Lack of a distinct gradient in biomarker responses in small mammals collected at different distances from a highway.

This study describes biomarker effects in small mammals exposed to traffic emissions. Animals were collected at 10-50 m (site 1), 150-200 m (site 2), and 5 km (site 3) from a very busy highway (A2). To distinguish between routes of exposure, strictly carnivorous common shrews ( Sorex araneus) and predominantly herbivorous bank voles ( Clethrionomys glareolus) were collected. As a measure of exposure to polycyclic aromatic hydrocarbons (PAHs), aromatic DNA adduct levels were determined by (32)P-postlabeling techniques in tissue from heart, lung, and liver. Lead (Pb), cadmium (Cd), and copper (Cu) levels were analyzed in kidney as a measure of exposure to heavy metals. EROD and PROD activity and retinoid levels were determined in liver as effect biomarkers for exposure to PAHs and polyhalogenated aromatic hydrocarbons (PHAHs). Relatively high Cd levels in S. araneus and in particular elevated DNA adduct levels in C. glareolus indicated that small mammals at site 3 were exposed to more compounds than at sites 1 and 2 (3 > or = 1 > 2). The latter effect is probably due to an incidental and actual input of airborne pollutants that is deposited on plant surfaces. By consumption of above-ground vegetation, voles are chronically exposed to this pollution. Relatively high background input of PAHs probably hinders that the traffic-related gradient of airborne PAH concentrations found in an earlier study is reflected in DNA adduct levels in small mammals in the present study. Moreover, historical biomarkers for exposure to traffic emissions, such as increased kidney Pb levels, increased hepatic EROD activity, and disturbed hepatic vitamin A homeostasis are no longer applicable to indicate differences in exposure. This is a result of the ban on addition of Pb and chlorinated scavengers to gasoline and of cleaner combustion techniques, which were enforced by law over the past decade. Finally, it is advisable to use only juvenile small mammals for in situ monitoring of diffuse pollution because DNA adduct levels increased with age.

Biological and chemical analysis of the toxic potency of pesticides in rainwater.

A newly developed method for measuring the integrated esterase inhibiting potency of rainwater samples was applied in practice, and the results are compared to the toxic potency calculated from concentrations of 31 organophosphate (OP) and carbamate pesticides, out of a total of 66 chemically analyzed pesticides. In addition, the general toxic potency of the rainwater samples was evaluated in a microtiter luminescence assay with Vibrio fischeri bacteria. Rainwater samples were collected over four consecutive 14-day periods in both open and wet-only samplers. The esterase inhibiting potency of the open rainwater samples (expressed as ng dichlorvos-equivalents/l) corresponded well with the chemical analyses of the rainwater samples collected by both types of samplers (r = 0.83-0.86). By far, the highest esterase inhibiting potency was found in a sample collected in an area with intense horticultural activities in June, and was attributed to high concentrations of dichlorvos, mevinphos, pirimiphos-methyl and methiocarb. The esterase inhibiting potency of this sample was equivalent to a dichlorvos concentration of 1380 ng/l in the rainwater, which is almost 2000 times higher than the maximum permissible concentration (MPC) of dichlorvos set for surface water in Netherlands. Maximum individual concentrations of dichlorvos and pirimiphos-methyl even exceeded the EC50 for Daphnia, suggesting that pesticides in rainwater pose a risk for aquatic organisms. Not all responses of the luminescence-assay for general toxicity could be explained by the analyzed pesticide concentrations. The bio-assays enable a direct assessment the toxic potency of all individual compounds present in the complex mixture of rainwater pollutants, even if they are unknown or present at concentrations below the detection limit. Therefore, they are valuable tools for prescreening and hazard characterization purposes.

The application of reporter gene assays for the determination of the toxic potency of diffuse air pollution.

Diffuse air pollution consists of a mixture of numerous compounds. It is emitted by many distributed sources and is omnipresent due to atmospheric transport. Risk assessment of the complex mixture of air pollutants on the basis of the toxicity of the individual compounds is not yet possible because the chemical identity and/or toxicity of the constituencies of a substantial fraction is unknown. In addition, no adequate procedures are available to integrate toxicity data of such complex mixtures, so that an individual risk assessment of the constituents of air pollution disregards possible combination effects. In the present study, an approach has been developed to assess the toxic potency by using in vitro bio-assay techniques. Genotoxicity was assessed in the umu-assay, a reporter gene assay using a strain of Salmonella typhimurium stably transfected with a plasmid (pSK1002) carrying the SOS-gene umuC fused to the reporter gene lacZ. Arylhydrocarbon-receptor activation was assessed in the DR-CALUX-assay, using a stably transfected H4IIE hepatoma cell line containing a plasmid for the luciferase gene under transcriptional control of dioxin-responsive elements. Samples of airborne particulate matter (APM) were collected with a high volume sampler next to a highway and in a natural conservation area. Both assays proved to be applicable to quantify genotoxicity and the presence of polycyclic aromatic hydrocarbons (PAHs) in small extracts from air-filter samples. Results indicate that PAHs from traffic exhausts seem to be largely responsible for an increased genotoxic activity of APM collected down-wind from the highway (western wind). APM collected at eastern wind directions seems to have a different composition of compounds, with a higher genotoxic activity that is less related to highway-emitted PAH-like compounds. At northern wind directions, APM is relatively less genotoxic and contains less PAHs than at other wind directions. Dioxin-like compounds contribute negligibly to the Ah-receptor agonistic potency of APM. Airborne pollutants with genotoxic and/or PAH-like characteristics form an undesired mutagenic risk, which will be evaluated in further in vivo studies.

A small-volume bioassay for quantification of the esterase inhibiting potency of mixtures of organophosphate and carbamate insecticides in rainwater: development and optimization.

The goal of this study was to develop a sensitive in vitro bioassay for quantification of the total esterase inhibiting potency of low concentrations of organophosphate and carbamate insecticides in relatively small rainwater samples. Purified acetylcholinesterase (AChE) from electric eel (Electrophorus electricus) and carboxylesterases from a homogenate of honeybee heads (Apis mellifera) were used as esterases, each having different affinities for the substrates S-acetylthiocholine-iodide (ATC) and N-methylindoxylacetate (MIA). MIA hydrolysis by honeybee homogenate was more sensitive to inhibition by organophosphate insecticides than ATC hydrolysis by purified AChE, although the latter parameter is often used for in vitro monitoring of esterase inhibitors. The higher sensitivity of carboxylesterases is attributed to the instant formation of a reversible Michaelis-Menten complex with the inhibitor, which competes with MIA for the active sites of the free enzymes. This dose-dependent instant inhibition can be quantified with kinetics for competitive inhibition at dichlorvos concentrations < 16 nM. At similar concentrations, purified AChE was not instantly inhibited, whereas both AChE and carboxylesterases were irreversibly and progressively inhibited at higher dichlorvos concentrations (IC50(10min) >/= 0.1 microM). Honeybee homogenate mediated MIA hydrolysis was applied as the most sensitive enzyme-substrate combination for experiments with fractionated extracts of 4 rainwater samples collected in a natural conservation area. Most esterase inhibiting potency was found in the polar methanol fraction, with recalculated concentrations equivalent to 12-125 ng dichlorvos per liter rainwater.

Development of a bioassay to test the possible role of thiamine disturbance as a mechanism behind pollution-induced reproductive failures in birds.

A test system was developed to examine the effects of environmental contaminants on thiamine homeostasis in bird embryos. This system employs fresh chicken egg yolk lipids as a vehicle for use in egg injection studies. Furazolidone, an antibiotic suspected to interfere with thiamine metabolism, was used as a positive control to evaluate the utility of the test system. It was determined that fresh chicken egg yolk lipids were preferable over chemical vehicles as it resulted in lower mortality rates (16% versus 23-62%) and did not induce any observable effects in the embryo. Injection of 1 mg/egg of furazolidone at day 0 of development resulted in decreased respiration followed by death, with mortality rates being twice as high as in carrier controls. In addition, transketolase activity, which was measured as an indicator of thiamine availability in the body, was decreased 25% in brains of 19-day-old embryos. This mechanism may be of importance for effects of environmental contaminants in wild bird populations.

Contribution of planar (0-1 ortho) and nonplanar (2-4 ortho) fractions of Aroclor 1260 to the induction of altered hepatic foci in female Sprague-Dawley rats.

The hepatic tumor promoting activity of the planar 0-1 ortho ( approximately 9.7% w/w) and the nonplanar 2-4 ortho ( approximately 90.3% w/w) fraction of the commercial PCB mixture Aroclor 1260 was studied using a medium-term two-stage initiation/promotion bioassay in female Sprague-Dawley rats. Fractionation was carried out on an activated charcoal column. The composition of the effluent from the column was tested by GC-ECD. The absence of planar compounds in the 2-4 ortho fraction was confirmed by GC-MS analysis. The dioxin-like toxic potency of the fractions was determined with the DR-CALUX assay. The animal experiment was started with the initiation procedure (diethylnitrosamine injection, 30 mg/kg body wt ip, 24 h after (2)/(3) hepatectomy), followed 6 weeks later by the promotion treatment, which consisted of a weekly subcutaneous injection during 20 weeks. Exposure groups (n = 10) received the following treatments (dose/kg body wt/week): Aroclor 1260 (10 mg), 0-1 ortho fraction (0.97 mg), 2-4 ortho fraction (1, 3, or 9 mg), a reconstituted 0-4 ortho fraction (9.97 mg), 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153; 1 or 9 mg), 2,3,7,8-TCDD (1 microg; positive control) or corn oil (1 ml; vehicle control). One group did not receive a promotion treatment. All exposure groups exhibited a significantly increased volume fraction of the liver occupied by hepatic foci positive for the placental form of glutathione-S-transferase-p compared to the corn oil control, except for the groups treated with 0-1 ortho fraction and 1 mg PCB 153/kg body wt/week. Approximately 80% of the total tumor promoting capacity of the reconstituted 0-4 ortho fraction could be explained by the 2-4 ortho PCB fraction while the 0-1 ortho fraction had only a negligible contribution. These results suggest that the majority of the tumor promotion potential of PCB mixtures resides in the non-dioxin-like fraction, which is not taken into account in the toxic equivalency factor (TEF) approach for risk assessment of PCBs. This may result in an underestimation of the tumor promotion potential of environmental PCB mixtures.

Interactions of prostaglandin A2 with the glutathione-mediated biotransformation system.

The cyclopentenone prostaglandin A2 (PGA2) is known to inhibit cell proliferation, and metabolism of this compound thus might be important in controlling its ultimate function. The glutathione-related metabolism of PGA2 was therefore investigated both with purified glutathione S-transferase P1-1 (GSTP1-1) and with IGR-39 human melanoma cells. Firstly, the irreversible inhibition of human GSTP1-1 and its mutants C47S, C101S, and C47S/C101S was studied. PGA2 appeared to inhibit GSTP1-1 mainly by binding to the cysteine 47 moiety of the enzyme. This binding was reversed by a molar excess of GSH, indicating that retro-Michael cleavage occurs. Secondly, after exposing IGR-39 human melanoma cells to PGA2, both diastereoisomers of the PGA2-glutathione conjugate are excreted into the medium, although with a clear excess of the S-form, due to its preferential formation by the GSTP1-1 present in the cells. Thirdly, the effect of PGA2 on intracellular GST activity was determined by quantification of the excreted glutathione conjugate S-(2,4-dinitrophenyl)glutathione (DNPSG) after exposure to 1-chloro-2,4-dinitrobenzene. DNPSG excretion was inhibited after incubation with 10 or 20 microM PGA2 for 1 or 4 hr, as a result of glutathione depletion, reversible GST inhibition, and covalent modification of intracellular GST. Furthermore, PGA2 also inhibited transport of DNPSG by the multidrug resistance-associated protein, an effect that was reversible and competitive. In conclusion, PGA2 modulates all three aspects of the glutathione-mediated biotransformation system, i.e. GSH levels, GSTP1-1 activity, and transport of GSH conjugates. A role for GSTP1-1 as a specific transport protein inside the cell is indicated.

Induction of altered hepatic foci by a mixture of dioxin-like compounds with and without 2,2',4,4',5,5'-hexachlorobiphenyl in female Sprague-Dawley rats.

The hepatic tumor-promoting activity of a mixture of polyhalogenated aromatic hydrocarbons (PHAHs) was studied in a medium term two-stage initiation/promotion bioassay in female Sprague-Dawley rats. The PHAH mixture contained 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 1, 2,3,7,8-pentachlorodibenzo-p-dioxin (PeCDD), 2,3,4,7, 8-pentachlorodibenzofuran (PeCDF), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), 2,3',4,4',5-pentachlorobiphenyl (PCB 118), 2,3,3',4,4', 5-hexachlorobiphenyl (PCB 156), 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153) and covered >90% of the total toxic equivalents (TEQ) present in Baltic herring. To determine possible interactive effects of di-ortho-substituted PCBs, the PHAH mixture was tested with (PHAH+) and without (PHAH-) PCB 153. Rats were initiated by a diethylnitrosamine injection (30 mg/kg body wt i.p.) 24 h after a partial 23 hepatectomy. Six weeks after initiation, the PHAH mixtures were administered once a week by subcutaneous injections for 20 weeks. Treatment with the PHAH mixtures caused liver enlargement and an increased activity of the hepatic cytochrome P4501A1/2 and P4502B1/2. All PHAH exposure groups exhibited an increased occurrence of hepatic foci positive for the placental form of glutathione-S-transferase. In the PHAH-group dosed 1 microgram TEQ/kg body wt/week, the volume fraction of the liver occupied by foci was significantly lower compared to the TEQ equivalent dosed TCDD group (3.8 vs 8.7%). The volume fraction was significantly increased in the groups treated with 0.5, 1, or 2 micrograms TEQ/kg body wt/week of the PHAH+ mixture (4.5, 5.2, and 6.6%, respectively) compared to the corn oil group (2.0%), but to a lower extent than expected on basis of the TEQ doses. Overall, the TEQ-based administered dose overestimated the observed tumor-promoting effects of this PHAH mixture. The applicability of the toxic equivalency factor concept, the role of differences in toxicokinetic properties and interactive effects of PCB 153 on hepatic deposition of the dioxin-like congeners are discussed.

Low inducibility of CYP1A activity by polychlorinated biphenyls (PCBs) in flounder (Platichthys flesus): characterization of the Ah receptor and the role of CYP1A inhibition.

Several studies have reported a low inducibility of hepatic cytochrome P4501A (CYP1A) activity in European flounder (Platichthys flesus) following exposure to mixtures of polychlorinated biphenyls (PCBs). Here we report on mechanistic studies toward understanding this low CYP1A inducibility of flounder, involving molecular characterization of the Ah receptor (AhR) pathway as well as inhibition of the CYP1A catalytic activity by PCB congeners. Hepatic cytosolic AhR levels in flounder were determined using hydroxylapatite, protamine sulfate adsorption analysis, or velocity sedimentation on sucrose gradients. AhR levels in flounder (approximately 2-7 fmol/mg protein) were much lower than observed generally in rodents (approximately 50-300 fmol/mg protein). Molecular characterization of the flounder AhR was provided by first-strand cDNA synthesis and amplification of flounder hepatic poly(A)+ RNA using RT-PCR. A 690-bp product was found, similar in size to a Fundulus AhR cDNA. The specificity of the 690-bp band was established by Southern blotting and hybridization with a degenerate AhR oligonucleotide. The deduced amino acid sequence of the flounder AhR fragment was 59-60% identical to mammalian AhR sequences. Although the AhR is present in flounder cytosol, we were unable to demonstrate detectable amounts of inducible TCDD-AhR-DRE complex in gel-retardation assays. High induction levels of CYP1A protein and associated EROD activity have been previously found in flounder following exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In contrast, the induction of CYP1A catalytic activity by PCB mixtures remains unexpectedly low. Therefore, we further characterized the inhibitory potential of PCB congeners on CYP1A activity in flounder and compared this with inhibitory effects of PCB congeners on rat CYP1A activity. Analysis in vitro demonstrated that 3,3',4,4'-tetraCB, 3,3',4,4',5-pentaCB, 2,2',4,4',5,5'-hexaCB, 3,3',4,4',5,5'-hexaCB, and the commercial PCB mixture Clophen A50 are potent competitive inhibitors of hepatic microsomal CYP1A catalytic activity in flounder and rat. The K(m) for ethoxyresorufin (0.095 microM) in flounder is strikingly close to Ki's found for the tested PCBs. This emphasizes the possible involvement of PCB congeners in inhibition of EROD activity in PHAH exposed fish. Finally, our data indicate that flounder CYP1A is more efficient in metabolizing ethoxyresorufin than that of rat CYP1A.

Absence of an inhibitory effect of a vegetables-fruit mixture on the initiation and promotion phases of azoxymethane-induced colorectal carcinogenesis in rats fed low- or high-fat diets.

The potential inhibitory effects of a vegetables-fruit mixture on the initiation and promotion phases of azoxymethane-induced colorectal carcinogenesis were examined in rats fed low- or high-fat diets. Rats were fed low-fat diets (20 energy percent, Diets A and B) or high-fat diets (40 energy percent, Diets C and D), supplemented with a vegetables-fruit mixture (19.5% wt/wt, Diets B and D) or unsupplemented (Diets A and C) for 36 weeks. After the animals were maintained on the respective diets for four weeks, they were given three weekly injections of azoxymethane at 15 mg/kg body wt sc. Eight weeks after the start of the study, animals maintained on Diet A were switched to Diet B or C or maintained on the same diet. Animals maintained on Diet B or D were switched to Diet A or C, respectively. Furthermore, animals maintained on Diet C were switched to Diet A or D or maintained on the same diet. Multiplicity of colorectal tumors did not differ between groups fed a vegetables-fruit mixture during the initiation or the promotion phase (Group B-->A vs. Group A-->B; Group D-->C vs. Group C-->D). However, multiplicity was significantly lower in animals fed low-fat diets than in animals fed high-fat diets in combination with a vegetables-fruit mixture (Group A-->B/B--A vs. Group C-->D/D-->C). Furthermore, multiplicity was significantly increased in groups fed a high-fat diet during the promotion phase only in comparison with animals fed a low-fat diet during the whole experiment (Group A-->C vs. Group A-->A). No other differences in multiplicity or tumor incidences were observed among the eight experimental groups.

Food plant toxicants and safety Risk assessment and regulation of inherent toxicants in plant foods.

The ADI as a tool for risk management and regulation of food additives and pesticide residues is not readily applicable to inherent food plant toxicants: The margin between actual intake and potentially toxic levels is often small; application of the default uncertainty factors used to derive ADI values, particularly when extrapolating from animal data, would prohibit the utilisation of the food, which may have an overall beneficial health effect. Levels of inherent toxicants are difficult to control; their complete removal is not always wanted, due to their function for the plant or for human health. The health impact of the inherent toxicant is often modified by factors in the food, e.g. the bioavailability from the matrix and interaction with other inherent constituents. Risk-benefit analysis should be made for different consumption scenarios, without the use of uncertainty factors. Crucial in this approach is analysis of the toxicity of the whole foodstuff. The relationship between the whole foodstuff and the pure toxicant is expressed in the `product correction factor' (PCF). Investigations in humans are essential so that biomarkers of exposure and for effect can be used to analyse the difference between animals and humans and between the food and the pure toxicant. A grid of the variables characterising toxicity is proposed, showing their inter-relationships. A flow diagram for risk estimate is provided, using both toxicological and epidemiological studies.

Macrophages influence gap junctional intercellular communication between smooth muscle cells in a co-culture model.

The present study demonstrates for the first time that cells cultured on pore membrane inserts (macrophages) modulate gap junctional intercellular communication (GJIC) between a second cell type (smooth muscle cells (SMC)) co-cultured in Transwell-COL cell culture chambers. Unstimulated J774A.1 murine macrophages reduced GJIC between human SMC. Stimulation of J774A.1 cells by lipopolysaccharide (LPS) or interferon-γ abrogated this modulation of GJIC. Unstimulated human monocyte-macrophages did not affect GJIC between human SMC. Upon stimulation of these monocyte-macrophages with LPS, a substantial increase in GJIC between co-cultured SMC was observed. Thus, activation of macrophages alters their interaction with co-cultured SMC. Since these results were obtained in an indirect co-culture system in which direct cell-cell contact is prevented, it is hypothesized that soluble factors released by macrophages may be involved in this modulation of GJIC between SMC. The possible nature of the responsible soluble factors is discussed in the context of atherosclerosis.

Interaction of dietary fat with a vegetables-fruit mixture on 1,2-dimethylhydrazine-induced colorectal cancer in rats.

The aim of the present investigation was to study the interaction of dietary fat in combination with a vegetables-fruit mixture on 1,2-dimethylhydrazine (DMH)-induced colorectal carcinogenesis in rats. For this purpose, 120 weanling male. Wistar rats received a semisynthetic diet without (Groups A and C) or with a vegetables-fruit mixture (Groups B and D; vegetables and fruit content 19.5% wt/wt) for 35 weeks. Diets of Groups A and B contained 20 energy percent (20e%) fat, whereas diets of Groups C and D contained 40e% fat. The vegetables and fruit used the amount of fat, and its fatty acid composition were chosen according to the mean consumption values of The Netherlands. After the animals were maintained for four weeks on the respective diets, they were given 10 weekly injections of DMH at 50 mg/kg body wt sc. After sacrifice, their colons were removed and examined macroscopically and microscopically for the presence of tumors. Rats fed high-fat diets developed significantly more tumors than rats fed low-fat diets. Furthermore, although not statistically significant, a lower number of colorectal tumors was observed in rats fed a low- or a high-fat diet containing the vegetables-fruit mixture than in rats fed diets without the vegetables-fruit mixture. No differences were observed in intestinal tumor incidences among all groups. The results suggest that the vegetables-fruit mixture used in this experiment, present in an amount comparable with the mean consumption in The Netherlands, has no significant inhibitory effect on the development of colorectal tumors induced by DMH in rats maintained on diets low or high in fat.

Modulation of dietary fat-enhanced colorectal carcinogenesis in N-methyl-N'-nitro-N-nitrosoguanidine-treated rats by a vegetables-fruit mixture.

The modulation of a vegetables-fruit mixture on N-methyl-N'-nitro-N-nitrosoguanidine (MNNG)-induced colorectal carcinogenesis was studied in rats maintained on a low- or a high-fat diet. For this purpose, 120 rats received a semisynthetic diet without (Groups A and C) or with a vegetables-fruit mixture (19.5% wt/wt, Groups B and D) for 35 weeks. Diets of Group A and B contained 20 (low) energy percent (20e%) fat, whereas diets of Groups C and D contained 40e% (high) fat. Between Weeks 4 and 9 the animals were given weekly intrarectal instillations of 6 mg MNNG/kg body wt. The colorectal adenocarcinoma incidences showed a significant decrease in animals fed high-fat diets with a vegetables-fruit mixture compared with animals fed a high-fat diet alone. Furthermore, without a vegetables-fruit mixture, diets high in fat caused a significant increase in adenocarcinoma incidence compared with diets low in fat. Although not significant, the adenoma incidences tended to be lower in animals fed a vegetables-fruit mixture than in animals maintained on a diet without this mixture. The results demonstrate that a vegetables-fruit mixture has a significant inhibitory potency on the development of colorectal tumors induced by MNNG in rats fed diets high in fat.

The role of calcium in the tumor promoter-induced inhibition of gap junctional intercellular communication.

The effect of several tumor promoters (12-O-tetradecanoyl-phorbol-13-acetate (TPA); 1,1'-(2,2,2-trichloroethylidene)bis[4-chlorobenzene] (DDT); Aroclor1260, and clofibrate) on the inhibition of gap junctional intercellular communication (GJIC) and intracellular calcium concentration ([Ca(2+)](i)) was studied in a cell line consisting of initiated cells (3PC). In addition, the effect of different extracellular calcium concentrations ([Ca(2+)](e)) on the effects of tumor promoters on both GJIC and [Ca(2+)](i) were studied. Agents with GJIC inhibiting capacity increased [Ca(2+)](i). However, the increase of [Ca(2+)](i) did not (always) precede GJIC inhibition. The effect of tumor promoters on GJIC were similar under low (0.05 mM) and high (1.20 mM) Ca(2+)(e) conditions, while different effects on [Ca(2+)](i) were found. These results suggest that tumor promoters can inhibit GJIC and change [Ca(2+)](i), but that there is no direct relationship between these two processes.

Transport and metabolism of glutathione conjugates of menadione and ethacrynic acid in confluent monolayers of rat renal proximal tubular cells.

Confluent monolayers of primary rat renal proximal tubular (RPT) cells were used to compare transepithelial transport and concomitant metabolism of two different glutathione (GSH) S-conjugates. For the GSH-conjugated quinone compound, [35S]GSH-conjugated menadione (MGNQ), no specific transepithelial transport was observed. Most likely, [35S]MGNQ passed the monolayer via paracellular leakage as the result of a reduction in monolayer integrity due to toxicity via extensive redox cycling of the quinone under the culture conditions. RPT cell monolayers metabolise MGNQ into a cysteinylglycine conjugate, which after intramolecular cyclization yields 2H-(3-glycinyl)-9-hydroxy-10-methyl-1,4-naphthothiazine. Acivicin, an inhibitor of gamma-glutamyltranspeptidase, inhibited the formation of this 1,4-napthothiazine adduct. The second product formed is 1,4-napthothiazine formed by loss of glycine via the action of dipeptidases. Similarly, no basolateral (B) to apical (A) transport of a GSH-conjugated alpha, beta unsaturated ketone, [14C]ethacrynic acid (EASG), occurred. However, net transport of [14C] radioactivity could be observed from A=>B direction. After 8 h, 23% of total [14C] radioactivity was transported from the apical to the basolateral chamber. In both the apical and basolateral chambers, free, unconjugated ethacrynic acid (EA) was observed. gamma GT-mediated metabolism of EASG to the much more unstable cysteinylglycine conjugate leads to relatively large amounts of free EA. Thus, the GSH conjugate is not transported but rather the cysteine adduct and/or free, unconjugated EA. In agreement with this, acivicin reduced A=>B transport of EASG and inhibited the formation of free EA. In conclusion, the confluent monolayers of RPT cells do not or no longer possess active basolateral transport systems for GSH conjugates. However, they are still quite useful for studying biotransformation reactions of thioether conjugates.

Alterations in rat brain thyroid hormone status following pre- and postnatal exposure to polychlorinated biphenyls (Aroclor 1254).

The effect of daily oral maternal exposure to 0, 5, or 25 mg/kg body wt of a polychlorinated biphenyl (PCB) mixture (Aroclor 1254) on Days 10 to 16 of gestation on plasma and brain thyroid hormone concentrations and peripheral thyroid hormone concentrations and peripheral thyroid hormone metabolism were examined in fetal and weanling rats. Plasma thyroid hormone levels and hepatic microsomal thyroid hormone glucuronidation were also examined in pregnant rats and the adult offspring. Plasma and brain levels of PCBs and hydroxylated PCB metabolites were analyzed in fetal, weanling, and adult offspring. Maternal exposure to Aroclor 1254 significantly decreased fetal (Gestation Day 20) and neonatal (Postnatal Day 4) plasma total thyroxine (T4) and free T4 levels in a dose-dependent manner. Effects of maternal Aroclor 1254 exposure on plasma total and free T4 concentrations were less pronounced in offspring at 21 days of age and absent 90 days after birth. Plasma concentrations of thyroid-stimulating hormone were unaltered in fetuses, neonates, weanling rats, and adult offspring following maternal treatment with Aroclor 1254. the concentration of T4 was severely depressed in the forebrain and cerebellum of fetal rats on Day 20 of gestation following maternal Aroclor 1254 exposure. Brain triiodothyronine (T3) concentrations in the Aroclor-exposed fetuses were significantly decreased relative to control values only in the low-dose group. On Day 21 postpartum T4 concentrations were significantly decreased in the forebrains of female weanling rats from the 25 mg Aroclor 1254/kg dose group, and no reductions were observed in forebrain T3 concentrations in male or female neonates. The deiodination of T4 to T3 was significantly increased in fetal forebrain homogenates by both PCB treatments. In female weanling brain homogenates the deiodination of T4 to T3 was significantly decreased in the low-dose group and unaltered in the high-dose group. No alterations in brain thyroid hormone metabolism were observed in forebrain homogenates from adult offspring exposed pre- and postnatally to Aroclor 1254. Hepatic microsomal T4 glucuronidation was significantly decreased in fetal microsomes following perinatal PCB exposure and significantly increased in weanling hepatic microsomes in a dose-dependent manner. An accumulation of mainly one PCB metabolite, 2,3,3',4',5-pentachloro-4-biphenylol was observed in fetal plasma and forebrain on Gestation Day 20 and in neonatal and weanling rat plasma on Postnatal Days 4, 21, and 90. The plasma level of 2,3,3',4',5-pentachloro-4-biphenylol was higher than that of the persistent PCB congener 2,2',4,4',5,5'-hexachlorobiphenyl in the control and PCB-exposed offspring up to Postnatal Day 21, and even after 90 days, the 2,3,3',4',5-pentachloro-4-biphenylol was present in amounts approximately equal to those of CB 153. Although PCB levels were relatively high in the weanling rat forebrain, no hydroxylated PCB metabolites were detected. On Day 90 postpartum, plasma levels of PCBs and 2,3,3',4',5-pentachloro-4-biphenylol were still elevated in the offspring of PCB-treated dams relative to controls. These results suggest that the accumulation of hydroxylated PCB metabolites in fetal plasma can reduce fetal plasma T4 levels and accordingly fetal brain T4 levels. However, in late gestational fetuses, the induction of brain type II thyroxine 5'-deiodinase activity compensates for decreases in brain T4 levels, so that brain T3 levels are maintained.