Toxaphene, which was added to glycerol/corn oil, was administered at a level of 1 mg/kg body weight/day in gelatin capsules to four healthy young adult cynomolgus (Macaca fascicularis) monkeys for 52 weeks. Four control monkeys ingested capsules containing only glycerol/corn oil. Each group had two males and two females. On a daily basis, each monkey's feed and water consumption was determined, its health was monitored and the females were swabbed to evaluate menstrual status. On a weekly basis, each monkey's body weight was determined and a detailed clinical evaluation was performed. At 4-week intervals, blood samples were taken for serum biochemistry, haematology and toxaphene analysis. Also, a local anaesthetic was administered to the nuchal fat pad area of each monkey, and adipose samples were obtained for toxaphene analysis. 1 day prior to the biopsies, a 24-h urine and faecal collection was obtained for toxaphene analysis. After 34 weeks of treatment, the immune system of the monkeys was evaluated. After 52 weeks of dosing, all treated and two control animals were necropsied. Liver samples were obtained and microsomal fractions were prepared immediately. A portion of liver and kidney was taken for toxaphene analysis. All of the major internal organs were weighed and bone marrow evaluations were conducted. Organ and tissue samples were fixed in 10% formalin and processed for light microscopy. There was no effect of treatment on body weight gain, feed consumption, water consumption or haematological parameters. Two major clinical findings were inflammation and/or enlargement of the tarsal gland and impacted diverticulae in the upper and lower eye lids. At necropsy, the relative spleen and thymus weights were greater for the treated monkeys than the controls. Toxaphene administration produced an increase in metabolism of aminopyrene, methoxyresorufin and ethoxyresorufin, three substrates that are altered specifically by cytochrome P450-based hepatic monooxygenase enzymes. Histopathological examination of tissues was unremarkable by light microscopy. Tissue analysis for toxaphene and immunology findings have been published elsewhere.

Synthetic phenolic antioxidants can interact with peroxides produced by food. This paper reviews correlation between BHA, BHT and TBHQ metabolism and harms they cause and provides a theoretical basis for rational use of BHA, BHT and TBHQ in food, and also put some attention on the transformation and metabolic products of PG. We introduce BHA, BHT, TBHQ, PG and their possible metabolic pathways, and discuss possible harms and their specific mechanisms responsible. Excessive addition or incorrect use of synthetic phenolic antioxidants results in carcinogenicity, cytotoxicity, oxidative stress induction and endocrine disrupting effects, which warrant attention. BHA carcinogenicity is related to production of metabolites TBHQ and TQ, and cytotoxic effect of BHA is the main cause of apoptosis induction. BHT carcinogenicity depends on DNA damage degree, and tumour promotion is mainly related to production of quinone methylation metabolites. TBHQ carcinogenicity is related to induction of metabolite TQ and enzyme CYP1A1.

Domoic acid was orally administered to 3 cynomolgus monkeys at doses of 0.5 mg/kg for 15 days and then at 0.75 mg/kg for another 15 days. After the 30-day dosing period, the treated monkeys were killed. Parameters monitored as markers for toxicity included body weight, food and water consumption, clinical observations, hematology, serum chemistry, light microscopy of all major organs (including brain and retina), and glial fibrillary acid protein immunohistochemistry. Domoic acid in serum and 24-hour urine samples was measured at several time points. All parameters measured remained unremarkable. Domoic acid concentrations measured in the 24-hour urine samples indicated that gastrointestinal absorption in the monkey was approximately 4-7 percent of the administered dose, which is at least twice that previously reported for the rat.

Mathematically based carcinogen risk assessment is based on a number of prudent default assumptions which are becoming progressively less tenable as new scientific evidence is adduced. For example, the assumptions that all rodent carcinogens will be carcinogenic in humans and that there is no safe dose of any carcinogen may, in specific examples, be shown to be untrue. The mechanisms by which carcinogens exert their effects, especially the induction of DNA lesions, DNA repair of these lesions, and cell proliferation, are considered; it is suggested that with recently developed experimental techniques they might be employed to develop a more biologically based approach to risk assessment and might avoid at least, some of the pitfalls associated with the present mathematically based carcinogen risk assessment models. They might lead to an improved appreciation of the shape of the carcinogen dose–response curve, at least at medium to high exposure levels.

Toxaphene is a pesticide whose use was banned in North America because of concerns regarding its toxicity. To obtain better data on the metabolism and toxicity of toxaphene in primates, a one year feeding study was carried out in cynomologous monkeys at a dose of 1 mg/kg/day for one year. Levels of toxaphene residues in blood and adipose tissue during the dosing period were measured by GC-ECD and ECNI GCMS. The dosing toxaphene mixture was found to be extensively metabolized. Four chlorinated bornane congeners were the predominate residues found in the tissue samples. Blood levels of toxaphene residues plateaued at 40 ppb, adipose levels at approximately 4000 ppb. Kidney, liver, feces and urine were analyzed for toxaphene residues after necropsy.

Male and female Sprague-Dawley rats were dosed by gavage for 64 days with 0, 0.1 or 5 mg/kg/day domoic acid. Treated animals showed no clinical abnormalities. Terminal values in haematology and clinical chemistry did not reveal differences between treated and control groups. Findings in histopathology and immunohistochemistry were unremarkable. The 24-hr urinary excretion rate for domoic acid determined at three time points was approximately 1.8% of the dose and remained unchanged during the study. Published by Elsevier Science Ltd.

A 2 year feeding study was conducted with male and female B6C3F1 mice that consumed diets containing 0, 1, 5, or 10 ppm deoxynivalenol (DON). Survivability was good and, while the test animals gained less weight with increasing levels of DON in the diet, there were no consistent toxic manifestations associated with DON consumption. There was some evidence for an increase in serum IgA and IgG in females, and there were sporadic changes noted in the clinical chemistry and hematology parameters conducted at the terminal sacrifice. However, these changes were not considered to be biologically significant. The pathology results provided statistically significant dose-related evidence for a decrease in liver preneoplastic and neoplastic lesions as the dose level of DON increased. This negative trend probably results from the known positive correlation between body weight and the appearance of spontaneous hepatic neoplasms in this strain of mouse.

Marine and terrestrial food sources are susceptible to contamination by various industrial chemicals and microbial pathogens. Both types of hazard are amenable to regulatory assessment using a single toxicology data base, along with some knowledge of contaminant levels and consumption figures for food. On the other hand, regulatory problems persist with acutely toxic naturally occurring phycotoxins, which may accumulate unpredictably to toxic levels in seafood. However, a scarce supply of pure toxin often precludes the availability of acceptable toxicology studies describing their biological effects. An exception to this situation is domoic acid, a neurotoxin phycotoxin that produced numerous cases of severe human intoxication which demanded extensive toxicological study. This paper describes a series of ongoing studies initiated in the wake of the outbreak of domoic acid toxicity that occurred in 1987 in Eastern Canada.

A wide variety of oxidative DNA lesions are commonly present in untreated human and animal DNA. One of these lesions, 8-hydroxydeoxyguanosine, has been shown to lead to base mispairing (mutation) on DNA replication. Other lesions remain to be investigated in this respect. Oxidative DNA lesions on cell replication may, in appropriate circumstances, lead to proto-oncogene activation. Oxidative DNA damage, on fixation, may also lead to cytotoxicity followed by regenerative proliferation. The probable or possible importance of oxidative DNA damage is reviewed for various classes of carcinogens and natural processes, including metal ions, high-energy radiation, miscellaneous chemicals, tumor-promoting agents, polyhydroxyphenols/quinones, lipid metabolism, peroxisome proliferators and thyroid function. It is concluded that although the evidence needs considerable strengthening in many of these examples, the available information indicates the potential importance of oxidative DNA damage in the induction of tumors by these agents. It is also possible that non-cancerous degenerative diseases associated with aging are the result of the accumulation of lesions resulting from unrepaired oxidative DNA damage.

Phenolic antioxidants have been used for many years to prevent oxidative spoilage of food (rancidity). They are of major importance in protecting foodstuffs during transportation and storage. Antioxidants thus constitute an essential element in the modem centralized food processing and distribution industries. In Canada, only three phenolic antioxidants are permitted to be added to food: butylated hydroxyanisole (BHA), butylated hydroxytoluene (BHT) and propyl gallate (PG). The mean dietary intake of BHA and BHT, as a result of their useas food additives, is relatively low; in Canada the intake overall ages is 7.40 mg/person/day for bothBHA and BHT, leading to a combined totalof 0.26 mg/kg/day (Kirkpatrick andLauer, 1986).

Cancers arise in specific tissues. One difficulty with the present definitions of the Maximum Tolerated Dose (MTD), as they pertain to the rodent cancer bioassay, is that they base MTD on relatively crude parameters associated with the well-being of the entire animal rather than with the lack of specific tissue toxicity. Additional factors that could be included in the MTD definition, or could be separately determined, are addressed. Many of these factors refer to toxic behavior in one or a few tissues and, if used in setting the MTD, may mask more relevant events occurring at higher dose levels in other tissues. Reducing the MTD to a level that fails to take into account pesticide or drug-related toxicity may lead to the loss of relevant information in the bioassay. It is concluded, therefore, that there are two possible approaches to a more appropriate use of the MTD. The highest dose of the test agent (MTD) may be chosen (i) to lie below the thresholds of carcinogenicity-related non-genotoxic toxicity or (ii) the present high level MTD may continue to be used and tumors that arise may be classified as being irrelvant to humans at some or all exposure levels. The latter approach is to be preferred. It has the potential to avoid missing high level effects of the test agent that may be relevant to the human population.

Forestomach neoplasia induced by the apparently non-genotoxic carcinogens, butylated hydroxyanisole and propionic acid, appears to arise by way of sustained high levels of cellular proliferation. Several other inducers of enhanced cellular proliferation, or the consequential incidence of hyperplastic lesions, have been identified in the rodent forestomach but the requisite carcinogenicity bioassays remain undone. In other tissues, such as the male rat kidney, the rodent thyroid follicular cell and the bladder epithelium, there is also evidence supporting the concept that sustained enhanced cellular proliferation may be an important early marker for non-genotoxic carcinogens. This reaction is, however, not likely to be the only marker necessary for the identification of non-genotoxic carcinogens.

A novel type of intoxication in Canada in 1987 was traced to consumption of cultivated mussels contaminated with the excitotoxin domoic acid. Studies carried out in rats and monkeys revealed that parenterally administered domoic acid induces in rats neuroexcitatory phenomena culminating in seizures. Monkeys respond with gagging, emesis and less clearly evident seizure activity. CNS damage consisting of dendrotoxic and gliotoxic edema and nerve cell degeneration occurs in structures of the limbic system and the retina in both species. CNS lesion distribution similarities in animals treated with domoic acid or kainic acid suggest that these excitotoxins share a common pathogenesis mediated by glutamic acid, a putative endogenous excitatory neurotransmitter.

A recent outbreak of marine food poisoning in humans was attributed to the consumption of blue mussels (Mytilus edulis L.) contaminated with domoic acid (DA) that was produced by the diatom Nitzschia pungens. The clinical and morphological effects of single oral doses of extracts of mussels contaminated with DA or of DA isolated from toxic mussels were investigated in small groups (one to six) of cynomolgus monkeys (Macaca fascicularis; 0.5-10 mg DA/kg body weight) and of Sprague-Dawley rats (60 to 80 mg DA/kg body weight). Control animals were either given saline or were not treated. To test whether monosodium glutamate, present in the food consumed by some affected humans, and dimethylsulphoxide, suspected of being present in the plankton, enhanced the response, monosodium glutamate (at 0.25% of mussel extract bolus) or dimethylsulphoxide (at 1 g per bolus) were co-administered to two (one each) of the DA-treated monkeys. DA-treated monkeys developed transient excitation characterized by vomiting. DA-treated rats showed withdrawal followed by hyperexcitation and death (in one case). Mild to moderate central nervous system lesions consistent with neuroexcitation were present in both monkeys and rats. The addition of monosodium glutamate and dimethylsulphoxide had no significant effect on the appearance and severity of central nervous system clinical signs and lesions. The wide variations in the response of test animals to orally administered DA were attributed to the protective effect of vomiting, and to suspected incomplete or slow gastro-intestinal absorption of the toxic agent. The results reinforce the view that DA is an emetic and that under appropriate conditions may also inflict excitotoxic central nervous system damage.

A recent outbreak of human food poisoning, characterized by severe gastrointestinal and neurologic abnormalities, with a fatal outcome in 3 patients, was attributed to the consumption of poisonous mussels containing domoic acid at an abnormally high concentration. The purpose of the present study was to determine if domoic acid, a glutamate analogue extracted from poisonous mussel, was neurotoxic to rats. Groups of female Sprague-Dawley rats were dosed once intraperitoneally with 0, 1, 2, 4, or 7.5 mg domoic acid/kg of body weight and observed for a maximum period of 24 hr. Clinically, control rats and rats in the 1 mg/kg group were unremarkable. Seventy-five percent of the animals in the 2 mg/kg group had equivocal transient behavioral signs. One that was given 2 mg/kg and all rats given in excess of 4 mg/kg of body weight developed unequivocal behavioral and neurologic signs culminating in partial seizures and status epilepticus. Histopathologically, severely affected rats developed selective encephalopathy characterized by neuronal degeneration and vacuolation of the neuropil in the limbic and the olfactory systems, and retinopathy characterized by neuronal hydropic degeneration of the inner nuclear layer and vacuolation of the external plexiform layer. The results of this study suggest that domoic acid is excitotoxic and causes a characteristic syndrome with clinical signs and histopathologic lesions similar to those reported for kainic acid.

To study the CNS effects of domoic acid (D.A.), 6 adult Cynomolgus monkeys (M. fascicularis) were dosed intraperitoneally (4 mg/kg) or intravenously (0.025-0.5 mg/kg) with D.A. obtained from cultured mussels contaminated with this neurotoxin. Clinical signs of neurotoxicity were preceded by a short presymptomatic period (2-3 min) and an even shorter prodromal period (0.5-1 min). The symptomatic period proper was characterized by persistent chewing with frothing, varying degrees of gagging, and vomit. Monkeys in the higher dose regimen exhibited additional signs including abnormal head and body positions, rigidity of movements and loss of balance, and tremors. The duration of the symptomatic period was dose dependent. Excitotoxic lesions consisting of vacuolation of the neuropil, astrocytic swelling, and neuronal shrinkage and hyperchromasia were detected in the area postrema, the hypothalamus, the hippocampus, and the inner layers of the retina in monkeys given D.A. at 0.5 mg/kg intravenously and 4 mg/kg intraperitoneally. It was concluded that D.A., administered intravenously, is neuroexcitatory and a powerful emetic at doses of 0.025 to 0.2 mg/kg. At higher doses (0.5 mg/kg intravenously and 4 mg/kg intraperitoneally), D.A. is strongly excitotoxic.

Consumption of cultivated blue mussels from Prince Edward Island was recently associated with episodes of gastro-intestinal and neurological distress. Extracts of the toxic mussels, tested in the mouse bioassay for paralytic shellfish poison, caused an atypical response characterized by scratching, convulsions and death. The present investigation shows that the domoic acid present in toxic mussels can produce in mice and rats signs identical to those induced by mussel extracts. These studies, preliminary in nature by virtue of the scarcity of domoic acid, gave ip no-effect levels in mice of 0.59 mg/kg body weight based on the behavioural response (scratching) and 2.4 mg/kg for death. These levels correspond to levels of 24 and 94 ppm in mussels. When administered orally doses of between 35 and 70 mg domoic acid/kg body weight were required to produce toxicity in mice and rats. This reduced toxicity is consistent with a lack of absorption from the gastro-intestinal tract: faecal excretion accounted for 102 +/- 17% and 98 +/- 12% (mean +/- SE) of the domoic acid administered to mice and rats, respectively. Since human intoxication occurred at an estimated 1-5 mg domoic acid/kg body weight, susceptible individuals appear to be more sensitive than rodents to the oral toxicity of domoic acid.