: The low kow is 1.6 and further bioaccumulation testing is not required. An oral adme study with 111-91-1 shows that the majority was excreted <24 hours in the urine, only 1.5 % remained in the carcass of rats and mice after 72 hours. Therefore the test substance has low bioaccumulation potential.
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
- Absorption rate - oral (%):
- 100
- Absorption rate - dermal (%):
- 100
- Absorption rate - inhalation (%):
- 100
Additional information
There is no information available for the test substance itself.
For one of the of the two major consituents, 40% is bis(2-chloroethoxy)methane CAS 111 -91 -1 + homologues, adme has been has been studied. These data are included here.
ADME bis(2-chloroethoxy)methane, CAS 111 -91 -1
Oral:
The highest concentration was found in the kidneys 15 minutes after doing. A peak of elimination was observed at or before the 15 minute time point.In the thymus the 14C concentration increased threefold between 15 minutes and 4 hours and remained constant through 8 hours post dosing. The majority was excreted <24 hours in the urine, only 1.5 % remained in the carcass of rats and mice after 72 hours (Black 2007) .
Dermal:
After dermal exposure to 10 mg/kg bw total dose absorption ranged from 12% to 18% for rats and 14% to 22% for mice in one study (Black 2007) and in another study (RTI 2002) it ranged from 33% to 55% for rats and 17% to 25% for mice. These results indicated that rats, but not mice, ingested a significant amount of bis(2-chloroethoxy)methane from grooming at the administration site. Most of the absorbed dose was excreted in the urine. Up to 50% of the total dose volatilized from the skin of some animals during these 24-hour experiments (Black 2007).
IV:
The substance was rapidly metabolized after IV administration, within 4 hours after dosing the parent chemical was near the limit of detection in blood and not detected in urine.The major metabolite (about 40% of the dose) of BCM in rat and mice was isolated and identified as thiodiglycolic acid. Thiodiglycolic acid is cleared fairly slowly and is highly concentrated in the liver (Black 2007).
Attached is a summary on ADME from NTP TR 536 + proposed metabolic route. Bis(2-chloroethoxy)methaneis rapidly absorbed, distributed and excreted after oral, dermal and IV exposure (Black 2007).
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