Effects of three biodiesels and a low sulfur diesel in male rats--a pilot 4-week oral study.

Because of the accessible and renewable nature of feedstock and the potential for the reduction of harmful combustion emissions and greenhouse gases, biodiesels have received increasing interest as an alternate fuel. Oral exposure to biodiesels is a concern because of contact during refuelling, accidental ingestion and exposure through ground water contamination. Although biodiesels from various feedstock are in use commercially and experimentally, very little is known about their potential adverse effects and no data is available on their potential for ground water contamination. A study was performed on male rats following oral treatment with experimental biodiesels (dissolved in corn oil) derived from canola oil (Bio-C), soy oil (Bio-S) and fish oil (Bio-F), at 500 mg/kg body weight/day, 5 days per week, for 4 weeks. Separate groups of animals were treated with low sulfur diesel (LSD) for comparison purpose, and with corn oil alone to serve as control. The potential for ground water contamination by biodiesels was investigated by the preparation of water-accommodated fractions (WAF) followed by gas chromatographic analysis. WAF from Bio-F and Bio-S was found to have the highest level of dichloromethane extractable materials. Gas chromatographic analysis indicated that the extractable materials from biodiesels contained much higher proportion of C15-C30 materials than LSD. Increased liver weight was observed in animal treated with Bio-C, Bio-S and LSD and decreased thymus weight was found in those treated with Bio-S. Histopathological changes typical of male-rat specific hyaline-droplet nephropathy were detected in kidney tubules of animals treated with LSD, Bio-S and Bio-C. Mild adaptive changes were observed in thyroids of animals treated with LSD, Bio-S and Bio-F. Clinical chemical and biochemical changes were confined to Bio-S and LSD treated rats and included elevation in some hepatic phase-I and phase-II drug metabolizing enzymes and hepatic palmitoyl Co-A oxidase, and elevated urinary concentrations of ascorbic acid and albumin. At the given dose level of 500 mg/kg bw/day, the overall treatment-related effects of biodiesels and LSD are mild, and the severity of the treatment effects may be ranked as: LSD>Bio-S>Bio-C>Bio-F. Considered together with the presence of a higher level of water extractable materials, Bio-S may be more of a concern for potential human health than Bio-C and Bio-F in an oral exposure scenario. Further studies are needed to identify and characterize the constituents contributing to the treatment-related effects specific to these experimental biodiesels.

Behavioral and thyroid effects of in utero and lactational exposure of Sprague-Dawley rats to the polybrominated diphenyl ether mixture DE71.

Exposure of rodents during gestation and lactation to polybrominated diphenyl ethers (PBDEs) has been reported to disrupt neurobehavioral function in offspring, as well as to disrupt thyroid function. To assess this we evaluated development and behavior after gestational and lactational exposure to the technical PBDE mixture DE71. Pregnant Sprague-Dawley rats were exposed to 0, 0.3, 3.0 or 30 mg/kg/day of DE71 from gestation day 1 to postnatal day (PND) 21 and were assessed on a wide range of behavioral functions from early postnatal period until old age (PND 450). DE71 exposure decreased thyroid hormone levels (T3 and T4) in mothers and offspring with offspring being more sensitive that mothers. Developmental landmarks, neuromotor function, anxiety, learning and memory were not affected by DE71 at any age. DE71 produced small changes in motor activity rearing only at PND 110 but not at any other age and no other activity measure was altered by DE71. Cholinergic sensitivity measured by nicotine-stimulated motor activity was not affected by perinatal DE71 exposure. Acoustic startle responses were potentiated by DE71 at PND 90 indicating delayed effects on sensory reactivity. Habituation was measured in motor activity tests at five ages but was not altered by DE71 at any age. Habituation measured in startle tests was also not affected by exposure to DE71. For thyroid hormone levels at PND 21, the lowest adverse effect level was 3.0 mg/kg. Few behavioral effects were observed and the lowest adverse effect level was 30 mg/kg. Our results confirm that DE71 produces transient effects on thyroid hormone levels but does not result in learning or motor impairment and does not alter non-associative learning (habituation).

Effects of acute exposure to PCBs 126 and 153 on anterior pituitary and thyroid hormones and FSH isoforms in adult Sprague Dawley male rats.

3,3'4,4',5-Pentachlorobiphenyl (PCB 126) and 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153) were administered to adult male rats in order to identify sensitive indicators of endocrine disruption. We tested the hypothesis that PCB exposure modifies follicle-stimulating hormone (FSH) pituitary isoforms, as well as the pituitary and serum concentrations of FSH, luteinizing hormone (LH), growth hormone, prolactin, and thyroid-stimulating hormone (TSH). Effects on serum levels of thyroxine (T4) and testosterone (T), and prostate androgen receptor content, were also tested. In one experiment, 5 groups of 8 rats each received two i.p. injections, one day apart, of either corn oil or 6.25, 25, 100 or 400 micrograms/kg/day of PCB 126. Decreases (p < 0.05) in the serum concentrations of T4 and LH started at doses of 25 and 100 micrograms/kg/day, respectively. Serum FSH concentrations were reduced (p = 0.07) in the highest dose group. In contrast, pituitary content of FSH and LH increased with PCB-126 doses (p = 0.004, p = 0.002, respectively). Despite changes in reproductive hormones, PCB-126 had no effect on the androgen receptor content of the prostate. The effect of PCB-126 was tested in the hemicastrated rat, and suggested adverse effects on testosterone secretion. To test the effects of PCB exposure on FSH pituitary isoforms, 4 groups of 10 male rats received two i.p. injections, one day apart, of either corn oil, PCB 153 (25 mg/kg/day), estradiol-17 beta (E2; 20 micrograms/kg/day), or PCB 126 (0.1 mg/kg/day). Serum T4 levels were higher (p < 0.01) in the E2 and PCB 153 groups, and slightly reduced in the PCB 126-treated groups, compared to controls. Simultaneous purification of pituitary FSH and TSH isoforms was performed by HPLC, using two chromatofocusing columns in series. In contrast to TSH isoforms, the distribution of FSH isoforms over the chromatography run differed slightly between treatment groups; the amounts of FSH isoform eluted during the pH gradient were lower (p < 0.05) in E2 and PCB 153-treated rats than in control or PCB 126-treated rats. The similarity between the effects of E2 and PCB 153 on T4 and FSH isoforms supports the contention that PCB 153 possesses estrogenic properties. Serum LH and T4 concentrations were the most sensitive and practical endocrine indicators of PCBs 126 and 153 exposure in male rats.

Effects of postnatal exposure to mixtures of non-ortho-PCBs, PCDDs, and PCDFs in prepubertal female rats.

There are concerns that postnatal exposure to organochlorines present in breast milk could lead to adverse health effects. We reconstituted four mixtures of aryl-hydrocarbon receptor (AhR) agonists (3 non-ortho polychlorinated biphenyls [PCBs], 6 polychlorinated dibenzodioxins [PCDDs], 7 polychlorinated dibenzofurans [PCDFs], or all 16 chemicals together [referred to as AhRM]) based on their concentrations in breast milk, and examined their effects following exposure by gavage from day 1 until day 20 of age. Female neonates received dosages of AhRM equivalent to 1, 10, 100, or 1000 times the amount consumed by an infant over the first 24 days of life. Other groups received the PCBs, the PCDDs, or the PCDFs at the 1000x level. All rats were sacrificed at 21 days of age. Changes in ethoxyresorufin-o-deethylase hepatic activity, thymus and body weights, and serum thyroxin were linked to the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxic equivalents (TEQ) of the four mixtures (1000x-AhRM > PCDDs > PCBs > PCDFs). To test for AhRM antiestrogenicity, two additional groups received 1.5 microg/kg of 17alpha-ethynyl estradiol (EE) with or without the 1000x-AhRM. The AhRM had no effect on uterine weight or EE-stimulated uterine growth. The actions of the combined EE and AhRM treatments suggest additive effects in decreasing pentoxyresorufin-o-deethylase activity and spleen weight, but nonadditive/antagonistic effects on adrenal weight and serum thyroxin. In conclusion, (1) 10x-AhRM had no detectable effects, (2) TEQ values relate to observed toxicities, even when testing complex mixtures of AhR agonists, and (3) indications of tissue-specific additive and nonadditive/antagonistic effects, but no synergism, were observed when doses of AhRM were increased, or combined with EE.

Uranyl nitrate: 91-day toxicity studies in the New Zealand white rabbit.

These studies were undertaken to derive a lowest-observed-adverse-effect level (LOAEL) in the New Zealand White rabbit following a 91-day exposure to uranium (U, as uranyl nitrate hexahydrate, UN) in drinking water. Males were exposed for 91 days to UN in their drinking water (0.96, 4.8, 24, 120, or 600 mg UN/L). Subsequently, females were similarly exposed for 91 days (4.8, 24, or 600 mg UN/L). Control groups were given tap water (< 0.001 mg U/L). Regular observations were recorded, and urine was collected periodically. Four males showed evidence of Pasteurella multocida infection and were excluded from the study. Following the study, all animals were euthanized, and multiple hematological and biochemical parameters were determined. Necropsies were conducted, and histopathological examination was performed. The hematological and biochemical parameters were not affected in a significant exposure-related manner. Dose-dependent differences consisted of histopathological changes limited primarily to kidney. Changes in renal tubules were characteristic of uranium toxicity. Based on changes in the tubular nuclei, the 91-day LOAEL for males in this study is 0.96 mg UN/L drinking water. The females drank 65% more water than the males, yet appeared to be less affected by the exposure regimen, although they also developed significant tubular nuclear changes in their lowest exposure group, deriving a LOAEL of 4.8 mg UN/L. Tissue uranium residue studies suggested that pharmacokinetic parameters for the males and females differ, possibly accounting for the difference in observed sensitivity to UN. An adverse effect of P. multocida infection cannot be excluded.

Uranyl nitrate: 28-day and 91-day toxicity studies in the Sprague-Dawley rat.

Although uranium (U) is a classic experimental nephrotoxin, there are few data on its potential long-term chemical toxicity. These studies were undertaken to derive a no-observed-adverse-effect level (NOAEL) in male and female Sprague-Dawley rats following 91-day exposure to uranium (as uranyl nitrate hexahydrate, UN) in drinking water. Following a 28-day range-finding study, five groups of 15 male and 15 female weanling rats were exposed for 91 days to UN in drinking water (0.96, 4.8, 24, 120, or 600 mg UN/L). A control group was given tap water (< 0.001 mg U/L). Daily clinical observations were recorded. Following the study, animals were euthanized and exsanguinated, and multiple hematological and biochemical parameters were determined. Necropsies were conducted, and multiple tissues were sampled for histopathological examination. The hematological and biochemical parameters were not affected in a significant exposure-related manner. Although there were qualitative and slight quantitative differences between males and females, histopathological lesions were observed in the kidney and liver, in both males and females, in all groups including the lowest exposure groups. Renal lesions of tubules (apical nuclear displacement and vesiculation, cytoplasmic vacuolation, and dilation), glomeruli (capsular sclerosis), and interstitium (reticulin sclerosis and lymphoid cuffing) were observed in the lowest exposure groups. A NOAEL was not achieved in this study, since adverse renal lesions were seen in the lowest exposed groups. A lowest-observed-adverse-effect level of 0.96 mg UN/L drinking water can be reported for both the male and the female rats (average dose equivalent 0.06 and 0.09 mg U/kg body wt/day, respectively).

Uranyl nitrate: 91-day exposure and recovery studies in the male New Zealand white rabbit.

This study was undertaken to examine the reversibility of renal injury in the male New Zealand White rabbit subsequent to a 91-day exposure to uranyl nitrate (UN) in drinking water, followed by various recovery periods. Specific pathogen-free (SPF) animals were exposed for 91 days to UN in their drinking water (24 or 600 mg UN/L). Control groups were given municipal tap water (< 0.001 mg U/L). Regular clinical observations were recorded, and urine was collected periodically. Recovery periods between the last UN exposure and termination were 0, 8, 14, 45, or 91 days. Following the study, all animals were anesthetized and terminated by exsanguination, and multiple hematological and biochemical parameters were determined. Necropsies were conducted, and histopathological examination was performed. Exposure-related histopathological changes were observed only at much higher doses than in our previous male rabbit study where non-SPF-free animals had been used. Minor increases in kidney to body weight ratios were observed in the high-dose groups following exposure and early recovery. Renal tubular injury with degenerative nuclear changes, cytoplasmic vacuolation, and tubular dilation was seen in the high-dose group, without consistent resolution even after 91 days recovery. Animals ingested approximately 33% more uranium per day in this study than did males in a comparable dose group in the previous study, yet their kidney tissue uranium residues were 30% lower. These results suggest that SPF rabbits are less sensitive to uranyl injury than the non-SPF animals. The lowest-observed-adverse-effect level is estimated to lie at or below 24 mg UN/L.

Systemic toxicity of a bitumen upgrading product in the rat following subchronic dermal exposure.

The subchronic toxicity following dermal exposure to a synthetic fuel, heavy gas oil No. 2 fraction of bitumen upgrading product (B-HGO II) was studied in the rat. B-HGO II was applied on the dorsal skin of rats at doses of 8, 20, 50 and 125 mg/kg bw/day daily for 13 weeks. Control animals received normal saline and positive controls received a medium-boiling coal liquefaction product (CLP) at 125 mg/kg bw/day. Both male and female rats in the treatment groups had reduced body weight gain, and males in the highest dose group were terminated in the 5th week due to overt toxicity. Increased liver weight relative to body weight was observed in males and females starting at 8 mg/kg. Increased relative heart and spleen weights were observed in males and females starting at the two intermediate doses (20, 50 mg/kg). Increased relative kidney weight was detected in males at 50 mg/kg and females at 125 mg/kg. Increased serum cholesterol was observed in both sexes starting at 50 mg/kg while elevated serum glucose was present in females starting at 8 mg/kg. Significant changes in AH, APDM and EROD activities were observed in treated rats of both sexes. Reduced red blood cell counts were detected in males starting at 8 mg/kg and females at 20 mg/kg. Microscopic examination of blood smears, spleen and hemosiderin accumulation patterns, as well as analysis of FEP and serum TIBC levels indicated that the cause of anemia was primarily intravascular hemolysis and secondarily iron deficiency. Marked thymic atrophy and thyroid abnormalities were the most prominent histological changes followed by changes in bone marrow (myelofibrosis) and liver. Both B-HGO II and CLP (positive control) caused kidney changes characterized by cytoplasmic inclusions and lesions in the tubular cells, which were observed in 50 mg/kg males but not in the females. B-HGO II was considered to be toxic at a subchronic dermal exposure level as low as 8 mg/kg/day.

Stimulating effects of 4-chlorodiphenyl ether on surgically induced endometriosis in the mouse.

The objectives of this study were to evaluate the effects of repeated injection of 4-chlorodiphenyl ether (4-CDE) on the survival and growth of endometriotic implants. Endometriosis was surgically induced in adult female B6C3F1 mice (n = 25) after ovariectomy. Seven days later the animals were randomly divided into five groups and treated with vehicle alone (corn oil, control), or 20 micrograms/kg/d estrone (positive control), or 10, 75, or 150 mg/kg/d 4-CDE in vehicle for 28 d. The number and size of the endometriotic cysts were recorded and the cysts were then harvested for histology at necropsy 2 d after the last treatment. There were significantly more cysts formed (P < 0.05) in the 150 mg/kg/d 4-CDE group compared to the vehicle-treated control (60 vs. 8%), but not compared to the estrone-treated positive control (90 vs. 60%). Hepatic enzymes were evaluated to confirm exposure and to further clarify the enzymatic route of 4-CDE biotransformation by the liver. In conclusion, the repeated exposure to 4-CDE increased the survival rates of the endometriotic cysts in the ovariectomized mouse, which suggests that 4-CDE mimics estrogen effects on endometriotic tissues because the endometrial tissues are dependent on estrogenic support for survival.

Effects of dibromoacetonitrile on rats following 13-week drinking water exposure.

The subchronic toxicity of dibromoacetonitrile (DBAN), a disinfection by-product in drinking water, was studied in the rat. Male (180+/-18 g) and female (152+/-9 g) Sprague-Dawley rats (10 animals per group) were fed DBAN in organic-free distilled water at concentrations of 0.1, 1, 10 and 100 ppm for 13 weeks. Control rats received organic-free distilled water only. Water intakes in the highest dose males and females were reduced by 25 and 32% as compared to the controls, respectively (P<0.05), with no significant reductions in food consumption and body weight gain. The organ to body weight ratio was significantly increased in the highest-dose males and females for kidneys but not for the brain, liver, spleen, thymus and testicles. In the males, decreases were detected in serum uric acid levels at 1 and 100 ppm, and in urinary uric acid at 10 and 100 ppm. Decreased serum protein was detected in the highest-dose males and decreased serum LDH was found in the highest-dose females. Both the white blood cell and lymphocyte counts were significantly elevated in the highest-dose females. A significant increase in hepatic catalase activity was observed only in males starting at 1 ppm, and increased palmitoyl-CoA oxidase (PCO) activity was found in males and females of the highest dose group. In the males, decreased thiobarbituric acid reactive substance (TBARS) level was detected in the liver at 1.0 and 100 ppm groups, while increased TBARS was found in the serum at 100 ppm DBAN. No treatment-related changes were detected in the activities of hepatic benzyloxyresorufin O-dealkylase (BROD), pentoxyresorufin O-dealkylase (PROD) and ethoxresorufin O-deethylase (EROD), and in hepatic UDP-glucuronosyltransferase (UDPGT) and glutathione S-transferases (GST). Although DBAN is a potent inhibitor of hepatic aldehyde dehydrogenase (ALDH) and GST in vitro, there was no evidence of suppression of these enzymes in the treated animals. Mild histological changes were detected in animals receiving the highest dose, consisting of collapsed angularity, increased epithelial height in the thyroid of both sexes, and cytoplasmic vacuolation and nuclear vesiculation in the thyroid of females, increased myeloid to erythroid ratio in the bone marrow of both sexes, and cytoplasmic inclusions in the proximal tubules of male kidneys. In summary, treatment effects occurred predominantly at 100 ppm and included in both sexes: increased kidney weights, histological changes in the thyroid and bone marrow, and increased peroxisomal enzyme activities; and in males: decreased serum and urinary uric acid levels, and indication of oxidative stress. The no-observed-adverse-effect level (NOAEL) was therefore judged to be 10 ppm, equivalent to 1.11 and 1.21 mg/kg/day in the males and females, respectively.

Effects of bis(4-chlorophenyl) sulfone on rats following 28-day dietary exposure.

The short-term oral toxicity of a recently identified environmental pollutant, bis(4-chlorophenyl) sulfone (BCPS), was studied. Groups of male Sprague-Dawley rats (n = 6) were administered BCPS via the diet at 0 (control), 10, 100, or 1000 ppm for 4 wk. Additional control and 1000 ppm groups were also treated for 1, 2, and 3 wk. At termination, high-dose animals showed depressed growth rate and food consumption, and 1 high dose animal in each of the wk-1, -3, and -4 groups had marked hematuria. Increased liver to body weight ratio was present at 100 ppm and increased kidney to body weight ratio at 1000 ppm. Marked increases in hepatic benzoylresorufin O-dealkylase (BROD) and pentoxyresorufin O-dealkylase (PROD) activities were detected starting at 10 ppm. There was a significant decrease in methoxyresorufin O-dealkylase (MROD) activity at 1000 ppm. Hepatic UDP-glucuronosyltransferase (UDPGT) and glutathione S-transferase (GST) activities also increased starting at 100 ppm. A marked increase in urinary excretion of ascorbic acid was apparent starting at 10 ppm, while there were no changes in urinary N-acetylglucosaminidase (NAG) activity and protein levels. A threefold increase in serum cholesterol and a 30% increase in platelet counts were observed in the 1000 ppm group. Levels of thiobarbituric acid-reactive substances (TBARS) were increased by threefold in the liver of the high-dose animals but were not significantly altered in the serum. Tissue BCPS concentrations were dose dependent and followed the order: adipose tissue >>> liver > kidneys > brain, spleen, lungs. In the time-course study involving the control and high-dose groups, most of the treatment effects were clearly present in wk 1, and the severity of the effects remained at more or less the same levels thereafter. The exceptions were hepatic BROD and PROD activities, which showed a trend toward further increases with time of treatment. Liver and adipose tissue concentrations of BCPS remained unchanged from wk 1 to wk 4, while kidney concentrations increased with time. The results indicated that BCPS produced hepatic effects at the lowest dose level tested (10 ppm in the diet or 0.8 mg/kg/d).

Subchronic toxicity of benzothiophene on rats following dietary exposure.

The systemic and neurobehavioral effects of benzo[b]thiophene (routinely referred to as benzothiophene) were studied in rats following 13-wk oral exposure. Male (170 +/- 16 g) and female (146 +/- 12 g) Sprague-Dawley rats (10 animals per group) were fed diet containing 0.5, 5, 50, or 500 ppm benzothiophene for 13 wk. Control animals were given rat feed plus vehicle (corn oil) only. No clinical signs of toxicity and neurobehavioral effects were observed using screening tests that included cage-side observations, righting reflex, open field activities, and forelimb and hindlimb grip strength. Elevated serum aspartate aminotransferase activity and bilirubin level were observed in highest dose females. Except for a statistically significant decrease in hematocrit in the highest dose males, benzothiophene exerted no marked effects on hematological parameters. Benzothiophene exposure did not result in alterations in hepatic alkaline phosphatase activity, or the typical hepatic phase I (aniline hydroxylase, ethoxyresorufin O-deethylase, pentoxyresorufin O-dealkylase, aminopyrine N-demethylase) and phase II (UDP-glucuronosyltransferase, glutathione S-transferase) drug-metabolizing enzyme activities. No significant elevation in urinary ascorbic acid, protein, and N-acetylglucosaminidase activity was detected in the treated animals. Peribiliary fibrosis was the most significant histological change and occurred in the liver of females in the 50 and 500 ppm groups. Mild epithelial hyperplasia in the renal pelvis was detected in the majority of 5 and 50 ppm females, with epithelial hyperplasia in the urinary bladder observed in the 50 ppm females. In males, increased incidence and severity of mild binucleation of hepatocytes and mild thickening of the basement membrane in kidney cortex were observed at 500 ppm. Benzothiophene was not detected in the urine of high-dose animals at the termination of the experiment. Based on the kidney, hepatic, and hematocrit changes, the no-observed-adverse-effect level (NOAEL) in the diet was determined to be 0.5 ppm (0.04 mg/kg/d) for females and 50 ppm (3.51 mg/kg/d) for males.

Mixture effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin and polychlorinated biphenyl congeners in rats.

Concern of the toxic effects and bioaccumulation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and polychlorinated biphenyls in the environment continues to be a focus of research in persistent organochlorine contaminants. Groups of five adult female S.D. rats were administered by gavage 0, 2.5, 25, 250 or 1000 ng TCDD/kg body weight/day or TCDD in combination with a mixture of PCB congeners (PCBs) at 2 or 20 microg/kg b.w./day for a period of 28 days. Growth suppression, increased absolute and relative liver weights, and decreased thymic weight were observed in either the 1000 ng TCDD group alone, or the groups receiving a mixture of 1000 ng TCDD + 2 microg PCBs. The TCDD induced increases in liver and thymic weights were not altered by co-administration with PCBs, however, growth suppression appeared to be more pronounced in the group receiving 1000 ng TCDD + 2 microg PCBs than with TCDD alone. Treatment with TCDD at 250 ng and 1000 ng/kg resulted in a significant increase in hepatic microsomal methoxy resorufin-O-demethylase and ethoxy resorufin-O-deethylase activities which were antagonized by co-administration with PCBs. Similarly, effects of 250 ng TCDD on serum cholesterol and liver UDP glucuronosyl transferase activity and ascorbic acid were significantly reduced by co-administration with 20 microg PCBs. Other biochemical effects elicited by treatment with 1000 ng TCDD, but not affected by co-administration with PCBs include the following: increased serum albumin, decreased liver vitamin A, and increased kidney vitamin A and liver microsomal glutathione-S-transferase activity. While decreased hemoglobin, platelet, packed cell volume and red cell indices were observed in TCDD treated rats, no interactive effects were seen. The above results indicate that the mixture effects of PCBs and TCDD may be additive or antagonistic depending on the dose level and endpoints measured. For the purpose of predicting mixture effects, knowledge of mechanisms of action and toxicokinetics is required.

Effects of tris(4-chlorophenyl)methanol on the rat following short-term oral exposure.

The systemic toxicity of tris(4-chlorophenyl)methanol (TCPM) was studied in male and female rats following 4 weeks dietary exposure dosed at 1, 10 and 100 ppm. An increased spleen to body weight ratio was observed in males at 10 and 100 ppm and in females at 100 ppm. An increased liver to body weight ratio was detected in both sexes at 100 ppm. Dose-related increases in hepatic Phase-I (AH, APDM, EROD and PROD) and Phase-II (UDPGT, GST) enzyme activities were observed generally at 10 and 100 ppm, with the elevation in PROD activity being the most marked. Increased urinary ascorbic acid was detected in both males and females after 1 week of treatment at 100 ppm and after 4 weeks of treatment at 10 and 100 ppm. At 10 and 100 ppm, elevated % lymphocytes were found in males, and higher white blood cell and lymphocyte counts were observed in females. In the liver, mild to moderate cytoplasmic changes consistent with proliferation of smooth endoplasmic reticulum were present in rats of both sexes at 10 and 100 ppm, and increased number of hepatocytes undergoing apoptosis were observed in male rats at 100 ppm. Mild splenic changes consisting of sinus hyperplasia in males and females at 100 ppm and mantle zone atrophy in males at 100 ppm were also observed. It was concluded that TCPM at a dietary concentration of 10 ppm (equivalent to 1.2 mg/kg/day) produced systemic changes in rats that included various hepatic effects, increased splenic weight, and modulations in white blood cells and lymphocyte counts.

Absorption and retention of uranium from drinking water by rats and rabbits.

Uranium in the form of uranyl nitrate hexahydrate was administered in drinking water to Sprague-Dawley rats for periods of 28 and 91 d and New Zealand White rabbits for 91 d. The animals consumed food and water ad libitum. Subgroups of rabbits were followed for recovery periods of up to 91 d; 24-h collections of urine and feces were performed for some of the rabbits at various times during the exposure and recovery periods. At the end of the experiment, all animals were sacrificed and femur and kidney samples were analyzed for uranium residues. The results show that both rats and rabbits absorb about 0.06% of ingested uranium in the gastrointestinal (GI) tract. The distribution and retention of uranium in the skeleton and kidneys of rats are comparable to parameters reported for humans. The retention half-time in rabbit bone is substantially longer than for humans. The implications of extrapolating from animal data to effects on humans are discussed.

Effects of an ethanol-gasoline mixture: results of a 4-week inhalation study in rats.

The inhalation toxicity of an ethanol-gasoline mixture was investigated in rats. Groups of 15 male and 15 female rats were exposed by inhalation to 6130 ppm ethanol, 500 ppm gasoline or a mixture of 85% ethanol and 15% gasoline (by volume, 6130 ppm ethanol and 500 ppm gasoline), 6 h a day, 5 days per week for 4 weeks. Control rats of both genders received HEPA/charcoal-filtered room air. Ten males and ten females from each group were killed after 4 weeks of treatment and the remaining rats were exposed to filtered room air for an additional 4 weeks to determine the reversibility of toxic injuries. Female rats treated with the mixture showed growth suppression, which was reversed after 4 weeks of recovery. Increased kidney weight and elevated liver microsomal ethoxyresorufin-O-deethylase (EROD) activity, urinary ascorbic acid, hippuric acid and blood lymphocytes were observed and most of the effects were associated with gasoline exposure. Combined exposure to ethanol and gasoline appeared to exert an additive effect on growth suppression. Inflammation of the upper respiratory tract was observed only in the ethanol-gasoline mixture groups, and exposure to either ethanol and gasoline had no effect on the organ, suggesting that an irritating effect was produced when the two liquids were mixed. Morphology in the adrenal gland was characterized by vacuolation of the cortical area. Although histological changes were generally mild in male and female rats and were reversed after 4 weeks, the changes tended to be more severe in male rats. Brain biogenic amine levels were altered in ethanol- and gasoline-treated groups; their levels varied with respect to gender and brain region. Although no general interactions were observed in the brain neurotransmitters, gasoline appeared to suppress dopamine concentrations in the nucleus accumbens region co-exposed to ethanol. It was concluded that treatment with ethanol and gasoline, at the levels studied, produced mild, reversible biochemical hematological and histological effects, with some indications of interactions when they were co-administered.

90-day repeated inhalation exposure of surfactant Protein-C/tumor necrosis factor-alpha, (SP-C/TNF-alpha) transgenic mice to air pollutants.

Tumor necrosis factor (TNF)-alpha, a cytokine present in inflammed lungs, is known to mediate some of the adverse effects of ozone and inhaled particles. The authors evaluated transgenic mice with constitutive pulmonary expression of TNF-alpha under transcriptional regulation of the surfactant protein-C promoter as an animal model of biological susceptibility to air pollutants. To simulate a repeated, episodic exposure to air pollutants, wild-type and TNF mice inhaled air or a mixture of ozone (0.4 ppm) and urban particles (EHC-93, 4.8 mg/m3) for 4 h, once per week, for 12 consecutive weeks and were sacrificed 20 h after last exposure. TNF mice exhibited chronic lung inflammation with septal thickening, alveolar enlargement, and elevated protein and cellularity in bronchoalveolar lavage fluid (genotype main effect, p < .001). Repeated exposure to pollutants did not result in measurable inflammatory changes in wild-type mice and did not exacerbate the inflammation in TNF mice. The pollutants decreased recovery of alveolar macrophages in tavage fluid of both wild-type and TNF mice (exposure main effect, p < .001). Exacerbation of the rate of protein nitration reactions specifically in the lungs of TNF mice was revealed by the high ratio of 3-nitrotyrosine to L-DOPA after exposure to the air pollutants (Genotype x Exposure factor interaction, p = .014). Serum creatine kinase-MM isoform increased in TNF mice exposed to pollutants (Genotype X Exposure factor interaction, p = .043). The marked pollutant-related nitration in the lungs of the TNF mice reveals basic differences in free radical generation and scavenging in the inflamed lungs in response to pollutants. Furthermore, elevation of circulating creatine kinase-MM isoform specifically in TNF mice exposed to pollutants suggests systemic adverse impacts from lung inflammatory mediators, possibly on muscles and the cardiovascular system.

Activity of erythrocyte delta-aminolevulinic acid dehydratase in the female cynomolgus monkey (Macaca fascicularis): kinetic analysis in control and lead-exposed animals.

Kinetic analysis of erythrocyte delta-aminolevulinic acid dehydrase (delta-ALAD) from female cynomolgus monkeys revealed differences in pH optimum and Michaelis constants according to their exposure to lead. In vitro incubation of delta-ALAD with 5 mM dithiothreitol (DTT) or 100-200 microM zinc resulted in an enhanced enzyme activity being expressed. These effects were additive. Activation with DTT or zinc resulted in the abolition of pH differences between control and exposed animals and revealed an increased quantity of enzyme in exposed animals. delta-ALAD in control monkeys was observed to be very sensitive to inhibition by lead in vitro with an apparent inhibition constant (Ki) of 0.12 microM. The effect of lead on monkey delta-ALAD enzyme kinetics is similar to that seen with human samples and thus is a useful model for measuring biological response to lead exposure.

Kinetic parameters of the inhibition of red blood cell aminolevulinic acid dehydratase by triethyl lead and its reversal by dithiothreitol and zinc.

In chronic or acute exposure to triethyl lead, a de novo synthesis of aminolevulinic acid dehydratase (delta-ALAD) in bone marrow and an increased activity in circulating red blood cells can be demonstrated by activating the enzyme with dithiothreitol (DTT) and zinc. We determined the median inhibitory concentration and the apparent inhibition constant for triethyl lead on delta-ALAD. After dosing with triethyl lead, in vivo inhibition of ALAD only occurred at the high dose, but activation analysis in vitro showed increased ALAD activity to be present at all dose levels in a dose-dependent fashion. The use of an activation assay for red blood cell ALAD may have value as a bio-effects monitor of exposure to organic lead.

Hemotoxic effects of a dermally applied coal coprocessing product in the rat.

The present study was conducted as part of a larger project to determine the toxicity of dermally applied coal coprocessing products. Groups of male and female rats were administered, dermally, heavy gas oil II (HGOII) at 8.7, 20.8, 50.0 and 120 mg kg(-1) body wt, day(-1) for 91 days. A coal liquefaction product was given as positive control at 120 mg kg(-1) body wt. day(-1). Saline was used on control animals. At termination, the blood and bone marrow were taken from the animals and subjected to hematological examination. Dose-dependent hematological effects were seen in peripheral blood in HGOII-treated animals and consisted of significantly reduced hemoglobin, hematocrit, red cell count and platelet count. Mean corpuscular volume was increased, along with mean corpuscular hemoglobin, at the highest dose level. Red cell protoporphyrin, total iron and total iron binding capacity were also significantly elevated at this dose level. Morphological analysis of blood showed increases in polychromatic red cells, schizocytes, Howell-Jolly bodies, injured cells, hypersegmented neutrophils and shift platelets primarily at the highest dose level. In addition, there was notable anisocytosis, microcytosis and macrocytosis. Quantitative bone marrow evaluation revealed a significant reduction in the myeloid/erythroid ratio for the three highest treatment levels of HGOII. These data indicate that the effect of HGOII on the hemopoietic system is a treatment-related, partially compensated, hemolytic anemia. The apparent reduction in myelopoiesis may be compensated for by a concurrent increase in marrow volume.