N-Butylbenzenesulfonamide

N-Butylbenzenesulfonamide (NBBS) is a widely used plasticizer and hence there is potential for human exposure via oral routes. This work investigates the toxicokinetic behavior of NBBS in rodents following a single gavage (20, 60, and 200 mg/kg body weight) or multi-day feed administration (500, 1000, and 2000 ppm). In male and female rats following gavage administration, maximum plasma NBBS concentration, Cmax, was reached at ≤0.539 h. Cmax increased proportionally to the dose. Area under the curve (AUC) increased more than proportionally to the dose and was 4- to 5-fold higher in females than in males. In mice, plasma Cmax was reached at ≤0.136 h and increased proportionally to the dose in female mice and more than proportionally to the dose in males. AUC increased more than proportionally to the dose with no apparent sex difference. Elimination of NBBS in plasma was faster in mice (half-life (h); mice ≤0.432, rat ≤3.55). Oral bioavailability was higher in female rats (≥60%) than males (23-52%) with apparent saturation of clearance at ~200 mg/kg body weight in females. In mice, bioavailability (5-14%) was lower with no apparent sex difference. NBBS was detected in brains of rats and mice but with low brain:plasma ratios (rats, ≤5; mice, ≤1) suggesting low potential to cross the blood brain barrier. Systemic exposure in male rats and mice following a single gavage administration was ≥48-fold higher than multi-day feed exposure. These data demonstrate potential species, sex, dose- and route-related difference in toxicokinetics of NBBS in rodents.

N-Butylbenzenesulfonamide (NBBS) is a plasticizer detected in the environment suggesting potential human exposure. These studies investigated the in vitro hepatic clearance and disposition of [14C]NBBS in rodents following a single gavage (2, 20 or 200 mg/kg) or intravenous (IV) administration (20 mg/kg). NBBS was cleared slower in hepatocytes from humans compared to rodents. [14C]NBBS was well-absorbed in male rats following gavage administration and excreted extensively in urine (70-76 %) and feces (11-15 %) 72 h following administration. Following a 20 mg/kg gavage dose in male rats, 25 % of the dose was excreted in bile by 24 h suggesting that observed fecal excretion was due to biliary excretion. The radioactivity was distributed to tissues with 14 % and 8 % of the administered dose remaining in tissues at 24 and 72 h, respectively. There was no apparent dose-dependent effect in disposition in male rats. Disposition patterns were similar in female rats (urine, 83 %; feces, 14 %) and male (urine, 69 %; feces, 11 %) and female (urine, 72 %; feces, 9 %) mice following gavage administration of 20 mg/kg. The disposition following IV administration was similar to that of gavage. Urinary radiochemical profiles were similar between doses, routes, species, and sexes. Among numerous metabolites identified, oxidative metabolites of NBBS predominated.

N-Butylbenzenesulfonamide (NBBS) is a plasticizer and emerging contaminant that has been detected in a wide array of environmental samples. There are very little toxicity data available with which to evaluate potential risk from exposure to NBBS or other structurally-related sulfonamide plasticizers. To address this knowledge gap, NBBS was selected by the National Toxicology Program for evaluation. The current short-term pre- and post-natal (perinatal) study aims to provide preliminary toxicity and gestational transfer data for NBBS. NBBS was administered via dosed feed at concentrations of 0, 625, 1250, 2500, 5000, and 10,000 ppm to time-mated Sprague Dawley (Hsd:Sprague Dawley SD®) rats from gestation day (GD) 6 through postnatal day (PND) 28. The high concentration of 10,000 ppm NBBS was overtly toxic to dams, and the group was removed on GD 17-18. Exposure to NBBS resulted in lower maternal weights during the gestational period in the 5000 and 10,000 ppm groups as compared to control weights. Dams also displayed lower weights in the lactational period, which resolved to control levels by PND 28. NBBS exposure did not affect pregnancy or littering parameters in F0 dams. However, pup survival was lower in the 5000 ppm group, and pup weights were dose-responsively lower than control pup weights with the difference expanding over the postnatal period. The lowest observed effect level (LOEL) based on significantly lower body weights was 5000 ppm NBBS for F0 dams and 2500 ppm NBBS for F1 pups. Preliminary data for NBBS levels indicated that the chemical was transferred from dams to offspring during the gestational period.