Michael P. Dieter

Immunological and biochemical responses in mice treated with mercuric chloride.

Adult B6C3F1 male mice were given water containing 3, 15, and 75 ppm mercury (as mercuric chloride) for 7 weeks. There were dose-related increases in blood and kidney mercury levels but only the former showed a time-dependent change. Mercury was not detected in any of the lymphoid organs except for the spleen. There was no mortality and only minimal histological changes occurred in kidneys of dosed mice. Nonspecific toxicity occurred at the 75 ppm dose level, consisting of small differences in body and organ weights, hematological changes, and general enzyme inhibition in the bone marrow and spleen. However, there were specific immunotoxic and biochemical alterations in lymphoid organs of mice treated at the lower doses of mercury. The immunological defects were consistent with altered T-cell function as evidenced by decreases in both T-cell mitogen and mixed leukocyte responses. There was a particular association between the T-cell defects and inhibition of thymic pyruvate kinase, the rate-limiting enzyme for glycolysis. The differences in the pattern of enzyme responses among lymphoid organs implied that two mechanisms of mercury toxicity were operative--one at high concentrations that caused physicochemical enzyme inhibition and another at low concentrations that caused indirect enzyme inhibition.

Myelotoxicity and macrophage alteration in mice exposed to ochratoxin A

Six- to seven-week-old female B6C3F1 mice were administered a total of 0, 20, 40, or 80 mg/kg of ochratoxin A (OCT A) ip on alternate days over an 8-day period. Twenty-four hours following the final dose, histopathology, bone marrow, and macrophage parameters were assayed. There was a dramatic dose related decrease in thymic mass with the mean thymus weight of the high dose animals being only 33% of controls. Histologic evidence of nephrotoxicity was minimal and restricted to the inner cortex. Myelotoxicity was present as evidenced by bone marrow hypocellularity, decreased marrow pluripotent stem cells (CFU-S), granulocyte-macrophage progenitors (CFU-GMs), and decreased 59Fe uptake in marrows and spleens of exposed mice. Peritoneal macrophages from sc as well as ip injected mice demonstrated increased phagocytic capacities and increased capacity to inhibit tumor cell growth. These alterations in bone marrow cells and macrophages suggest myelotoxicity is an additional potential hazard of OCT A exposure.

Comparison of lead bioavailability in F344 rats fed lead acetate, lead oxide, lead sulfide, or lead ore concentrate from Skagway, Alaska

An animal model using rats was developed to initiate investigations on the bioavailability of different sources of environmental lead. Lead must be absorbed and transported to target organs like brain, liver, kidney, and bone, before susceptible cells can be harmed. The bioavailability and therefore the toxicity of lead are dependent upon the route of exposure, dose, chemical structure, solubility, particle size, matrix incorporation, and other physiological and physicochemical factors. In the present study male F344 rats were fed < or = 38 microns size particles of lead sulfide, lead oxide, lead acetate, and a lead ore concentrate from Skagway, Alaska, mixed into the diet at doses of 0, 10, 30, and 100 ppm as lead for 30 d. No mortality or overt symptoms of lead toxicity were observed during the course of the study. Maximum blood lead concentrations attained in the 100 ppm groups were approximately 80 micrograms/dl in rats fed lead acetate and lead oxide, and were approximately 10 micrograms/dl in those fed lead sulfide and lead ore concentrate. Maximum bone lead levels in rats fed soluble lead oxide and lead acetate were much higher (approximately 200 micrograms/g) than those seen in rats fed the less soluble lead sulfide and lead ore (approximately 10 micrograms); kidney lead concentrations were also about 10-fold greater in rats fed the more soluble compared to the less soluble lead compounds. However, strong correlations between dose and tissue lead concentrations were observed in rats fed each of the four different lead compounds. Kidney lesions graded as minimal occurred in 7/10 rats fed 30 ppm and in 10/10 rats fed 100 ppm lead acetate, but not at lower doses or from other lead compounds. Similarly, urinary aminolevulinic acid excretion, a biomarker for lead toxicity, was increased in rats fed 100 ppm lead acetate or lead oxide, but was unaffected at lower doses or by the less soluble lead compounds. Although the histological and biochemical responses to lead toxicity were restricted to the more soluble lead compounds in this study, lead from Skagway lead ore concentrate and lead sulfide was also bioavailable, and accumulated in proportion to dose in vulnerable target organs such as bone and kidney. Longer-term studies with different mining materials are being conducted to determine if tissue lead continues to increase, and whether the levels attained are toxic. Data from such studies can be used to compare the toxicity and bioavailability of lead from different sources in the environment.

Toxicokinetics of cinnamaldehyde in F344 rats

The toxicokinetic profile of cinnamaldehyde (CNMA) was investigated in Fischer 344 rats. CNMA was found to be unstable in blood. After iv administration, a large fraction of CNMA was immediately oxidized to cinnamic acid. The biological half-life of CNMA after iv administration was found to be 1.7 hr. After administration by gavage of CNMA at 250 or 500 mg/kg body weight using corn oil as vehicle, the maximum blood concentrations of CNMA were in the order of 1 microgram/ml. These low blood concentrations were maintained over a 24-hr period after a dose of 500 mg/kg, which is relatively long considering the short (1.7 hr) biological half-life of CNMA. The estimated oral bioavailability of CNMA was less than 20% for both the 250 and 500 mg/kg doses. No CNMA was present in blood at any time in rats dosed with 50 mg CNMA/kg body weight. Only a small amount of the administered CNMA was excreted in rat urine as free cinnamic acid or beta-glucuronide-conjugated cinnamic acid. The majority of CNMA administered orally was excreted in urine as hippuric acid within 24 hr. The maximum excretion rate occurred at 8 hr after gavage. Hippuric acid recovered in 50-hr urine samples was found to be directly proportional to the oral dose of CNMA.

Development of renal toxicity in F344 rats gavaged with mercuric chloride for 2 weeks, or 2, 4, 6, 15, and 24 months

Both sexes of F344 rats were gavaged with maximal tolerated doses of mercuric chloride for periods from 2 wk to up to 2 yr to investigate chronic nephrotoxicity and potential carcinogenicity. The toxicity of mercuric chloride was excessive after 2 wk of exposure to doses ranging from 1.25 to 20 mg/kg, compromising renal function by selectively destroying cells of the proximal tubules, and eliciting marked elevations in urinary biomarker enzymes diagnostic for acute renal tubule necrosis. In the 2-wk studies, urinary alkaline phosphatase and aspartate amino-transferase were most sensitive to renal mercury toxicity among a panel of six enzymes, exhibiting twofold increases above controls at the 5.0 mg/kg dose, before changes in the other enzymes occurred. Urinary lactate dehydrogenase was the most responsive enzyme, with up to 11-fold increases in activity above controls. In response to mercuric chloride exposure of 5.0 mg/kg for 2-6 mo, the greatest and most persistent increases in elevation of urinary enzyme activities were exhibited by alkaline phosphatase and gamma-glutamyl transferase, which increased two-to threefold above controls. At this interval, the maximal severity of the renal lesions in both sexes of rats was graded as minimal to mild. Beyond 6 mo none of the urinary enzymes measured in this study was adequate as biomarkers of nephrotoxicity, although the severity of the renal lesions had progressed. Mercury accumulated in a dose-related fashion primarily in the kidney, and to a lesser extent in the liver. The severity of the renal lesions was increased by continued exposure to mercuric chloride, as tissue concentrations of mercury rose in proportion to dose. Mercuric chloride treatment for 2 yr clearly exacerbated the severity of the spontaneous nephrotoxicity prevalent in aging F344 rats. The excessive mortality that occurred in the male rats was probably due to a combination of these factors. No renal tumors were detected in rats, possibly because the potential for their development was reduced; however, direct tissue contact with mercury induced squamous-cell papillomas of the forestomach in both sexes.

Mechanisms of estrogen-induced myelotoxicity: Evidence of thymic regulation

Mice exposed to pharmacological levels of steroidal and nonsteroidal estrogens including alpha-dienestrol, 17 beta-estradiol, and diethylstilbestrol demonstrate bone marrow hypocellularity, and decreased numbers of pluipotent hemopoietic stem cells. Hormones with little estrogenic activity including testosterone and progesterone failed to induce myelotoxicity as did nonestrogenic metabolites of DES. Myelotoxicity associated with estrogen exposure is regulated by a complex bimodal mechanism. One of these mechanisms is mediated through the thymus since surgical thymectomy abolished the ability of estrogens to suppress CFU proliferation. Furthermore, supernatants of thymic epithelial cells cultured in the presence of estradiol were capable of inhibiting CFU-GM colony formation. Specific myelotoxic events can also be disassociated chemically by testing weakly estrogenic compounds such as zearalanol which shows different sensitivity on cytoxic and antiproliferative events. Myelotoxicity is not mediated indirectly through the ovary or adrenal gland. That the initial events in estrogen-induced myelotoxicity may be mediated through a receptor mechanism was suggested by the ability of antiestrogens to induce antagonism when administered prior to estradiol and the presence of estrogen binding components in lymphoreticular tissues including the thymus and bone marrow. These studies suggest that reduced CFU kinetics observed following estrogen exposure is, in part, due to alterations in regulatory factors produced by thymic epithelial cells in response to a specific estrogen stimulus. Estrogens may also influence bone marrow functions through non-thymic mechanisms at higher dose levels.

Comparative toxicity and tissue distribution of antimony potassium tartrate in rats and mice dosed by drinking water or intraperitoneal injection

Antimony potassium tartrate (APT) is a complex salt that until recently was used worldwide as an antischistosomal drug. Treatment was efficacious only if APT was administered intravenously to humans at a near lethal total dose of 36 mg/kg. Because unconfirmed epidemiologic studies suggested there might be an association between APT treatment and bladder cancer, we initiated prechronic toxicity studies with the drug to select a route of administration and doses in the event that chronic studies of APT were needed. The toxicity and concentration of tissue antimony levels were compared in 14-d studies with F344 rats and B6C3F1 mice administered APT in the drinking water or by ip injection to determine the most appropriate route for longer term studies. Drinking water doses estimated by water consumption were 0, 16, 28, 59, 94 and 168 mg/kg in rats and 0, 59, 98, 174, 273, and 407 mg/kg in mice. APT was poorly absorbed and relatively nontoxic orally, whereas ip administration of the drug caused mortality, body weight decrements, and lesions in the liver and kidney at doses about one order of magnitude below those in drinking water. Because of these data and the dose-related accumulation of antimony in the target organs, an ip dose regimen was selected for subsequent studies. Both sexes of F344 rats and B6C3F1 mice were given 0, 1.5, 3, 6, 12, and 24 mg/kg doses of APT every other day for 90 d by ip injection. There were no clinical signs of toxicity nor gross or microscopic lesions in mice that could be attributed to toxicity of APT, although elevated concentrations of antimony were detected in the liver and spleen of mice. Rats were more sensitive than mice to the toxic effects of APT, exhibiting dose-related mortality, body weight decrements, and hepatotoxicity. The concentrations of antimony measured in liver, blood, kidney, spleen, and heart of rats were proportional to dose, but there were no biochemical changes indicative of toxicity except in the liver. Hepatocellular degeneration and necrosis occurred in association with dose-related elevations in activities of the liver-specific serum enzymes sorbitol dehydrogenase and alanine aminotransferase. By alternating the site of abdominal injection and the days of treatment, mesenteric inflammation at the site of administration was minimized in the rats and mice, indicating that the ip route would be suitable for chronic studies.(ABSTRACT TRUNCATED AT 400 WORDS)

Comparison of the toxicity of cinnamaldehyde when administered by microencapsulation in feed or by corn oil gavage

The toxicity of cinnamaldehyde (CNMA) was compared after administration by gavage and in dosed feed. Rats and mice of both sexes received CNMA by daily corn oil gavage (for 2 wk), or in microencapsulated form in feed (2 wk for rats, 3 wk for mice). Feed formulations contained 0-10% CNMA microcapsules, equivalent to approximate daily doses of 0-3000 mg CNMA/kg body weight for rats and 0-10,000 mg CNMA/kg body weight for mice. Concentrations were chosen to deliver CNMA doses approximately equal to doses in the gavage study. Gavage doses of 2620 mg/kg/day and above in mice and 940 mg/kg/day and above in rats produced nearly 100% mortality; there were no deaths in animals receiving microencapsulated CNMA. Rats and mice receiving CNMA in feed showed a dose-related decrease in body weight gain, which was accompanied in rats by hypoplastic changes in reproductive organs and accessory sex glands. CNMA administration by either route caused hyperplasia of the forestomach mucosa. These results demonstrate that microencapsulation in feed can present a useful alternative to gavage dosing for repeated-dose or prolonged-exposure studies, in that (1) the toxic effects of CNMA were similar after gavage dosing and after administration in microencapsulated form in feed, (2) ingestion of chemical in the feed more closely approximates human exposures, and (3) microencapsulation allows the delivery of higher net doses of chemical, while avoiding the acutely toxic effects of a bolus dose.

Application of Microencapsulation for Toxicology Studies: III. Bioavailability of Microencapsulated Cinnamaldehyde

The bioavailability of microencapsulated cinnamaldehyde (CNMA) was investigated in male F344 rats. Rats were gavaged with CNMA in corn oil using either microencapsulated or the neat chemical at doses of 50, 250, and 500 mg/kg. No differences between the two formulations at any of the doses were found in either CNMA blood concentration profiles or in the rate of urinary hippuric acid excretion. Both formulations showed a low bioavailability (< 20%) at 250 and 500 mg/kg. Regardless of the formulation used, oral gavage of CNMA significantly increased the urinary excretion of hippuric acid. About 75% of the dose of CNMA was metabolized to hippuric acid and recovered in the urine. The total amount of hippuric acid recovered in a 50-hr urinary collection correlated well with the CNMA dose. The data suggest that there was complete release of CNMA from the microcapsules and that microencapsulation of CNMA does not affect its bioavailability or its metabolism. Since CNMA microcapsules are stable in rodent diet, the microencapsulation of CNMA, and perhaps other labile chemicals, will prevent degradation and facilitate the testing of such compounds in toxicology studies.

Comparison of the toxicity of citral in F344 rats and B6C3F1 mice when administered by microencapsulation in feed or by corn-oil gavage

A study of the potential effects of microencapsulation on the toxicity of citral was conducted in 14-day continuous feeding studies with both sexes of F344 rats and B6C3F1 mice. Toxicity by the feeding route was compared with that from bolus doses of the neat chemical in corn oil administrated by gavage. Both sexes of rats and mice were given diet containing 0, 0.63, 1.25, 2.5, 5 and 10% citral microcapsules. These feed formulations were equivalent to daily doses of 0, 142, 285, 570, 1140 and 2280 mg citral/kg body weight for rats and 0, 534, 1068, 2137, 4275 and 8550 mg citral/kg body weight for mice. The daily gavage doses were 0, 570, 1140 and 2280 mg citral/kg body weight for both sexes of rats, and 0, 534, 1068 and 2137 mg citral/kg body weight for both sexes of mice. Citral microcapsules administered in the diet did not cause mortality in mice or rats. Toxicity was confined to decreases in body weight at the 10% concentration in mice, at the 5 and 10% concentrations in rats, and decreases in absolute weights of the liver, kidney and spleen at the 10% concentration in rats. The only histopathological change observed was minimal to mild hyperplasia and/or squamous metaplasia of the respiratory epithelium in the anterior portion of the nasal passages of rats fed 5 or 10% citral microcapsules. By contrast, citral gavage caused mortality in five out of five male and female mice at 2137 mg/kg body weight, and in two out of five male mice at 1068 mg/kg body weight. There were dose-related increases in absolute liver weights of male and female mice. Cytoplasmic vacuolization of hepatocytes occurred in all female mice gavaged with 1068 and 2137 mg citral/kg body weight, and in male mice from the 2137 mg/kg dose group. Necrosis, ulceration and/or acute inflammation of the forestomach occurred in the high-dose mice of both sexes. Inflammation and/or hyperplasia of the forestomach occurred in about half of the male and female mice dosed with 1068 mg citral/kg. Citral gavage at doses that were equivalent to up to 10% in the diet (2280 mg/kg body weight) did not cause toxicity in rats, except for minimal hyperplasia of the squamous epithelium of the forestomach in high-dose males.(ABSTRACT TRUNCATED AT 400 WORDS)