David L. Rick

Chlorpyrifos: Pharmacokinetics in human volunteers

The kinetics of chlorpyrifos, an organophosphorothioate insecticide, and its principal metabolite, 3,5,6-trichloro-2-pyridinol (3,5,6-TCP), were investigated in six healthy male volunteers given a single 0.5 mg/kg po and, 2 or more weeks later, a 0.5 or 5.0 mg/kg dermal dose of chlorpyrifos. No signs or symptoms of toxicity or changes in erythrocyte cholinesterase were observed. Plasma cholinesterase was depressed to 15% of predose levels by the 0.5 mg/kg po dose but was essentially unchanged following the 5.0 mg/kg dermal dose. Blood chlorpyrifos concentrations were extremely low (less than 30 ng/ml), and no unchanged chlorpyrifos was found in the urine following either route of administration. Mean blood 3,5,6-TCP concentrations peaked at 0.93 micrograms/ml 6 hr after ingestion of the oral dose and at 0.063 micrograms/ml 24 hr after the 5.0 mg/kg dermal dose. 3,5,6-TCP was cleared from the blood and eliminated in the urine with a half-life of 27 hr following both the po and dermal doses. An average of 70% of the po dose but less than 3% of the dermal dose was excreted in the urine as 3,5,6-TCP; thus only a small fraction of the dermally applied chlorpyrifos was absorbed. Chlorpyrifos and its principal metabolite were rapidly eliminated and therefore have a low potential to accumulate in man on repeated exposures. Based on these data, blood and/or urinary 3,5,6-TCP concentrations could be used to quantify the amount of chlorpyrifos absorbed under actual use conditions.

Kinetics and Metabolism of Inhaled Methyl Chloroform (1,1,1-Trichloroethane) in Male Volunteers

The kinetics of inhaled methyl chloroform (MC) and its principal metabolites, trichloroethanol (TCE) and trichloroacetic acid (TCA), were defined in six healthy male volunteers following single 6-hr exposures of 350 and 35 ppm. Blood and expired air MC concentrations were proportional to the exposure concentration and indicated that about 25% of the MC inhaled during the 6-hr exposure was absorbed. Elimination of MC was triexponential with half-lives estimated as 44 min, 5.7 hr, and 53 hr for the initial, intermediate, and terminal phases. Over 91% of the absorbed MC was excreted unchanged via the lungs, 5-6% was metabolized and excreted as TCE and TCA, and less than 1% remained in the body after 9 days. Urinary TCE and TCA excretion was extremely variable and indicated that urinary TCE and TCA measurements provide at best only a rough estimate of the exposure. These data suggest that the kinetics of MC in man are essentially first order at or below the current TLV of 350 ppm. Based on a comparison of the blood MC levels and amounts of MC metabolized, the rat is a better model than the mouse to predict the toxicity of MC in man.

Assessment of diurnal systemic dose of agrochemicals in regulatory toxicity testing--an integrated approach without additional animal use.

Integrated toxicokinetics (TK) data provide information on the rate, extent and duration of systemic exposure across doses, species, strains, gender, and life stages within a toxicology program. While routine for pharmaceuticals, TK assessments of non-pharmaceuticals are still relatively rare, and have never before been included in a full range of guideline studies for a new agrochemical. In order to better understand the relationship between diurnal systemic dose (AUC(24h)) and toxicity of agrochemicals, TK analyses in the study animals is now included in all short- (excluding acute), medium- and long-term guideline mammalian toxicity studies including reproduction/developmental tests. This paper describes a detailed procedure for the implementation of TK in short-, medium- and long-term regulatory toxicity studies, without the use of satellite animals, conducted on three agrochemicals (X11422208, 2,4-D and X574175). In these studies, kinetically-derived maximum doses (KMD) from short-term studies instead of, or along with, maximum tolerated doses (MTD) were used for the selection of the high dose in subsequent longer-term studies. In addition to leveraging TK data to guide dose level selection, the integrated program was also used to select the most appropriate method of oral administration (i.e., gavage versus dietary) of test materials for rat and rabbit developmental toxicity studies. The integrated TK data obtained across toxicity studies (without the use of additional/satellite animals) provided data critical to understanding differences in response across doses, species, strains, sexes, and life stages. Such data should also be useful in mode of action studies and to improve human risk assessments.

Reconstruction of Exposure to m-Xylene from Human Biomonitoring Data Using PBPK Modelling, Bayesian Inference, and Markov Chain Monte Carlo Simulation

There are numerous biomonitoring programs, both recent and ongoing, to evaluate environmental exposure of humans to chemicals. Due to the lack of exposure and kinetic data, the correlation of biomarker levels with exposure concentrations leads to difficulty in utilizing biomonitoring data for biological guidance values. Exposure reconstruction or reverse dosimetry is the retrospective interpretation of external exposure consistent with biomonitoring data. We investigated the integration of physiologically based pharmacokinetic modelling, global sensitivity analysis, Bayesian inference, and Markov chain Monte Carlo simulation to obtain a population estimate of inhalation exposure to m-xylene. We used exhaled breath and venous blood m-xylene and urinary 3-methylhippuric acid measurements from a controlled human volunteer study in order to evaluate the ability of our computational framework to predict known inhalation exposures. We also investigated the importance of model structure and dimensionality with respect to its ability to reconstruct exposure.

Simultaneous quantitation of testosterone and estradiol in human cell line (H295R) by liquid chromatography/positive atmospheric pressure photoionization tandem mass spectrometry

The possible interaction of environmental contaminants with the endocrine system has been an environmental concern since the early 1990s. To examine these interactions test guidelines have been introduced by regulatory agencies to screen for possible endocrine active compounds. One of these guidelines is the EPAs OPPTS 890.1550 [Steroidogenesis (Human Cell Line-H295R)]. This guideline requires the quantification of two major biomarkers (testosterone and estradiol) in various biological test systems. Traditional quantitation methodologies such as Radioimmunoassay (RIA) and Enzyme-linked Immunosorbent Assay (ELISA) have been used to quantify low levels of steroids. However, those methodologies have drawbacks such as the radioactive safety, antibody availability, separate assay for each biomarker, and lack of selectivity. In the current study, a rapid and sensitive liquid chromatography/positive atmospheric pressure photoionization tandem mass spectrometry method (LC/APPI-MS/MS) has been developed and validated for the simultaneous quantitation of testosterone and estradiol in the H295R cell line. Briefly, the media from cultured cells was extracted with dichloromethane (CH(2)Cl(2)) containing internal standards of both testosterone-d(3) and estradiol-(13)C(3); then, the extracted organic layer was concentrated down to dryness. The final residue was derivatized with dansyl chloride solution, and directly analyzed by LC/APPI-MS/MS. The calibration curves, with concentration ranging from 10 to 2500 pg/mL, were linear with coefficient >0.99. The lower limits of quantitation for both testosterone and estradiol were 10 pg/mL. This method was successfully validated to support requirements of the current EPA Steroidogenesis guideline. This type of method may also provide value for rapid and precise measurements of these two hormones in other in vitro or in vivo test systems.

Investigations of Oxidative Stress, Antioxidant Response, and Protein Binding in Chlorpyrifos Exposed Rat Neuronal PC12 Cells

ABSTRACT Chlorpyrifos (CPF) is a widely used organophosphate insecticide. In addition to its known properties of cholinesterase inhibition, the production of reactive oxygen species (ROS) has been suggested as a possible toxic mechanism. To investigate CPF-generated ROS, rat neuronal PC12 cells were exposed to CPF concentrations of 0 to 5000 μg/mL in Krebs buffered media (KRH), KRH + 4% bovine serum albumin (BSA), and KRH + 25 μM of the antioxidant Trolox for 0 to 5 h. Paraquat served as a positive control for ROS. The fluorescent probe 2,7-dichlorodihydro-fluorescein and the MTS assay were used to measure ROS and cytotoxicity, respectively. Examinations into CPF-albumin binding were also conducted. CPF was not strongly cytotoxic to PC12 cells, causing only mild cytotoxicity at 5000 μg/ml. In KRH media, CPF-generated ROS was observed at 4 and 5 h at 500 and 1000 μg/mL, and at 1 to 5 h at 5000 μg/mL CPF. In KRH + 4% BSA, ROS was seen only at 5 h in 5000 μg/mL CPF. Trolox significantly reduced CPF- and paraquat-induced ROS. Calculated CPF-albumin binding at 1, 10, and 100 μg/mL CPF in 4% BSA was 96%, 75%, and 15%. These data show CPF at ≥500 μg/mL induced ROS in PC12 cells, but the addition of the antioxidant Trolox and 4% BSA dramatically reduced ROS levels.

Development of a physiologically-based pharmacokinetic model of 2-phenoxyethanol and its metabolite phenoxyacetic acid in rats and humans to address toxicokinetic uncertainty in risk assessment ☆

2-Phenoxyethanol (PhE) has been shown to induce hepatotoxicity, renal toxicity, and hemolysis at dosages ≥ 400 mg/kg/day in subchronic and chronic studies in multiple species. To reduce uncertainty associated with interspecies extrapolations and to evaluate the margin of exposure (MOE) for use of PhE in cosmetics and baby products, a physiologically-based pharmacokinetic (PBPK) model of PhE and its metabolite 2-phenoxyacetic acid (PhAA) was developed. The PBPK model incorporated key kinetic processes describing the absorption, distribution, metabolism and excretion of PhE and PhAA following oral and dermal exposures. Simulations of repeat dose rat studies facilitated the selection of systemic AUC as the appropriate dose metric for evaluating internal exposures to PhE and PhAA in rats and humans. Use of the PBPK model resulted in refinement of the total default UF for extrapolation of the animal data to humans from 100 to 25. Based on very conservative assumptions for product composition and aggregate product use, model-predicted exposures to PhE and PhAA resulting from adult and infant exposures to cosmetic products are significantly below the internal dose of PhE observed at the NOAEL dose in rats. Calculated MOEs for all exposure scenarios were above the PBPK-refined UF of 25.

In vitro metabolism and covalent binding of ethylbenzene to microsomal protein as a possible mechanism of ethylbenzene-induced mouse lung tumorigenesis

This study was conducted to determine species differences in covalent binding of the reactive metabolites of ethylbenzene (EB) formed in the liver and lung microsomes of mouse, rat and human in the presence of NADPH. These data further the understanding of the mechanism by which EB causes mouse specific lung toxicity and a follow-up to our earlier report of the selective elevation, although minor, of the ring-oxidized reactive metabolites in mouse lung microsomes (Saghir et al., 2009). Binding assays were also conducted with or without 5-phenyl-1-pentyne (5P1P), an inhibitor of CYP 2F2, and diethyldithiocarbamate (DDTC), an inhibitor of CYP 2E1 to evaluate their role in the formation of the related reactive metabolites. Liver and lung microsomes were incubated with (14)C-EB (0.22 mM) in the presence of 1mM NADPH under physiological conditions for 60 min. In lung microsomes, binding activity was in the order of mouse (812.4+/-102.2 pmol/mg protein)>>rat (57.0+/-3.2 pmol/mg protein). Human lung microsomes had little binding activity (15.7+/-1.4 pmol/mg protein), which was comparable to the no-NADPH control (9.9-16.7 pmol/mg protein). In liver microsomes, mouse had the highest activity (469.0+/-38.5 pmol/mg protein) followed by rat (148.3+/-14.7 pmol/mg protein) and human (89.8+/-3.0 pmol/mg protein). Presence of 5P1P or DDTC decreased binding across species and tissues. However, much higher inhibition was observed in mouse (86% [DDTC] and 89% [5P1P]) than rat (56% [DDTC] and 59% [5P1P]) lung microsomes. DDTC showed approximately 2-fold higher inhibition of binding in mouse and human liver microsomes than 5P1P (mouse=85% vs. 40%; human=59% vs. 36%). Inhibition in binding by DDTC was much higher (10-fold) than 5P1P (72% vs. 7%) in rat liver microsomes. These results show species, tissue and enzyme differences in the formation of reactive metabolites of EB. In rat and mouse lung microsomes, both CYP2E1 and CYP2F2 appear to contribute in the formation of reactive metabolites of EB. In contrast, CYP2E1 appears to be the primary CYP isozyme responsible for the reactive metabolites of EB in the liver.

Mechanism of ethylbenzene-induced mouse-specific lung tumor: metabolism of ethylbenzene by rat, mouse, and human liver and lung microsomes.

This study was conducted to determine species differences in the metabolism of ethylbenzene (EB) in liver and lung. EB (0.22-7.0mM) was incubated with mouse, rat and human liver and lung microsomes and the formation of 1-phenylethanol (1PE), acetophenone (AcPh), 2-ethylphenol (2EP), 4-ethylphenol (4EP), 2,5-ethylquinone, and 3,4-ethylquinone were measured. Reactive metabolites (2,5-dihydroxyethylbenzene-GSH [2EP-GSH] and 3,4-dihydroxyethylbenzene-GSH [4EP-GSH]) were monitored via glutathione (GSH) trapping technique. None of the metabolites were formed at detectable levels in incubations with human lung microsomes. Percent conversion of EB to 1PE ranged from 1% (rat lung; 7.0mM EB) to 58% (mouse lung; 0.22 mM EB). More 1PE was formed in mouse lung than in mouse liver microsomes, although formation of 1PE by rat liver and lung microsomes was similar. Metabolism of EB to 1PE was in the order of mouse > rat > human. Formation of AcPh was roughly an order of magnitude lower than 1PE. Conversion of EB to ring-hydroxylated metabolites was much lower (0.0001% [4EP-GSH; rat lung] to 0.6% [2EP-GSH; mouse lung]); 2EP-GSH was typically 10-fold higher than 4EP-GSH. Formation of 2EP-GSH was higher by lung (highest by mouse lung) than liver microsomes and the formation of 2EP-GSH by mouse liver microsomes was higher than rat and human liver microsomes. Increasing concentrations of EB did lead to a decrease in amount of some formed metabolites. This may indicate some level of substrate- or metabolite-mediated inhibition. High concentrations of 2EP and 4EP were incubated with microsomes to further investigate their oxidation to ethylcatechol (ECat) and ethylhydroquinone (EHQ). Conversion of 2EP to EHQ ranged from 6% to 9% by liver (mouse > human > rat) and from 0.1% to 18% by lung microsomes (mouse >> rat >> human). Conversion of 4EP to ECat ranged from 2% to 4% by liver (mouse > human approximately rat) and from 0.3% to 7% by lung microsomes (mouse >> rat >> human). Although ring-oxidized metabolites accounted for a relatively small fraction of overall EB metabolism, its selective elevation in mouse lung microsomes is nonetheless consistent with the hypothesized mode of action for observed preferential toxicity of EB to the lung in this species.

Biodegradation of an Epoxy-Based Thermoplastic Polyester, Poly(Hydroxy Ester Ether) in a Laboratory-Scale Compost System

An epoxy-based thermoplastic polyester, poly(hydroxy ester ether), was incubated under aerobic conditions in a laboratory-scale compost system for 168 days to evaluate its potential for biodegradation. Radiolabeled test polymer [uniformly 14C ring-labeled, poly(hydroxy ester ether)] was incorporated into a mature compost and a sludge-amended compost at a loading of ∼3 mg test polymer/g compost. 14C-Cellulose was used as the positive control and a biologically inhibited control reactor was used to assess abiotic degradation of the test polymer. Degradation of the test polymer was assessed by measuring the amount of 14C-CO2 from each of the test reactors. In addition, at selected time intervals subsamples of the compost were collected and serially extracted with water, methanol, and dimethylformamide to monitor degradation of the 14C-test polymer and provide a partial characterization of the degradation intermediates. Extensive degradation of 14C-poly(hydroxy ester ether) was observed in the test reactors with degradation half-life of the parent polymer (t1/2) of approximately 32 days. By the end of the study, only 2% of the total 14C activity in the test reactors was attributed to intact polymer, with most of the measurable 14C activity converted to either 14C-CO2 (26% of total 14C activity) or nonextractable products (accounting for ∼60% of the total activity). In contrast to the test reactors, only 3% of the 14C-poly(hydroxy ester ether) added to the biologically inhibited control reactor was mineralized to 14C-CO2. The results obtained from the microbially active and biologically inhibited compost systems indicate that the poly(hydroxy ester ether) polymer was degraded, at least in part, by a biologically mediated process.