The development of synthetic fertilizers has led to an explosive increase in crop production, which has resulted in a continuous increase in the world''s population. Human activities such as indiscriminate fertilizer application and use of fossil fuels have continuously increased anthropogenic greenhouse gas emissions, and the concentration is currently at its highest level in the past 800,000 years. As a result, each country is implementing greenhouse gas reduction policies, and Korea has presented a goal of reducing emissions by 37% compared to the Business as usual, and the non-energy sector in agriculture among each industry sector has a reduction target of about 1.6 million tons, equivalent to 7.9% of the predicted level of cabbage. Has been set the main greenhouse gases generated in the agricultural sector are CO2, CH4, and N2O, and CO2 and N2O are mainly generated from open fields and facility cultivation. Incubation experiment was carried out to investigate greenhouse gas emissions and soil quality in agricultural soils through varying rates of two biochars (BC) derived from rice hull biochar and livestock manure biochar. all treatment was supplemented inorganic fertilizers (by N-P2O5-K2O : 32-7.8-19.8 kg 10a-1 ) and compost (540 kg 10a-1 ) with BC derived from rice hull and livestock manure biochars at varying rates of 5, 10 and 20 t ha-1 (BC5, BC10 and BC20, respectively); the control (BC0) area was untreated only biochar. Our results reveal that soil quality and emissions of CO2 and N2O varied significantly with the biochar application rate. Peak emissions of CO2 and N2O were mainly observed in the early period of incubation experiment, followed by basal emissions. During the incubation experiment periods, the overall N2O emission was significantly decreased with BC5, BC10 and BC20 applications as compared to the control, ranging from 11.1 to 13.6%, 8.7 to 15.4%, 23.1 to 26.0%, and 15.0 to 19.6%, respectively. Soil quality results after the incubation experiment show, T-C, pH, and cation exchange capacity (CEC) were significantly improved by biochar application, as compared to the control. Inorganic nitrogen content was evaluated for nitrification potential, and it was confirmed that the nitrification rate was slowed down as biochar applied. And a field experiment was carried out to investigate crop productivity, emissions of CO2 and N2O and soil quality of an upland field treated with compost and varying rates of biochar (BC) derived from rice hull during crop growing periods in Chinese cabbage cultivation. Compost was supplemented with BC at varying rates of 1, 3, and 5 t ha-1 (BC1, BC3, and BC5 respectively); the control (BC0) area was untreated. crop productivity was improved after BC application as compared to the control treatment area, by 28.5% for upland field and 10.6% for greenhouse field Chinese cabbage cultivation. Greenhouse gases emissions were calculated and evaluated by greenhouse warming potential and greenhouse gas intensity. Compared to the control area, emissions during the cropping period, the overall N2O emission was significantly decreased with by 1.91 - 5.35 times at maximum BC1, BC3 and BC5 applications as compared to the control, ranging from 1.91 to 5.35 times at maximum, respectively. Soil quality results after field experiments Similar to the results of incubation experiments, T-C, pH and cation exchange capacity (CEC) were significantly improved by biochar fertilization compared to the control group. Thus, our results indicate that application supplemented that fertilizer with biochar is for achieving high crop productivity and improving soil quality in upland and greenhouse field conditions. In conclusion, the application of biochar has the side benefit of enriching soil quality, reducing the use of inorganic fertilizers and reducing greenhouse gas emissions.
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I. 서 론 1II. 재료 및 방법 41. 항온실험을 통한 바이오차 시용에 따른 온실가스 배출 변화 및 토양 화학적 특성 변화 평가 41) 공시 재료 4① 공시 토양 4② 공시 바이오차 62) 시험구 처리 및 항온배양실험 8① 항온배양실험 8② 토양 및 바이오차 분석 10③ 무기태 질소 및 질산화속도 조사 11④ 가스 flux 측정 및 분석 122. 현장실험을 통한 바이오차 시용에 따른 온실가스 배출 변화 및 토양 이화학적 특성 변화 평가 141) 시험포장 142) 공시재료 153) 재배방법 및 시험처리 174) 가스 flux 측정 및 분석 18III. 결과 및 고찰 191. 항온실험을 통한 온실가스 배출 변화 및 토양 화학적 특성 변화 평가 191) 항온실험 후 토양 화학적 특성 평가 192) 암모니아태 질소 함량 평가 233) 질산태 질소 함량 평가 294) 질산화 잠재율 평가 355) 이산화탄소 배출량 평가 376) 아산화질소 배출량 평가 432. 현장실험을 통한 바이오차 시용에 따른 온실가스 배출 변화 및 토양 이화학적 특성 변화 평가 501) 무기태 질소 변화 평가 502) 토양 화학성 변화 평가 533) 토양 물리적 특성 554) 배추 생육조사 575) 온실가스 배출량 분석 606) 농경지별 온실가스 잠재능 및 온실가스 배출강도 평가 65IV. 적요 67