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Biomedical subjects

M Mizuochi

Publications and source records attributed to M Mizuochi.

6 recordsLinked to original sources

Nitrous oxide emissions from aerated composting of organic waste.

The composting of high organic content wastes has been shown to produce nitrous oxide (N2O). This study was initiated to investigate the mechanisms of N2O emissions from aerated composting and to determine the optimal operational conditions that minimize N2O emissions. The results of our experiment in laboratory-scale composters showed that more than 95% of N2O was produced during the later period of composting when readily available carbon sources had been depleted. Significant increases in N2O emission after nitrite (NO2-) addition, and good NO(2-)-N2O correlation, indicates that N2O was transformed from NO2-. Extremely high N2O generation was observed after NO2- addition in the presence and absence of composted cattle manure. This suggests an identical mechanism for N2O production in both treatments. However, the addition of composted cattle manure resulted in an earlier initiation of the main N2O generation period. Intermittent feeding of fresh food waste postponed the main N2O generation period, and reduced the mass-based N2O emissions by 20%.

Air Pollutants↗

Effects of fill modes on N2O emission from the SBR treating domestic wastewater.

Nitrous oxide (N2O) gas is emitted as an intermediate in the biological nitrogen removal process. A track study was performed to investigate the characteristics of N2O emission depending on the cyclic mode of a sequencing batch reactor (SBR). A major emission of N2O took place at the aerobic phase, while N2O emission at the anoxic phase was insignificant. Especially, the highest N2O emission rate was observed at the initial stage of aerobic phase under the limited dissolved oxygen (DO) condition. Under such a condition, nitrite (NO2-) was transiently accumulated along with significant N2O emission due to incomplete nitrification. In addition, N2O production at the aerobic phase was strongly related with incomplete denitrification by nitrifiers. N2O emission could be reduced by change in fill modes in the SBR. A significant conversion to N2O took place in the SBR with the anoxic fill mode, while only small amount of N2O was conversed in the SBR with the aerobic fill mode. Relatively high concentration of ammonia nitrogen (NH4+) accelerated N2O production at the aerobic phase in the SBR with the anoxic fill compared to the aerobic fill. For control of N2O emission in the SBR, the aerobic fill mode could be an effective method even if denitrification efficiency may be reduced at the anoxic phase.

Aerobiosis↗

Up-to-date modification of the anaerobic sludge digestion process introducing a separate sludge digestion mode.

Sewage treatment plants in Japan are subjected to advanced treatment to remove nutrients and hence control eutrophication problems in lakes and bays. This paper discusses the advantages and disadvantages of the separate digestion treatment mode for sludge generated from advanced wastewater treatment. In the separate digestion only primary sludge is digested and the excess activated sludge is directly dewatered. Separate digestion can reduce the return load of nutrients to approximately one third, and has major potential for the beneficial use of sludge.

Bioreactors↗

Measurements of N2O and CH4 from the aerated composting of food waste.

Emissions of N2O and CH4 from an aerated composting system were investigated using small-scale simulated reactors. The results show relatively high emissions of N2O at the beginning of composting, in proportion to the application amount of food waste. After 2 days, the N2O emission decreased to 0.53 ppmv on average, near to the background level in the atmosphere (0.45 ppmv). The addition of composted cattle manure increased N2O emissions not only at the beginning of composting, but also during the later period and resulted in two peak emission curves. Good correlation was observed between the N2O concentration at the air outlet and NO2- concentration in waste, suggesting a generation pathway for N2O from NO2- to N2O. Methane was only detected in treatments containing composted cattle manure. The high emission of methane illustrates the involvement of anoxic/anaerobic microorganisms with the addition of composted manure. The result suggests the existence of anoxic or anaerobic microsite inside the waste particles even though ventilation was employed during the composting process.

Animals↗

Stereoselectivity in the hydroxylation of propafenone enantiomers in mouse hepatic microsomes.

Stereoselectivity in the oxidative metabolism of propafenone (PPF) enantiomers to 5-hydroxypropafenone was studied with untreated and inducer-treated mouse hepatic microsomes. In the untreated microsomes, Lineweaver-Burk plots of the 5-hydroxylation of R(-)- and S(+) PPF. single lines, and the intrinsic clearance (Vmax/Km) value of R(-)-PPF was 1.3-fold higher than that of S(+)-PPF. When racemic PPF was used as a substrate, the plot was shifted to the upper region, in comparison with that estimated from the sum of the individual 5-hydroxylase activities of each enantiomer, suggesting enantiomer/enantiomer interaction. In phenobarbital-induced microsomes, the Lineweaver-Burk plot for R(-)-PPF was a single line, but that for S(+)-PPF was biphasic. When racemic PPF was used as a substrate, the plot was biphasic and was shifted to the upper region in comparison with that estimated from the sum of the individual 5-hydroxylase activities of each enantiomer. The observed value of intrinsic clearance of the PPF racemate at lower concentrations (Vmax/Km1) was consistent with the estimated value, suggesting no interaction between R(-)- and S(+)-PPF. These findings indicate that most of the 5-hydroxylation of R(-)- and S(+)-PPF is catalyzed by common cytochrome P-450 species, but a part of S(+)-PFF 5-hydroxylation is catalyzed by another phenobarbital inducible cytochrome P-450 species, particularly at lower substrate concentrations.

Animals↗