Methylmercury distribution, metabolism, and neurotoxicity in the mouse brain

Methylmercury distribution, biotransformation, and neurotoxicity in the brain of male Swiss albino mice were investigated. Mice were orally dosed with [203 Hg]methylmercury chloride (10 mg/kg) for 1 to 9 days. Methylmercury was evenly distributed among the posterior cerebral cortex, subcortex, brain stem, and cerebellum. The The anterior cerebral cortex had a significantly higher methylmercury concentration than the rest of the brain. The distribution of methylmercury's inorganic mercury metabolite was found to be uneven in the brain. The pattern of distribution was cerebellum greater than brain stem greater than subcortex greater than cerebral cortex. The order of the severity of histological damage was cerebral cortex greater than cerebellum greater than subcortex greater than brain stem. There was no correlation between methylmercury distribution in the brain and structural brain damage. However, there was a relationship between the distribution of methylmercury's inorganic mercury metabolite and structural damage in the anterior cerebral cortex (positive correlation) and the anterior subcortex (negative correlation). There was also a positive correlation between the fraction of methylmercury's metabolite of the total mercury present and structural brain damage in the anterior cerebral cortex. This study suggests that biotransformation may have a role in mediating methylmercury neurotoxicity.     

Degradation of methylmercury by selenium

When methylmercury was incubated in the presence of selenite and reduced glutathione (GSH), the mercury which was extracted into benzene under acidic condition decreased gradually with the elapse of time. This decrease was due to the cleavage of mercury-carbon bond of methylmercury. The reaction did not proceed when selenite or GSH was singly added to the reaction mixture. L-Cysteine, 2-mercaptoethanol and sodium sulfide in place of GSH also were effective for decomposition of methylmercury in combination with selenite, but oxidized glutathione (GSSG) and L-cystine were not. This suggests that reduction of selenite is needed for the degradation of methylmercury. Thus, the effect of reduced metabolites of selenite produced by GSH was investigated. Glutathione selenotrisulfide (GSSeSG) requierd GSH for the degradation of methylmercury, whereas H₂Se possessed a strong activity even in the absence of GSH. This may indicate that H₂Se is involved directly in the conversion of methylmercury to inorganic mercury. This phenomenon found in $\text{in vitro}$ experiments is discussed in relation to the biotransformation of methylmercury.     

Accumulation of mercury in estuarine food chains

To understand the accumulation of inorganic mercury and methylmercury at the base of the estuarine food chain, phytoplankton (Thalassiosira weissflogii) uptake and mercury speciation experiments were conducted. Complexation of methylmercury as methylmercury-bisulfide decreased the phytoplankton uptake rate while the uptake rate of the methylmercury-cysteine and -thiourea complexes increased with increasing complexation by these ligands. Furthermore, our results indicated that while different ligands influenced inorganic mercury/methylmercury uptake by phytoplankton cells, the ligand complex had no major influence on either where the mercury was sequestered within the phytoplankton cell nor the assimilation efficiency of the mercury by copepods. The assimilation efficiency of inorganic mercury/methylmercury by copepods and amphipods feeding on algal cells was compared and both organisms assimilated methylmercury much more efficiently; the relative assimilation efficiency of methylmercury to inorganic mercury was 2.0 for copepods and 2.8 for amphipods. The relative assimilation is somewhat concentration dependent as experiments showed that as exposure concentration increased, a greater percentage of methylmercury was found in the cytoplasm of phytoplankton cells, resulting in a higher concentration in the copepods feeding on these cells. Additionally, food quality influenced assimilation by invertebrates. During decay of a T. weissflogii culture, which served as food for the invertebrates, copepods were increasingly less able to assimilate the methylmercury from the food, while even at advanced stages of decay, amphipods were able to assimilate mercury from their food to a high degree. Finally, fish feeding on copepods assimilated methylmercury more efficiently than inorganic mercury owing to the larger fraction of methylmercury found in the soft tissues of the copepods.     

Phenobarbital protection against methyl mercury neophrotoxicity.

Phenobarbital injections to rats given a low oral dose level of methl mercury for 2 or 4 wk decreased methyl mercury-induced ultrastructural alterations in kidney proximal tubule cells, increased urinaryexcretion of inorganic mercury and increased blood concentrations of methylmercury. These effects were not seen after 2 wk of treatment but were highly significant after 4 wk.     

汞在新建水库食物网中生物累积与风险评价研究进展

汞是唯一参与全球循环的液态重金属。1974年,自美国学者Smith首次报道水库中鱼类总汞含量高于邻近自然湖泊以来,水库中鱼类汞升高的风险成为新建水库环境影响评价中的重要内容之一。汞在水库生态系统生物组分和非生物组分中含量升高的现象先后在世界各国报道,包括加拿大、美国、芬兰、泰国和巴西等。通过对系列的野外研究进行回顾,表明了水库形成后生态系统中汞的甲基化过程发生了变化。水库形成对汞在食物网中的鱼类、底栖生物、浮游生物的累积产生影响。水库中汞的生物累积、迁移转化主要与被淹没土壤和植物腐解过程有着直接或间接的关系。水库形成后,总汞、甲基汞和甲基汞比例在生态系统食物网各组分中的变化并不一致。蓄水后,水体中总汞变化较小,甲基汞和甲基汞比例上升明显;浮游生物尤其是浮游动物中总汞升高,但甲基汞和甲基汞比例升高更为明显;与浮游动物类似,底栖水生昆虫中总汞升高,甲基汞和甲基汞比例升高也更为明显;鱼类作为食物网顶级消费者,甲基汞比例一般在80%以上,在水库形成后鱼类总汞和甲基汞均明显升高,但甲基汞比例变化已经不大。这些变化揭示了水库形成后甲基汞在食物网传递的两个主要可能途径,一是微型生物食物网。通过悬浮颗粒物、浮游植物、浮游动物这一环节,甲基汞和甲基汞比例有明显的增加。第二个途径是底层生物食物网。通过悬浮颗粒物、细菌、碎屑食性底栖水生昆虫、肉食型底栖水生昆虫环节,甲基汞和甲基汞比例明显增加。这两种途径均能导致以水生昆虫、小鱼、甲壳类等为食的肉食性鱼类汞含量增加。水库形成后,生态系统中汞的甲基化发生了明显的"加速"过程。这种"加速"过程最直接的因素是成库后大量土壤淹没使得汞的甲基化平衡被打破。这个过程主要有两方面的影响。一方面是直接影响,被淹没土壤和植被在腐解过程中主动或被动地将甲基汞释放到水库生态系统中;另一方面是间接影响,被淹没土壤和植被的腐解使水库底部形成厌氧环境,有利于无机汞从被淹没土壤和植被中溶出,为甲基化反应提供充裕的、可供甲基化的无机汞,同时腐解产生的大量营养物质为微生物提供丰富食物来源,使硫酸盐还原菌大量繁殖,促进无机汞的甲基化。在我国,有关汞在新建水库食物网中生物累积和风险评价的研究有待进一步加强。     

Temperature and species differences in susceptibility of kidney cell cultures to mercury toxicity

The effect of temperature on inorganic mercury toxicity was investigated using kidney tissue culture systems. The relative susceptibility of rabbit (homeothermic) kidney to mercury intoxication was compared to that of Coho salmon (poikilothermic) kidney to mercury intoxication was compared to that of Coho salmon (poikilothermic) kidney over temperature ranges consistent with the habitat of each of the two species. It was demonstrated that susceptibility to mercury toxicity is species dependent; that is, the rabbit kidney cells tolerated higher mercury concentrations in the medium than did the fish-derived cells. Within a given species, susceptibility to mercury toxicity was temperature dependent. Decreasing the temperature increased the toxicity of mercury to cultures of rabbit kidney cells, whereas decreasing temperatures decreased the effect of mercury toxicity on the salmon kidney cells. As a consequence, fish taken from arctic waters are liable to be more toxic when introduced into mammalian food chains. Albumin was shown to act as a protective agent in vitro against inorganic mercury toxicity.     

Accumulation of methylmercury and inorganic mercury in the brain

Differences in metabolism between different mercury species are well recognized. Conclusions that only a minor demethylation of methylmercury takes place in the brain are based primarily on results from short term studies. Results from a number of studies on humans exposed for many years to methylmercury have shown high concentrations of inorganic mercury in the brain in relation to total mercury. Similar evidence is available from studies on monkeys exposed for several years to methylmercury. The results indicate that a significant accumulation of inorganic mercury takes place with time despite the fact that the demethylation rate is slow. Differences in biological halftimes between different mercury species will explain the results. Some data do still need confirmation using different analytical methods. There is reason to believe that the one-compartment model for methyl mercury cannot be used without reservations. Inorganic mercury has a complicated metabolism. After exposure to metallic mercury vapor, inorganic mercury, probably bound to selenium, accumulates in the brain. A fraction of the mercury is excreted, with a long biological halftime. Studies on rats and monkeys indicate that inorganic mercury penetrates the blood-brain barrier only to a very limited-extent.     

Effects of complexing agents on the distribution of Hg(II) species provided by food to starfish Leptasterias polaris

Abstract

Mature starfish Leptasterias polaris were exposed to labelled mercury (II) species via food contaminated at a level of 5.0 μg g^?1. The distribution of inorganic Hg and methylmercury (MeHg) in starfish organs and tissues and the effect of a series of complexing agents on mercury translocation between organs and tissues were examined over a 24-h period. The distribution of mercury species in coelomic fluid components, ammonia excretion rate and mercury excretion were also measured. The highest concentrations were observed in the stomach (the source organ) and in pyloric caecum (up to 0.32 μg g^?1 wet weight for inorganic Hg and 0.22 μg g^?1 for MeHg). Concentrations of MeHg in gonads ranged from ≤ 0.01 to 0.08 μg g^?1 whereas concentrations of inorganic Hg never exceeded 0.06 μg g^?1. In all studied cases, mercury concentration was very low the coelomic fluid (≤ 0.01 μg g^?1). The short-term distribution of Hg species via contaminated food in starfish L. polaris seems to be controlled by the haemal system, a primitive circulatory system responsible for the transport of soluble nutrients from the digestive track towards organs and tissues, but a possible role of the coelomic fluid can not be excluded. Very low Hg contents were observed in gonads and in the coelomic fluid which fills the general cavity. Except for mercaptoethanol (merOH) and dimercaptosuccinic acid (DMSA), the addition of complexing agents to the food had little effect on the distribution of Hg species. MerOH appeared as an efficient carrier for methylmercury transport through the digestive system. DMSA enhanced the translocation of inorganic mercury from stomach and pyloric caecum toward external tissues and markedly increased its excretion.     

The accumulation of organic mercury from sea water by the plaice, Pleuronectes platessa L

The accumulation of organic mercury from sea water by plaice eggs, larvae and adult fish has been studied using CH₃²⁰³HgCl as a tracer. The isotope was rapidly accumulated, the largest fraction being taken up by muscle tissue. High concentration factors were attained by many internal organs, particularly blood, spleen, and kidney. Longer biological half-times than previous estimates with ²⁰³HgCl₂ were obtained: the possible consequences of inorganic mercury accumulated from sea water being excreted at the rate for methylmercury have been calculated.     

Temperature and species differences in susceptibility of kidney cell cultures to mercury toxicity

Summary The effect of temperature on inorganic mercury toxicity was investigated using kidney tissue culture systems. The relative susceptibility of rabbit (homeothermic) kidney to mercury intoxication was compared to that of Coho salmon (poikilothermic) kidney over temperature ranges consistent with the habitat of each of the two species. It was demonstrated that susceptibility to mercury toxicity is species dependent; that is, the rabbit kidney cells tolerated higher mercury concentrations in the medium than did the fish-derived cells. Within a given species, susceptibility to mercury toxicity was temperature dependent. Decreasing the temperature increased the toxicity of mercury to cultures of rabbit kidney cells, whereas decreasing temperatures decreased the effect of mercury toxicity on the salmon kidney cells. As a consequence, fish taken from arctic waters are liable to be more toxic when introduced into mammalian food chains. Albumin was shown to act as a protective agent in vitro against inorganic mercury toxicity. Research was supported in part by the University of Victoria Faculty Grant No. 08-869 and a Medical Staff Research and Education Fund Grant from Wayne County General Hospital, Eloise, Michigan.     

Change in permeability of liposomes caused by methylmercury and inorganic mercury

The effects of two mercurial compounds, methylmercury and inorganic mercury, on lipids were examined by measuring permeability change of lipid bilayer, liposome. Both decrease in the cholesterol content and increase in the content of unsaturated fatty acid moieties in the lipid bilayers, augmented to susceptibility of the liposomes to the mercurial compounds. Inorganic mercury and methylmercury disrupted the lipid membrane to essentially the same extent. The influence on the permeability seems to be specific for mercury compounds. The significant increase in the permeability of some liposomal preparation noted even at the mercurial concentration of 10(-7) M strongly suggests that lipid in biomembrane could be one of the primary targets of these toxic substances.     

Toenail mercury concentration as a biomarker of methylmercury exposure

The aim of the study was to assess the value of toenail mercury as an alternative biomarker of methylmercury exposure compared with blood and hair. Blood, hair and toenail total mercury concentrations were determined simultaneously in a southern urban sea n = 35 and an eastern rural lake n = 37 group and separately in a central Finnish rural lake n = 39 group. A questionnaire based index was used for estimating frequency of exposure taking into account high vs low mercury fish. Total mercury concentration was determined by cold vapour atomic absorption spectrophotometry. The mean Fish Consumption Frequency Index varied from 4.7 to 9.9 on a scale of 1-20. The blood, hair and toenail mercury mean concentrations ranged from 2.9 to 14.6 g l-1, 0.45 to 1.57 mg kg-1 and 0.20 to 0.54 mg kg-1, respectively. In the combined southern and eastern groups n = 72 sampled simultaneously, the correlations between blood and hair mercury were r = 0.92 and that of blood and toenails r = 0.78 p 0.0001 . In the central Finnish group the correlations were more moderate. In the three groups all three biomarkers correlated highly with the fish consumption index, r = 0.43-0.76 p 0.0001 . Men consumed high mercury fish more frequently than women, 8.6 vs 6.6 n.s. . The mean mercury levels of blood and hair were two fold, but toenail mercury levels were only 30 higher in men compared with those of the women. The relative sensitivity slope of the sources decreased in the order, blood hair toenails. In conclusion, toenails, an easily accessible tissue for the estimation of methylmercury exposure, have been shown to be closely correlated with the well established samples for biomarkers, viz. blood and hair mercury.     

Toenail mercury concentration as a biomarker of methylmercury exposure

The aim of the study was to assess the value of toenail mercury as an alternative biomarker of methylmercury exposure compared with blood and hair. Blood, hair and toenail total mercury concentrations were determined simultaneously in a southern urban sea n = 35 and an eastern rural lake n = 37 group and separately in a central Finnish rural lake n = 39 group. A questionnaire based index was used for estimating frequency of exposure taking into account high vs low mercury fish. Total mercury concentration was determined by cold vapour atomic absorption spectrophotometry. The mean Fish Consumption Frequency Index varied from 4.7 to 9.9 on a scale of 1-20. The blood, hair and toenail mercury mean concentrations ranged from 2.9 to 14.6 g l-1, 0.45 to 1.57 mg kg-1 and 0.20 to 0.54 mg kg-1, respectively. In the combined southern and eastern groups n = 72 sampled simultaneously, the correlations between blood and hair mercury were r = 0.92 and that of blood and toenails r = 0.78 p 0.0001 . In the central Finnish group the correlations were more moderate. In the three groups all three biomarkers correlated highly with the fish consumption index, r = 0.43-0.76 p 0.0001 . Men consumed high mercury fish more frequently than women, 8.6 vs 6.6 n.s. The mean mercury levels of blood and hair were two fold, but toenail mercury levels were only 30 higher in men compared with those of the women. The relative sensitivity slope of the sources decreased in the order, blood hair toenails. In conclusion, toenails, an easily accessible tissue for the estimation of methylmercury exposure, have been shown to be closely correlated with the well established samples for biomarkers, viz. blood and hair mercury.     

Evaluation of protein requirements for trained strength athletes.

Leucine kinetic and nitrogen balance (NBAL) methods were used to determine the dietary protein requirements of strength athletes (SA) compared with sedentary subjects (S). Individual subjects were randomly assigned to one of three protein intakes: low protein (LP) = 0.86 g protein.kg-1.day-1, moderate protein (MP) = 1.40 g protein.kg-1.day-1, or high protein (HP) = 2.40 g protein.kg-1.day-1 for 13 days for each dietary treatment. NBAL was measured and whole body protein synthesis (WBPS) and leucine oxidation were determined from L-[1-13C]leucine turnover. NBAL data were used to determine that the protein intake for zero NBAL for S was 0.69 g.kg-1.day-1 and for SA was 1.41 g.kg-1.day-1. A suggested recommended intake for S was 0.89 g.kg-1.day-1 and for SA was 1.76 g.kg-1.day-1. For SA, the LP diet did not provide adequate protein and resulted in an accommodated state (decreased WBPS vs. MP and HP), and the MP diet resulted in a state of adaptation [increase in WBPS (vs. LP) and no change in leucine oxidation (vs. LP)]. The HP diet did not result in increased WBPS compared with the MP diet, but leucine oxidation did increase significantly, indicating a nutrient overload. For S the LP diet provided adequate protein, and increasing protein intake did not increase WBPS. On the HP diet leucine oxidation increased for S. These results indicated that the MP and HP diets were nutrient overloads for S. There were no effects of varying protein intake on indexes of lean body mass (creatinine excretion, body density) for either group. In summary, protein requirements for athletes performing strength training are greater than for sedentary individuals and are above current Canadian and US recommended daily protein intake requirements for young healthy males.     

The metabolism of methoxyethylmercury salts

The metabolism of methoxy[(14)C]ethylmercury chloride in the rat has been investigated. After a single subcutaneous dose a small proportion is excreted unchanged in urine and a larger amount in bile with some resorption from the gut. The greater part of the dose is rapidly broken down in the tissues with a half-time of about 1 day to yield ethylene and inorganic mercury. Ethylene is exhaled in the breath and the mercury migrates to the kidney and is excreted in urine. A small proportion of the dose appears as carbon dioxide in the breath and about 12% in urine as a mercury-free metabolite. It is possible that the breakdown of methoxyethylmercurychloride to ethylene and inorganic mercury is not catalysed by an enzyme system.     

Methylmercury distribution in the pregnant rat and embryo during early midbrain organogenesis

BACKGROUND: The period of neurogenesis represents a window of susceptibility for in utero methylmercury (MeHg) exposure. This study examined the toxicokinetics of potentially neurotoxic doses of MeHg during neurogenesis in the developing rat to provide additional information in the areas of mercury speciation and inter-study variability. METHODS: Pregnant Sprague-Dawley rats were dosed s.c. with 5-22 mg/kg MeHg on Day 11 of gestation to target rapidly dividing cells of the developing midbrain. Maternal liver, kidney, skin, blood, placenta, and the embryonic body and brain were evaluated for total and inorganic mercury content at 24, 48, and 72 hr after dosing. Tissue Hg partitioning ratios derived from our data were then compared to those derived from previous studies. RESULTS: Mercury was present in all tissues examined by 24 hr after dosing, and levels remained relatively stable over the subsequent 2 days in most tissues. The exceptions were the maternal blood and kidney, in which total mercury decreased significantly over the three days after dosing. Inorganic mercury concentrations were similarly stable over time. At maternal MeHg doses above 12 mg/kg, non-linearities were observed in mercury accumulation in the embryo, placenta and maternal liver. The mercury tissue partitioning coefficients ranged from 0.09 for maternal blood:embryo to 1.97 for maternal blood:kidney. CONCLUSIONS: Our observations at the 5 mg/kg dose were consistent with those of previous studies that involved evaluations at slightly later gestational times. The estimates of tissue partitioning coefficients we derived using multiple studies provide valuable insight into the effects of inter-study variability.     

Effects of mercury compounds on the spontaneous and potassium-evoked release of [3H]dopamine from mouse striatal slices

The effects of mercury compounds on the spontaneous and potassium-evoked release of [3H]dopamine from mouse striatal slices have been examined. All mercury compounds examined produced concentration-dependent increases in the spontaneous release of [3H]dopamine, with an order of potency of methylmercury greater than mercuric (Hg2+) mercury greater than p-choloromercuribenzene sulfonic acid. Methylmercury had no effect on the 25 mM potassium evoked release of [3H]dopamine in the presence of 1.3 mM calcium. However, in calcium-free conditions, methylmercury significantly increased the potassium-evoked release of [3H]dopamine. Mercuric mercury significantly reduced the 25 mM potassium evoked release of [3H]dopamine in the presence of 1.3 mM calcium, and this response was not reversible with brief washing of the tissue. In calcium-free conditions, mercuric mercury significantly elevated the evoked release of [3H]dopamine, similar to the result obtained with methylmercury. It is suggested that mercury compounds alter dopaminergic synaptic function, possibly by disrupting calcium homeostasis or calcium-dependent processes, and that methylmercury and mercuric mercury can have differential effects to alter dopaminergic neurotransmission.     

Acute ethanol intake induces mitogen-activated protein kinase activation,platelet-derived growth factor receptor phosphorylation,and oxidative stress in resistance arteries

In the present study, we investigated the role of angiotensin type I (AT₁) receptor in reactive oxygen species (ROS) generation and mitogen-activated protein kinases (MAPK) activation induced by acute ethanol intake in resistance arteries. We also evaluated the effect of ethanol on platelet-derived growth factor receptors (PDGF-R) phosphorylation and the role of this receptor on ROS generation by ethanol. Ethanol (1 g/kg; p.o. gavage) effects were assessed within 30 min in male Wistar rats. Acute ethanol intake did not alter angiotensin I or angiotensin II levels in the rat mesenteric arterial bed (MAB). Ethanol induced vascular oxidative stress, and this response was not prevented by losartan (10 mg/kg; p.o. gavage), a selective AT₁ receptor antagonist. MAB from ethanol-treated rats displayed increased SAPK/JNK and PDGF-R phosphorylation, responses that were not prevented by losartan. The phosphorylation levels of protein kinase B (Akt) and eNOS were not affected by acute ethanol intake. MAB nitrate levels and the reactivity of this tissue to acetylcholine, phenylephrine, and sodium nitroprusside were not affected by ethanol intake. Ethanol did not alter plasma antioxidant capacity, the levels of reduced glutathione, or the activities of superoxide dismutase and catalase in the rat MAB. Short-term effects of ethanol (50 mmol/l) were evaluated in vascular smooth muscle cells (VSMC) isolated from rat MAB. Ethanol increased ROS generation, and this response was not affected by AG1296, a PDGF-R inhibitor, or losartan. Finally, ethanol did not alter MAPK or PDGF-R phosphorylation in cultured VSMC. Our study provides novel evidence that acute ethanol intake induces ROS generation, PDGF-R phosphorylation, and MAPK activation through AT(1)-independent mechanisms in resistance arteries in vivo. MAPK and PDGF-R play a role in vascular signaling and cardiovascular diseases and may contribute to the vascular pathobiology of ethanol.     

Sediment Microbial Community Composition and Methylmercury Pollution at Four Mercury Mine–Impacted Sites

Mercury pollution presents a globally significant threat to human and ecosystem health. An important transformation in the mercury cycle is the conversion of inorganic mercury to methylmercury, a toxic substance that negatively affects neurological function and bioaccumulates in food chains. This transformation is primarily bacterially mediated, and sulfate-reducing bacteria (SRB) have been specifically implicated as key mercury methylators in lake and estuarine sediments. This study used phospholipid fatty acid (PLFA) analysis to investigate sediment microbial community composition at four abandoned mercury mine–impacted sites in the California Coast Range: the Abbott, Reed, Sulphur Bank, and Mt. Diablo mines. Differences in watershed and hydrology among these sites were related to differences in microbial community composition. The Abbott and Sulphur Bank mines had the highest levels of methylmercury. Floc (a type of precipitate that forms when acid mine drainage contacts lake or river water) and sediment samples differed in terms of several important environmental variables and microbial community composition, but did not have statistically different methylmercury concentrations. Quantification of PLFA biomarkers for SRB (10Mel6:0 for Desulfobacter and i17:1 for Desulfovibrio) revealed that Desulfobacter and Desulfovibrio organisms made up higher percentages of overall microbial biomass at the Sulphur Bank and Mt. Diablo mines than at the Abbott and Reed mines. Correlations between these SRB biomarker fatty acids and methylmercury concentrations suggest that Desulfobacter and Desulfovibrio organisms may contribute to methylmercury production in the Abbott, Reed, and Sulphur Bank mines but may not be important contributors to methylmercury in the Mt. Diablo Mine.     

Gas-liquid chromatographic determination of the distribution of 3,3',4,4'-tetrachlorobiphenyl in the adult female rat following short-term oral administration

A gas-liquid chromatographic assay using electron-capture detection was developed for the quantitation of 3,3',4,4'-tetrachlorobiphenyl (TCBP) in the serum, urine, brain, liver, adipose tissue, and feces of the rat. The sample preparation involves extraction of 3,3',4,4'-TCBP with hexane under neutral or alkaline conditions (and washing with concentrated acid for feces only). Aqueous standards are used for calibration of the assay, except for adipose tissue. The lower limit of quantitative sensitivity of the assay for 3,3',4,4'-TCBP is 25 ng/mL for serum and urine and 125 ng/g for brain, liver, adipose tissue, and feces, which can be extended to 5 ng/mL and 25 ng/g, respectively, by analyzing a larger aliquot of the hexane extract. The overall accuracy is greater than 95% for serum, urine, brain and feces and 86% for liver, and the within-day coefficient of variation does not exceed 8.6%. 3,3',4,4'-TCBP was administered orally to adult, female, Sprague-Dawley rats in the dosage regimens: 0.2, 0.5 and 2 mg X kg-1 X day-1 for 10 days and 5 mg X kg-1 X day-1 for 4 days. 3,3',4,4'-TCBP distributed preferentially into adipose tissue and liver, where the xenobiotic concentration was greater in adipose tissue. The adipose tissue and hepatic 3,3',4,4'-TCBP concentrations were dependent on both the absolute dose and dosing schedule of the xenobiotic. Only trace concentrations, usually below the lower limit of quantitation, were detected in the serum, brain and kidney. Fecal excretion of 3,3',4,4'-TCBP was greater than urinary excretion for the 5 mg X kg-1 X day-1 X 4-day regimen.