Testicular toxicity evaluation of arsenic-containing binary compound semiconductors, gallium arsenide and indium arsenide, in hamsters.

The testicular toxicities of gallium arsenide (GaAs), indium arsenide (InAs) and arsenic trioxide (As2O3) were examined by repetitive intratracheal instillation using hamsters. GaAs (7.7 mg/kg) and As2O3 (1.3 mg/kg) were instilled twice a week a total of 16 times and InAs (7.7 mg/kg) was instilled a total of 14 times. GaAs caused testicular spermatid retention and epididymal sperm reduction, though the degrees were less severe than those in rats shown in our previous experiment. InAs and As2O3 did not show any testicular toxicities. Serum arsenic concentration in GaAs-treated hamsters was less than half of that in As2O3-treated hamsters in which no testicular toxicities were found. Serum molar concentration of gallium was 32-times higher than that of arsenic in GaAs-treated hamsters. Therefore gallium may play a main role in the testicular toxicity of GaAs in hamsters.

Testicular toxicity of gallium arsenide, indium arsenide, and arsenic oxide in rats by repetitive intratracheal instillation.

The testicular toxicities of two compound semiconductor materials, gallium arsenide (GaAs) and indium arsenide (InAs), and arsenic oxide (As2O3) were examined in rats by repetitive intratracheal instillation of these substances in suspension twice a week, a total of 16 times. A single instillation dose was 7.7 mg/kg in the GaAs and the InAs groups and 1.3 mg/kg in the As2O3 group. A significant decrease in sperm count and significant increase in the proportion of morphologically abnormal sperm were found in the epididymis in the GaAs group. Especially, abnormal sperm with a straight head increased markedly in this group. In the GaAs-treated rats, there was 40-fold increase in the degenerating late elongated spermatids at the postspermiation stages, stages IX, XI, and XI. From these results, it is indicated that GaAs disturbed the spermatid head transformation at the late spermiogenic phases and caused spermiation failure. InAs caused a sperm count decrease in the epididymis, though its testicular toxicity was relatively weak compared with that of GaAs. As2O3, a probable dissolution arsenic product of GaAs and InAs in vivo, did not show any testicular toxicities in this study. It seems likely that, along with arsenics, gallium and indium play a role in the testicular toxicities of GaAs and InAs.

Chronic toxicity of indium arsenide and indium phosphide to the lungs of hamsters.

Chronic toxicity of indium arsenide (InAs) and indium phosphide (InP) was studied in male Syrian golden hamsters which received InAs or InP particles containing a total dose of 7.5 mg of arsenic or phosphorus by intratracheal instillations once a week for 15 weeks. As a control, hamsters were treated with the vehicle, phosphate buffer solution. During their total life span, the cumulative body weight gain of hamsters in the InAs group was suppressed significantly compared with that in the control group, but not in the InP group when compared with that in the control group. Concerning the histopathological findings of the lung, the incidence rates of proteinosis-like lesions, alveolar or bronchiolar cell hyperplasia, pneumonia, emphysema and metaplastic ossification observed in the InAs or InP group were significantly higher than those observed in the control group. From these results, it would seem that InAs and InP produced severe damage to the lungs of hamsters.

Chronic toxicity of tar from heavy-duty diesel exhaust following intratracheal instillations to the lungs of hamsters.

Chronic toxicity of tar from heavy-duty diesel exhaust (HD tar) was studied in male Syrian golden hamsters which received 15 mg, 7.5 mg or 1.5 mg of HD tar as the total dosages by intratracheal instillations once a week for 15 weeks. As a control group, hamsters were treated with the 0.1 ml of Tween 60: ethanol: phosphate buffer (pH 6.88, 0.25 M) solution (5.8: 8.7: 100 by volume) once a week in the same manner. The survival rate during the instillation period in the group given 15 mg of HD tar, the high-dose group of HD tar, was the lowest, and the effect was dose-dependent. However, the survival rates during the subsequent observation period showed no marked differences among HD tar treated groups. During their total life span, one papilloma in the larynx was seen in the 44 hamsters in the group given 1.5 mg of HD tar, one papilloma in the larynx was appeared in the 59 hamsters in the group given 1.5 mg of HD tar and one lung adenoma was developed in the 58 hamsters in the control group. There were no tumors in the respiratory tract in the group given 7.5 mg of HD tar. Concerning the histopathological findings of the lung, the incidence of alveolar cell or bronchiolar cell hyperplasia in the group given 1.5 mg of HD tar was significantly higher than that in the control group. From these results, although we could not observe any tumorigenicity or carcinogenic effect of HD tar, it would seem that HD tar caused weak but positive damage to the lungs of hamsters.

Effect of dietary vitamin A on forestomach tumorigenesis during the total and postinitiation stages in mice treated with high- or low-dose benzo(a)pyrene.

The effects of dietary vitamin A on forestomach tumorigenesis during the total stage of the initiation and postinitiation periods and during the postinitiation stage were evaluated in ICR/Jcl mice treated with either high or low doses of benzo(a)pyrene (B(a)P). In experiment 1, the animals were initiated with a high carcinogenic dose of B(a)P to a total of 20 mg, while in experiment 2 the animals were treated with a low dose of B(a)P to a total of 2 mg. A control group of animals received no carcinogens. Five different dietary levels of vitamin A supplements were used in each experiment and in the control study. In experiment 1, a high incidence of tumorigenesis was observed in every group, with 74% to 96% developing papilloma and 19% to 46% developing carcinoma. In experiment 2, the incidence of tumorigenesis in the high-dose vitamin A groups, including those given during the total and postinitiation stages, was found to be significantly reduced at 7.4%, compared with that in the low-dose vitamin A group of 57.7% (P < 0.05). These results suggest that a high dietary level of vitamin A can reduce the incidence of tumorigenesis when low carcinogenic dose levels of B(a)P are given in both the total and postinitiation stages.

Evaluation of carcinogenicity and chronic toxicity associated with orthopedic implants in mice.

The carcinogenicity and chronic toxicity of 316L stainless steel, nickel, Ti-6A1-4V, hydroxyapatite (HA)-coated Ti-6A1-4V, aluminum oxide containing yttrium oxide, and zirconium oxide containing yttrium oxide were evaluated by implanting solid rods of each material in the thigh muscle of C57BL/6N mice for 24 months. Nickel alloy showed high carcinogenic and toxic potencies, whereas other materials showed no evidence of them. Tumors retaining nickel alloys were malignant fibrous histiocytoma or fibrosarcoma. In some cases, lymphomata that seemed to develop spontaneously were found around the implants because lymphocytes were known to accumulate in chronic inflammatory lesions, and this phenomenon also might be applied to lymphoma.

Subchronic (12-week) inhalation toxicity study of methanol-fueled engine exhaust in rats.

To evaluate the inhalation toxicity to rats of exhaust at low concentration for longer periods, Fischer 344 rats were exposed to 3 concentrations of exhaust generated by an M85 methanol-fueled engine (methanol with 15% gasoline) without catalyst for 8 h/d, 6 d/wk for 4, 8, or 12 wk. Concentration- and time-dependent increase carboxyhemoglobin in the erythrocytes and decrease in cytochrome P-450 in the lungs were observed in all treated groups. Furthermore, significant increases in plasma formaldehyde were observed in all treated groups. Furthermore, significant increases in plasma formaldehyde were observed in the group exposed to the highest concentration of exhaust (carbon monoxide, 89.8 ppm; formaldehyde, 2.3 ppm; methanol, 8.1 ppm; nitrogen oxides, 22.9 ppm; nitrogen dioxide, 1.1 ppm) for 8 or 12 wk. No change of plasma folic acid was observed in any group, and no methanol or formic acid was detected in the plasma in any animals. Histopathologically, exposure-related changes were found only in the nasal cavity of the high-concentration group. Slight hyperplasia/squamous metaplasias of the respiratory epithelium lining the nasoturbinate and maxilloturbinate were observed after 4 wk of exposure, and the incidences and degrees of these lesions increased slightly with the exposure time. No changes were found in the olfactory epithelium of the nasal cavity. As judged by optical microscopy, the exhaust concentration with no effect on the nasal cavity under the experimental conditions was concluded to be the medium concentration level containing 0.55 ppm formaldehyde. In the present study, however, concentration- and time-dependent increase of carboxyhemoglobin in the erythrocytes and decrease of the lung P-450 level were observed. Therefore, further study on more long-term inhalation of lower concentrations of exhaust might be needed.

Recovery from changes in the blood and nasal cavity and/or lungs of rats caused by exposure to methanol-fueled engine exhaust.

One group of male, pathogen-free, Fischer 344 rats was exposed to about 17-fold diluted exhaust generated by an M85 methanol-fueled engine (methanol with 15% gasoline) without catalyst for 8 h, and then the rates of recovery from the resulting increased levels of plasma formaldehyde and carboxyhemoglobin in their erythrocytes were measured. The carboxyhemoglobin level in the erythrocytes was restored within 4 h, whereas the plasma formaldehyde level was still elevated after 4 h but was restored to the normal level within 8 h. No methanol or formic acid was detected in the plasma. Another group of rats was exposed to the same dilution of exhaust for 8 h/d for 7 d, and then the recovery from histopathological damage of the nasal cavity and lungs was also examined. Hyperplasia/squamous metaplasia and erosion of the respiratory epithelium lining the nasoturbinate, maxilloturbinate, or nasal septum, and infiltration of neutrophils into the submucosa at level 1 (level of the posterior edge of the upper incisor teeth) were observed immediately after the exposure period. Lesions of the respiratory epithelium at level 2 (incisive papilla) were less than those at level 1. Slight lesions at levels 1 or 2 were still noticed 1 wk after exposure, but not 4 wk after exposure. Just after exposure, decreases of Clara cells in the terminal bronchiolus and of cilia in the bronchial/bronchiolar epithelium were also observed. Moreover, focal hypertrophy of alveolar walls and increase of macrophages were observed in parts adjacent to respiratory bronchiolus. One week after the exposure period, these changes were no longer seen. These results indicate that changes in the blood and in the nasal cavity and lungs caused by methanol-fueled engine exhaust are reversible. However, complete recovery from damage of the nasal cavity caused by 7-d exposure to the exhaust takes 4 wk, and recovery from elevated plasma formaldehyde and erythrocyte carboxyhemoglobin levels caused by a single 8-h exposure takes 4-8 h.

Mutagenic activity of the leachate of municipal solid waste landfill.

Organic concentrates were recovered using XAD-2/8 resin adsorption from the leachates of municipal solid waste landfills and their mutagenic activities were tested for 8 months using the Ames Salmonella/microsome assay. Highly polluted leachates (COD and BOD > or = 40 mg/l) generally had equal or higher mutagenic activities than lightly polluted leachates (COD and BOD < 40 mg/l). But there was no clear difference in mutagenicity per amount of concentrate between the two leachates. These results suggest that the mutagenic activity of landfill leachate is decided to some degree by the organic concentration in the leachate. The mutagenic activities detected even in lightly polluted leachates were not so low as those of various kind of surface waters ever reported. It is suggested that it is important to investigate the mutagenic activity of the leachate for evaluation of the impact of landfill leachate on the environment.

Toxicity to rats of methanol-fueled engine exhaust inhaled continuously for 28 days.

Fischer 344 rats were exposed to three concentrations of exhaust generated by an M85 methanol-fueled engine (methanol with 15% gasoline) without catalyst for 8 h/d, 7 d/wk for 7, 14, 21, or 28 d. Concentration- and time-dependent yellowing of the fur was prominent in all treated groups. Concentration-dependent increases in the erythrocyte count, hematocrit, hemoglobin concentration, formaldehyde in plasma, and carboxyhemoglobin in the erythrocytes, and decrease in serum alkaline phosphatase activity were seen after all exposure periods. Histopathologically, lesions were found in the nasal cavity and lungs after 7 d of exposure. Squamous metaplasia of the respiratory epithelium of level 1 (level of the posterior edge of the upper incisor teeth) lining of the nasoturbinate and/or maxilloturbinate and infiltration of neutrophils into the submucosa, and decreases of Clara cells in the terminal bronchiolus and of cilia in the bronchiolar epithelium, were observed in the high-concentration group (carbon monoxide, 94 ppm; formaldehyde, 6.9 ppm; methanol, 17.9 ppm; nitrogen oxides, 52.7 ppm; nitrogen dioxide, 10.6 ppm). The histopathological extents of several lesions increased slightly with the exposure time. Slight squamous metaplasia and hyperplasia of the respiratory epithelium at level 1 were also observed in the medium-concentration group (one in three of the high-concentration group). No histopathological changes were found in the olfactory epithelium of the nasal cavity. In the low-concentration group (one in nine of the high-concentration group), no marked histopathological changes in these organs were observed. These results may suggest that the lesions observed in the nasal cavity of rats exposed to methanol-fueled engine exhaust were mainly caused by formaldehyde, although other components in the exhaust also may have affected nasal cavity and/or lungs to less extent.

The frequency of spontaneously-occurring neoplasms in the male Syrian golden hamster.

The frequency of spontaneously-occurring neoplasms in the male Syrian golden hamster, often used as a control in carcinogenic studies, was examined. The hamsters were divided into 2 groups: Group 1 received 0.1 ml of the phosphate buffer vehicle intratracheally once a week for 15 w; Group 2 received 0.1 ml of Tween 60:ethanol:buffer (5.3:8.7:100 by volume) in the same manner. The mean survival days of hamsters' total life-span were 574.9 +/- 176.1 d in Group 1 and 427.7 +/- 178.1 d in Group 2. Tumor incidence rates were 10.6% (16/148) in Group 1 and 11.5% (13/113) in Group 2. The mean survival days for tumor-bearing hamsters in Group 1 was 692.0 +/- 80.7 d and was 650.8 +/- 74.2 d in Group 2. Most tumors increased with advancing hamster age. The most common neoplasm was adrenal gland tumors (Group 1 = 4.7%, Group 2 = 8.8%). The occurrence of other tumors in other organs was low. The Syrian golden hamster is a suitable animal model for evaluating chemical carcinogenicity.

Effects of glutathione depletion on the acute nephrotoxic potential of arsenite and on arsenic metabolism in hamsters.

Our previous study showed that pretreatment with buthionine sulfoximine (BSO), which inhibits glutathione synthesis, results in acute renal failure with oliguria in hamsters ingesting sodium arsenite (5 mg As/kg). For a deeper understanding of the relationship between arsenic metabolism and the subsequent development of nephrotoxicity, we studied excretion, tissue retention, biotransformation, pharmacokinetics, and histopathological events in the kidneys of hamsters both with and without BSO pretreatment. The total amount of arsenic excreted in the urine and feces within 72 hr of arsenite administration was more than fivefold lower in BSO-pretreated animals than in the controls without pretreatment (9.2 versus 53.4% of the arsenic dose). The persistence of high amounts of total arsenic was apparent in the blood, liver, and kidneys of BSO-pretreated hamsters, even though the content of inorganic arsenic steadily decreased with time. The disappearance of inorganic arsenic from the blood showed a biphasic elimination pattern characterized first by a rapid component with a half-life of 4.5 hr and second by a slower component with a half-life of 58.0 hr in the BSO-pretreated hamsters, while these half-lives were 0.6 and 11.0 hr, respectively, in the controls. BSO pretreatment not only impaired the excretion of inorganic arsenic, but also impaired its methylation. Combined BSO/arsenite treatment resulted in renal tubular necrosis which was prominent at 1 hr after arsenite administration. By 1 hr, the renal content of inorganic arsenic in the BSO-pretreated animals was 1.7 times higher than that in the controls. This study demonstrates that glutathione depletion elicits the nephrotoxic manifestations of arsenic poisoning.

Arsenic intake and excretion by Japanese adults: a 7-day duplicate diet study.

The amount of arsenic in the urine, faeces and in duplicate diets of two couples who had eaten customary Japanese meals were monitored for 7 days by arsine-generator atomic absorption spectrophotometry. For the four volunteers, the mean daily intake of arsenic from their diets was 182 micrograms (range 27 to 376 micrograms). The dietary arsenic was composed of 5.7% inorganic arsenic, 3.6% methylarsonic acid, 27.4% dimethylarsinic acid and 47.9% trimethylarsenic compounds. The mean amounts of arsenic eliminated daily in urine and faeces were 148 micrograms (50-416 micrograms) and 46 micrograms (0-138 micrograms), respectively. The urinary arsenic was composed of 1.4% inorganic arsenic, 3.5% methylarsonic acid, 33.6% dimethylarsinic acid and 61.4% trimethylarsenic compounds. The daily intake of arsenic influenced the total amount of arsenic excreted in the urine (r = 0.7302, P less than 0.01) and the amount eliminated in the faeces (r = 0.5900, P less than 0.01) the next day. Specifically, there was also a significant correlation between the daily intakes of trimethylarsenic compounds and dimethylarsinic acid and the amounts of these compounds found in the urine the following day (r = 0.6833, P less than 0.01 and r = 0.6630, P less than 0.01, respectively). Considering the amounts of arsenic compounds present in seafood and in other components of the diet together with the urinary elimination patterns of arsenic compounds, it seemed probable that the trimethylarsenic compounds in the urine originated largely from fish and shellfish, which contain mainly arsenobetaine. Trimethylarsenic compounds in the urine should therefore be the preferred indicator of arsenic arising from the ingestion of seafood, especially fish and shellfish. In this study, the mean daily intake of inorganic arsenic from the diet (0.18 micrograms/kg) did not exceed the FAO/WHO JECFA Tolerable Daily Intake of 2 micrograms inorganic arsenic kg.

Variation of trace metals in ancient and contemporary Japanese bones.

Excavated and contemporary bones (rib cortexes) of a mature age (40-60 yr) were analyzed by atomic absorption spectrometry for the concentration of seven elements, including Ca, Cd, Cu, Fe, Mn, Ni, and Pb, with a view to historically evaluating the chemical composition of the bones. Fifty-two well-preserved specimens, obtained from western Japan, were classified into six groups according to Japanese prehistoric and historic eras (Jomon, Yayoi, Kofun, Muromachi, Edo, and Contemporary). Average concentrations of Ca were 0.20-0.33 g/g in the excavated bones and 0.17 g/g in the contemporary bones. Among the trace metals, such as Cu, Fe, Mn, and Pb, which showed remarkably elevated concentrations in the Edo era bones, Cu, Fe, and Mn were found to be strongly associated with soil contamination. Lead levels only slightly increased between the Jomon and Kofun eras, but became abruptly elevated following the Edo era. In contrast, the concentrations of Cd increased abruptly in the Yayoi era to a level with an order of magnitude higher than the Edo era, and they have recently decreased to rather low contemporary levels. This tendency becomes clearer when comparing the molar ratio of trace metals to Ca. The cause of elevated Cd concentrations in early excavated bones is discussed in relation to the mineralization of bones and the surrounding environment.

A comparison of the carcinogenicity of N-nitrosodiethylamine and N-nitrosodimethylamine after intratracheal instillation into Syrian golden hamsters.

N-Nitrosodiethylamine (NDEA) and N-nitrosodimethylamine (NDMA) were instilled intratracheally into male Syrian golden hamsters once a week for 15 wk. The total dosages were 1.5 mg and 7.5 mg of NDEA and 0.75 mg and 1.5 mg of NDMA. A control group simultaneously received phosphate buffer vehicle. Tumours related to instillation appeared principally in the respiratory tract and the liver. Over the entire lifespan of the animals tumour incidence rates in the respiratory tract were 100% in both the NDEA groups, 6% in both NDMA groups and 8% in the control group. The total incidences of liver tumours were 6% in the 0.75 mg NDMA group, 19% in the 1.5 mg NDMA group, zero in the NDEA groups, and 4% in the control group. These results indicate that, when administered by this route, NDEA is a much more potent carcinogen in the respiratory tract than is NDMA but NDMA alone seems to be carcinogenic to the liver, at a total dosage of 1.5 mg.

Changes in body proportions of Japanese medical students between 1961 and 1986.

Since 1945, the Japanese physique has changed a great deal. Physical examinations of medical students at Kyushu University have been carried out on an annual basis since 1939. We investigated changes in body proportions using data on 813 medical students examined from 1961 to 1986. During these 26 years, standing height has increased by 4.69 cm, arm length by 2.58 cm, and sitting height by 0.79 cm. Thus, the Japanese have grown taller and their extremities are longer, yet the trunk has not changed significantly. This study also shows a 10-year delay in increase in length of the upper extremities.

Comparative study on the carcinogenicity of N-nitrosodiethylamine, N-nitrosodimethylamine, N-nitrosomorpholine, N-nitrosopyrrolidine and N-nitrosodi-n-propylamine to the lung of Syrian golden hamsters following intermittent instillations to the trachea.

N-Nitrosodiethylamine (NDEA), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR), N-nitrosopyrrolidine (NPYR) and N-nitrosodi-n-propylamine (NDPA) were instilled into the lungs of male Syrian golden hamsters by intratracheal instillations once a week for 15 weeks. The total doses given were 1.5 mg of each drug. As a control, hamsters were treated with the vehicle, phosphate buffer solution. During the total lifespan, tumor incidence rates in the respiratory organs were 100% in the NDEA group, 6% in the NDMA group, 43% in the NMOR group, 0% in the NPYR group, 72% in the NDPA group and 4% in the control group. The incidence rates in the liver were 19% in the NDMA group and 4% in the NPYR group. No liver tumors developed in the other groups. The carcinogenic potencies of these N-nitroso compounds to the respiratory organs was provisionally estimated to be in the following order: NDEA greater than NDPA greater than NMOR greater than NDMA = NPYR, at the 1.5 mg dosage level. However, the difference in the rates of tumor incidence between the NDMA or NPYR group and the control group was not significant.

Lead levels in ancient and contemporary Japanese bones.

During the past few centuries, lead production, consumption and emissions, to our total environment have increased remarkably. We have determined the concentrations of lead in 41 well-preserved ancient and 11 contemporary rib bones of a mature age (40-60 y), with a view of historically evaluating lead exposure in humans. The oldest Japanese bones (1000-300 B.C.) were found to contain a mean of 0.58 microgram Pb/g dry wt and a mean molar ratio of lead to calcium of 0.6 x 10(-6), compared with 4.7-5.2 x 10(-6) in the bones of the Edo era (1600-1867 A.D.) and contemporary residents in Japan. The mean molar ratios of female bones were always higher than those of male bones for each era. From this fact we may assume that facial cosmetics were one of the main routes of lead exposure among the ancient Japanese, especially those who lived during the Edo era.

Ingestion of parsley inhibits the mutagenicity of male human urine following consumption of fried salmon.

The urinary mutagenicity of 3 nonsmoking, healthy men was investigated after strictly defined meals by means of the Ames Salmonella/microsome test. When the subjects ate 150 g of fried salmon at one meal, a potent mutagenicity of almost 5000 revertants of TA98 strain was present in all 6-h urine samples. On the other hand, less than 2500 revertants was present in the urine when the subjects simultaneously consumed 70 g of parsley and 150 g of fried salmon. Thus, the protection against mutagenicity affected by parsley warrants further attention.