Perfluorooctanesulfonate (PFOS) is one of a class of industrial chemicals known as perfluoroalkyl acids, which have a wide variety of uses as surfactants and stain repellants. The presence of fluorochemical residues in human blood, plasma, or serum from sample populations worldwide is indicative of widespread human exposure. Previous studies demonstrated that PFOS alters fatty acid metabolism in the liver of rodents and that this leads to peroxisome proliferation. This study was undertaken to (1) confirm the effects of PFOS on rat liver, (2) identify additional target organs and systems, and (3) further explore the biochemical and molecular changes associated with PFOS exposure. The results confirmed that liver was a primary target for PFOS. Hepatomegaly, decreased serum triglycerides and cholesterol, and increased expression of the genes for acyl-coenzymeA oxidase 1 (ACOX1) and cytochrome P-450 4A22 (CYP4A22) were indicative of exposure to a peroxisome proliferator. Changes in liver fatty acid profiles included increased total monounsaturated fatty acid levels and decreased total polyunsaturated fatty acids, as well as an increase in linoleic acid levels and a decrease in longer chain fatty acids. These changes were similar to those induced by relatively weak peroxisome proliferators. Disruptions in hepatic fatty acid metabolism may contribute to changes in red blood cell membranes, resulting in increased lysis and cell fragility. Serum thyroid hormone levels were decreased in PFOS-treated rats, while the kidney and cardiovascular systems were not significant targets. Residue analyses indicated that PFOS accumulation in tissues was dose dependent, appearing preferentially in the liver at lower doses but increasing in serum and other organs relative to liver at higher doses.

Perfluorooctanesulfonate (PFOS) is a stable and environmentally persistent metabolic or degradation product of perfluorooctanyl compounds that were manufactured for a variety of industrial and consumer applications. PFOS itself was sold for use as a surfactant. The structurally related contaminants perfluorooctanoic acid (PFOA), perfluorodecanoic acid (PFDA), and N-ethyl perfluorooctane sulfonamide (N-EtPFOSA) were shown to suppress immune responses in laboratory rodents. Relatively low doses of PFOS were found to be immunosuppressive in mice. To assess effects of PFOS on the rat immune system at doses known to alter hepatic function, changes in the morphology and function of immune tissues and cells were measured in adult rats exposed to PFOS in their diet for 28 d at levels ranging from 2 to 100 mg PFOS/kg diet (corresponding to approximately 0.14 to 7.58 mg/kg body weight [bw]/d) and compared to those receiving control diet. Body weight reductions were significant in male and female rats exposed to 50 and 100 mg PFOS/kg diet. Liver/body weight was significantly increased in females exposed to 2 mg PFOS/kg diet and in males exposed to 20 mg PFOS/kg diet. Female rats exposed to 100 mg PFOS/kg diet exhibited a significant increase in spleen weight relative to body weight; these changes lacked a histologic correlate and were not observed in males. While thymus weights relative to body weights were not affected, numbers of apoptotic lymphocytes rose in thymus with increasing dietary PFOS. There was a significant dose-related increase in total peripheral blood lymphocyte numbers in female but not male rats. In both genders the percentages of cells within lymphocyte subclasses were altered. There was a significant trend toward increasing T and T-helper (Th) cells and decreasing B cells with higher PFOS dose. Serum total immunoglobulin (Ig) G1 levels were significantly reduced in males exposed to 2 and 20 mg PFOS/kg diet. The ability of male and female rats to mount delayed-type hypersensitivity (DTH) responses to the T-cell-dependent antigen keyhole limpet hemocyanin (KLH) was not altered by PFOS. There was a significant trend toward elevated KLH-specific IgG in serum from male rats exposed to increasing levels of PFOS in diet. Splenic T- and B-cell proliferation in response to ex vivo mitogen exposure was unaffected by exposure to dietary PFOS. In conclusion, changes in immune parameters in rat did not manifest as functional alterations in response to immune challenge with KLH and may be secondary to hepatic-mediated effects of PFOS in this model.

Isomers and metabolites of the organochlorine pesticide chlordane persist in the environment and bioaccumulate in Arctic marine food webs. Rodent studies indicate that there are gender-related differences in trans-nonachlor and oxychlordane metabolism. Thus, comparative tissue depletion studies were undertaken in male and female rats exposed to trans-nonachlor, oxychlordane, or trans-chlordane at 2.5 mg/kg body weight/d by gavage for 28 d followed by two consecutive 28-d depletion periods. None of the test chemicals were overtly toxic at this dose, although increased liver weights in some groups were consistent with microsomal enzyme induction. The metabolite oxychlordane accumulated in tissues from rats exposed to trans-nonachlor and trans-chlordane. Trans-Nonachlor and oxychlordane residue levels were highest in tissues from female rats at each time point; however, trans-chlordane was completely eliminated from males and females by the end of the study. Body burden calculations showed no significant clearance of oxychlordane in females over 56 d postdosing, whereas males lost approximately half their oxychlordane body burden in the same period. For the chiral contaminants oxychlordane and trans-chlordane, tissues from male and female rats were selectively depleted of the (+)-enantiomer; however, there were gender-related differences in enantiomer depletion patterns over time. In general, residue analyses confirmed that gender-related metabolic differences and contaminant structural properties, including chirality, influenced chlordane contaminant elimination from rat tissues. The study points to a need for similar knowledge of gender-related responses in humans in order to provide relevant dietary recommendations for populations exposed to chlordane-related contaminants in foods.

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