An evidence-based analysis of epidemiologic associations between lymphatic and hematopoietic cancers and occupational exposure to gasoline.

The presence of benzene in motor gasoline has been a health concern for potential increased risk of acute myelogenous leukemia and perhaps other lymphatic/hematopoietic cancers for approximately 40 years. Because of the widespread and increasing use of gasoline by consumers and the high exposure potential of occupational cohorts, a thorough understanding of this issue is important. The current study utilizes an evidence-based approach to examine whether or not the available epidemiologic studies demonstrate a strong and consistent association between occupational exposure to gasoline and lymphatic/hematopoietic cancers. Among 67 epidemiologic studies initially identified, 54 were ranked according to specific criteria relating to the relevance and robustness of each study for answering the research question. The 30 highest-ranked studies were sorted into three tiers of evidence and were analyzed for strength, specificity, consistency, temporality, dose-response trends and coherence. Meta statistics were also calculated for each general and specific lymphatic/hematopoietic cancer category with adequate data. The evidence-based analysis did not confirm any strong and consistent association between occupational exposure to gasoline and lymphatic/hematopoietic cancers based on the epidemiologic studies available to date. These epidemiologic findings, combined with the evidence showing relatively low occupational benzene vapor exposures associated with gasoline formulations during the last three decades, suggest that current motor gasoline formulations are not associated with increased lymphatic/hematopoietic cancer risks related to benzene.

Concentration and age-dependent elimination kinetics of polychlorinated dibenzofurans in Yucheng and Yusho patients.

Half-life estimates of three polychlorodibenzofurans (PCDFs) were calculated using serial blood samples collected over a 15 to 19-year period. Blood fat PCDFs were modeled in eight individuals who were exposed to contaminated rice oil in Japan (Yusho, n = 5) and in Taiwan (Yucheng, n = 3). The elimination kinetics of PCDFs were concentration-dependent, with faster rates observed at higher concentrations and the apparent transition to slower rates occurring at about 1-3 ppb. Average half-lives of 1.1, 2.3, and 1.5 years above the transition concentration and 7.2, 5.7, and 3.5 years below it were estimated for 2,3,4,7,8-pentaCDF, 1,2,3,4,7,8-hexaCDF, and 1,2,3,4,6,7,8-heptaCDF, respectively. A positive linear correlation of half-life with age was observed for the combined group, with a rate of increase of 0.19, 0.12, and 0.05-year half-life per year of increase in age for penta-, hexa-, and hepta-CDF, respectively. The distinctly younger Yucheng patients exhibited far lower variability in half-lives and age-related trends that were quite consistent with the corresponding data on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) for younger persons exposed in the Seveso incident. These age- and concentration-dependent half-lives for PCDFs may have important risk assessment implications for estimating body burdens. The current study provides limited additional evidence that PCDFs, like TCDD, are more rapidly eliminated in younger individuals.

A physiologically based model for the ingestion of chromium(III) and chromium(VI) by humans.

A physiologically based model of human chromium kinetics has been developed, based on an existing physiologically based model of human body and bone growth (O'Flaherty, 1993, Toxicol. Appl. Pharmacol. 118, 16-29; 1995a, Toxicol. Appl. Pharmacol. 131, 297-308; 2000, Toxicol. Sci. 55, 171-18) and an existing physiologically based model of chromium kinetics in rats (O'Flaherty, 1996, Toxicol. Appl. Pharmacol. 138, 54-64). Key features of the adapted model, specific to chromium, include differential absorption of Cr(VI) and Cr(III), rapid reduction of Cr(VI) to Cr(III) in all body fluids and tissues, modest incorporation of chromium into bone, and concentration-dependent urinary clearance consistent with parallel renal processes that conserve chromium efficiently at ambient exposure levels. The model does not include a physiologic lung compartment, but it can be used to estimate an upper limit on pulmonary absorption of inhaled chromium. The model was calibrated against blood and urine chromium concentration data from a group of controlled studies in which adult human volunteers drank solutions generally containing up to 10 mg/day of soluble inorganic salts of either Cr(III) (chromic chloride, CrCl(3)) or Cr(VI) (potassium dichromate, K(2)Cr(2)O(7)) (Finley et al., 1997, Toxicol. Appl. Pharmacol. 142, 151-159; Kerger et al., 1996, Toxicol. Appl. Pharmacol. 141, 145-158; Paustenbach et al., 1996, J. Toxicol. Environ. Health 49, 453-461). In one of the studies, in which the chromium was ingested in orange juice, urinary clearance was observed to be more rapid than when inorganic chromium was ingested. Chromium kinetics were shown not to be dependent on the oxidation state of the administered chromium except in respect to the amount absorbed at these ambient and moderate-to-high exposures. The fraction absorbed from administered Cr(VI) compounds was highly variable and was presumably strongly dependent on the degree of reduction in the gastrointestinal tract, that is, on the amount and nature of the stomach contents at the time of Cr(VI) ingestion. The physiologically based model is applicable to both single-dose oral studies and chronic oral exposure, in that it adequately reproduced the time dependence of blood plasma concentrations and rates of urinary chromium excretion in one of the subjects who, in a separate experiment, ingested daily 4 mg of an inorganic Cr(VI) salt in 5 subdivided doses of 0.8 mg each for a total of 17 days. The high degree of variability of fractional absorption of Cr(VI) from the gastrointestinal tract leads to uncertainty in the assignment of a meaningful value to this parameter as applied to single Cr(VI) doses. To model chronic oral chromium exposure at ambient or moderately above-ambient levels, the physiologically based model in its present form should be usable with urinary clearance set to a constant value of 1-2 liters/day and the gastrointestinal absorption rate constants set at 0.25/day for Cr(III) and 2.5/day for Cr(VI). The model code is given in full in the Appendix.

Assessment of airborne exposure to trihalomethanes from tap water in residential showers and baths.

This study evaluates airborne concentrations of common trihalomethane (THM) compounds in bathrooms during showering and bathing in homes supplied with chlorinated tap water. Three homes in an urban area were selected, each having three bedrooms, a full bath, and approximately 1,000 square feet of living area. THMs were concurrently measured in tap water and air in the shower/bath enclosure and the bathroom vanity area using Summa canisters. Chloroform (TCM), bromodichloromethane (BDCM), and chlorodibromomethane (CDBM) were quantified using U.S. Environmental Protection Agency (EPA) Method TO-14. Air samples were collected prior to, during, and after the water-use event for 16 shower and 7 bath events. Flow rate and temperature were measured, but not controlled. The increase in average airborne concentration (+/- standard error) during showers (expressed as microg/m3 in shower enclosure or bathroom air per microg/L in water) was 3.3+/-0.4 for TCM, 1.8+/-0.3 for BDCM, and 0.5+/-0.1 for CDBM (n = 12), and during baths was 1.2+/-0.4 for TCM, 0.59+/-0.21 for BDCM, and 0.15+/-0.05 for CDBM (n = 4). The relative contribution of each chemical to the airborne concentrations was consistent for all shower and bath events, with apparent release of TCM > BDCM > CDBM. The results are therefore consistent with their relative concentration in tap water and their vapor pressures. When the shower findings for TCM are normalized for water concentration, flow rate, shower volume, and duration, the average exposure concentrations in these urban residences are about 30% lower than those reported by other investigators using EPA analytical methods. This difference is likely attributable primarily to greater air exchange rates in residential shower/bath stalls compared to more "airtight" laboratory shower chambers. This appears to be the first field study to thoroughly evaluate THM exposures from residential showers and baths, and can be used to validate previously published models of tap water volatile chemical transfer to indoor air.

In vitro reduction kinetics of hexavalent chromium in human blood.

This study examines time- and concentration-dependent changes in distribution of hexavalent chromium [Cr(VI)] and total chromium [Cr-(TOT)] in reconstituted human blood following addition of potassium dichromate. Fresh human blood stabilized with EDTA was obtained from human volunteers soon after meal ingestion and at 2.5 h after a light meal (herein defined as "2.5-h fasted" conditions). Cr(VI) spiked into plasma under 2.5-h fasting conditions at 3.0-12.5 micrograms/L was stable for several hours, indicating a lack of appreciable reductive capacity in isolated plasma. Spiked plasma following a recent meal exhibited immediate but variable reduction of Cr(VI) up to 300 micrograms/L. When the spiked plasma was recombined with the red blood cell (RBC) fraction, rapid reduction occurred in both the plasma and the RBC fractions based on measurement of Cr(VI) and Cr(TOT). The data indicate that plasma reduction capacity is enhanced by a recent meal, but may be overwhelmed at Cr(VI) concentrations between 2000 and 10,000 micrograms/L. These data also suggest that the RBC fraction apparently has the capacity to reduce Cr(VI) at concentrations in blood up to 15,000 micrograms/L, and that the rate of Cr(VI) uptake into RBCs may not exceed the rate of intracellular reduction at these concentrations.

Systemic uptake of chromium in human volunteers following dermal contact with hexavalent chromium (22 mg/L).

This study examined the systemic uptake of chromium in four human volunteers following three hours of contact with water containing hexavalent chromium [Cr(VI)] at a concentration of 22 mg/L. Volunteers were immersed below the shoulders in water at 91 +/- 2.5 degrees F. On the day prior to the experiment and for five days afterwards, samples of urine, plasma, and red blood cells (RBCs) were collected and analyzed for total chromium. Red blood cell chromium concentrations were used as a specific biomarker for systemic uptake of Cr(VI). Although total chromium concentrations in RBCs and plasma increased relative to historical background concentrations on the day of exposure, no sustained elevation of chromium concentrations was observed in RBCs or plasma of the volunteers tested. Since absorption of chromium in the hexavalent state would result in the irreversible binding of Cr(VI) to hemoglobin within the RBC (manifested as a sustained elevation of total chromium concentrations in the RBC), the pattern of blood uptake and urinary excretion observed was consistent with uptake and distribution of chromium in the trivalent state. Small increases were observed in the concentration of total chromium in urine within 48 h of exposure, indicating that some trivalent chromium [Cr(III)] may have penetrated the skin at a rate of about 3.3 x 10(-5) to 4.1 x 10(-4) micrograms/ cm2-h. In short, the data indicated that a 3-h contact with Cr(VI) at concentrations in water plausible for environmental exposure (e.g., swimming) was not expected to result in systemic uptake of measurable amounts of Cr(VI), although a small quantity of Cr(VI) may have penetrated the skin where it was subsequently reduced to Cr(III) prior to systemic uptake.

Estimates of the chromium(VI) reducing capacity in human body compartments as a mechanism for attenuating its potential toxicity and carcinogenicity.

Estimates of the overall reducing capacity of hexavalent chromium(VI) in some human body compartments were made by relating the specific reducing activity of body fluids, cell populations or organs to their average volume, number, or weight. Although these data do not have absolute precision or universal applicability, they provide a rationale for predicting and interpreting the health effects of chromium(VI). The available evidence strongly indicates that chromium(VI) reduction in body fluids and long-lived non-target cells is expected to greatly attenuate its potential toxicity and genotoxicity, to imprint a threshold character to the carcinogenesis process, and to restrict the possible targets of its activity. For example, the chromium(VI) sequestering capacity of whole blood (187-234 mg per individual) and the reducing capacity of red blood cells (at least 93-128 mg) explain why this metal is not a systemic toxicant, except at very high doses, and also explain its lack of carcinogenicity at a distance from the portal of entry into the organism. Reduction by fluids in the digestive tract, e.g. by saliva (0.7-2.1 mg/day) and gastric juice (at least 84-88 mg/day), and sequestration by intestinal bacteria (11-24 mg eliminated daily with feces) account for the poor intestinal absorption of chromium(VI). The chromium(VI) escaping reduction in the digestive tract will be detoxified in the blood of the portal vein system and then in the liver, having an overall reducing capacity of 3300 mg. These processes give reasons for the poor oral toxicity of chromium(VI) and its lack of carcinogenicity when introduced by the oral route or swallowed following reflux from the respiratory tract. In terminal airways chromium(VI) is reduced in the epithelial lining fluid (0.9-1.8 mg) and in pulmonary alveolar macrophages (136 mg). The peripheral lung parenchyma has an overall reducing capacity of 260 mg chromium(VI), with a slightly higher specific activity as compared to the bronchial tree. Therefore, even in the respiratory tract, which is the only consistent target of chromium(VI) carcinogenicity in humans (lung and sinonasal cavities), there are barriers hampering its carcinogenicity. These hurdles could be only overwhelmed under conditions of massive exposure by inhalation, as it occurred in certain work environments prior to the implementation of suitable industrial hygiene measures.

Ingestion of chromium(VI) in drinking water by human volunteers: absorption, distribution, and excretion of single and repeated doses.

This study examines the magnitude of hexavalent chromium [Cr(VI)] absorption, distribution, and excretion following oral exposure to 5 and 10 mg Cr(VI)/L in drinking water administered as a single bolus dose (0.5 L swallowed in 2 min) or for 3 d at a dosage of 1 L/d (3 doses of 0.33 L each day, at 6-h intervals). Adult male volunteers ingested deionized water containing various concentrations of potassium chromate, and samples of urine, plasma, and red blood cells (RBCs) were collected and analyzed for total chromium throughout the studies. In the bolus dose studies, a fairly consistent pattern of urinary chromium excretion was observed, with an average half life of about 39 h. However, 4-d total urinary chromium excretion and peak concentrations in urine and blood varied considerably among the 5 volunteers. Studies of repeated exposure to smaller volumes ingested at a more gradual rate (i.e., 0.33 L over 5-15 min) showed similar urinary chromium excretion patterns but generally lower chromium uptake/excretion. Given that sustained elevations in RBC chromium levels provide a specific indication of chromium absorption in the hexavalent state, these data suggest that virtually all (> 99.7%) of the ingested Cr(VI) at 5 and 10 mg Cr(VI)/L was reduced to Cr(III) before entering the blood-stream. The interindividual differences in total chromium uptake and excretion are plausibly explained by ingestion of appreciable doses on an empty stomach, which likely results in the formation of well-absorbed Cr(III) organic complexes in gastrointestinal tissues and possibly the blood. The lack of any clinical indications of toxicity in the volunteers and the patterns of blood uptake and urinary excretion of chromium are consistent with a predominant uptake of Cr(III) organic complexes [derived from Cr(VI)] that are excreted more slowly than inorganic forms of Cr(III). Therefore, it appears that the endogenous reducing agents within the upper gastrointestinal tract and the blood provide sufficient reducing potential to prevent any substantial systemic uptake of Cr(VI) following drinking-water exposures at 5-10 mg Cr(VI)/L. Based on these data, the chemical environment in the gastrointestinal tract and the blood is effective even under relative fasting conditions in reducing Cr(VI) to one or more forms of Cr(III).

Human ingestion of chromium (VI) in drinking water: pharmacokinetics following repeated exposure.

Regulatory agencies have established safe drinking water concentrations for hexavalent chromium [Cr(VI)] based in part on the presumed capability of human gastric juices to rapidly reduce Cr(VI) to nontoxic trivalent chromium [Cr(III)] prior to systemic absorption. This study examines dose-related pharmacokinetics in humans following repeated oral exposure to Cr(VI) in drinking water. In particular, we sought to examine whether plausible drinking water exposures to Cr(VI) caused a sustained increase in red blood cell chromium levels, a specific marker for systemic uptake of Cr(VI). Adult male volunteers ingested a liter (in three volumes of 333 ml, at approximate 6-hr intervals) of deionized water containing Cr(VI) concentrations ranging from 0.1 to 10.0 mg/liter. Samples of urine, plasma, and red blood cells were collected and analyzed for chromium. A dose-related increase in urinary chromium excretion was observed in all volunteers. Red blood cell and plasma chromium concentrations became elevated in certain individuals at the highest doses. The RBC chromium profiles suggest that the ingested Cr(VI) was reduced to Cr(III) before entering the bloodstream, since the chromium concentration in the RBCs dropped rapidly postexposure. These findings suggest that the human gastrointestinal tract has the capacity to reduce ingested Cr(VI) following ingestion of up to 1 liter of water containing 10.0 mg/liter of Cr(VI), which is consistent with USEPA's position that the Cr(VI) drinking water standard of 0.10 mg Cr(VI)/liter is below the reductive capacity of the stomach.

Observation of steady state in blood and urine following human ingestion of hexavalent chromium in drinking water.

The uptake and elimination of Cr(VI) in a male volunteer who ingested 2 L/d of water containing 2 mg/L for 17 consecutive days was measured. Total chromium was measured in urine, plasma, and red blood cells (RBCs) for 4 d prior to and 2 wk after dosing (34 d total). The estimated bioavailability (2%) and the plasma elimination half-life (36 h) were consistent with our previous studies of Cr(VI) ingestion in humans. Steady-state chromium concentrations in urine and blood were achieved after 7 d of Cr(VI) ingestion. Both plasma and red blood cell (RBC) chromium concentrations returned rapidly to background levels within a few days after cessation of dosing. Since the concentration of chromium in the RBC should not decrease quickly if the chromium had entered the RBC as Cr(VI), these data support our prior work suggesting that concentrations of 10 mg Cr(VI)/L or less in drinking water of exposed humans appears to be completely reduced to Cr(III) prior to systemic distribution. Clinical chemistry data indicate that no toxicity occurred.

Absorption and elimination of trivalent and hexavalent chromium in humans following ingestion of a bolus dose in drinking water.

These studies investigate the magnitude and valence state of chromium absorbed following plausible drinking water exposures to chromium(VI). Four adult male volunteers ingested a single dose of 5 mg Cr (in 0.5 liters deionized water) in three choromium mixtures: (1) Cr(III) chloride (CrCl3), (2) potassium dichromate reduced with orange juice (cr(III)-OJ); and (3) potassium dichromate [Cr(VI)]. Blood and urine chromium levels were followed for 1-3 days prior to and up to 12 days after ingestion. The three mixtures showed quite different pharmacokinetic patterns. CrCl3 was poorly absorbed (estimated 0.13% bioavailability) and rapidly eliminated in urine (excretion half-life, approximately 10 hr), whereas Cr(III)-OJ was absorbed more efficiently (0.60% bioavailability) but more slowly (half-life, approximately 17 hr), and Cr(VI) had the highest bioavailability (6.9%) and the longest half-life (approximately 39 hr). All three chromium mixtures caused temporary elevations in red blood cell (RBC) and plasma chromium concentrations, but the magnitude and duration of elevation showed a clear trend (Cr(VI) > Cr(III)-OJ > CrCl3). The data suggest that nearly all the ingested Cr(VI) was reduced to Cr(III) before entering the bloodstream based on comparison to RBC and plasma chromium patterns in animals exposed to high doses of Cr(VI). These findings support our prior work which suggests that water-soluble organic complexes of Cr(III) formed during the reduction of Cr(VI) in vivo explain the patterns of blood uptake and urinary excretion in humans at drinking water concentrations of 10 mg/liter or less.

Measurement of DNA-protein cross-links in human leukocytes following acute ingestion of chromium in drinking water.

Increased DNA-protein cross-linking (DPX) in circulating leukocytes has been proposed as a potential biomarker for exposure and genotoxic damage caused by inhalation of certain reactive chemicals, such as hexavalent chromium [Cr(VI)]. This study was designed to determine whether ingestion of a single dose of potassium dichromate alone [Cr(VI)] or potassium dichromate fully reduced to Cr(III) with orange juice (prior to ingestion) causes an increase in DPX of circulating leukocytes in humans. Four adult male volunteers ingested a bolus dose of 5000 micro chromium in a 0.51 volume of water (10 p.p.m.), and blood samples were collected at 0, 60, 120, 180 and 240 min afterwards for analysis of DPX formation in circulating leukocytes. Results were compared to each person's own background concentration of DPX in leukocytes. Blood and urine samples were also collected for up to 2 weeks following the dose to examine the pattern of uptake and excretion of chromium. The results showed that there was no significant change in DPX observed following either Cr(VI) or Cr(III) ingestion, even though blood and urine chromium measurements indicated systemic uptake of a substantial fraction of the ingested chromium. Since Cr(III) does not possess DPX-inducing properties while Cr(VI) does, these results suggest that the Cr(VI) was reduced to Cr(III) intragastrically prior to absorption or that the amount of Cr(VI) absorbed into the blood was insufficient to produce DPX. These results are consistent with prior research that indicated that DPX would not occur following exposure to Cr(VI) except at very high doses.

Refined exposure assessment for ingestion of tapwater contaminated with hexavalent chromium: consideration of exogenous and endogenous reducing agents.

Laboratory studies were conducted to determine how rapidly and completely chromium (VI) [Cr(VI)] is reduced upon contact with common beverages mixed with tapwater. Studies were performed for five common beverages (coffee, tea, orange juice, Kool Aid, and powdered lemonade) spiked with either 10 or 50 mg Cr(VI)/l. The concentrations of Cr(VI) were measured at several time intervals for up to four hours. It was demonstrated that each of these beverages had the capacity to reduce a concentration of > or = 8 mg Cr(VI)/l within a 15-minute time frame, and that continued monitoring of the beverages revealed greater reduction of the Cr(VI). These findings are consistent with the observation that many foods and beverages, as well as endogenous body fluids such as saliva and gastric juices, are capable of reducing substantial quantities of Cr(VI) to Cr(III). Our exposure assessment shows that the estimated high-end ingested dose of Cr(VI) from tapwater at both 1 and 5 mg Cr(VI)/l is generally two to three orders of magnitude below doses shown to have no adverse health effect in animal studies. When considered in conjunction with studies demonstrating that the reductive capacity of gastric juices may exceed 50 mg Cr(VI) daily, these observations suggest that little or no Cr(VI) is likely to be absorbed orally at a reasonable water concentration of Cr(VI), since tapwater is bright yellow at 5 mg Cr(VI)/l.

Assessment of airborne hexavalent chromium in the home following use of contaminated tapwater.

Field studies were conducted to estimate the plausible uptake of hexavalent chromium [Cr(VI)] aerosols inhaled during indoor residential use of a shower or an evaporative cooler supplied with water containing Cr(VI). In the evaporative cooler study, water concentrations of 20 mg Cr(VI)/L did not produce an increased concentration of airborne Cr(VI). The indoor air concentration of Cr(VI), measured over 24 hours of use, was 0.3-2.7 ng/m3, about the same as the concurrent outdoor concentrations. In the shower study, the average airborne concentrations of Cr(VI) aerosols at breathing-zone height ranged from 87 to 324 ng Cr(VI)/m3 when the water concentration of Cr(VI) was 0.89 to 11.5 mg/L. The Cr(VI) concentration in air was correlated directly to water concentration. The lifetime average daily doses and incremental cancer risk estimates corresponding to 30-year residential exposures were calculated using the measurements in this study and published exposure guidelines. The plausible upperbound lifetime cancer risk associated with continuous exposure to "background" Cr(VI) in outdoor air was estimated at 6.9 per million for a person exposed during ages 0-30, and 4.0 per million for ages 30-60. Similarly estimated upperbound cancer risks due to inhalation of shower aerosols from water containing 2-10 mg Cr(VI)/L over the same exposure period ranged from 0.9 to 5.5 per million. Our calculations demonstrate that shower aerosols do not contribute appreciably to background Cr(VI) exposures and risks, even at concentrations exceeding 2 mg Cr(VI)/L, which exhibit a discernible and unaesthetic yellow color that may limit the potential for long-term exposures of this type. We conclude that exposure to indoor aerosols from water containing Cr(VI) is unlikely to create a health hazard at concentrations up to 10 mg Cr(VI)/L. Furthermore, these aerosol measurements may be relevant to estimating airborne exposures to other nonvolatile chemicals.

Antagonism of bromobenzene-induced hepatotoxicity by the alpha-adrenoreceptor blocking agents phentolamine and idazoxan: role of hypothermia.

A recent study from our laboratory revealed that cotreating mice with the alpha-adrenoreceptor antagonists phentolamine and idazoxan markedly diminished bromobenzene-induced hepatotoxicity. Subsequent studies also revealed that such cotreatment does not alter the pharmacokinetic disposition of bromobenzene in mice nor its bioactivation to reactive metabolites. In the present study, the possible role of hypothermia in the phentolamine antagonism of bromobenzene-induced hepatotoxicity was investigated. Bromobenzene alone caused a significant, dose-related hypothermia. The high dosage regimen (10 mg/kg per dose) of phentolamine or idazoxan that had been found to be hepatoprotective in earlier studies potentiated this hypothermia and more than doubled the net decrease in core body temperature experienced by the animals. Placing mice receiving bromobenzene in an environment with an ambient temperature of 10 degrees C likewise increased the hypothermia experienced by animals receiving bromobenzene. The magnitude of the net change in core body temperature elicited by exposure to cold was similar to but slightly less than the net change produced by cotreatment with either alpha-adrenoreceptor antagonist and the magnitude of the hepatoprotection this procedure provided against bromobenzene hepatotoxicity was equivalent to that observed with phentolamine cotreatment. In contrast, a lower dosage regimen of either adrenoreceptor antagonist (2.5 mg/kg per dose) resulted in no additional hypothermia yet still produced a near maximal antagonism of bromobenzene-induced hepatotoxicity. Further, increasing the ambient temperature to 30 degrees C completely reversed the phentolamine-induced (10 mg/kg per dose) increase in hypothermia, but did not affect phentolamine's antagonism of the bromobenzene-induced changes in hepatic glutathione levels, serum alanine aminotransferase activity, or 24-hr mortality. Therefore, we conclude that while the hepatoprotective intervention of phentolamine can be mimicked by an exposure to cold that results in hypothermia, it is clear that alpha-adrenergic antagonists diminish the hepatotoxicity induced by bromobenzene by a mechanism that is independent of hypothermia.

Comparison of human and mouse liver microsomal metabolism of bromobenzene and chlorobenzene to 2- and 4-halophenols.

Bromobenzene is metabolized by hepatic microsomes to two different epoxide intermediates, which then rearrange to form either ortho- or para-bromophenol. A rapid and sensitive technique utilizing HPLC with electrochemical detection is presented for the quantitation of these primary bromobenzene metabolites. This analytical procedure allows selective quantitation of phenolic products of microsomal metabolism without prior extraction. Application of this assay method to the microsomal metabolism of bromobenzene and chlorobenzene revealed that three important differences exist between mice and humans regarding the metabolism of these compounds. First, human liver microsomes have a greater affinity for halobenzene biotransformation to the hepatotoxic 3,4-epoxide, as indicated by the approximately 2-fold lower Km values for para-halophenol production compared with mouse liver microsomes. Second, human liver microsomes produce the hepatotoxic metabolite at a 2-fold greater rate than mouse liver microsomes, relative to the microsomal cytochrome P-450 content. And third, human liver microsomes produce less of the nonhepatotoxic ortho-halophenol metabolites at Vmax resulting in an average ratio of the hepatotoxic: nonhepatotoxic metabolite production that is 3.5 times higher than the ratio for B6C3F1 mice. These results indicate humans preferentially metabolize halobenzenes through the hepatotoxic 3,4-epoxide pathway, suggesting that humans may be more susceptible than mice to halobenzene-induced hepatotoxicity.

Antagonism of bromobenzene-induced hepatotoxicity by phentolamine: evidence for a metabolism-independent intervention.

A previous study has revealed that phentolamine markedly antagonizes the bromobenzene-induced hepatotoxicity and lethality in B6C3F1 mice. One potential mechanism by which phentolamine may diminish the bromobenzene-induced hepatotoxicity is by a direct or indirect interference with the metabolism of bromobenzene to toxic metabolites. In the present study, phentolamine cotreatment failed to alter the elimination of bromobenzene from serum or the distribution of bromobenzene to liver. This suggests that phentolamine cotreatment does not indirectly interfere with bromobenzene bioactivation secondary to changes in bromobenzene absorption, distribution, or elimination. Further, a phentolamine concentration 10- to 20-fold greater than those measured in vivo failed to alter the in vitro metabolism of bromobenzene to its ortho- and para-phenolic metabolites. It is believed that para-bromophenol represents the rearrangement product of the hepatotoxic 3,4-epoxide and that ortho-bromophenol is a product of the nonhepatotoxic 2,3-epoxide pathway. Thus, it appears that phentolamine does not antagonize bromobenzene-induced hepatotoxicity by inhibiting the formation of hepatotoxic intermediates, nor by enhancing metabolism via the nonhepatotoxic pathway. On the basis of these studies, we conclude that phentolamine antagonism of bromobenzene-induced hepatotoxicity occurs through a mechanism independent of bromobenzene bioactivation.

Antagonism of bromobenzene-induced hepatotoxicity by the alpha-adrenergic blocking agents, phentolamine and idazoxan.

The coadministration of phentolamine, an alpha-adrenoreceptor antagonist, was found to be effective in antagonizing the hepatotoxicity produced by bromobenzene in B6C3F1 mice. Multiple doses of phentolamine, administered in dosages of 10 mg/kg, attenuated almost completely the acute lethality resulting from a 0.5 ml/kg dosage of bromobenzene. Consistent with this decline in lethality, the coadministration of phentolamine significantly altered the magnitude of hepatocellular necrosis, the elevation of serum alanine aminotransferase activity, and the glutathione depression normally produced by this dose of bromobenzene. These protective effects were not limited to phentolamine. Idazoxan, an adrenergic antagonist more specific for alpha 2-receptors, was equally effective in antagonizing the bromobenzene-induced hepatotoxicity. Measurements of serum catecholamine levels revealed that the administration of hepatotoxic doses of bromobenzene elevates serum epinephrine levels. Furthermore, the phentolamine antagonism of the bromobenzene hepatotoxicity could be correlated to elevated serum epinephrine levels in both a temporal and dose-dependent manner. Although the mechanism of the phentolamine antagonism remains to be established, one promising hypothesis involves its prevention of an epinephrine-mediated compromise in the glutathione-dependent detoxification of bromobenzene.

An assay for phentolamine using high performance liquid chromatography with electrochemical detection.

A new method is presented for the detection of phentolamine by high performance liquid chromatography with electrochemical detection. The electrochemical detector was used in the oxidative mode at +900 mV potential versus Ag/AgCl reference. The on-column detection limit for phentolamine using this method was 3 ng, and detector response was linear for 3-1000 ng injected on column. The coefficient of variation for replicate injections was 2.4%. The measurement of phentolamine in biological samples was accomplished using yohimbime as the internal standard; retention time for yohimbine was 3.0 min while phentolamine eluted at 4.75 min. Biological samples were buffered to pH 9.2 and extracted with diethyl ether, followed by back extraction into 0.1 N HCl. The extraction efficiency for this method was 99.4% for phentolamine in serum and 59.3% in liver tissue. The detection limit for phentolamine was 5 ng/ml for 1.0-ml serum samples, and was 10 ng/ml for 1.0-ml liver homogenate samples. The disappearance of phentolamine from serum and liver after administration of a single ip dose of phentolamine to mice was determined using this method. Absorption from the ip route was rapid, with peak phentolamine concentrations achieved in 15 min or less. The elimination half-life of phentolamine in serum was approximately 50 min and was paralleled by disappearance of phentolamine in the liver.