Tissue Distribution and Immunomodulation in Channel Catfish (Ictalurus punctatus) Following Dietary Exposure to Polychlorinated Biphenyl Aroclors and Food Deprivation.

Although most countries banned manufacturing of polychlorinated biphenyls (PCBs) over 40 years ago, PCBs remain a global concern for wildlife and human health due to high bioaccumulation and biopersistance. PCB uptake mechanisms have been well studied in many taxa; however, less is known about depuration rates and how post-exposure diet can influence PCB concentrations and immune response in fish and wildlife populations. In a controlled laboratory environment, we investigated the influence of subchronic dietary exposure to two PCB Aroclors and food deprivation on tissue-specific concentrations of total PCBs and PCB homologs and innate immune function in channel catfish (Ictalurus punctatus). Overall, we found that the concentration of total PCBs and PCB homologs measured in whole body, fillet, and liver tissues declined more slowly in food-deprived fish, with slowest depuration observed in the liver. Additionally, fish that were exposed to PCBs had lower plasma cortisol concentrations, reduced phagocytic oxidative burst activity, and lower cytotoxic activity, suggesting that PCBs can influence stress and immune responses. However, for most measures of immune function, the effects of food deprivation had a larger effect on immune response than did PCB exposure. Taken together, these results suggest that short-term dietary exposure to PCBs can increase toxicity of consumable fish tissues for several weeks, and that PCB mixtures modulate immune and stress responses via multiple pathways. These results may inform development of human consumption advisories and can help predict and understand the influence of PCBs on fish health.

Concentration dependence of human and mouse aryl hydrocarbon receptor responsiveness to polychlorinated biphenyl exposures: Implications for aroclor mixtures.

1. Aryl hydrocarbon receptor (AhR) ligands, including 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and polychlorinated biphenyls (PCBs), are endocrine disrupting chemicals associated with nonalcoholic fatty liver disease. This study documents the species-specific differences between mouse (high affinity mAhR) and human AhR (hAhR) activation by PCB congeners and Aroclor mixtures. 2. AhR activation by TCDD or PCBs 77, 81, 114, 114, 126, and 169 was measured using luciferase reporter constructs transfected into either Hepa1c1c7 mouse or HepG2 human liver cell lines. The EC50 values were lower in Hepa1c1c7 cells than HepG2 cells for all compounds tested except PCB 81. The results for TCDD and PCB 126 were validated in primary human and mouse hepatocytes by measuring CYP1A1 gene transcript levels. 3. Because humans are exposed to PCB mixtures, several mixtures (Aroclors 1254; 1260; and 1260 + 0.1% PCB126 each at 10 µg/ml) were then tested. Neither Aroclor 1254 nor Aroclor 1260 increased luciferase activity by the transfected AhR reporter construct. The Aroclor 1260 + 0.1% PCB 126 mixture induced mAhR-mediated transactivation, but not hAhR activation in cell lines. 4. In summary, significant concentration-dependent differences exist between human and mouse AhR activation by PCBs. Relative effect potencies differed, in some cases, from published toxic equivalency factors.

Comparison of metabolite profiles generated in Aroclor-induced rat liver and human liver subcellular fractions: considerations for in vitro genotoxicity hazard assessment.

Because it is well known that metabolites of chemicals and drugs are frequently the ultimate species responsible for genotoxicity and carcinogenicity, in vitro testing to identify the human genotoxicity hazard potential of new chemicals and drugs routinely utilizes liver S-9 fraction from rats treated with Aroclor 1254 as a system that can generate metabolites. However, it is frequently questioned as to whether such an in vitro metabolite generation system is the most relevant for human risk, or whether the assay would be better served by using a human-derived in vitro system. To address this, 16 common drugs have been examined for profiles of metabolites in Aroclor-induced rat liver S-9 and pooled human liver S-9. Metabolite profiles were compared using high pressure liquid chromatography coupled with ion trap mass spectrometry, in line with ultraviolet or radiometric detection to help make semiquantitative comparisons. Results showed that, with few exceptions, metabolites generated in the human system were also generated in the rat system. Also, in several cases the rat system generated considerably more metabolites, suggesting that there is a potential that positive genotoxicity findings could be caused by metabolites that have no relevance to humans. These findings suggest that when conducting in vitro genotoxicity testing using the Aroclor-induced rat liver S-9 system, knowledge of the metabolite profile in the system is important, and a comparison to the profile generated in human liver S-9 could be of value when interpreting the genotoxicity results.

Clapper rails as indicators of mercury and PCB bioavailability in a Georgia saltmarsh system.

Clapper rails (Rallus longirostris) were used as an indicator species of estuarine marsh habitat quality because of their strong site fidelity and predictable diet consisting of mostly benthic organisms. Mercury (Hg) and the polychlorinated biphenyl (PCB) Aroclor 1268 concentrations were determined for sediments, crabs, as well as clapper rail adults and chicks collected from salt marshes associated with the LCP Superfund site in Brunswick, Georgia. Home ranges were established for adult rails, and sediment and crab samples were taken from each individual's range. The study was designed to minimize the spatial variability associated with trophic transfer studies by choosing an endpoint species with a potentially small home range and specifically sampling its foraging range. The mean home range for clapper rails was 1.2 ha with a median of 0.28 ha. Concentrations of Hg and Aroclor 1268 were shown to increase with each trophic level. Transfer factors between media followed the same pattern for both contaminants with the highest between fiddler crabs and clapper rail liver. Hg and PCB transfer factors were similar between sediment to fiddler crab and fiddler crab to muscle, however the PCB transfer factor from fiddler crabs to liver was over twice as large as for Hg. PCB congener profiles did not significantly differ between media types.

Polychlorinated biphenyl-induced reduction of dopamine transporter expression as a precursor to Parkinson's disease-associated dopamine toxicity.

Epidemiological and laboratory studies have suggested that exposure to polychlorinated biphenyls (PCBs) may be a risk factor for Parkinson's disease. The purpose of this study was to examine the potential mechanisms by which PCBs may disrupt normal functioning of the nigrostriatal dopamine (DA) system. We utilized an environmentally relevant exposure of PCBs (7.5 or 15 mg/kg/day Aroclor 1,254:1,260 for 30 days by oral gavage) to identify early signs of damage to the DA system. This dosing regimen, which resulted in PCB levels similar to those found in human brain samples, did not cause overt degeneration to the DA system as shown by a lack of change in striatal DA levels or tyrosine hydroxylase levels. However, we did observe a dramatic dose-dependent decrease in striatal dopamine transporter (DAT) levels. The observed reductions appear to be specific to the DAT populations located in the striatum, as no change was observed in other dopaminergic brain regions or to other neurotransmitter transporters present in the striatum. These data demonstrate that PCB tissue concentrations similar to those found in postmortem human brain specifically disrupt DA transport, which acts as a precursor to subsequent damage to the DA system. Furthermore, DAT imaging may be useful in evaluating alterations in brain function in human populations exposed to PCBs.

Dermal absorption in rhesus monkeys of polychlorinated biphenyls from soil contaminated with Aroclor 1260.

Human health risk assessments involving contaminated soil include dermal absorption as a potential pathway contributing to the total exposure burden. For PCB-contaminated soil, the U.S. Environmental Protection Agency uses a dermal absorption factor of 14%, based on a 1993 study of dermal absorption in rhesus monkeys. The current study examined several parameters that can influence the dermal absorption of lipophilic hydrocarbons, including soil organic content, particle size, skin residence time, and contaminant "aging" in the soil. Four groups of four female rhesus monkeys each were exposed to radiolabeled Aroclor 1260 either intravenously (100% absorption) or dermally with PCB-spiked soil. Groups exposed for 12 or 24 h to PCBs aged in soil exhibited percutaneous absorption values of 3.43 +/- 0.35 and 4.26 +/- 0.52%, respectively, while a group exposed for 24 h to soil freshly spiked with PCBs exhibited a dermal absorption value of 4.07 +/- 0.46%. Evidence strongly suggests that the factor most responsible for modulating the percutaneous absorption of highly lipophilic compounds from soil is its organic content. The base soil used in the current study with Aroclor 1260 had an organic content of 5-6% (< or =2 mm particle fraction), a value typical for U.S. soil. The organic content of the soil applied to the skin was 8.7% (<150 microm particle fraction), a value that contrasts sharply with the soil containing 0.9% organics used in the 1993 study with Aroclors 1242 and 1254 that produced a dermal absorption value of 14% for PCBs.

PCBs reduce long-term potentiation in the CA1 region of rat hippocampus.

Prenatal exposure to polychlorinated biphenyls (PCBs) has been associated with a lower IQ in childhood. We have examined the effects of acute exposure to PCB mixtures and two single congeners on synaptic transmission between Schaffer collaterals and CA1 neurons of the rat hippocampus as well as posttetanic potentiation (PTP), paired pulse facilitation (PPF), and long-term potentiation (LTP). PTP and PPF represent transient increases in transmitter release immediately after stimulation, while LTP is a measure of long-term changes in synaptic plasticity that has been related to learning and memory. LTP, but neither PTP nor PPF, was reduced by Aroclor 1016 in a dose-dependent fashion at concentrations that had little effect on general synaptic transmission. The more highly chlorinated Aroclor 1254 at low concentrations specifically blocked LTP, but at higher concentrations also reduced synaptic transmission. The mono-ortho PCB congener 2,4,4'-trichlorobiphenyl and the coplanar congener 3,3',4,4'-tetrachlorobiphenyl also blocked LTP without effect on PTP or PPF. We conclude that PCBs selectively impair the process of LTP in CA1 neurons of the hippocampus.

Aroclor 1254-induced alterations in hypothalamic monoamine metabolism in the Atlantic croaker (Micropogonias undulatas): correlation with pituitary gonadotropin release.

Male Atlantic croaker (Micropogonias undulatus) were exposed to Aroclor 1254 (a PCB mixture) in the diet (0.1 mg/100 g body wt./day) for 30 days during gonadal recrudescence to investigate the effects of the PCB mixture on reproductive neuroendocrine function. The concentrations of biogenic amines (epinephrine [E], norepinephrine [NE], dopamine [DA], and 5-HT) and their major metabolites (3,4-dihydroxyphenylacetic acid [DOPAC], 3-methoxytyramine [3-MT], homovanillic acid [HVA], and 5-hydroxyindolacetic acid [5-HIAA]) were measured in the preoptic-anterior hypothalamus (POAH) and medial and posterior hypothalamus (MPH) using HPLC with electrochemical detection. There was a significant decline in 5-HT and DA concentrations and an increase in their metabolite to parent amine ratios in both the POAH and MPH of Aroclor 1254-exposed fish. In addition, Aroclor 1254 exposure resulted in the loss of the in vitro pituitary gonadotropic response to stimulation by a luteinizing hormone-releasing hormone analog (LHRHa). We have previously shown that 5-HT modulates the gonadotropin release in response to LHRHa in Atlantic croaker. Therefore, the reduced availability of neuronal 5-HT may be at least partially responsible for the loss of the gonadotropic response to stimulation by LHRHa.

Toxicological consequences of Aroclor 1254 ingestion by female rhesus (Macaca mulatta) monkeys and their nursing infants. Part 3: post-reproduction and pathological findings.

A group of 80 menstruating rhesus (Macaca mulatta) monkeys were randomly allocated to four similar rooms (20 monkeys/room) and then to one of five dose groups (four females/dose group/room). Each day the monkeys self-ingested capsules containing doses of 0, 5, 20, 40 or 80 microg Aroclor 1254/kg body weight. After 25 months of continuous dosing, approximately 90% of the treated females had attained a qualitative pharmacokinetic steady state with respect to the concentration of polychlorinated biphenyl (PCB) in their nuchal fat pad. Concurrently, sebaceous glands were being examined for changes analogous to chloracne. Subsequently, the females were paired with untreated males. The infants' blood PCB levels at birth were not correlated with its dam's dose or blood PCB level. However, there was an association between an infants preweaning blood PCB levels and its dam's dose and PCB milk levels. After weaning, the infants were not dosed with PCB. The half-life for the PCB in the infants' blood was determined and found to be slightly more than 15 wk. After 6 yr on test, three monkeys from the 0, 5, 20 and 40 microg dose groups were randomly allocated to a depletion study to ascertain the half-lives of specific PCB congeners (Mes et al., Chemosphere 1995, 30, 789-800). Concurrently, necropsies began of the remaining females, and of seven infants from the treated dams and four infants from the control dams, which had attained an age of 2 yr. Approximately 3 yr later, the depletion monkeys were necropsied. The only statistically significant treatment-related pathological changes found during the study were in the adult females, in which an involution of the sebaceous glands and a dose related increase in liver weight due to hyperplasia were evident.

Transfer of PCBs via lactation simultaneously induces the expression of P450 isoenzymes and the protooncogenes c-Ha-ras and c-raf in neonates.

At the first day of lactation, maternal rats were injected with a single i.p. dose of 100 or 250 mg/kg body weight of a mixture of polychlorinated biphenyls (Aroclor 1254). This treatment caused significant increases in both material and neonatal hepatic cytochrome P-450, cytochrome b5, and cytochrome-c-(P-450) reductase. Transfer of PCBs via lactation resulted in significant increases in hepatic enzyme activities catalysed by neonatal CYP1A1, CYP1A2, CYP2B1, CYP3A1, and CYP2E1 using a variety of substrates. In contrast, the metabolism of dimethylnitrosamine and aminopyrine was only marginally (up to 2-fold) increased in maternal animals four days post treatment. Further measurements showed significant increases in maternal and neonatal epoxide hydrolase, glutathione-S-transferase, and UDP-glucuronyl transferase activities, thus suggesting a coordinated response for an induction of CYP1A1, CYP1A2, CYP2A1, CYP2B1, CYP2E1, CYP3A1, and CYP4A1 in both maternal and neonatal CYP2C6, and at the higher dose the expression of neonatal CYP2E1 was significantly reduced. Northern blot analysis provided further evidence for significant increases in maternal and neonatal hepatic CYP1A1, CYP1A2, CYP2B1, and CYP2E1 mRNA, but reduced amounts of CYP2C7 and CYP4A1 mRNA. Additional Northern blot hybridization experiments may suggest an increased expression of the protooncogenes c-Ha-ras and c-raf in the mother and the neonate upon treatment of maternal rats with Aroclor 1254. Lactation itself may result in an increased expression of the latter protooncogenes, but the mRNA of the protooncogenes c-erb A and c-erb B was not detected in any of the tissues examined.

Postmortem tissue levels of polychlorinated biphenyls in female rhesus monkeys after more than six years of daily dosing with Aroclor 1254 and in their non-dosed offspring.

Polychlorinated biphenyl (PCBs) analyses were made on prenecropsy blood samples and postmortem adipose, liver, kidney, and brain tissues from female rhesus monkeys fed a daily dose of 0, 5, 20, 40, or 80 micrograms Aroclor 1254/kg body weight for approximately 6 years. During this time, the females were bred with non-dosed males. All resulting offspring were nursed for 22 weeks and fed no additional PCBs until they were necropsied at approximately 120 weeks after birth. PCBs were also measured in necropsied infant tissues to determine PCB levels due to intake of PCB-contaminated milk from the dosed dams, in addition to in utero exposure. Polychlorinated biphenyl levels in all tissues of the adult monkeys increased with their dosage. The highest PCB levels were found in adipose tissue and the lowest levels were found in the brain. Polychlorinated biphenyl residues in the cortex of the kidney were lower than in the medulla, while in the brain no appreciable differences were observed between the occipital and frontal lobes. Necropsy tissues of infants from dosed dams contained more PCBs than those nursed by controls, but less than tissues from stillborn infants. Although no differences were observed between PCB tissue levels from monkeys having offspring and those having no offspring, those having a stillborn infant had higher PCB levels in their tissues than those with a viable infant. Similarly, monkeys that were euthanized because of poor health had higher PCB levels in their tissues than those necropsied at the conclusion of the study and showed a dramatic shift from tetra- and hexachlorobiphenyls to penta- and heptachlorobiphenyls in their tissues. The PCB distribution pattern in tissues from a dosed mother/infant pair differed considerably. A larger percentage of heptachlorobiphenyls was found in the infant than in its dam. The adipose/blood PCB ratio in the adult monkeys remained remarkably constant.

Aroclor 1254 alters the binding of 125I-labeled nerve growth factor in PC12 cells.

The effects of Aroclor 1254, a mixture of polychlorinated biphenyls (PCBs), on nerve growth factor (NGF) receptors and neurite outgrowth in PC12 cells were examined. Aroclor 1254 enhanced the NGF-stimulated neurite elongation and decreased the Kd value for binding of 125I-labeled NGF to the high-affinity NGF receptors. The NGF dose-response curve for neurite outgrowth was also shifted to the left in cells pretreated with Aroclor 1254, suggesting that NGF was more potent in the presence of PCBs. Thus, one mechanism by which PCBs may enhance NGF-stimulated neurotrophic effects is in increasing the affinity of binding of NGF to the high-affinity NGF receptors, which are believed to mediate the neurotrophic effects of NGF. The data suggest that PCBs have the potential to influence the NGF neurotrophic system.

Aroclor 1242 stimulates the production of inositol phosphates in polymorphonuclear neutrophils.

Exposure in vitro to the mixture of polychlorinated biphenyls (PCBs), Aroclor 1242, stimulates superoxide anion (O2-) production and degranulation in rat polymorphonuclear neutrophils (PMNs). The mechanism by which PCBs activate PMNs is unknown. Phospholipase C-dependent hydrolysis of membrane phosphoinositides is an important early event in PMN activation in response to several agonists including N-formyl-methionyl-leucyl phenylalanine (fMLP); therefore, the present study was undertaken to determine whether Aroclor 1242 stimulates the production of inositol phosphates in isolated rat PMNs. PMNs elicited with glycogen from rat peritoneum were labeled with myo-[2-3H]inositol, and the effect of fMLP and Aroclor 1242 on accumulation of [3H]inositol phosphates was determined. Both fMLP (in the presence of cytochalasin B) and Aroclor 1242 induced rapid breakdown of inositol-containing phospholipids. Peak accumulation of [3H]inositol phosphates occurred within 5 sec in response to Aroclor 1242 and within 15-30 sec in response to fMLP. In cytochalasin B-treated PMNs, significant O2- generation occurred within 5 min of exposure to fMLP or Aroclor 1242. 2,2',4,4'-Tetrachlorobiphenyl (TCB), but not 3,3',4,4'-TCB, stimulates O2- production and degranulation in isolated rat PMNs. To determine whether inositol phosphate accumulation parallels PMN activation, [3H]inositol monophosphate (IP) production was measured in response to Aroclor 1242, 2,2'4,4'-TCB, and 3,3'4,4'-TCB in LiCl-treated cells. Both Aroclor 1242 and 2,2',4,4'-TCB, but not 3,3',4,4'-TCB, caused significant accumulation of [3H]IP. Previous reports indicate that cytochalasin B enhances PMN activation in response to fMLP by increasing the production of inositol phosphates. Pretreatment of PMNs with cytochalasin B significantly enhanced O2- production in cells exposed to Aroclor 1242 but did not alter [H]IP accumulation. These data suggest that treatment of rat PMNs with Aroclor 1242 stimulates PI turnover and are consistent with the hypothesis that hydrolysis of membrane phospholipids is important in PMN activation by PCBs. The enhancing effect of cytochalasin B on PCB-induced O2- production, however, likely involves other mechanisms.

The elimination and estimated half-lives of specific polychlorinated biphenyl congeners from the blood of female monkeys after discontinuation of daily dosing with Aroclor 1254.

The levels of thirty polychlorinated biphenyl congeners in the blood of female rhesus monkeys, previously dosed with Aroclor 1254 for over six years, were monitored every two weeks during the first year and monthly during the subsequent two years after dosing was discontinued. Both blood lipid and polychlorinated biphenyl congener levels generally declined during this post dosing period. The percent distribution of the PCB congeners during the post dosing period remained relatively constant with more than half of all polychlorinated biphenyls consisting of the mono-orthochlorine substituted biphenyls. The contribution of the mono-orthochlorine substituted biphenyls was significantly different for one out of three monkeys in two of the three dose groups, during the post dosing period. Half-life, estimations for nine of the congeners ranged from 0.3-7.6 years.

PCB congeners in the rat brain: selective accumulation and lack of regionalization.

Perturbations in the developing nervous system have been associated with perinatal exposures to polychlorinated biphenyls (PCBs). It remains unclear whether these neurotoxic effects are direct or secondary to other toxic processes. This study was designed to determine which PCB congeners accumulate in the brain as a result of perinatal exposure and if this accumulation is regionally specific. Sprague-Dawley rat dams were dosed by gavage with corn oil or Aroclor 1242 in corn oil (4 or 16 mg/kg/d) on d 10-16 of gestation. At weaning (d 21), one male and one female pup from each litter were euthanatized and three specific regions of the brain (frontal cortex, hippocampus, and caudate putamen) were collected for PCB analysis by gas chromatography. Ten peaks, which represent 10-14 PCB congeners, were detected in all samples. There were no differences in PCB concentration between sexes or among brain regions, but the different congeners differed from each other in degree of bioaccumulation. Brain PCB concentrations increased with increased dose for all congeners except PCB 28 (2,4,4'), which was present at a higher concentration in the lower dose-group. To characterize regionalization of PCBs in the brain further, weanling rats were dosed intravenously with [14C]-PCB 77 (3,3',4,4'-tetrachlorobiphenyl; 0.25 microCi/g; 2.0 micrograms/g) or [14C]-PCB 47 (2,2',4,4'-tetrachhlorobiphenyl; 0.25 microCi/g; 5.3 micrograms/g) in dimethyl sulfoxide (DMSO). Rats were killed after 72 h and the brains were quickly removed and frozen on dry ice. The brains were serially sectioned on a cryostat and the sections (16 microns) subjected to autoradiography (3-5 mo of exposure). The radioactivity was homogeneously distributed in the brain tissue for both PCBs. PCB 77-treated, but not PCB 47-treated, pups showed increased activity in areas with blood vessels present. This was consistent with differences in the blood-brain ratios for PCB 47 and PCB 77, which were determined to be 0.44 and 16.8, respectively.

Effects of persistent chlorinated hydrocarbons on fertility and embryonic development in the rabbit.

The commercial polychlorinated biphenyl (PCB) formulation Aroclor 1260 (4 mg/kg body weight), technical grade dichlorodiphenyltrichloroethane (DDT; 3 mg) and Lindane (gamma-hexachlorocyclohexane; 0.8 mg) were administered orally, either separately or in combination, to sexually mature female rabbits three times per week for 12-15 weeks. Oviductal and uterine luminal fluid, cleavage stage embryos (day 1 post coitum), blastocysts (day 6), fetuses, exocoelic fluid and placentae (day 11) were analysed, firstly for chlorinated hydrocarbon residues, and secondly for embryonic and fetal development. The doses applied were well tolerated by the treated animals. PCB and DDT accumulated in uterine secretions (day 6) but not in oviductal luminal fluid (day 1). Both chlorinated hydrocarbons were found in preimplantation blastocysts. Residues in day 11 fetuses were 16- (DDT) or 18-fold (PCB) higher than in day 6 blastocysts. Significant amounts were also detected in placental tissue and in exocoelic fluid. A specific accumulation of the highly chlorinated biphenyl congener no. 180 was noted in fetuses, placentae and exocoelic fluid. The clear accumulation of the chlorinated hydrocarbon compounds in luminal fluid and embryonic tissue is contrasted by rather weak effects on fertility. No statistically significant differences between treated animals and controls were observed for fertilization rate and pre- and post-implantation (up to day 11 post coitum) losses. However, in females exposed to PCB, a 20% higher loss of blastocysts was noticed, as compared with controls (P > 0.05). This effect was shown on day 6 of embryonic development and may be due to the embryotoxic activities of PCB.

Decreases in dopamine concentrations in adult, non-human primate brain persist following removal from polychlorinated biphenyls.

Adult male non-human primates, Macaca nemestrina, were orally exposed for 20 weeks to 3.2 mg/kg per day of either Aroclor 1016 or Aroclor 1260 made up in corn oil. Following cessation of exposure, the animals were observed for either an additional 24 or 44 weeks. After killing, regional brain concentrations of biogenic amines and polychlorinated biphenyls were determined by high-performance liquid chromatography (HPLC) and gas chromatography (GC), respectively. Brain dopamine (DA) concentrations were significantly decreased, compared to controls, in all polychlorinated biphenyl-exposed animals. Most importantly, in spite of significant decreases in brain polychlorinated biphenyl concentrations observed following removal from exposure (an average decline of 60%), there was no statistically discernible relationship of the changes in brain DA concentrations to either time following removal from polychlorinated biphenyls or brain polychlorinated biphenyl concentrations. These findings demonstrate that sub-chronic exposure of the adult non-human primate to polychlorinated biphenyls results in long-lasting changes in brain DA concentrations.

Accumulation of polychlorinated terphenyls in aquatic biota of an estuarine creek.

Aroclor 5432, a mixture of polychlorinated terphenyls (PCT), was detected in several biological compartments including saltmarsh cordgrass (Spartina alterniflora), American oysters (Crassostrea virginica), red-jointed fiddler crabs (Uca minax), wharf crabs (Sesarma reticulatum), and mummichogs (Fundulus heteroclitus) collected from Tabbs Creek. This tidal creek is located in the southern Chesapeake Bay region and contains sediments with high concentrations of PCT. Samples were collected at four sites, ranging from a suspected outfall near the head of the creek, to its mouth, approximately 2.5 river kilometers downstream. Species from several phyla were selected in order to examine PCT accumulation in physiologically and ecologically different organisms. PCT concentrations in sediment, saltmarsh cordgrass, native oysters, and fiddler crabs decreased with distance downstream. Residues in transplanted oysters and mummichogs showed a more variable trend with distance downstream. The organism with the highest mean concentration (18,300 micrograms/kg dry wt) was the native oyster, a benthic filter feeder.

Toxicological consequences of Aroclor 1254 ingestion by female rhesus (Macaca mulatta) monkeys. Part 1B. Prebreeding phase: clinical and analytical laboratory findings.

A group of 80 menstruating rhesus (Macaca mulatta) monkeys, with an average estimated age of 11.1 +/- 4.1 yr SD were first randomly allocated to four similar test rooms (20 monkeys/room), and then randomly allocated to one of five dose groups (four females/dose group/room). Each day, the monkeys self-ingested capsules containing doses of 0, 5, 20, 40 or 80 micrograms Aroclor 1254/kg body weight. After 25 months of daily dosing, approximately 90% of the treated females attained a qualitative pharmacokinetic steady state with respect to the concentration of polychlorinated biphenyl (PCB) in their adipose tissue. Subsequently, oestrogen and progesterone concentrations in serum were determined for one complete oestrous cycle and various immunological tests were conducted, while the monkeys continued to receive their daily dose of PCB. During the prebreeding phase of the study, blood for clinical and analytical monitoring including haematology, serum biochemistry, serum hydrocortisone, serum proteins (alpha 1, alpha 2, beta and gamma-globulins), serum immunoglobulins (A, G and M) and thyroid variables (thyroxine/triiodothyronine (T3) uptake ratio, percentage T3 uptake and free thyroxine index), were obtained monthly, as were specimens to ascertain the concentration of PCB in the blood, adipose tissue and faeces. Major findings among treated monkeys included the following: changes in haematology (decreased erythrocyte count, haematocrit, reticulocyte count, and mean platelet volume), serum biochemistry (decreased cholesterol and total bilirubin), immunotoxicity (decreased antibody production to sheep red blood cells and alterations in the percentage of T helper and T suppressor cells) and pathology (the number of regions of sebaceous gland lobules per unit of histological length was significantly reduced). These effects were observed at PCB doses lower than those previously reported for non-human primates.

Comparison of transplacental and neonatal initiation of mouse lung and liver tumors by N-nitrosodimethylamine (NDMA) and 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and promotability by a polychlorinated biphenyls mixture (Aroclor 1254).

We have previously shown a positive tumor-promoting effect of a single dose of Aroclor 1254 on lung and liver tumors initiated neonatally in the mouse by N-nitrosodimethylamine (NDMA). In this study, we have confirmed and extended this observation with NDMA and the tobacco-specific nitrosamine, 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) given either transplacentally or postnatally, followed by a single dose of Aroclor 1254 on day 56. This polychlorinated biphenyl (PCB) mixture was an effective promoter of both lung and liver tumors; however, there were specific initiator and sex-related differences in this response. Aroclor administration significantly increased the incidence of lung tumors initiated transplacentally by NDMA or NNK in male mice. Neither nitrosamine initiated tumors transplacentally in females, but lung tumors initiated with NNK and liver tumors caused by NDMA in neonatal females were promoted by PCBs. Both liver and lung tumors initiated neonatally by NDMA in male animals, but not NNK-initiated tumors, were promoted by PCBs. These data confirm that PCBs are able to promote both NDMA- and NNK-initiated tumors, but with chemical-, sex- and age-dependent difference; this suggests influences of both quantitative and qualitative factors in susceptibility to tumor promotion.