Abstract

As an alternative to perfluorooctanesulfonate (PFOS), novel fluorotelomer surfactants (6:2 fluorotelomer sulfonamide alkylbetaine (6:2 FTAB) and 6:2 fluorotelomer sulfonamide alkylamine (6:2 FTAA)) are widely used in aqueous film-forming foams and are frequently found to coexist in the environment. However, their potential toxicities remain unknown. Here, we investigated the chronic toxicity of 6:2 FTAB (65%) and 6:2 FTAA (35%) coexposure on adult zebrafish at doses of 0, 5, 50, or 500 μg/L using a flow-through exposure system for 180 days. Results showed that 6:2 FTAB was undetected in adult tissue and their offspring, while 6:2 FTAA was highly dominant, accounting for ∼92% of total quantified poly/perfluoroalkyl substances (PFASs), and their metabolic products (6:2 fluorotelomer sulfonamide and 6:2 fluorotelomer sulfonate) further accounting for 2.8%-8.5%. 6:2 FTAA accumulation exhibited a sex-bias, with higher levels found in male livers than that in female, but in gonad showed an opposite pattern. Co-exposure to 6:2 FTAB and 6:2 FTAA mixture (50 and 500 μg/L) could decrease the average number of eggs production and increase the malformation and mortality in their offspring. Testosterone (T) and 17 β-estradiol (E2) levels increased in the 50 and 500 μg/L exposed females, but T level decreased in the 500 μg/L exposed males. Correspondingly, the transcriptional pattern of hypothalamus-pituitary-gonad axis genes was different between male and female. Increased liver vitellogenin levels in the 50 and 500 μg/L-exposed males indicated that these compounds might possess estrogen-like activity. Furthermore, 3,5,3'-triiodothyronine (T3) and thyroxine (T4) levels decreased in the 50 and 500 μg/L females and increased T4 level in 500 μg/L exposed males. These results suggest that 6:2 FTAB is extensively metabolized in fish, whereas 6:2 FTAB and 6:2 FTAA coexposure disrupted the adult endocrine system and impaired offspring development.

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