Single-dose toxicokinetics of aluminum in the rat

The toxicokinetics of aluminum (Al) in male Wistar rats was studied after single intragastric (IG) doses of 1000 and 12000 g Al/kg and intravenous (IV) doses of 10, 100, 1000, and 12000 g Al/kg. Serial blood samples, daily samples of urine and feces as well as brain, liver, kidney, spleen, quadriceps muscle, and femur samples were collected. Al was measured by atomic absorption spectrometry. Al blood profiles after IV doses were adequately described by a two-compartment open model. Al toxicokinetics was dose dependent and appeared to plateau at 12000 g/kg. At IV doses between 10 and 1000 g/kg the terminal half-life of elimination from whole blood (t_1/2) increased from 29.9±7.8 to 209.3±32.6 min, and the total body clearance (CL) decreased from 2.45±0.64 to 0.28±0.03 ml min^–1 kg^–1. Following an IV bolus of 10 and 100 g/kg the administered Al was recovered completely from urine (94.4%±9.9% and 98.5%±3.2%). Twenty-nine days after the IV dose of 1000 g/kg daily renal excretion decreased to baseline values while only 55.1%±8.0% of the dose was excreted. Nineteen days after the single IV dose of 1000 g/kg Al accumulated in liver (28.1±7.7 versus 1.7±0.5 g/g of control rats) and spleen (72.5±21.1 versus <0.4 g/g). After the single 1000 g/kg IG dose no absorption of Al was detectable. The IG dose of 12000 g/kg resulted in a maximum blood Al level of 47.9±12.4 g/l after 50 min. The blood concentration time curve fitted a one-compartment open model with a half-life of absorption of 28.2±3.6 min and a t_1/2 of 81.2±20.2 min. Cumulative renal Al excretion was 0.18%±0.10% of the dose and oral bioavailability was 0.02%. Seventeen days after the 12000 g/kg IG dose the Al content in femur samples was increased (2.7±1.3 versus 0.6±0.4 g/g). In no case was fecal elimination of incorporated Al observed.     

Embryo–fetal exposure and developmental outcome of thalidomide following oral and intravaginal administration to pregnant rabbits

Studies in pregnant rabbits were conducted to evaluate if there are any differences in the uptake of thalidomide into the intrauterine compartment and developmental toxicity risk following oral and intravaginal administration. Thalidomide concentrations in maternal plasma, yolk sac cavity (YSC) fluid and embryo following intravaginal administration were 2- to 7-fold lower than their respective levels after oral administration. Ratios of thalidomide concentration in YSC fluid to maternal plasma were similar between these two routes, indicating no difference in uptake into the intrauterine compartment. A rabbit embryo–fetal development study using oral and intravaginal thalidomide administration at 2 mg/kg/day (a dose >10,000-fold higher than the expected amount of thalidomide in human semen) did not result in any developmental abnormalities. These data demonstrated no preferential transfer mechanism of thalidomide from vagina to conceptus, and no additional embryo–fetal developmental toxicity risks with thalidomide exposure via the vaginal route.     

Interpreting in vitro developmental toxicity test battery results: The consideration of toxicokinetics

In the EU collaborative project ChemScreen an alternative, in vitro assay-based test strategy was developed to screen compounds for reproductive toxicity. A toxicokinetic modeling approach was used to allow quantitative comparison between effective concentrations in the in vitro test battery and observations of developmental toxicity in vivo. This modeling strategy is based on (1) the definition of relevant observations of toxicity in vivo, (2) simulation of the corresponding systemic concentrations in vivo by toxicokinetic modeling, and (3) correction for differences in protein binding and lipid partitioning between plasma and in vitro test media. The test results of a feasibility study with a number of known reproductive toxicants has been described previously (Piersma et al. [15]). In the present paper, we take a more detailed look at the toxicokinetics of these compounds, and add the analysis of some compounds from subsequent studies. We discuss how the consideration of toxicokinetics allowed comparison between test systems with differing test medium composition, has helped to interpret the in vitro findings in light of in vivo observations, and to gain confidence in the predictive value of the test battery outcomes. The same toxicokinetic modeling strategy, in reverse order, can now be used for risk assessment purposes to predict toxic doses in vivo from effective concentrations in vitro.     

Biomarkers for monitoring transfluthrin exposure: Urinary excretion kinetics of transfluthrin metabolites in rats

The urinary excretion kinetics of a fluorine-containing pyrethroid transfluthrin [(2,3,5,6-tetrafluorophenyl)methyl 3-(2,2-dichloroethenyl)-2,2-dimethylcyclopropane-1-carboxylate], which is widely used recently as mosquito repellents, was examined in rats to search for urinary metabolites suitable as biomarkers for monitoring transfluthrin exposure of the general population. After a single dose of 26, 64, 160 or 400 mg/kg body weight of transfluthrin had been administered intraperitoneally to male Sprague-Dawley rats, their urine was collected periodically for one week. Three major urinary transfluthrin metabolites were measured: 2,3,5,6-tetrafluorobenzyl alcohol, 2,3,5,6-tetrafluorobenzoic acid and 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid. The kinetics was evaluated by moment analysis of the urinary excretion rate of the metabolites versus time curves.The urinary excretion amounts of these three metabolites were estimated to be proportional to the absorption amounts of transfluthrin over a wide exposure range. Urinary 2,3,5,6-tetrafluorobenzoic acid was considered to be an optimal biomarker for monitoring transfluthrin exposure.     

Sex differences in the toxicokinetics of inhaled solvent vapors in humans 2. 2-propanol

The aim of this study was to evaluate possible sex differences in the inhalation toxicokinetics of 2-propanol vapor. Nine women and eight men were exposed on different occasions for 2 h during light physical exercise (50 W) to 2-propanol (350 mg/m3) and to clean air (control exposure). The level corresponds to the Swedish occupational exposure limit. 2-Propanol and its metabolite acetone were monitored up to 24 h after exposure in exhaled air, blood, saliva, and urine by headspace gas chromatography. Body fat and lean body mass were estimated from sex-specific equations using bioelectrical impedance, body weight, height, and age. Genotypes were determined by PCR-based assays for alcohol dehydrogenase and cytochrome P450 2E1 (CYP2E1). The CYP2E1 phenotype was assessed by the 2-h plasma 6-hydroxychlorzoxazone/chlorzoxazone metabolic ratio in vivo. The toxicokinetic profile in blood was analyzed using a one-compartment population model. The following sex differences were significant at the p = 0.05 level (Student's t test). The respiratory uptake was lower and the volume of distribution smaller in females. The women had a slightly shorter half-time of 2-propanol in blood and a higher apparent total clearance when corrected for body composition. However, women reached approximately four times higher 2-propanol levels in exhaled air at 10-min postexposure and onward. Acetone in blood was markedly higher in females than in males in the control experiment and slightly higher following exposure to 2-propanol. A marked sex difference was that of a 10-fold higher in vivo blood:breath ratio in men, suggesting sex differences in the lung metabolism of 2-propanol. The most marked sex difference was that of salivary acetone, for which an approximately 100-fold increase was seen in women, but no increase in men, after exposure to 2-propanol compared to clean air. The toxicokinetic analysis revealed no significant differences in toxicokinetics between subjects of different metabolic genotypes or phenotypes. In conclusion, the study indicates several sex differences in the inhalation toxicokinetics of 2-propanol. Most of these differences are consistent with anatomical differences between women and men. However, body build can not explain the sex differences in 2-propanol levels in expired air and acetone in saliva.     

Tissue distribution of 20 nm, 100 nm and 1000 nm fluorescent polystyrene latex nanospheres following acute systemic or acute and repeat airway exposure in the rat

Understanding tissue distribution and clearance of nanomaterials following different routes of exposure is needed for risk assessment. F344 female rats received single or multiple exposures to 20 nm, 100 nm or 1000 nm latex fluorospheres by intravenous (i.v.) injection or oral pharyngeal aspiration into the airways. The presence of fluorospheres in tissues was assessed up to 90–120 days after the final dose. Blood, perfusion fluid, bone marrow, brain, eyes, feces, gut, heart, kidney, liver, lung, muscle, skin, spleen, thymus, tongue, urine and uterus plus ovaries were collected for analysis. Liver, spleen and lung were the greatest tissue depots for all particles following i.v. injection. The proportion of 100 nm and 1000 nm but not 20 nm spheres significantly increased in the spleen over time. Lung was the greatest tissue depot for all particles following single or repeat airway exposure. Greater than 95% of 1000 nm spheres that were recovered were in the lung in contrast to 70–80% of 20 nm spheres or 89–95% of 100 nm spheres. All 3 sizes were found in gut or gut + feces 1–7 days after lung exposure. The thymus was the largest extra-pulmonary depot for the particles; up to 25% of recovered 20 nm particles were in the thymus up to 4 months after exposure compared to 6% of 100 nm particles and 1–3% of 1000 nm particles. A small proportion of 20 nm particles were detected in kidney following both acute and repeat airway exposure. Low numbers of particles were found in the circulation (blood, perfusion), bone marrow, brain, heart, liver and spleen but not in eye, muscle, skin, tongue, ovaries, uterus or urine. These data show that the tissue targets of nano- and micron-sized spheres are very similar whether exposure occurs systemically or via the airways while the proportion of particles in some tissues and tissue clearance varies based on particle size.     

Toxicity and toxicokinetics of metformin in rats

Metformin is a first-line drug for the treatment of type 2 diabetes (T2D) and is often prescribed in combination with other drugs to control a patient's blood glucose level and achieve their HbA1c goal. New treatment options for T2D will likely include fixed dose combinations with metformin, which may require preclinical combination toxicology studies. To date, there are few published reports evaluating the toxicity of metformin alone to aid in the design of these studies. Therefore, to understand the toxicity of metformin alone, Crl:CD(SD) rats were administered metformin at 0, 200, 600, 900 or 1200 mg/kg/day by oral gavage for 13 weeks. Administration of ≥ 900 mg/kg/day resulted in moribundity/mortality and clinical signs of toxicity. Other adverse findings included increased incidence of minimal necrosis with minimal to slight inflammation of the parotid salivary gland for males given 1200 mg/kg/day, body weight loss and clinical signs in rats given ≥ 600 mg/kg/day. Metformin was also associated with evidence of minimal metabolic acidosis (increased serum lactate and beta-hydroxybutyric acid and decreased serum bicarbonate and urine pH) at doses ≥ 600 mg/kg/day. There were no significant sex differences in mean AUC_0-24 or C_max nor were there significant differences in mean AUC_0-24 or C_max following repeated dosing compared to a single dose. The no observable adverse effect level (NOAEL) was 200 mg/kg/day (mean AUC_0-24 = 41.1 μg h/mL; mean C_max = 10.3 μg/mL based on gender average week 13 values). These effects should be taken into consideration when assessing potential toxicities of metformin in fixed dose combinations.     

Biomonitoring equivalents for DDT/DDE

Biomonitoring Equivalents (BEs) are defined as the concentration or range of concentrations of a chemical or its metabolite in a biological medium (blood, urine, or other medium) that is consistent with an existing health-based exposure guideline such as a reference dose (RfD) or tolerable daily intake (TDI). BE values can be used as a screening tool for the evaluation of population-based biomonitoring data in the context of existing risk assessments. This study reviews available health based risk assessments and exposure guidance values for DDT (1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane, CAS #50-29-3) and related metabolites and degradation products DDE (1,1-dichloro-2,2-bis(p-chlorophenyl)ethane, CAS #72-55-90) and DDD (1,1-dichloro-2,2-bis(p-chloro-phenyl)ethane) based on both non-cancer and cancer risk assessments from the Food and Agriculture Organization/World Health Organization (FAO/WHO), the United States Environmental Protection Agency (US EPA), and other organizations. Laboratory data on distribution and toxicokinetics of DDT and metabolites and estimates of human elimination half-lives were used to estimate BE values (lipid-adjusted blood, serum, or plasma concentrations) corresponding to the various non-cancer exposure guidance values and cancer risk-specific doses. The BE values based on non-cancer risk assessments range from 5000 to 40,000ng/g lipid for the sum of DDT, DDE, and DDD. The BE values corresponding to a 1E-05 cancer risk level for DDT and DDE based on the US EPA assessment are 300 and 500ng/g lipid, respectively. Sources of uncertainty relating to both the basis for the BE values and their use in evaluation of biomonitoring data are discussed. The BE values derived here can be used as a screening tools for evaluation of population biomonitoring data for DDT and related compounds in the context of the existing risk assessment and can assist in prioritization of the potential need for additional risk assessment efforts for DDT relative to other chemicals.     

Toxicokinetic modeling of captan fungicide and its tetrahydrophthalimide biomarker of exposure in humans

Measurement of tetrahydrophthalimide (THPI) in urine has been used for the biomonitoring of exposure to the widely used captan fungicide in workers. To allow a better understanding of the toxicokinetics of captan and its key biomarker of exposure, a human multi-compartment model was built to simulate the transformation of captan into THPI and its subsequent excretion while accounting for other non-monitored metabolites. The mathematical parameters of the model were determined from best-fits to the time courses of THPI in blood and urine of five volunteers administered orally 1mg/kg and dermally 10mg/kg of captan. In the case of oral administration, the mean elimination half-life of THPI from the body (either through faeces, urine or metabolism) was found to be 13.43 h. In the case of dermal application, mean THPI elimination half-life was estimated to be 21.27 h and was governed by the dermal absorption rate. The average final fractions of administered dose recovered in urine as THPI were 3.6% and 0.02%, for oral and dermal administration, respectively. Furthermore, according to the model, after oral exposure, only 8.6% of the THPI formed in the GI reaches the bloodstream. As for the dermal absorption fraction of captan, it was estimated to be 0.09%. Finally, the average blood clearance rate of THPI calculated from the oral and dermal data was 0.18 ± 0.03 ml/h and 0.24 ± 0.6 ml/h while the predicted volume of distribution was 3.5 ± 0.6l and 7.5 ± 1.9l, respectively. Our mathematical model is in complete accordance with both independent measurements of THPI levels in blood (R(2)=0.996 for oral and R(2)=0.908 for dermal) and urine (R(2)=0.979 for oral and R(2)=0.982 for dermal) as well as previous experimental data published in the literature.     

N-Acetyl-S-(1-carbamoyl-2-hydroxy-ethyl)-L-cysteine (iso-GAMA) a further product of human metabolism of acrylamide: comparison with the simultaneously excreted other mercaptuic acids

The N-acetyl-S-(1-carbamoyl-2-hydroxy-ethyl)-l-cysteine (iso-GAMA) could be identified as a further human metabolite of acrylamide. In this study, we report the excretion of d₃-iso-GAMA in human urine after single oral administration of deuterium labelled acrylamide (d₃-AA). One healthy male volunteer ingested a dose of about 1 mg d₃-AA which is equivalent to a dose of 13 μg/kg bodyweight. Over a period of 46 h the urine was collected and the d₃-iso-GAMA levels analysed by LC-ESI-MS/MS. The excretion of iso-GAMA begins five hours after application. It rises to a maximum concentration (c _max) of 43 μg/l which was quantified in the urine excreted after 22 h (t _max). The excretion pattern is parallel to that of the major oxidative metabolite N-acetyl-S-(2-carbamoyl-2-hydroxy-ethyl)-l-cysteine (GAMA). Total recovery of iso-GAMA was about 1% of the applied dose. Together with N-acetyl-S-(2-carbamoylethyl)-l-cysteine (AAMA) and GAMA, 57% of the applied dose is eliminated as mercapturic acids. The elimination kinetics of the three mercapturic acids of AA are compared. We show that dietary doses of acrylamide (AA) cause an overload of detoxification via AAMA and lead to the formation of carcinogenic glycidamide (GA) in the human body.