연안어장 준설 퇴적물에 함유된 유기물 및 중금속의 친환경적 처리
DC Field | Value | Language |
---|---|---|
dc.contributor.author | 고성정 | - |
dc.date.accessioned | 2017-02-22T06:42:58Z | - |
dc.date.available | 2017-02-22T06:42:58Z | - |
dc.date.issued | 2005 | - |
dc.date.submitted | 56823-03-29 | - |
dc.identifier.uri | http://kmou.dcollection.net/jsp/common/DcLoOrgPer.jsp?sItemId=000002175481 | ko_KR |
dc.identifier.uri | http://repository.kmou.ac.kr/handle/2014.oak/9709 | - |
dc.description.abstract | A study on the treatment of an dredged sediment from a coastal fisheries and it's reuse were performed. Sediment sample was taken from a coastal fisheries near Jinhae bay and the pollutants contained in the sediment were analyzed. For the stabilization of organic pollutants, a liquid stabilization technology was studied, and bioleaching process was adopted for removal of the heavy metals from the sediment. Adsorption characteristics for nutrients on the activated sediment was also studied to find out a proper reuse method. The sediment was severely contaminated with organics, but the levels of nutrients including nitrogen and phosphorus were not serious. The organics contained in the sediment were consisted of about 2% of cellulose, 27% of hemicellulose, 3% of total sugar, and 13% of lipid. For the heavy metals, the levels of cadmium and chromium were much higher than the standards for soil contamination concern. The sediment was also contaminated with PAHs (Polyaromatic hydrocarbons), dioxin and PCB (Polychrolinated biphenyl). For the stabilization of organic materials contained in the sediment, the easily biodegradable organics, indicating that the portion could be stabilized, was around 30-40% of the total organics. The biodegradability of the organics was affected by the inoculation of compost or sewage sludge, and could be enhanced by the increase of inoculation amount. The biodegradability of the organics was also affected by the incubation temperature, and was higher at 35℃ than that at 25℃. The biodegradability of the organic could be enhanced by the ultrasonic pretreatment. The organic materials diluted with water, around three times, was more easily stabilized, but the removal of ammonia nitrogen was slightly higher when the sediment was diluted six times with water. For the removal of heavy metals from the sediment using bioleaching process, both elemental sulfur and ferrous sulfate were the effective the energy sources for bioleaching bacteria, and the proper amounts of energy sources for the effective acidification for the leaching of heavy metals were around 0.3% for both elemental sulfur and ferrous sulfate. However, pyrite was not suitable as the energy source for the bioleaching bacteria. The solubilization efficiency of heavy metals from the sediment was affected by kinds of heavy metals, as well as the energy source. Copper was rapidly solubilized, and final percentage of solubilization was amount to around 81-84%. The solubilization efficiency of cadmium was around 87-89%, but the efficiency for chromium was just 22.6-32%. Plumbum was slowly solubilized, and the final efficiency was not high because of low solubility of PbSO4. Overall, most of the heavy metals contained in the sediment could be cleaned satisfactorily and their remaining concentrations are unlikely to be toxic. However, the remaining concentrations of plumbum and chromium in sediment seem to be somewhat unsatisfactory. For the study on the reuse of the cleaned sediment, the sediment was treated with various activation methods, and their adsorption characteristics for nutrients were also studied. The time for adsorption equilibrium and adsorption capacity for nitrate were affected by the activation methods, but were amount to about 17min and 2.2mg NO3-N/g, respectively. This indicates that the sediment from coastal fisheries could be reused as a material for the improvement of coastal water quality by a proper activation. | - |
dc.description.tableofcontents | List of contents ⅰ List of figures ⅴ List of tables ⅷ Abstract ⅸ 제 1장 서론 1 1.1 연구 배경 및 목적 1 1.2 연구 수행 방법 2 제 2장 문헌연구 4 2.1 연안해역 오염현황 4 2.1.1 연안해역 현황 5 가. 수질 오염 현황 6 나. 저질 오염 현황 9 2.1.2 연안어장 오염현황 12 가. 남해 연안어장의 각 만의 수질 및 저질 오염 현황 13 나. 연안어장 생산성 평가 15 2.2 준설 퇴적물의 처리기술 18 2.2.1 물리적 처리 20 가. 탈수 20 나. 입자분리 21 2.2.2 생물학적 처리 22 가. 원 리 24 나. 미생물의 역할 24 다. 분해 과정 25 라. 저해 인자 31 2.2.3 난분해성 물질 처리 31 가. 독성 물질 32 나. 부분 산화 33 다. 낮은 농도로 인한 오염 물질 제거 불능 34 2.2.4 생물학적 처리 공정 35 가. 생물학적 통풍법 35 나. 고도퇴비화 공법 35 다. 생물반응기 방법 37 라. 경작법 40 마. 생물학적 고형물 처리법 42 바. 탈염화법 43 사. 유동층 생물막 반응기 44 아. 생물침출 45 자. 합병소화 46 제 3장 실험재료 및 방법 47 3.1 연안 어장 퇴적물의 물리· 화학적 성상 47 3.1.1 대상어장 부근의 지형 특성 및 준설 퇴적물 시료 채취 47 3.1.2 준설 퇴적물의 물리· 화학적 기초성상 분석 50 3.2 준설 퇴적물에 함유된 유기오염물질의 안정화 52 3.2.1 연안 어장 준설 퇴적물에 함유된 유기오염물질의 처리 52 3.2.2 준설 퇴적물에 함유된 유기오염물질의 안정화/숙성공정 53 3.2.3 유기물질의 정량 분석 55 3.3 연안어장 준설 퇴적물에 함유된 중금속의 생물침출 58 3.3.1 중금속의 회분식 생물침출 58 3.3.2 수정 연속회분식 생물침출 공정 58 3.4 영양염류제거를 위한 활성 준설토의 흡착특성 60 제 4장 결과 및 고찰 62 4.1 연안 어장 퇴적물의 물리· 화학적 성상 62 4.2 준설 퇴적물에 함유된 유기 오염물질의 안정화 64 4.2.1 연안 어장 준설 퇴적물에 함유된 유기오염물질의 처리 64 가. 준설 퇴적물에 함유된 유기물의 구성 64 나. 준설토 퇴적물에 함유된 유기오염물질의 생분해도 66 4.2.2 준설 퇴적물에 함유된 유기물질의 안정화/숙성 공정 70 4.3 연안 어장 준설 퇴적물의 중금속 침출 기술 76 4.3.1 준설 퇴적물에 함유된 중금속의 회분식 생물침출 76 가. 생물침출공정에서의 산성화반응 76 나. 생물침출공정에 의한 준설 퇴적물로부터 중금속의 용출 80 4.3.2 수정 연속회분식 생물침출공정 85 가. pH 변화에 따른 중금속 용출 효율 87 4.4 준설 퇴적물의 재활용을 위한 연구 91 4.4.1 접촉시간의 영향 91 4.4.2 흡착동력학 92 Ⅴ. 결 론 96 참고문헌 98 | - |
dc.language | kor | - |
dc.publisher | 한국해양대학교 대학원 | - |
dc.title | 연안어장 준설 퇴적물에 함유된 유기물 및 중금속의 친환경적 처리 | - |
dc.title.alternative | Treatment of Organic Material and Heavy Metal from Dredged Sediments in the Coastal Fishing Ground | - |
dc.type | Thesis | - |
dc.date.awarded | 2005-02 | - |
dc.contributor.alternativeName | Ko | - |
dc.contributor.alternativeName | Seong-Jeong | - |
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