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Short-term biomarkers of toxicity have an increasingly important role in the screening and prioritization of new chemicals. In this study, we examined early indicators of liver toxicity for three reference organophosphate (OP) chemicals, which are among the most widely used insecticides in the world. The OP methidathion was previously shown to increase the incidence of liver toxicity, including hepatocellular tumors, in male mice. To provide insights into the adverse outcome pathway (AOP) that underlies these tumors, effects of methidathion in the male mouse liver were examined after 7 and 28 day exposures and compared to those of two other OPs that either do not increase (fenthion) or possibly suppress liver cancer (parathion) in mice. None of the chemicals caused increases in liver weight/body weight or histopathological changes in the liver. Parathion decreased liver cell proliferation after 7 and 28 days while the other chemicals had no effects. There was no evidence for hepatotoxicity in any of the treatment groups. Full-genome microarray analysis of the livers from the 7 and 28 day treatments demonstrated that methidathion and fenthion regulated a large number of overlapping genes, while parathion regulated a unique set of genes. Examination of cytochrome P450 enzyme activities and use of predictive gene expression biomarkers found no consistent evidence for activation of AhR, CAR, PXR, or PPARα. Parathion suppressed the male-specific gene expression pattern through STAT5b, similar to genetic and dietary conditions that decrease liver tumor incidence in mice. Overall, these findings indicate that methidathion causes liver cancer by a mechanism that does not involve common mechanisms of liver cancer induction.

Current strategies for predicting carcinogenic mode of action for nongenotoxic chemicals are based on identification of early key events in toxicity pathways. The goal of this study was to evaluate short-term key event indicators resulting from exposure to androstenedione (A4), an androgen receptor agonist and known liver carcinogen in mice. Liver cancer is more prevalent in men compared with women, but androgen-related pathways underlying this sex difference have not been clearly identified. Short-term hepatic effects of A4 were compared with reference agonists of the estrogen receptor (ethinyl estradiol, EE) and glucocorticoid receptor (prednisone, PRED). Male B6C3F1 mice were exposed for 7 or 28 days to A4, EE, or PRED. EE increased and PRED suppressed hepatocyte proliferation, while A4 had no detectable effects. In a microarray analysis, EE and PRED altered >3000 and >670 genes, respectively, in a dose-dependent manner, whereas A4 did not significantly alter any genes. Gene expression was subsequently examined in archival liver samples from male and female B6C3F1 mice exposed to A4 for 90 days. A4 altered more genes in females than males and did not alter expression of genes linked to activation of the mitogenic xenobiotic receptors AhR, CAR, and PPARα in either sex. A gene expression biomarker was used to show that in female mice, the high dose of A4 activated the growth hormone-regulated transcription factor STAT5b, which controls sexually dimorphic gene expression in the liver. These findings suggest that A4 induces subtle age-related effects on STAT5b signaling that may contribute to the higher risk of liver cancer in males compared with females.

A method based on regression modeling was developed to discern the contribution of component chemicals to the toxicity of highly complex, environmentally realistic mixtures of disinfection byproducts (DBPs). Chemical disinfection of drinking water forms DBP mixtures. Because of concerns about possible reproductive and developmental toxicity, a whole mixture (WM) of DBPs produced by chlorination of a water concentrate was administered as drinking water to Sprague–Dawley (S–D) rats in a multigenerational study. Age of puberty acquisition, i.e., preputial separation (PPS) and vaginal opening (VO), was examined in male and female offspring, respectively. When compared to controls, a slight, but statistically significant delay in puberty acquisition was observed in females but not in males. WM-induced differences in the age at puberty acquisition were compared to those reported in S–D rats administered either a defined mixture (DM) of nine regulated DBPs or individual DBPs. Regression models were developed using individual animal data on age at PPS or VO from the DM study. Puberty acquisition data reported in the WM and individual DBP studies were then compared with the DM models. The delay in puberty acquisition observed in the WM-treated female rats could not be distinguished from delays predicted by the DM regression model, suggesting that the nine regulated DBPs in the DM might account for much of the delay observed in the WM. This method is applicable to mixtures of other types of chemicals and other endpoints.

Current strategies for predicting adverse health outcomes of environmental chemicals are centered on early key events in toxicity pathways. However, quantitative relationships between early molecular changes in a given pathway and later health effects are often poorly defined. The goal of this study was to evaluate short-term key event indicators using qualitative and quantitative methods in an established pathway of mouse liver tumorigenesis mediated by peroxisome proliferator-activated receptor alpha (PPARα). Male B6C3F1 mice were exposed for 7 days to di (2-ethylhexyl) phthalate (DEHP), di-n-octyl phthalate (DNOP), and n-butyl benzyl phthalate (BBP), which vary in PPARα activity and liver tumorigenicity. Each phthalate increased expression of select PPARα target genes at 7 days, while only DEHP significantly increased liver cell proliferation labeling index (LI). Transcriptional benchmark dose (BMDT) estimates for dose-related genomic markers stratified phthalates according to hypothetical tumorigenic potencies, unlike BMDs for non-genomic endpoints (relative liver weights or proliferation). The 7-day BMDT values for Acot1 as a surrogate measure for PPARα activation were 29, 370, and 676 mg/kg/day for DEHP, DNOP, and BBP, respectively, distinguishing DEHP (liver tumor BMD of 35 mg/kg/day) from non-tumorigenic DNOP and BBP. Effect thresholds were generated using linear regression of DEHP effects at 7 days and 2-year tumor incidence values to anchor early response molecular indicators and a later phenotypic outcome. Thresholds varied widely by marker, from 2-fold (Pdk4 and proliferation LI) to 30-fold (Acot1) induction to reach hypothetical tumorigenic expression levels. These findings highlight key issues in defining thresholds for biological adversity based on molecular changes.

The introduction of drinking water disinfection greatly reduced waterborne diseases. However, the reaction between disinfectants and natural organic matter in the source water leads to an unintended consequence, the formation of drinking water disinfection byproducts (DBPs). The haloace-taldehydes (HALs) are the third largest group by weight of identified DBPs in drinking water. The primary objective of this study was to analyze the occurrence and comparative toxicity of the emerging HAL DBPs. A new HAL DBP, iodoacetaldehyde (IAL) was identified. This study provided the first systematic, quantitative comparison of HAL toxicity in Chinese hamster ovary cells. The rank order of HAL cytotoxicity is tribromoacetaldehyde (TBAL) ≈ chloroacetaldehyde (CAL) > dibromoacetaldehyde (DBAL) ≈ bromochloroacetaldehyde (BCAL) ≈ dibromochloroacetaldehyde (DBCAL) > IAL > bromoacetaldehyde (BAL) ≈ bromodichloroacetaldehyde (BDCAL) > dichloroacetaldehyde (DCAL) > trichloroacetaldehyde (TCAL). The HALs were highly cytotoxic compared to other DBP chemical classes. The rank order of HAL genotoxicity is DBAL > CAL ≈ DBCAL > TBAL ≈ BAL > BDCAL > BCAL ≈ DCAL > IAL. TCAL was not genotoxic. Because of their toxicity and abundance, further research is needed to investigate their mode of action to protect the public health and the environment.

As the use of alternative drinking water treatment increases, it is important to understand potential public health implications associated with these processes. The objective of this study was to evaluate the formation of disinfection byproducts (DBPs) and cytotoxicity of natural organic matter (NOM) concentrates treated with chlorine, chloramine, and medium pressure ultraviolet (UV) irradiation followed by chlorine or chloramine, with and without nitrate or iodide spiking. The use of concentrated NOM conserved volatile DBPs and allowed for direct analysis of the treated water. Treatment with UV prior to chlorine in ambient (unspiked) samples did not affect cytotoxicity as measured using an in vitro normal human colon cell (NCM460) assay, compared to chlorination alone when toxicity is expressed on the basis of dissolved organic carbon (DOC). Nitrate-spiked UV+chlorine treatment produced greater cytotoxicity than nitrate-spiked chlorine alone or ambient UV+chlorine samples, on both a DOC and total organic halogen basis. Samples treated with UV+chloramine were more cytotoxic than those treated with only chloramine using either dose metric. This study demonstrated the combination of cytotoxicity and DBP measurements for process evaluation in drinking water treatment. The results highlight the importance of dose metric when considering the relative toxicity of complex DBP mixtures formed under different disinfection scenarios.

Previously, we reported that acute treatment with propoxur or carbaryl decreased the duration of the photic after discharge (PhAD) of flash evoked potentials (FEPs). In the current studies, we compared the effects of acute or repeated exposure to a mixture of carbaryl and propoxur (1:1.45 ratio; propoxur:carbaryl) on the duration of the PhAD and brain ChE activity in Long Evans rats. Animals were exposed (po) either to a single dose (0, 3, 10, 45 or 75 mg/kg), or 14 daily dosages (0, 3, 10, 30, 45 mg/kg), of the mixture. Acute and repeated treatment with 3mg/kg (or greater) of the mixture produced dose-related inhibition of brain ChE activity. Compared to controls, the PhAD duration decreased after acute administration of 75 mg/kg or repeated treatment with 30 mg/kg of the mixture. The linear relationship between the percent of control brain ChE activity and the PhAD duration was similar for both exposure paradigms. Dose-response models for the acute and repeated exposure data did not differ for brain ChE activity or the duration of the PhAD. Repeated treatment with the mixture resulted in slightly less (13-22%) erythrocyte ChE inhibition than acute exposure. Both acute and repeated treatment resulted in dose-additive results for the PhAD duration and less than dose-additive responses (6-16%) for brain ChE activity for the middle range of dosages. Acute treatment resulted in greater than dose-additive erythrocyte ChE inhibition (15-18%) at the highest dosages. In contrast, repeated treatment resulted in less than dose-additive erythrocyte ChE inhibition (16-22%) at the middle dosages. Brain and plasma levels of propoxur and carbaryl did not differ between the acute and repeated dosing paradigms. In summary, a physiological measure of central nervous system function and brain ChE activity had similar responses after acute or repeated treatment with the carbamate mixture, and brain ChE showed only small deviations from dose-additivity. Erythrocyte ChE activity had larger differences between the acute and repeated treatment paradigms, and showed slightly greater deviations from dose-additivity. Because these treatments utilized larger dosages than anticipated environmental exposures, concern for non-additive effects in humans is minimized. The small magnitude of the deviations from dose-additivity also suggest that in the absence of repeated exposure data, results from an acute study of readily reversible carbamate toxicity can be used to estimate the response to repeated daily exposures.

Large-scale differential gene expression analysis was used to examine the biological effects of disinfected surface waters on cultured rat hepatocytes. Source water from East Fork Lake (Harsha Lake), a reservoir on the Little Miami River in Ohio, was spiked with iodide and bromide and disinfected by chlorination or ozonation/postchlorination. The chlorinated and ozonated/postchlorinated waters were concentrated, respectively, 136- and 124-fold (full strength) by reverse-osmosis membrane techniques. Volatile disinfection by-products (DBP) lost during concentration were restored to the extent possible. Primary rat hepatocytes were exposed to either full-strength or 1:10 or 1:20 dilutions of the concentrates for 24 h and assayed for cytotoxicity and gene expression alterations. The full-strength concentrates were cytotoxic, whereas the diluted samples exhibited no detectable cytotoxicity. Differential gene expression analysis provided evidence for the underlying causes of the severe cytotoxicity observed in rat hepatocytes treated with the full-strength ozonation/postchlorination concentrate (e.g., cell cycle arrest, metabolic stasis, oxidative stress). Many gene expression responses were shared among the hepatocyte cultures treated with dilutions of the ozonation/ postchlorination and chlorination concentrates. The shift in the character of the response between the full-strength concentrates and the diluted samples indicated a threshold for toxicity. A small subset of gene expression changes was identified that was observed in the response of hepatocytes to peroxisome proliferators, phthalate esters, and haloacetic acids, suggesting a peroxisome proliferative response.

Risk assessments often must consider exposures that vary over time or for which the exposure duration of concern differs from the available data, and a variety of extrapolation procedures have been devised accordingly. The present experiments explore the relationship(s) between exposure concentration (C) and time (t) to investigate procedures for assessing the risks of short-term solvent exposures. The first hypothesis tested was that the product of C x t would produce a constant health effect (Haber's rule). The second hypothesis tested was that exposure conditions produce effects in proportion to the tissue concentrations created. Awake, adult, male Long-Evans (LE) rats were exposed to trichloroethylene (TCE) vapor in a head-only exposure chamber while pattern onset/offset visual evoked potentials (VEPs) were recorded. Exposure conditions were designed to provide C x t products of 0 ppm/h (0 ppm for 4 h) or 4000 ppm/h created through four exposure scenarios: 1000 ppm for 4 h; 2000 ppm for 2 h; 3000 ppm for 1.3 h; or 4000 ppm for 1h (n = 9-10/concentration). The amplitude of the VEP frequency double component (F2) was decreased significantly by exposure; this decrease was related to C but not to t or to the C x t product, indicating that Haber's rule did not hold. The mean amplitude (+/- SEM in muV) of the F2 component in the control and treatment groups measured 4.4 +/- 0.5 (0 ppm/4 h), 3.1 +/- 0.5 (1000 ppm/4 h), 3.1 +/- 0.4 (2000 ppm/2 h), 2.3 +/- 0.3 (3000 ppm/1.3 h), and 1.9 +/- 0.4 (4000 ppm/1 h). A physiologically based pharmacokinetic (PBPK) model was used to estimate the concentrations of TCE in the brain achieved during each exposure condition. The F2 amplitude of the VEP decreased monotonically as a function of the estimated peak brain concentration but was not related to the area under the curve (AUC) of the brain TCE concentration. In comparison to estimates from the PBPK model, extrapolations based on Haber's rule yielded approximately a 6-fold error in estimated exposure duration when extrapolating across only a 4-fold change in exposure concentration. These results indicate that the use of a linear form of Haber's rule will not predict accurately the risks of acute exposure to TCE, nor will an estimate of AUC of brain TCE. However, an estimate of the brain TCE concentration at the time of VEP testing predicted the effects of TCE across exposure concentrations and durations.

Haber's rule as commonly interpreted in inhalation toxicology, can be stated as exposure concentration times duration equals a constant biological effect, or C × t = k . In other words, identical products of concentration and duration lead to the same effect. The goals of this paper are to develop a biological and pharmacokinetic modeling approach for chloroform, and to evaluate Haber's rule for different ages by taking into account the physiological changes due to growth and aging in rats. Three-dimensional dose–response surfaces for liver toxicity were generated for each age group of interest: adolescent, adult, and senescent rats. The three-dimensional surfaces were then characterized with a generalized description of Haber's rule for each age group. The simulations suggest that adolescent rats need higher exposure levels in order to achieve similar levels of liver damage compared to adults or senescent rats, if the comparison is made using the same exposure length. In summary, a pharmacokinetic modeling approach with a biological framework including the chemical's mode of action, was used to relate concentration, exposure duration and effect. Major advantages of this approach include: the potential ability to extrapolate to humans, the inclusion of aging in the simulations, and the ability to summarize the results using a generalized form of Haber's rule.

Increases in the use of methanol (MeOH) as a transportation fuel would result in greater potential for inhalation exposure. Because oral exposure to MeOH potentiates the hepatotoxicity of carbon tetrachloride (CCl4), we examined the ability of inhaled MeOH to potentiate CCl4 hepatotoxicity and the time course of injury and recovery. Adult male F-344 rats were exposed to 0 or to 10,000 ppm MeOH by inhalation for 6 h and gavaged with 0.075 ml CCl4/kg 24 h later. Hepatotoxicity was assessed 0.5, 1, 1.5, 2, 3, 7, 15, 30, and 61 d after CCl4 exposure. For CCl4 alone, hepatotoxicity was most severe at 0.5 and 1 d, when minimal centrilobular hepatocellular necrosis and predominately mild centrilobular hepatocellular vacuolar degeneration occurred. By d 3, the livers from the CCl4 rats were histologically normal. For MeOH+CCl4, peak severity of hepatic injury was at 1 and 1.5 d, when moderate centrilobular necrosis and moderate/marked centrilobular degeneration occurred. MeOH+CCl4 resulted in serum levels of aspartate aminotransferase (AST) and alanine aminotransferase (ALT) that were increased, relative to CCl4 alone, 171- and 113-fold, respectively, on d 1, and 166- and 140-fold, respectively, on d 1.5. Significant serum elevations in MeOH+CCl4 rats, relative to CCl4 alone rats, were present until d 7 and d 15 for AST and ALT, respectively. By d 3 and d 7, degeneration and necrosis, respectively, due to MeOH+CCl4 were essentially resolved. On d 7, the MeOH+CCl4 hepatic injury consisted mainly of chronic inflammation and centrilobular fibrosis. By d 30, the livers of MeOH+CCl4 rats were histologically normal. These data demonstrate that inhaled MeOH potentiates the hepatotoxicity of orally ingested CCl4, increasing the severity of CCl4 hepatotoxicity as well as the time required for recovery.

Bromodichloromethane (BDCM) is a disinfection by-product of drinking water chlorination and is the second most common trihalomethane (THM) in finished drinking water. THMs have generally been administered to experimental animals in corn oil, rather than drinking water, which can influence the site and magnitude of toxicity. To examine the effects of gavage vehicle on the acute renal and hepatic toxicity of orally administered BDCM, 95-day-old male F344 rats were given single doses of 0, 200, or 400 mg BDCM/kg in corn oil or an aqueous 10% Emulphor solution. Activities of serum hepatoxicity indicators were significantly greater 48 hr after administration of 400 mg BDCM/kg in corn oil compared to the aqueous vehicle, but delivery of the low dose in either dosing vehicle had little effect on serum enzymes. In contrast, significant elevations in urinary renal toxicity indicators were noted at 200 and 400 mg BDCM/kg in both vehicles after 24 hr, indicating that the kidney is more sensitive to low doses of BDCM than the liver. Significantly greater increases were observed in urinary indicators after delivery of 200 mg BDCM/kg in 10% Emulphor compared to corn oil. However, administration of the high dose in corn oil resulted in greater nephrotoxicity than in the aqueous vehicle. Significant interactions between vehicle of administration and BDCM dose observed for both urinary and serum parameters further indicate that vehicle differences noted in BDCM acute toxicity are dose dependent. This observation may be due to pharmacokinetic differences in gastrointestinal rates of absorption of BDCM from corn oil as compared to an aqueous solution.

Reactions between chemicals used to disinfect drinking water and compounds present in source waters produce chemical mixtures containing hundreds of disinfection byproducts (DBPs). Although the results have been somewhat inconsistent, some epidemiological studies suggest associations may exist between DBP exposures and adverse developmental outcomes. The potencies of individual DBPs in rodent and rabbit developmental bioassays suggest that no individual DBP can account for the relative risk estimates reported in the positive epidemiologic studies, leading to the hypothesis that these outcomes could result from the toxicity of DBP mixtures. As a first step in a mixtures risk assessment for DBP developmental effects, this paper identifies developmentally toxic DBPs and examines data relevant to the mode of action (MOA) for DBP developmental toxicity. We identified 24 developmentally toxic DBPs and four adverse developmental outcomes associated with human DBP exposures: spontaneous abortion, cardiovascular defects, neural tube defects, and low birth weight infancy. A plausible MOA, involving hormonal disruption of pregnancy, is delineated for spontaneous abortion, which some epidemiologic studies associate with total trihalomethane and bromodichloromethane exposures. The DBP data for the other three outcomes were inadequate to define key MOA steps.

The acute hepatotoxicity and response of hepatic cytochrome P450 to treatment with the three isomers of dichlorobenzene (DCB) have been investigated. The objectives were to estimate the onset of toxicity and to further elucidate the role of cytochrome P450 in the metabolism and toxicity of these compounds. In a study design employing one animal per dose level, Fischer-344 rats were gavaged with up to 25 different dosages, then evaluated 24 h later. Hepatic necrosis, serum alanine aminotransferase, and serum aspartate aminotransferase exhibited similar patterns demonstrating that ortho-DCB (o-DCB) was the most toxic in terms of both earliest onset and degree of response at higher dosages. For these three endpoints, meta-DCB (m-DCB) exhibited a lesser toxicity. Para-DCB (p-DCB) did not cause changes in these three endpoints, but hepatic degenerative changes were found. Total hepatic cytochrome P450 responses were also different after treatment with each isomer. The o-DCB produced a dose-dependent decrease in P450 beginning at dosages lower than the onset of necrosis and appeared to be a suicide substrate for P450. The m-DCB treatment increased P450 at dosages below the onset of necrosis and decreased P450 at higher dosages, with the decline preceding the onset of hepatocyte death. Treatment with p-DCB increased P450 beginning at 380 mg/kg. The combination of toxicity and P450 profiles has provided a framework for interpreting literature data on the metabolism and toxicity of the DCBs in rats. It is also noteworthy that o-DCB and p-DCB were administered at dosages several times the oral rat LD-50 (RTECS) without any lethality.

Chlorination of drinking water yields hundreds of disinfection by-products (DBPs). Among the DBPs, four trihalomethanes (THMs; chloroform, bromodichloromethane, chlorodibromomethane, bromoform) and five haloacetic acids (HAAs; chloroacetic, dichloroacetic, trichloroacetic, bromoacetic, and dibromoacetic acid) are U.S. EPA regulated. We assessed the combined toxicity of these DBPs. F344 rats were treated with mixtures of the four THMs (THM4), the five HAAs (HAA5), or nine DBPs (DBP9; THM4+HAA5). Mixtures were administered in 10% Alkamuls(®) EL-620 daily by gavage on gestation days 6-20. Litters were examined postnatally. All three mixtures caused pregnancy loss at ≥ 613 μmol/kg/day. In surviving litters, resorption rates were increased in groups receiving HAA5 at 615 μmol/kg/day and DBP9 at 307 μmol/kg/day. HAA5 caused eye malformations (anophthalmia, microphthalmia) at ≥ 308 μmol/kg/day. Thus, both HAAs and THMs contributed to DBP9-induced pregnancy loss. The presence of THMs in the full mixture, however, appeared to reduce the incidence of HAA-induced eye defects.

The immunotoxicity, hepatotoxicity, and nephrotoxicity of subacute exposure to carbon tetrachloride (CCl 4 ) were evaluated in young adult (8–9 weeks old) male Fischer 344 rats dosed by gavage with CCl 4 for 10 consecutive days at 0, 5, 10, 20 or 40 mg/kg/day. Two days following the last treatment rats were evaluated for alterations in immune function by monitoring the following: body and lymphoid organ weights; mitogen and mixed leukocyte reaction lymphoproliferative responses; natural killer cell activity; and cytotoxic T lymphocyte responses. A separate group of similarly dosed rats was immunized with sheep red blood cells (SRBC) on Day 9 of dosing, and the primary antibody response was assessed 4 days later. Hepatic and renal toxicity were assessed 2 days after the last treatment by monitoring organ weights, serum indicators of hepatic and renal damage, and hepatic cytochrome P450 levels, as well as by histological evaluation. Significant increases in relative liver weights were observed in rats dosed at 40 mg/kg/day. Histologically, these livers displayed mild to moderate vacuolar degeneration and minimal to mild hepatocellular necrosis. In addition, serum levels of aspartate aminotransferase and alnine aminotransferase were elevated at this dosage, as well as at 20 mg/kg/day. There were no renal effects observed at these dosages of CCl 4 . In addition, no consistent alterations were observed in the immune parameters examined in these same animals nor in the rats immunized with SRBC. Furthermore, there was no difference in the antibody response to SRBC in another set of rats dosed at 40, 80, or 160 mg/kg/day CCl 4 . These results indicate that CCl 4 is not immunotoxic in the rat at dosages that produce overt hepatotoxicity.

Epidemiological and animal toxicity studies have raised concerns regarding possible adverse health effects of disinfection by-products (DBPs) found in drinking water. The classes and concentrations of DBPs are influenced by the choice of disinfection process (e.g., chlorination, ozonation) as well as source water characteristics (e.g., pH, total organic carbon, bromide content). Disinfected waters were found to contain more than 500 compounds, many of which remain unidentified. Therefore, a "whole-mixture" approach was used to evaluate the toxic potential of alternative disinfection scenarios. An in vivo developmental toxicity screen was used to evaluate the adverse developmental effects of the complex mixtures produced by two different disinfection processes. Water was obtained from East Fork Lake, Ohio; spiked with iodide and bromide; and disinfected either by chlorination or by ozonation/postchlorination, producing finished drinking water suitable for human consumption. These waters were concentrated approximately 130-fold by reverse osmosis membrane techniques. To the extent possible, volatile DBPs lost in the concentration process were spiked back into the concentrates. These concentrates were then provided as drinking water to Sprague-Dawley rats on gestation days 6-16; controls received boiled, distilled, deionized water. The dams (19-20 per group) were allowed to deliver and their litters were examined on postnatal days (PD) 1 and 6. All dams delivered normally, with parturition occurring significantly earlier in the ozonation/postchlorination group. However, no effects on prenatal survival, postnatal survival, or pup weight were evident. Skeletal examination of the PD-6 pups also revealed no treatment effects. Thus, approximately 130-fold higher concentrates of both ozonated/postchlorinated and chlorinated water appeared to exert no adverse developmental effects in this study.

To determine the course of hepatic recovery from subchronic oral administration of carbon tetrachloride (CCl 4 ), male F-344 rats were gavaged with 0, 20, or 40 mg CCl 4 /kg, 5 days/week, for 12 weeks. Exposure to CCl 4 caused dosage-dependent increases in relative liver weight and the serum levels of aspartate aminotransferase, alanine aminotransferase, lactate dehydrogenase, alkaline phosphatase, and cholesterol as well as a dosage-dependent decrease in hepatic cytochrome P450. Centrilobular hepatocellular vacuolar degeneration, necrosis, and cirrhosis occurred at both 20 and 40 mg/kg, with dosage-dependent severity. Reversibility of these reported effects varied with parameter. By Day 8 postexposure, necrosis had disappeared and all serum indicators and cytochrome P450 had returned to control levels. By Day 15 postexposure, the severity of the vacuolar degeneration had decreased. Reversibility of cirrhosis was dosage dependent; complete recovery occurred in the low- but not the high-dose group by Day 15. The disappearance of the increase in relative liver weight was also dependent on dosage; the low- but not the high-dose group had returned to the control level by Day 22. In an attempt to measure persistent hepatic damage, liver uptake relative to the spleen was determined for a sulfur colloid labeled with technetium-99m and for tritiated 2-deoxyglucose. Neither method consistently measured hepatic damage in cirrhotic livers due, in part, to the high degree of variability in the tracer uptake data.

The effect of inhaled epichlorohydrin on rat sperm motility characteristics was evaluated. Male F-344 rats were exposed to 100 ppm epichlorohydrin via inhalation for 4 hr in the morning of Day 0 and killed immediately and on Days 1, 2, 6, and 14 postexposure. Videotapes of cauda epididymal sperm were analyzed (300–350 sperm/sample) with a Hamilton Thorn motility analyzer (HTM-2000, Hamilton Thorn Research, Danvers, MA). Epichlorohydrin did not affect the percentage of motile sperm at any time. However, transient changes in sperm velocity were found. On Day 1 postexposure mean progressive (straight line) and mean path (smoothed curvilinear) velocity were significantly decreased to 80 and 85% of control, respectively. The progressive velocities of sperm from both control and treated rats were normally distributed, indicating a general effect of epichlorohydrin on all sperm as opposed to a more severe effect on a specific sperm subpopulation. Sperm velocity was not significantly affected at later times. Other endpoints (testis and epididymis weights, testicular spermatid counts, and cauda epididymal sperm reserves) were unaltered by epichlorohydrin. Thus, inhaled epichlorohydrin at 100 ppm produced specific, transient decreases in rat sperm velocity. Furthermore, computer-assisted sperm analysis was able to detect these relatively subtle, toxicant-induced changes in rat sperm velocity, demonstrating the utility of this technology in reproductive toxicology studies.

Acute Exposure Guideline Level (AEGL) recommendations are developed for 10-minute, 30-minute, 1-hour, 4-hours, and 8-hours exposure durations and are designated for three levels of severity: AEGL-1 represents concentrations above which acute exposures may cause noticeable discomfort including irritation; AEGL-2 represents concentrations above which acute exposure may cause irreversible health effects or impaired ability to escape; and AEGL-3 represents concentrations above which exposure may cause life-threatening health effects or death. The default procedure for setting AEGL values across durations when applicable data are unavailable involves estimation based on Haber's rule, which has an underlying assumption that cumulative exposure is the determinant of toxicity. For acute exposure to trichloroethylene (TCE), however, experimental data indicate that momentary tissue concentration, and not the cumulative amount of exposure, is important. We employed an alternative approach to duration adjustments in which a physiologically-based pharmacokinetic (PBPK) model was used to predict the arterial blood concentrations [TCE a ] associated with adverse outcomes appropriate for AEGL-1, -2, or -3-level effects. The PBPK model was then used to estimate the atmospheric concentration that produces equivalent [TCE a ] at each of the AEGL-specific exposure durations. This approach yielded [TCE a ] values of 4.89 mg/l for AEGL-1, 18.7 mg/l for AEGL-2, and 310 mg/l for AEGL-3. Duration adjustments based on equivalent target tissue doses should provide similar degrees of toxicity protection at different exposure durations.

Bromodichloromethane (BDCM) is a by-product of water chlorination and is the second most common trihalomethane (THM) in finished drinking water. It has been reported that delivery of THMs in corn oil can influence the site and magnitude of toxic and carcinogenic responses in rodents, perhaps by inducing metabolizing enzymes or altering tissue composition. To determine if corn oil influences the acute toxicity of BDCM, adult male F-344 rats were pretreated 5 days/week for 6 weeks with oral doses of corn oil or water at a volume of 5 ml/kg. Following pretreatment, animals were gavaged with a single dose of 0, 200 or 400 mg BDCM/kg in 10% Emulphor. Urine was collected at timed intervals over a 48-h period following BDCM administration. Rats were sacrificed at this time and organs and blood removed. Urine and serum were analyzed for indicators of toxicity. Corn oil pretreatment did not enhance the acute hepato- or nephrotoxicity of BDCM, suggesting that vehicle effects noted in previous THM toxicity and carcinogenicity studies are more likely due to pharmacokinetic differences between administration in corn oil and aqueous gavage vehicles than to altered tissue composition or physiological changes.

Carbon tetrachloride (CCl4) is a potent hepatotoxic agent whose toxicity is mediated through cytochome P450-dependent metabolism. Results from anaerobic in vitro experiments with hepatic microsomes isolated from male F-344 rats indicate that chlorofom (CHCl3) formation from CCl4 is nonlinear with dose. Dose is traditionally expressed as the amount of CCl4 added to the vial. In this study, a pharmacokinetic model has been developed to calculate the concentration of CCl4 in the microsomal suspension. Hepatic microsomes prepared from fed and fasted animals were incubated with CCl4 under anaerobic conditions and formation of CHCl3 over a 5-min incubation period was monitored by headspace gas chromatography. Dose-response curves, based on total amount of CCl4 added to the microsomes, revealed a nonlinear, biphasic appearance of CHCl3, with fasting slightly increasing CHCl3 production in microsomes prepared from fasted rats. Microsomes were also pretreated with the CYP2E1 inhibitor, diallyl sulfone (DAS), before addition of CCl4. In uninhibited microsomes, there appeared to be a high-affinity saturable phase of metabolism occurring at lower concentrations followed by a linear phase at higher CCl4 concentrations. Following DAS pretreatment, the saturable portion of the dose-response curve was inhibited more than the linear phase with the biphasic CHCl3 production becoming more linear. DAS inhibition eliminated the effect of fasting on CHCl3 formation. The best fit kinetic constants for the saturable phase resulted in an estimate of V(max) of 0.017 mg/h/mg protein (V(maxc) = 7.61 mg/h/kg) and Km of 2.3 mg/l (15 microM). The linear phase rate constant (kf) was determined to be 0.046 h-1) (kfc = 0.03 h-1). In conclusion, a pharmacokinetic model has been developed for anaerobic in vitro metabolism of CCl4 to CHCl3 that estimates metabolic rates based on CHCl3 formation and actual CCl4 concentration in the microsomal suspension.

Because groundwater contamination is an important environmental concern, we examined the hepatic and renal effects of repeated exposure to a mixture of 25 chemicals frequently found in groundwater near hazardous-waste disposal sites and the effect of such exposure on carbon tetrachloride (CCI4) toxicity. Adult male F-344 rats received ad libitum deionized water and feed (Ad Lib Water) or ad libitum 10% MIX (referring to 10% of a technically achievable stock mixture) and feed for 14 d. Because exposure to the 25-chemical mixture via the drinking water resulted in decreased water and feed consumption, restricted deionized water and feed controls (Restricted Water) were included. On d 14, rats were gavaged with 0, 0.0375, 0.05, 0.075 or 0.15 ml CCl4/kg, and hepatic and renal toxicity assessed 24 h later. Little or no hepatic and renal toxicity was observed in rats exposed to 10% MIX alone. No hepatic or renal lesions occurred that could be attributed to 10% MIX alone. Slight but statistically significant alterations, of uncertain biological significance, resulted from the water treatments: 10% MIX increased alanine aminotransferase, urea nitrogen (BUN), and BUN/creatinine ratio; Restricted Water increased 5'-nucleotidase and decreased alkaline phosphatase. Relative kidney weight was increased by both 10% MIX and Restricted Water. CCI4 resulted in significant dosage-dependent hepatotoxicity in all three water treatment groups but had little or no effect on renal indicators of toxicity. Relative to Ad Lib Water, significantly greater hepatotoxicity occurred in both 10% MIX and Restricted Water rats. The response to CCI4 in the Restricted Water rats was similar to that of 10% MIX rats, indicating that a substantial portion of the effect of 10% MIX on CCI4 hepatotoxicity is due to decreased water and feed intake.

To assess whether potential toxic interactions occur between ethanol and allyl alcohol or carbon tetrachloride following subacute, concurrent chemical exposure, male Fischer 344 rats, approximately 70 d of age, were given ethanol at 0, 0.05, 0.1, 0.2, or 0.5 ml/kg in corn oil daily by gavage for 14 d (ETOH group), or the same levels of ethanol with 21 mg allyl alcohol/kg (ALAC group), or the same levels of ethanol with 20 mg carbon tetrachloride/kg (CCL4 group). Hepatic response was assessed 24 h after the last dose. Interactions were evaluated by comparing the ETOH group with either the ALAC group or the CCL4 group using multivariate analysis of variance procedures. No statistically significant interaction was seen between the ETOH group and the ALAC group at the dosages used. Although an interaction between ethanol and carbon tetrachloride given simultaneously was not statistically significant, a small interactive effect on weight gain from d 0 to termination was apparent (p = .057). Exposure to ethanol alone resulted in a concentration-dependent decrease in absolute and relative liver weight, with a threshold between 0.05 and 0.1 ml/kg. There was no histopathological evidence of hepatic damage with ethanol alone, and no effect on hepatic cytochrome P-450 and glutathione levels or on serum levels of alanine aminotransferase (ALT), aspartate aminotransferase (AST), and alkaline phosphatase (ALK). Exposure to allyl alcohol alone resulted in significant increases in absolute and relative liver weights, liver glutathione, and periportal hepatocellular vacuolar degeneration. Exposure to carbon tetrachloride alone resulted in significant increases in absolute and relative liver weight, serum levels of ALT, AST, and ALK, and centrilobular hepatocellular vacuolar degeneration and necrosis. These observations indicate that subacute, concurrent exposure of ethanol with carbon tetrachloride or allyl alcohol at ethanol levels comparable to those reported in gavage vehicles did not result in interactive toxicity.

Due to the ubiquitous presence of p-xylene in air and the existing uncertainty regarding its hepatotoxic potential, we examined the effect of acute and short-term exposure to inhaled p-xylene on the liver. Male F-344 rats were exposed to 0 or to 1600 ppm p-xylene, 6 h/d, for 1 or 3 d. Exposure to inhaled p-xylene caused no histopathological evidence of hepatic damage and had little or no effect on the serum levels of aspartate aminotransferase, alanine aminotransferase, lactate dehydrogenase, ornithine carbamyl transferase, alkaline phosphatase, and total bilirubin. Exposure to p-xylene for 1 or 3 d resulted in an increase in relative liver weight on d 1 post-exposure. The concentration of hepatic cytochrome P-450 was increased by both p-xylene exposure regimens on d 1 postexposure and had returned to control levels by d 3 following the single p-xylene exposure and by d 2 following the 3-d exposure. These observations provide consistent evidence that acute and short-term exposure to 1600 ppm p-xylene by inhalation did not produce overt hepatotoxicity but resulted in a significant increase in the concentration of hepatic cytochrome P-450, the principal enzyme system involved in the metabolic biotransformation of xenobiotics.

Male F344 rats were exposed by gavage to samples of complex mixtures and evaluated 24 hr later. Seven of the 10 samples caused death at doses ranging from 1 to 5 ml/kg body wt. Eight of the 10 samples were hepatotoxic based on histopathologic evaluation; 6 were centrilobular and 2 were periportal hepatotoxicants. The waste samples exerted toxicity through different mechanisms, as indicated by differences in the severity and lobular location of the tissue damage. Nine of the 10 samples caused an increase in the ratio of liver weight to body weight (relative liver weight). With histopathological evaluation as the criterion, relative liver weight was the single best indicator of hepatotoxicity. Exposure to several of the waste samples increased serum total bilirubin and serum enzyme activities of alanine aminotransferase, aspartate aminotransferase, lactate dehydrogenase, alkaline phosphatase, and ornithine carbamyl transferase. As a battery, but not individually, the serum indicators separated the 8 hepatotoxic samples from the 2 nonhepatotoxic samples. In general, the hepatotoxicity of the waste samples did not appear to be readily predicted from (partial) chemical characterization data. An approach that includes both chemical characterization and biological testing should provide valuable information regarding the hazardous nature of complex wastes.

Four chemicals that had been tested in an in vivo toxicological screen were tested in a Chinese hamster ovary (CHO) cytotoxicity assay. Cell density, viability, ATP concentration, rate of protein synthesis, and cellular protein concentration were decreased by exposure to acrylamide (AC), chlordecone (CHL), cyclophosphamide (CYC), and diethylstilbestrol (DES). Based on the in vitro toxicity rankings, DES and CHL were more toxic than AC or CYC. The ability of the CHO assay to respond to DES and CHL was comparable to other published in vitro assays. However, the CHO assay was unresponsive to concentrations of AC and CYC detected by assay systems composed of cells derived from the nervous system and assays containing metabolic activation, respectively. In vivo, the four chemicals were toxic following 10 daily treatments. While CYC was the least toxic chemical in vitro, it was one of the most toxic in vivo. This lack of correlation between the in vivo and the in vitro data in this study may be due to ...