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EC number: 700-080-3 | CAS number: 752225-55-1
- 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
Key value for chemical safety assessment
Additional information
With
respect to molecular weight and their physico-chemical properties, it
can be concluded that X-110/X-500 and Cargill BP-A are poorly absorbed
as such. A metabolic step by enzyme lipases is however likely to happen
in the gastrointestinal tract to form better absorbable substrates. By
hydrolysis, some parts of X-110/X-500 and Cargill
BP-A
are assumed to be cleaved in epoxidized fatty acids and glycerol.
While
X-110/X-500 and Cargill
BP-A
themselves are probably poorly absorbed, their cleavage products are
likely to be absorbed somewhat more effectively than the parental
compounds. With respect to their chain length, fatty acid epoxides are
assumed to be absorbed in the gastro-intestinal tract by
carrier-mediated transport, as known for structurally related long-chain
fatty acids. Data from studies in humans and animals indicate glycerol
is rapidly absorbed in the intestine and distributed throughout the
blood. The
probable bioavailability of such cleavage products is affirmed by
studies with the structure-related ESBO. Its cleavage products,
comparable to those of X-110/X-500 and Cargill
BP-A,
might be bioavailable to some extent and the slight organ weight changes
in liver and kidney after repeated administration may be attributable to
their systemic exposure.
Absorption of X-110/X-500 and Cargill
BP-A
via skin is expected to be very low, since molecular weight and its high
log POW impede skin permeability. This is supported by the
absence of systemic toxicity in the acute dermal study conducted with
ESBO. Inhalative
exposure to X-110/X-500
and Cargill
BP-A
is
of no relevance due to the low vapour pressure.
Metabolism from X-110/X-500 and Cargill BP-A and their cleavage products is assumed to occur already in the gastrointestinal tract. In principle, the epoxide moieties may be metabolically inactivated in the body by two different enzymatic routes: conjugation of the epoxide moiety with the endogenous tripeptide glutathione (GSH) catalysed by glutathione S-transferase (GST) or hydrolysis of the epoxide moiety catalysed by epoxide hydrolase (EH), yielding the corresponding 1,2-diols. The X-110/X-500 and Cargill BP-A cleavage products fatty acid epoxides are classically hydrated by soluble epoxide hydrolase (sEH). Although epoxy-fatty acids are relatively poor substrates for microsomal epoxide hydrolase (mEH) compared to sEH, the former enzyme hydrolyzes them with a high enantioselectivity, whereas the latter shows little or no enantiomeric preference.
EH and GST are both
mainly expressed in liver and the GI-tract mucosa, where detoxification
of epoxy-fatty
acids
presumably proceeds. This
is confirmed by repeated dose effects in liver induced by the
structure-related ESBO, which are probably correlated to the metabolic
detoxification of the cleavage products.
Glycerol is
phosphorylated to alpha-glycerophosphate by glycerol kinase
predominantly in the liver (80-90%) and kidneys (10-20%) and
incorporated in the standard metabolic pathways to form glucose and
glycogen. Glycerol may also be combined with free fatty acids in the
liver to form triglycerides (lipogenesis). The turnover rate is directly
proportional to plasma glycerol levels.
Due to their low absorption rate, X-110/X-500 and Cargill BP-A are assumed to be eliminated predominantly via faeces.
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