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I Tahara

Publications and source records attributed to I Tahara.

At least 19 recordsLinked to original sources

Stability of 1-nitropyrene and 1,6-dinitropyrene in environmental water samples and soil suspensions.

This study examined the stability of mutagenic 1-nitropyrene (1-NP) and (1,6-dinitropyrene (1,6-diNP) in environmental water samples and various soil suspensions containing 0.1% peptone and in water samples containing no peptone. The water samples or the soil suspensions were mixed with NPs and incubated at 30 degrees C. The stability of NPs was expressed as mutagenic activity remaining in the test solutions. The mutagenicity decreased rapidly when 1-NP or 1,6-diNP was incubated in unautoclaved test solutions containing 0.1% peptone but not when incubated in autoclaved test solutions. The mutagenicity in the soil suspensions, especially in the sludge, decreased faster than in the water samples. This was due to the large number of colony-forming units (CFU) in the soil suspensions. In the water samples containing 0.1% peptone, the mutagenicity of NPs in the polluted Tamiya River water decreased faster than in the unpolluted Yoshino River water. The rate of decrease was dependent on the number of CFU in the water samples. A large number of CFU decreased the mutagenicity more rapidly than did a small number of CFU in samples. The disappearance of mutagenicity was dependent on the initial concentrations of NPs. The periods required for a 50% decrease in the mutagenicity of 1-NP at the low concentration (0.2 microgram/ml) was shorter than that at the high concentration (3 micrograms/ml). 1-Aminopyrene was detected in the 1-NP test solution after incubation when it was analyzed by high-pressure liquid chromatography. In the water samples containing no peptone, the mutagenicity of 1-NP (0.2 microgram/ml) decreased gradually during 30 days of incubation. After incubation for 1540 days, the remaining mutagenicity of 1-NP in the water samples was almost the same as that in autoclaved water samples. On the other hand, the mutagenicity of 1,6-diNP (10 ng/ml) decreased and the remaining mutagenicity, except in the Yoshino River water, was less than 20% after 30 days of incubation and was completely lost during the 1540-day incubation. However, the mutagenicity of 1,6-diNP in autoclaved water samples was very stable and almost all mutagenicity, except in sea water, remained after 1540 days of incubation at 30 degrees C. These results suggest that the microflora in the environment plays an important role in the primary degradation and decontamination of relatively low concentrations of NPs.

Biodegradation, Environmental↗

The efficiency of solvent extraction of mutagenic compounds in particulates exhausted from a small diesel engine.

Organic materials were extracted from particulates exhausted from a small diesel engine (displacement 269 ml) by the ultrasonic extraction method with three different solvent systems, methanol, dichloromethane and a 4:1 (v:v) mixture of benzene and ethanol. These solvent-extracted materials were tested for mutagenic activity by the Ames Salmonella/microsome assay system using Salmonella typhimurium strains TA98, TA100, TA98NR and TA98/1,8-DNP6. The concentrations of 1-nitropyrene (1-NP) and 1,6-dinitropyrene (1,6-diNP) in these extracted materials were also measured after nitroreduction by high pressure liquid chromatography. The methanol-extracted and benzene-ethanol-extracted materials showed the lowest and the highest mutagenic activity, respectively. The methanol-extracted, dichloromethane-extracted and benzene-ethanol-extracted materials induced 260, 1,570 and 3,240 His+ revertants per plate per mg of extracted materials, respectively, from strain TA98 in the absence of S9 mix. These materials showed decreased mutagenicity for strains TA98NR and TA98/1,8-DNP6, indicating that the particulates in the diesel engine exhaust contained 1-NP and diNPs. Actually, the amount of 1-NP and 1,6-diNP in the methanol-extracted, dichloromethane-extracted and benzene-ethanol-extracted materials were 17.0 and 0.03 ng, 37.5 and 0.97 ng, and 71.3 and 1.03 ng per mg of extracted materials, respectively, accounting for 11.9 and 3.2%, 4.4 and 17.3%, and 4.0 and 8.9%, respectively, of the total mutagenicity of the extracted materials. From these results it is concluded that a mixture of benzene-ethanol (4:1, v/v) is the most suitable solvent for extraction of organic matter containing nitrated polycyclic aromatic hydrocarbons such as NPs from particulates in diesel engine exhaust.

Benzene↗

Mutagenic 1-nitropyrene in wastewater from oil-water separating tanks of gasoline stations and in used crankcase oil.

Wastewater collected from oil-water separating tanks of ten gasoline stations for a year was fractionated into diethyl ether-soluble neutral, acidic, and basic fractions. Mutagenicity of these fractions was measured with Salmonella typhimurium strains TA98 and TA100 in the presence or absence of S9 mix. The neutral fractions showed high mutagenicity in the absence of S9 mix. Each neutral fraction was subjected to high-performance liquid chromatography (HPLC) and fractionated. A 1-nitropyrene(1-NP)-corresponding fraction was collected and analyzed by gas chromatography-mass spectrometry (GC-MS) and HPLC to prove that wastewater contains 1-NP and to quantitate 1-NP in wastewater. GC-MS patterns showed the following molecular and fragment ion peaks of 1-NP: 247, 217, 201, and 189. The amount of 1-NP in 36 samples of wastewater was 4.2-25,600 ng per liter of wastewater, and 1-NP accounted for 0.3-58.5% of the total mutagenicity of the neutral fractions. The other 19 samples of wastewater did not contain any detectable 1-NP. The mutagenicity of wastewater may be due to water from car washing and contamination by used crankcase oil. A Soxhlet extract of crankcase oil used in a gasoline was fractionated into three fractions as above. Mutagenicity was measured with strains TA98, TA100, TA98NR, and TA98/1,8-DNP6 in the absence or presence of S9 mix. The neutral fraction showed the highest mutagenicity with strain TA98 in the absence of S9 mix, and its mutagenicity was decreased in strains TA98NR and TA98/1,8-DNP6. The latter result indicates that the used engine-oil contained 1-NP and dinitropyrenes. Actually, the amounts of 1-NP and 1,6-diNP in used crankcase oil were 138 and 2.0 ng per ml of oil, respectively, and these concentrations accounted for 0.45 and 2.7%, respectively, of the total mutagenicity of the neutral fraction with strain TA98 in the absence of S9 mix. Moreover, the concentrations of 1-NP and 1,6-diNP in used crankcase oil of a diesel engine were 349 and 31 ng per ml of oil, respectively, accounting for 0.9 and 12%, respectively, of the total mutagenicity of the neutral fraction in the same assay system.

Chromatography, High Pressure Liquid↗

Detection of mutagenic activity in automobile exhaust.

Using the Ames Salmonella-microsome system, we detected mutagenic activity in the exhaust from two kinds of 4-cycle gasoline engines of unregulated and regulated cars, and from diesel engines, as well as in the particulates from air collected in tunnels. The mutagenicity of particulates from a car equipped with a catalyst (regulated car), as compared with that from an unregulated car, was reduced very much (down to 500 from 4500 revertants/plate/m3 in tester strain TA98). However, the mutagenicity of the ether-soluble acid and neutral fractions from the condensed water of emissions from a regulated car was still high (down to 2880 from 10 900 revertants/plate/m3 in tester strain TA100). The mutagenic activity of emission exhaust from old diesel car engines was very high; the particulates showed 9140 and 19 600 revertants/plate/m3 from strain TA98 incubated with an activating rat-liver S9 fraction. A small diesel engine of the type used for the generation of electric power or in farm machinery also produced exhaust with highly mutagenic particulates. The mutagenic activity of a methanol extract of particulate air pollutants collected in a highway tunnel showed 39 revertants/plate/m3 toward strain TA98 and 87 toward strain TA100. The ether-soluble neutral fraction yielded 86 revertants/plate/m3 from strain TA98 and 100 from strain TA100. This fraction also contained carcinogenic compounds, including benzo[a]pyrene, benzo[e]pyrene, benz[a]anthracene, benzo[ghi]perylene and chrysene. Very high mutagenic activity was detected, especially in the particulate air pollutants collected at night, in another tunnel on a superhighway: 60-88 revertants/plate/m3 from strain TA100 for the sample collected by day, but 121-238, by night. Night traffic includes many more diesel-powered vehicles compared with gasoline-powered automobiles.

Air Pollutants↗

[Clinical study on the shock organs in relation to the duration of shock (author's transl)].

To elucidate the mechanism of development of renal, pulmonary and liver insufficiency after serious shock, retrospective analysis was performed in 85 patients with traumatic shock. Among them, 14 patients died of renal, pulmonary or liver insufficiency after the resuscitation of shock, where kidney and lung were damaged concomitantly in most patients. There was a close correlation between the death related to both insufficiency and the duration of the shockp when the shock was treated completely within 10 hours, there was almost no death related to shock organ, but when the shock persisted more than 10 hours, the death rate was increased as the shock persisted longer. On the contrary, no relation was revealed between death caused by liver insufficiency and the duration of the shock. Renal and pulmonary functions were also correlated with the duration of the shock. It was revealed that the lower PaO2/PAO2 ratio was, the higher urea-N was in these patients, when shock persisted more than 10 hours. On the other hand, no relation was found between the change in liver function and the duration of shock. It can be concluded that the kidney and lung have the same nature as a shock organ. In general both functions were impaired concomitantly, where 10 hours of persistence could be regarded as the critical border to develop the shock organ. The liver seemed to be independent of the others as the shock organ, so that it should be discussed separately.

Acute Kidney Injury↗

Occurrence of pulmonary insufficiency in abdominal trauma.

The alteration of pulmonary function in 35 patients with abdominal trauma admitted to the Trauma ICU of Oska University Hospital were studied. A fall of PaO2 reaching the lowest level on the third post-traumatic day, incomplete recovery even on the seventh posttraumatic day and of longer duration was remarkable in comparison to those seen after elective abdominal surgery. Thirty two patients recovered without need of particular respiratory control but remaining three died with progressive decrease of PaO2 in spite of the intensive respiratory care. The hypoxia seen in the fatal cases was irresponsive to the administration of 100 per cent O2 with mechanical ventilation. Therefore, increase in intrapulmonary shunt was likely to be responsible for their fatal course.

Abdominal Injuries↗

[Liver injury].

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Age Factors↗