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황산염환원박테리아(SRB) 지하미생물을 이용한 용존 세슘 제거 연구

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Abstract
Radioactive cesium (Cs-137) is one of the main radioactive materials causing severe ecological damage and environmental pollution because it has a relatively long half-life (30.17 years), emitting the high energy of gamma-rays. When the ocean was contaminated by Cs-137, resulting from the accidents of the nuclear power plants such as Chernobyl and Fukushima nuclear reactors, the removal of Cs-137 from seawater has been difficult causing great costs because it is not easily separated from water with highly-concentrated salt components. The popular process for the Cs-137 removal from water has been the adsorption and/or the precipitation technologies, however the development of the outstanding adsorbents or precipitant for Cs-137 from seawater has been very limited in previous researches.
This study focused on the development of the effective and the environment-friendly Cs-137 removal technology by using the biogenic sulfide generation process, which uses a sulfate reducing bacterium (SRB), D. vulgaris, in here rather than commercial inorganic absorbents. D. vulgaris was cultivated in an incubator (30℃) for the experiment and cesium, iron and lactate with various concentration were injected into the SRB media. The batch experiment for a feasibility study was performed to remove Cs-137 from seawater by the sulfide mineralization process and to define its optimal operation conditions. At first, several batch experiments for removing stable cesium (Cs-133) from both the freshwater and the seawater were performed with different cesium concentrations (0.01 - 10 mg/L), iron concentrations (0.5 - 3 mM), and two lactate concentrations (3 mM and 6 mM). Another batch experiment containing radioactive Cs (Cs-137; 133 Bq/mL) was duplicated for the seawater under the condition of iron concentration of 3 mM and lactate concentration of 6 mM and their results were compared with those of the commercial absorbent (R9160-G), which is now used for the Cs-137 removal from seawater at Fukushima nuclear power plant in Japan.
From the results of SEM-EDS and XRD analyses, we found that the sulfate ions dissolved in both seawater and freshwater were transformed into a sulfide mineral, mackinawite (FeS), by the biomineralization of D. vulgaris. The dissolved Cs-137 (or Cs-133) was removed during the experiment, suggesting that Cs was successfully separated from the water as a solid form. For the freshwater experiment, the stable cesium (Cs-133) removal efficiency was the highest under the condition of iron concentration of 1 mM and lactate concentration of 3 mM. At Cs-133 concentration of 10 mg/L and 1 mg/L, the removal efficiency was 17 % and 47 %, respectively. At 0.1 mg/L of Cs-133, the removal efficiency was 96 % and in the lowest concentration (0.01 mg/L), it was almost 100 %, suggesting that Cs-133 removal efficiency was inversely proportional to Cs concentrations in freshwater. For the seawater experiment, the Cs removal efficiency was the highest under the condition of iron concentration of 3 mM and lactate concentration of 6 mM. At Cs-133 concentration of 10 mg/L and 1 mg/L, the removal efficiency was 21 % and 39 %, respectively. At 0.1 mg/L of Cs-133, the removal efficiency was 86 % and in the lowest concentration (0.01 mg/L), it was almost 100 % in seawater. Interestingly, the Cs removal efficiency increased with the decrease of Cs concentration in seawater, which was similar to the results obtained from freshwater.
For the seawater experiment, the Cs-137 removal efficiency of R9160-G was 71.3 % and the removal efficiency using D. vulgaris was 96.1 %. For the experiment with the Cs biomineralization using D. vulgaris, the amount of produced sludge as a precipitate after the experiment was 0.3 D.W. g/L, which was only one tenth of that with the usage of R9160-G, suggesting that the radioactive cesium was successfully removed by the biotechnology, producing a very small volume of radioactive Cs waste. In addition, this experiment verified that the Cs-137 removal process by using sulfate reducing bacteria (SRB) can effectively treat a large volume of seawater that was contaminated with cesium.
Author(s)
황진하
Issued Date
2017
Awarded Date
2017. 2
Type
Dissertation
Keyword
방사성세슘(Cs-137) 세슘 제거 황산염환원박테리아(SRB) D. vulgaris 방사성 폐수
Publisher
부경대학교 대학원
URI
https://repository.pknu.ac.kr:8443/handle/2021.oak/13849
http://pknu.dcollection.net/jsp/common/DcLoOrgPer.jsp?sItemId=000002332024
Affiliation
부경대학교 대학원
Department
대학원 지구환경공학학ㆍ연협동과정
Advisor
이민희
Table Of Contents
Ⅰ. 서론 1
Ⅱ. 연구 배경 3
1. 원전 사고와 관련된 방사능 오염 3
2. 방사성폐기물의 종류 6
2.1. 원자력 발전과 방사성폐기물 6
2.2. 방사성폐기물 분류 7
2.2.1 고준위 방사성페기물 8
2.2.2 중·저준위 방사성폐기물 8
3. 세슘 9
3.1. 방사성세슘(Cs-137) 9
3.2. 화학적 특성 10
4. 황산염환원박테리아(SRB) 12
4.1. SRB의 황화광물 형성 기작 12
4.2. 탄소원과 에너지원 13
4.3. SRB 서식환경 14
4.3.1 온도 14
4.3.2 pH 14
4.4. 황화광물(sulfide mineral)의 형성 16
Ⅲ. 실험재료 및 방법 18
1. 실험재료 18
1.1. Desulfovibrio vulgaris 18
1.2. SRB 배양 18
2. 실험방법 20
2.1. 안정세슘 제거 실험 20
2.1.1 담수조건 20
2.1.2 해수조건 21
2.1.3 흡착실험 22
2.2. 방사성세슘 제거 실험 24
3. SRB에 의해 형성된 황화광물 분석 26
Ⅳ. 결과 및 고찰 27
1. 생기원 황화철의 형성 및 특징 27
1.1. 침전된 황화철의 광물학적 특성 27
1.2. 황화광물 성분 분석 30
2. 세슘 제거 특성 32
2.1. 철과 세슘 농도의 영향 32
2.1.1 SRB에 의한 황화광물 형성과 세슘 제거량과의 상관관계 32
2.1.2 담수실험 33
2.1.3 해수실험 35
2.2. 다양한 흡착제들과의 세슘 제거 효율 비교 39
2.3. 세슘 제거 기작 규명 42
3. SRB에 의한 방사성세슘(Cs-137) 제거 45
Ⅴ. 결론 47
참고문헌 50
요약문 64
감사의 글 67
Degree
Master
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