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Registration Dossier
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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

Immunotoxicity
Administrative data
- Endpoint:
- immunotoxicity: short-term oral
- 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:
- Gestational exposure to perfluorooctane sulfonate suppresses immune function in B6C3F1 mice
- Author:
- Keil DE, Mehlmann T, Butterworth L, Peden-Adams MM
- Year:
- 2 008
- Bibliographic source:
- Toxicol Sci 103, 77-85
Materials and methods
- Principles of method if other than guideline:
- Using the pairing of female C57BL/6N mice with male C3H/HeJ, developmental immunotoxicity was evaluated in B6C3F1 pups following oral maternal exposure to PFOS on gestations days (GD) 1-17. Exposure levels included 0.1, 1 and 5 mg/kg/day PFOS. Natural killer (NK) cell activity, SRBC IgM plaque assay, CD4/8 lymphocytic subpopulations, nitrite production in peritoneal macrophages, and body/organ weights were evaluated at 4 and 8 weeks of age in F1 pups.
- GLP compliance:
- not specified
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:
- Perfluorooctane sulfonate (PFOS, potassium salt; 91% pure) was obtained from Fluka Chemical (Sigma-Aldrich, Switzerland).
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: 0.5% Tween 20
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Dams were dosed until day 17 of gestation
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0.1, 1 or 5 mg/kg/day
Basis:
nominal conc.
- No. of animals per sex per dose:
- There were 10-12 plug positive females assigned to each treatment group; only litters with 6-9 pups were maintained and were kept with their birth mother following the first 3 weeks of birth. For the immunotoxicity studies, groups were compromised of one female or male from each litter.
- Control animals:
- not specified
Results and discussion
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 0.1 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: pubs
- Dose descriptor:
- LOAEL
- Effect level:
- 1 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: pubs
Any other information on results incl. tables
Body and Organ Mass and Immune Organ Cellularity
Body mass of male and female pups exposed to PFOS in utero was not significantly different from controls at either 4 or 8 weeks of age. Furthermore, pregnant dams did not experience any significant weight loss due to PFOS exposure (data not shown). In female pups at 4 weeks of age, liver mass was significantly decreased at the 0.1 mg/kg/day treatment and kidney mass was increased at the 5 mg/kg/day treatment, while spleen and thymus mass were not altered. In 4-week male pups spleen, thymus and kidney mass were not altered, but liver mass was significantly increased compared to control at the 5 mg/kg/day treatment level. In 8-week pups no alterations compared to control were noted in spleen, thymus, kidney, or liver mass regardless of gender. Additionally, splenic and
thymic cellularities were not altered compared to control at either 4 or 8 weeks of age in either gender.
NK-Cell Function and Plaque-Forming Cell (PFC) Assessments
NK-cell activity was assessed at both 4 and 8 weeks of age. There was no statistical interaction related to gender in the 4-week old pups; therefore, genders were combined for analysis. NK-cell activity was not altered compared to control in the 4-week old pups. At 8 weeks of age, however, differences in gender by treatment were noted and data were separated by gender for analysis. NK-cell activity was suppressed in 8-week old male offspring at the 1 and 5 mg/kg/day treatments (42.5% and 32.1% decrease, respectively) and was suppressed in female offspring at the 5 mg/kg/day treatment (35.1% decrease). The PFC response for SRBC-specific IgM production by B-cells was only assessed in the F1 adults (8 weeks of age). Differences in response by gender were observed, therefore, these data are presented with gender separated. In males, this response was significantly suppressed 53% in the 5 mg/kg/day exposure group, but it was not altered in the females.
Lymphocyte Immunophenotypes
Splenic or thymic lymphocyte subpopulations (B220+, CD3+, CD4+, CD8+, CD4-CD8- [DN], CD4+CD8+ [DP]) were assessed in pups at 4 and 8 weeks of age. Due to statistical interactions, genders were analyzed separately. Absolute numbers of splenic B220+ cells were significantly decreased by 21% in 4-week old female pups exposed to 5.0 mg/kg/day in utero while male pups remain unaffected (Table 3). By the adult age of 8 weeks, however, no significant changes in B220 labeled splenocytes were detected in either female or males for any of the treatments (data not shown). Absolute numbers of splenic or thymic CD8+, DP, and DN cells were not significantly altered at either age or gender (Table 3 and 4). In 4-week old pups, CD3+ or CD4+ cells were not significantly affected in either males or females. In 8- week old pups, the only significant differences detected were in male mice with a 25% decrease in CD3+ and 28% decrease in CD4+ thymocytes at the highest treatment level (Table 4). The thymocyte CD4:8 ratio was reduced from 4.2 in controls to 3.5 in the 5.0 mg/kg/day maternal dose group.
Nitrite Production by Peritoneal Macrophages
Peritoneal macrophage nitric oxide was assessed in F1 mice at 8 weeks of age only. It was not statistically altered in male or female offspring exposed to 5 mg/kg/day in utero. Furthermore, no difference in peritoneal cellularity was noted.
Applicant's summary and conclusion
- Executive summary:
Using the pairing of female C57BL/6N mice with male C3H/HeJ, developmental immunotoxicity was evaluated in B6C3F1 pups following oral maternal exposure to PFOS on gestations days (GD) 1-17. Exposure levels included 0.1, 1 and 5 mg/kg/day PFOS. Natural killer (NK) cell activity, SRBC IgM plaque assay, CD4/8 lymphocytic subpopulations, nitrite production in peritoneal macrophages, and body/organ weights were evaluated at 4 and 8 weeks of age in F1 pups. No significant dose-responsive changes in maternal or pup body weights, flow cytometry, or macrophage function were observed, yet hepatomegaly was indicated in F1 male pups at 4 weeks of age. Functional deficits were not evident until 8 weeks of age when NK cell function and IgM production were significantly decreased. When compared to females, male pups were more sensitive to the effects of PFOS thereby establishing a no observed adverse effect level (NOAEL) and low observed adverse effect level (LOAEL) of 0.1 and 1.0 mg/kg/day (males only) following maternal PFOS exposure level, respectively. This study establishes that the developing immune system is sensitive to the effects of PFOS and results in functional deficits in innate and humoral immunity detectable at adulthood.
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