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Diss Factsheets
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EC number: 260-375-3 | CAS number: 56773-42-3
- 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
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: well documented and scientifically acceptable
Data source
Reference
- Reference Type:
- publication
- Title:
- Gene expression profiling in the liver and lung of perfluorooctane sulfonate-exposed mouse fetuses: Comparison to changes induced by exposure to perfluorooctanoic acid
- Author:
- Rosen MB, Schmid JE, Das KP, Wood CR, Zehr RD, Lau C
- Year:
- 2 009
- Bibliographic source:
- Reprod toxicol 27, 278-288
Materials and methods
- Type of study / information:
- Gene expression in the liver and lung of perfluorooctane sulfonate-exposed mouse fetuses
- Principles of method if other than guideline:
- Pregnant CD-1 micewere dosed with 0, 5, or 10 mg/kg PFOS fromgestation days 1–17. Transcript profiling was conducted on the fetal liver and lung.
- GLP compliance:
- no
Test material
- Reference substance name:
- Potassium heptadecafluorooctane-1-sulphonate
- EC Number:
- 220-527-1
- EC Name:
- Potassium heptadecafluorooctane-1-sulphonate
- Cas Number:
- 2795-39-3
- IUPAC Name:
- potassium 1,1,2,2,3,3,4,4,5,5,6,6,7,7,8,8,8-heptadecafluorooctane-1-sulfonate
- Details on test material:
- PFOS (potassium salt, Sigma Aldrich, St. Louis, MO)
Constituent 1
Results and discussion
Any other information on results incl. tables
Exposure to PFOS had no observable effect on the body weight or general appearance of the dams utilized in the study, nor was
litter size affected by PFOS treatment (data not shown). Hematoxylin and eosin stained sections from representative treated
and control fetal tissues are shown in Fig. 1. Eosoinphilic granulescharacteristic of peroxisome proliferation were observed in liver sections from both PFOS dose groups, although such changes were not uniformly distributed across all sections as previously
observed in the PFOA-exposed fetal liver. No apparent treatment effectswere observed in the fetal lung by conventional bright
field microscopy.
PFOS up-regulated a number of putative markers of PPAR-alpha activity in the fetal liver, whereas, regulation of a more limited group of genes such as Cyp4a14, enoyl-Coenzyme A hydratase (Ehhadh), and fatty acid binding protein 1 (Fabp1) was observed in the fetal lung. Canonical pathways or functional groups significantly enriched by PFOS included fatty acid metabolism in the fetal liver and lung along with xenobiotic metabolism, peroxisome biogenesis, cholesterol biosynthesis, bile acid biosynthesis, and metabolism of glucose and glycogen.
In summary, most of the transcriptional changes induced by PFOS in the fetal mouse liver and lung were related to activation
of PPAR-alpha. When compared to the transcript profiles induced by PFOA, few remarkable differences were found other than upregulation of Cyp3a genes. These data suggest that changes related to PFOS-induced neonatal toxicity may not be evident in the
fetal transcriptome at term. Therefore, the mode of action of PFOS-induced neonatal toxicity remains uncertain, although by default these data lend support to the hypothesis that variables related to the physical properties of the chemical, such as altered fluid dynamics of pulmonary surfactant, may be associated with a PPAR-alpha-independent mode of action in PFOS-exposed rodent
neonates.
Applicant's summary and conclusion
- Executive summary:
Pregnant CD-1 micewere dosed with 0, 5, or 10 mg/kg PFOS fromgestation days 1–17. Transcript profiling was conducted on the fetal liver and lung.
PFOS-dependent changes were primarily related to activation of PPAR-alpha. No remarkable differences were found between PFOS and PFOA. Given that PPAR-alpha signaling is required for neonatal mortality in PFOA-treated mice but not those exposed to PFOS, the neonatal mortality observed for PFOS may reflect functional deficits related to the physical properties of the chemical rather than to transcript alterations.
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