복합 유용미생물을 우점시킨 폐수 슬러지의 호기성 퇴비화
DC Field | Value | Language |
---|---|---|
dc.contributor.author | 하신영 | - |
dc.date.accessioned | 2017-02-22T06:07:38Z | - |
dc.date.available | 2017-02-22T06:07:38Z | - |
dc.date.issued | 2015 | - |
dc.date.submitted | 57069-08-26 | - |
dc.identifier.uri | http://kmou.dcollection.net/jsp/common/DcLoOrgPer.jsp?sItemId=000002174984 | ko_KR |
dc.identifier.uri | http://repository.kmou.ac.kr/handle/2014.oak/9129 | - |
dc.description.abstract | Organic waste is an organic resource which can be converted into useful materials by microbes, and can be seen as a resource which can be recycled in a variety of ways. However, until now, organic waste has been disposed of through the inexpensive offshore dumping. However, with the implementation of a ban on offshore dumping set in place since 2014, demand for land-based treatment facilities for the stable and sustained treatment of organic waste has risen, and large budgets are being appropriated to this end. Sewage, wastewater sludge and food waste, which are representative organic wastes, have a high potential for conversion into animal feed or compost, but due to their odor and high moisture content, are difficult to handle. In addition, they have high concentrations of hazardous materials. This study focused on converting wastewater and sewage sludge treated with beneficial microorganism(BM) into compost, using food waste as a supplementary nitrogen source that the sludge lacks. First, a laboratory-scale reactor innoculated with BM agents was used to produce sludge treated with BM. In testing to compute the optimal amount of BM, the efficiency was highest when the amount of BM inoculation was 1%(w/w). Observation of changes in concentration of proteins and carbohydrates in the sludge resulting from the introduction of BM showed increases of 52% for protein and approximately 32% for carbohydrate. Also, due to introduction of the BM agent into the wastewater, the removal efficiencies of suspended solid (SS), chemical oxygen demand (COD), total nitrogen (T-N) and total phosphorus (T-P) were 94.5%, 91%, 79% and 81%, respectively satisfying domestic standards for the effluent. Secondly, the composting characteristics of BM sludge and the control sludge were compared. Feasibility of using coffee grounds as a bulking agent was examined, along with sawdust. It was observed that composting of BM sludge had a faster rate of reaction than with the control sludge, and higher temperatures were reached. When using coffee grounds as a bulking agent, the caffeine in the coffee seemed to absorb the odors, allowing a composting with almost no odors. Moreover, when coffee grounds used as the bulking agent, total organic matter content increased by approximately 17% over sawdust, while total nitrogen increased by 49%, and available phosphorus by approximately 3%. Comparative microbial community analysis based on pyrosequencing analysis was performed for the BM agents used for composting and for the control sludge. Analysis of the diversity of microorganisms showed 559 out of 1580 reads OTU for the control sludge, and 594 OTU out of 2174 reads for BM sludge, indicating a higher diversity control sludge. Pyrosequencing of BM sludge showed that Proteobacteria (41.30%) was the most dominant, followed by Gemmatimonadetes (14.12%). microbial diversity analysis in the compost showed 249 OTU out of 3406 reads in the control sludge compost, and 183 OTU out of 2632 reads for BM sludge compost. Whereas the diversity of microorganisms in the control sludge were observed to be slightly higher than that of BM sludge, the diversity were decreasing as the composting proceeded, leading to a larger proportion of Bacteroidetes, Proteobacteria and Firmicutes occurred during composting for both sludges. Fourthly, a study was conducted to investigate composting efficiency. In the test for germination rate, the control sludge failed in some cases to satisfy the standard of 70 for matured compost after 28 days, but when using composted BM sludge, all cases were shown to satisfy the requirement. The result for BCL compost was highest, at 101.5. Plant germination rate was shown to increase when using coffee grounds as the bulking agent. Use of BCL compost was observed to have a positive growth effect on leaf weight (g), leaf number (ea), leaf length (cm), root weight (g), root diameter (cm), and root length (cm), etc. Lastly, an economic feasibility analysis on BCL compost, which was shown to have the highest efficiency of composting, showed that approximately 22.2% cost savings relative to current food waste composting were possible, mainly because the caffeine in the coffee grounds absorbed odors, removing the need for odor reducing facilities, and enhanced the value of the compost by boosting the organic matter content and total nitrogen content of the completed compost. | - |
dc.description.tableofcontents | 목 차 목 차 ⅰ List of Figures ⅴ List of Tables ⅸ Abstract ⅺ 제 1 장 서론 1 제 2장 문헌연구 4 2.1 유기성 폐기물 4 2.1.1 하·폐수 슬러지 5 2.1.2 음식물폐기물 7 2.1.3 커피박 발생 및 처리현황 8 2.2 퇴비화 10 2.2.1 호기성 퇴비 단계별 환경변화 10 2.2.2 퇴비의 원료 11 2.2.3 퇴비화 장치의 영향인자 12 2.2.4 퇴비처리장의 악취물질 15 2.3 퇴비의 품질 15 2.4 복합미생물 제제 19 2.4.1 미생물제제 군집구조 20 제 3 장 복합유용미생물을 우점화한 활성슬러지 공법 22 3.1 서론 22 3.2 재료 및 방법 23 3.2.1 실험장치 및 운전방법 23 3.2.2 실험대상 유입원수 25 3.2.3 시험항목 및 측정방법 26 3.3 결과 및 고찰 27 3.3.1 복합미생물제제의 최적주입량의 산정 27 3.3.2 슬러지 EPS함량 변화 비교 28 3.3.4 활성슬러지공정의 MLSS 농도 변화 30 3.3.5 활성슬러지 공정의 처리효율 평가 31 3.4 소결론 33 제 4 장 복합유용미생물 우점슬러지를 이용한 퇴비화 34 4.1 서론 34 4.2 재료 및 방법 36 4.2.1 퇴비화 장치의 운전조건 36 4.2.2 실험장치 37 4.2.3 실험재료 38 4.2.4 시험항목 및 측정방법 39 4.3 결과 및 고찰 43 4.3.1 온도 변화 44 4.3.2 수분 변화 46 4.3.3 pH 48 4.3.4 염분 농도(%) 50 4.3.5 C/N의 변화 52 4.3.6 악취분석 54 4.3.7 카페인 성분의 변화 57 4.3.8 무기성분의 변화 59 4.3.9 퇴비 품질 검증 61 4.3.10 퇴비 공정규격 분석 63 4.4 소 결론 65 제 5 장 퇴비 내 세균군집의 Pyrosequencing 분석 67 5.1 서론 67 5.2 재료 및 방법 68 5.2.1 시료 채취 68 5.2.2 DNA 추출 68 5.2.3 Pyrosequencing 방법 69 5.3 결과 및 고찰 71 5.3.1 Rarefaction curve를 이용한 metagenome 분석 71 5.3.2 Pyrosequencing으로 분석한 Bacteria 군집 다양성 75 5.3.3 복합유용미생물 슬러지와 퇴비의 Community 분석 82 5.4 소 결론 85 제 6 장 퇴비 시용에 따른 토양의 이화학적특성과 식물생장에 관한 연구 86 6.1 서론 86 6.2 재료 및 방법 87 6.2.1 실험장소 87 6.2.2 공시식물 87 6.2.3 시용 퇴비 88 6.2.4 시험항목 및 측정방법 88 6.3 결과 및 고찰 91 6.3.1 퇴비 시용에 따른 식물성장 영향실험 91 6.3.2 토양 이화학적 성분 변화 93 6.3.3 중금속의 변화 102 6.3.4 퇴비에 따른 공시식물 성장률 비교 104 6.4 소 결론 109 제 7 장 경제성 분석 110 7.1 복합유용미생물 우점 슬러지를 이용한 퇴비화 110 7.2 복합유용미생물 우점 슬러지를 이용한 퇴비화의 팽화제로 커피박을 이용한 퇴비화 113 7.3 소결론 115 제 8 장 종합결론 116 참고문헌 118 | - |
dc.language | kor | - |
dc.publisher | 한국해양대학교 | - |
dc.title | 복합 유용미생물을 우점시킨 폐수 슬러지의 호기성 퇴비화 | - |
dc.title.alternative | Aerobic Composting of Wastewater Sludge Using Beneficial Microorganisms | - |
dc.type | Thesis | - |
dc.date.awarded | 2015-02 | - |
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