• 환경위생공학
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• 제9권1호
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• pp.62-66
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• 1994

Nitrous Oxide( NaO), one of the green house gases, is not confirmed it's sources, sinl life time in the atmosphere clearly so far, In this paper, the emission sources physical characteristics, concentration in the air, monitoring method and distribution for the global warming gas were summarized.

• 한국환경과학회:학술대회논문집
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• 한국환경과학회 2001년도 가을 학술발표회 발표논문집
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• pp.63-66
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• 2001

• 한국환경과학회:학술대회논문집
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• 한국환경과학회 1999년도 임시총회 및 가을 학술발표회 초록집 The Korean Environmental Sciences Society
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• pp.230-231
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• 1999

• 한국농림기상학회:학술대회논문집
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• 한국농림기상학회 2019년도 하계 학술발표초록집
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• pp.241-242
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• 2019

• 한국토양비료학회지
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• 제46권6호
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• pp.570-574
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• 2013

This study was conducted to assess $N_2O$ emissions in agricultural soils of Korea under the 1996 IPCC (Intergovernmental Panel on Climate Change) methodology. $N_2O$ emissions in agricultural soils were calculated the sum of direct emission and indirect emission by the N sources and emissions by field burning of crop residues. $N_2O$ emission was highest in animal manure as 1,547 $CO_2$-eq Gg. Indirect emissions by atmospheric deposition and leaching and runoff were 1,463 and 1,753 $CO_2$-eq Gg, respectively. $N_2O$ emission by field burning of crop residues was highest in pepper due to the residue/crop ratio and field burning ratio.

• 대한장애인치과학회지
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• 제2권2호
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• pp.142-146
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• 2006

환아의 연령, 과다체중, 환아의 약물 거부 등으로 인하여 chloral hydrate를 이용한 수면치료가 불가능한 경우, Midazolam을 이용한 정주진정요법이 전신마취를 대신하는 대안으로 사용될 수 있다. 본 환아의 경우, 0.3mg/kg의 midazolam을 근주하고, 70% 아산화질소 가스를 이용하여 초기 수면상태를 유도하고 정맥천자를 실시한 후, 0.2mg/kg midazolam을 정주하여 50분간 별다른 부작용 없이 성공적으로 치료할 수 있었다.

• Asian-Australasian Journal of Animal Sciences
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• 제18권6호
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• pp.873-878
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• 2005

Emissions of nitrous oxide (N$_2$O) and methane (CH$_4$) from poultry enteric fermentation were investigated using a respiration chamber. Birds were placed in a respiration chamber for certain intervals during their growing period or for the whole life cycle. The accumulated gas inside the chamber was sampled and analyzed for N$_2$O and CH$_4$ production. A curve for gas production during a life cycle was fitted. The calculated area under the curve estimated the emission factor of poultry enteric fermentation on a life cycle basis (mg bird$^{-1}$ life cycle$^{-1}$). This method can be used to estimate CH$_4$ or N$_2$O emissions from different types of avian species taking into account factors such as diet, season or thermal effects. The CH$_4$/N$_2$O emission factors estimated for commercial broiler chickens, Taiwan country chickens and White Roman Geese were 15.87/0.03, 84.8/16.4 and 1,500/49 (mg bird$^{-1}$ life cycle$^{-1}$), respectively, while the calculated CH$_4$/N$_2$O emission from enteric fermentations were 3.03/0.006, 14.73/2.84 and 9.5/0.31 (Mg year$^{-1}$), respectively in Taiwan in the year of 2000. The described method is applicable to most poultry species and the reported emission factors were applicable to meat type poultry only.

• Journal of Microbiology and Biotechnology
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• 제21권9호
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• pp.988-994
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• 2011

A significant amount of nitrous oxide ($N_2O$), which is one of the serious greenhouse gases, is emitted from nitrification and denitrification of wastewater. Batch wastewater nitrifications with enriched nitrifiers were carried out under oxygen-limited condition with synthetic (without organic carbon) and real wastewater (with organic carbon) in order to find out the effect of ammonium concentration on $N_2O$ emission. Cumulated $N_2O$-N emission reached 3.0, 5.7, 6.2, and 13.5 mg from 0.4 l of the synthetic wastewater with 50, 100, 200, and 500 mg/l ${NH_4}^+$-N, respectively, and 1.0 mg from the real wastewater with 125 mg/l ${NH_4}^+$-N. The results indicate that $N_2O$ emission increased with ammonium concentration and the load. The ammonium removal rate and nitrite concentration also increased $N_2O$ emission. Comparative analysis of $N_2O$ emission from synthetic and real wastewaters revealed that wastewater nitrification under oxygen-limited condition emitted more $N_2O$ than that of heterotrophic denitrification. Summarizing the results, it can be concluded that denitrification by autotrophic nitrifiers contributes significantly to the $N_2O$ emission from wastewater nitrification.

• Membrane and Water Treatment
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• 제9권2호
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• pp.123-128
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• 2018

Common aquaculture practices include the use of certain pharmaceuticals such as antibiotics in avoiding diseases and promoting a healthier growth of the culture. The aim of this study is to monitor and assess the influence of different low oxytetracycline concentrations on the transformation of nitrogen compounds under aeration condition in a lab-scale recirculating aquaculture system (RAS). Over $1mg\;L^{-1}$ dose of oxytetracycline to aquaculture had induced ammonia($NH_4-N$), nitrate($NO_3-N$), soluble COD accumulation in RAS. In addition, nitrous oxide ($N_2O$) emission from RAS was significantly reduced during the oxytetracycline dose periods. After ceasing the dose of oxytetracycline, ammonia oxidation and nitrous oxide re-emission were observed. This observation indicated that low concentrations of oxytetracycline could affect the nitrogen species in RAS. Also, the emission mechanisms of $N_2O$ may not be only dependent on nitrification process but also dependent on denitrification process in our RAS system.

• 한국토양비료학회지
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• 제36권4호
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• pp.256-262
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• 2003

밭벼와 콩 재배지에서 메탄과 아산화질소 배출을 측정하였다. 2001년 4월 28일 폭 30 cm 간격으로 대진벼를 파종하였다. 포장의 물관리는 스프링클러 관개와 천연강우 관개로 하였다. 콩 품종 장엽콩, 태광콩, 황금콩을 2001년 6월 16일에 $60{\times}15cm$ 간격으로 한 구멍에 2알씩 파종하였다. 기체시료는 주 2회씩 채취하여 메탄과 아산화질소를 분석하였다. 밭벼 작기중 메탄 배출은 스프링클러 관개구에서 $3.5kg\;CH_4\;ha^{-1}$ 였었고 천연관개구에서 $-1.7kg\;CH_4\;ha^{-1}$ 였었다. 밭벼 작기중 아산화질소 배출은 스프링클러 관개구에서 $50.8kg\;N_2O\;ha^{-1}$ 였었고 천연관개구에서 $8.3kg\;N_2O\;ha^{-1}$ 였었다. 밭벼 재배지에서 배출하는 온실가스 GWP는 스프링클러 관개구와 천연관개구에서 각각 15,822 및 $2,216kg\;CO_2\;ha^{-1}$ 였었다. 콩 작기중 메탄 배출은 장엽콩 재배구에서 $-14.7kg\;CH_4\;ha^{-1}$ 였었고 태광콩 재배구에서 $-4.3kg\;CH_4\;ha^{-1}$, 황금콩 재배구에서 $4.8kg\;CH_4\;ha^{-1}$ 였었다. 콩 작기중 아산화질소 배출은 장엽콩 재배구에서 $4.7kg\;N_2O\;ha^{-1}$, 태광콩 재배구에서 $4.6kg\;N_2O\;ha^{-1}$, 그리고 황금콩 재배구에서 $3.0kg\;N_2O\;ha^{-1}$ 였었다. 콩 작기중 배출하는 온실가스 GWP는 장엽콩, 태광콩, 황금콩 재배구에서 각각 1,152, 1,323 및 $1,027kg\;CO_2\;ha^{-1}$ 였었다.