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It appears that the substantially high concentrations of the studied contaminants constitute a potential health hazard to the rural population of Burundi.

Background:Given its hormonal activity, bisphenol S (BPS) as a substitute for bisphenol A (BPA) could actually increase the risk of endocrine disruption if its toxicokinetic (TK) properties, namely its oral availability and systemic persistency, were higher than those of BPA.Objectives:The TK behavior of BPA and BPS was investigated by administering the two compounds by intravenous and oral routes in piglet, a known valid model for investigating oral TK.Methods:Experiments were conducted in piglets to evaluate the kinetics of BPA, BPS, and their glucuronoconjugated metabolites in plasma and urine after intravenous administration of BPA, BPS, and BPS glucuronide (BPSG) and gavage administration of BPA and BPS. A population semiphysiologically based TK model describing the disposition of BPA and BPS and their glucuronides was built from these data to estimate the key TK parameters that drive the internal exposure to active compounds.Results:The data indicated that almost all the BPS oral dose was absorbed and transported into the liver where only 41% of BPS was glucuronidated, leading to a systemic bioavailability of 57.4%. In contrast, only 77% of the oral dose of BPA was absorbed and underwent an extensive first-pass glucuronidation either in the gut (44%) or in the liver (53%), thus accounting for the low systemic bioavailability of BPA (0.50%). Due to the higher systemic availability of BPS, in comparison with BPA, and its lower plasma clearance (3.5 times lower), the oral BPS systemic exposure was on average about 250 times higher than for BPA for an equal oral molar dose of the two compounds.Conclusion:Given the similar digestive tracts of pigs and humans, our results suggest that replacing BPA with BPS will likely lead to increased internal exposure to an endocrine-active compound that would be of concern for human health. https://doi.org/10.1289/EHP4599

A toxicokinetic model is proposed to predict the time evolution of malathion and its metabolites, mono- and dicarboxylic acids (MCA, DCA) and phosphoric derivatives (dimethyl dithiophosphate [DMDTP], dimethyl thiophosphate [DMTP], and dimethyl phosphate [DMP]) in the human body and excreta, under a variety of exposure routes and scenarios. The biological determinants of the kinetics were established from published data on the in vivo time profiles of malathion and its metabolites in the blood and urine of human volunteers exposed by intravenous, oral, or dermal routes. In the model, body and excreta compartments were used to represent the time varying amounts of each of the following: malathion, MCA, DCA, DMDTP, DMTP, and DMP. The dynamic of intercompartment exchanges was described mathematically by a differential equation system that ensured conservation of mass at all times. The model parameters were determined by statistically adjusting the explicit solution of the differential equations to the experimental human data. Simulations provide a close approximation to kinetic data available in the published literature. When simulating a dermal exposure to malathion, the main route of entry for workers, the model predicts that it takes an average of 11.8 h to recover half of the absorbed dose of malathion eventually excreted in urine as metabolites, compared to 3.2 h following an intravenous injection and 4.0 h after oral administration. This shows that following a dermal exposure, the absorption rate governs the urinary excretion rate of malathion metabolites because the dermal absorption rate is much slower than biotransformation and renal clearance processes. The model served to establish biological reference values for malathion metabolites in urine since it allows links to be made between the absorbed dose of malathion and the time course of cumulative amounts of metabolites excreted in urine. From the no-observed-effect level (NOEL) of 0.61 micromol/kg/day derived from the data of Moeller and Rider (1962), the model predicts corresponding biological reference values for MCA, DCA, and phosphoric derivatives of 44, 13, and 62 nmol/kg, respectively, in 24-h urine samples. The latter were used to assess the health risk of workers exposed to malathion in botanical greenhouses, starting from urinary measurements of MCA and DCA metabolites.

The toxicokinetics of benzo(a)pyrene (BaP) and 3-hydroxybenzo(a)pyrene (3-OHBaP) were assessed in 36 male Sprague-Dawley rats injected intravenously with 40 micromol kg(1) of BaP to explain the reported atypical urinary excretion profile of 3-OHBaP. Blood, liver, kidney, lung, adipose tissue, skin, urine and feces were collected at t = 2, 4, 8, 16, 24, 33, 48, 72 h post-dosing. BaP and 3-OHBaP were measured by high-performance liquid chromatography/fluorescence. A biexponential elimination of BaP was observed in blood, liver, skin and kidney (t((1/2)) of 4.2-6.1 h and 12.3-14.9 h for initial and terminal phases, respectively), while a monoexponential elimination was found in adipose tissue and lung (t((1/2)) of 31.2 and 31.5 h, respectively). A biexponential elimination of 3-OHBaP was apparent in blood, liver and skin (t((1/2)) of 7.3-11.7 h and 15.6-17.8 h for initial and terminal phases, respectively), contrary to adipose tissue, lung and kidney. In adipose tissue and lung, a monophasic elimination of 3-OHBaP was observed (t((1/2)) of 27.0 h and 24.1 h, respectively). In kidney, 3-OHBaP kinetics showed a distinct pattern with an initial buildup during the first 8 h post-dosing followed by a gradual elimination (t((1/2)) of 15.6 h). In the 72-h post-treatment, 0.21 +/- 0.09% (mean +/- SD) of dose was excreted as 3-OHBaP in urine and 12.9 +/- 1.0% in feces while total BaP in feces represented 0.40 +/- 0.16% of dose. This study allowed the identification of the kidney as a retention compartment governing 3-OHBaP atypical urinary excretion.

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