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EC number: 204-211-0 | CAS number: 117-81-7
- 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
Additional toxicological data
Administrative data
- Endpoint:
- additional toxicological information
- Adequacy of study:
- other information
Data source
Reference
- Title:
- No information
- Author:
- World Health Organization, International Agency for Research|on Cancer: IARC Monographs on the Evaluation of the|Carcinogenic Risk of Chemicals to Humans; DEHP; 77, 41-148|(2000)
Materials and methods
- Type of study / information:
- Type: other: Review (WHO; carcinogenicity, reproductive toxicity)
Test material
- Reference substance name:
- Bis(2-ethylhexyl) phthalate
- EC Number:
- 204-211-0
- EC Name:
- Bis(2-ethylhexyl) phthalate
- Cas Number:
- 117-81-7
- Molecular formula:
- C24H38O4
- IUPAC Name:
- 1,2-bis(2-ethylhexyl) benzene-1,2-dicarboxylate
Constituent 1
Results and discussion
Any other information on results incl. tables
RS-Freetext:
DEHP is ubiquitous in the general environment. Occupational
exposure is usually <1mg/m³, concentration in ambient air is
usually <0.1 mg/m³. Highest levels are found in foods rich
in fat, e.g. milk, where concentrations up to 10 mg/kg were
found. Large exposure may result from DEHP leaching out of
medical devices, e.g. during dialysis.
Human carcinogenicity data: one small (limited power) study
failed to show excess cancer mortality.
Animal carcinogenicity data: carcinogenic in rodents.
Considerable amount of information is available that
carcinogenicity is related to peroxisome proliferation via
binding an activation of the nuclear peroxisome proliferator
receptor a. This phenomenon is given in rodents, but not in
man.
Exposure during of rat and mice during organogenesis caused
malformations and fetal death. One study in knock-out mice
suggested that this was not mediated by the peroxisome
proliferator receptor a. No human reproductive and
developmental effect data were available. Exposure of rats
and mice to DEHP impaired fertility and damaged testes.
Young animals were much more susceptible. This effect was
independent from peroxisome proliferator receptor a as
evidenced in studies using knock-out animals. Sertoli cells
were the main target in the testes.
DEHP was extensively examined for genotoxic effects in vivo
and in vitro. However, the vast majority of results was
negative. No DNA-binding was found nor were DNA-strand
breaks.
Applicant's summary and conclusion
- Conclusions:
- CL-Freetext:
Evaluation:
There is adequate evidence of carcinogenicity in
experimental animals, and inadequate evidence of
carcinogenicity in humans.
Overall evaluation: DEHP is not classifiable as to its
carcinogenicity in humans (Group 3).
The overall evaluation takes into account:
a) carcinogenicity in rodents was not dependant on
DNA-binding but involved peroxisome proliferation
b) peroxisome proliferation and hepatocellular proliferation
were noted in rodents during carcinogenicity studies
c) peroxisome proliferation has not been demonstrated in
humans
It was therefore concluded that the mechanism of
carcinogenicity in rodents is not relevant to humans.
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