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금은광산 광석광물의 품위향상 및 유가금속 회수를 위한 용출특성

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Author(s)
김봉주
Issued Date
2016
Keyword
금/은, 유가금속, 미생물용출, 화학적용출 , 광미
Abstract
This study aims to collect valuable metal through the biological, physicochemical leaching and electrolysis and also to confirm if a resource-recycling can be used to handle tailings in bulk, which are considered to be environmentally problematic.

The enhancing of Au-Ag-Te content in tellurium-bearing ore mineral by bio-oxidation-leaching

The purpose of this study is to enhance the content of valuable metals such as Au-Ag-Te in tellurium-bearing minerals by bio-oxidation-leaching. It was confirmed that pyrite, chalcopyrite, sphalerite and galena were produced together with tellurium-bearing minerals including hessite, sylvanite and tellurobismuthite from ore minerals and concentrates through microscopic observation and SEM/EDS analysis. In a bio-oxidation-leaching experiment, with regard to Au, Ag, Te, Cu and Fe, the changes in the amount of leaching and the content of leaching residues were compared and analyzed with each other depending on the adaptation of an indigenous microbe identified as Acidithiobacillus ferrooxidans. As a result of the experiment, the Au-Ag-Te content in tellurium-bearing ore mineral was enhanced in the order of physical oxidation leaching, physical/non-adaptive bio-oxidation-leaching and physical/adaptive biological leaching. It suggests that the bio-oxidation-leaching using microbes adapted in tellurium-bearing ore mineral can be used as a pre-treatment and a main process in a recovery process of valuable metals.

Reductive leaching of Mn from deep-sea manganese crust, and upgrading of Au-Ag-Te contents from invisible gold concentrate by biooxidation

In order to upgrade Au-Ag-Te content in gold concentrate and reductively leach Mn from deep-sea manganese crust, bioleaching experiments were carried out. Indigenous acidiphile bacteria were collected from local mine drainage and then cultured for 6 years and 4 months. The bacteria were confirmed, by PCR and 16S rRNA analysis, as an Acidithiobacillus ferrooxidans, which can oxidize Iron and elemental sulfur. In order to increase the bacteria's tolerance to heavy metals, this indigenous acidophilic bacteria was repeatedly subcultured in an adaptation-medium containing 382.98 mg/l Cu for 35 periods of 21 days. As a result of bioleaching experiments with the bacteria, soluble ions, such as Cu and Fe, were increased in experimental samples in the order of the control, the non-adapted bacteria sample, the adapted bacteria without manganese crust sample, and the adapted bacteria sample. Mn content was increased in the order of control, non-adapted bacteria, and adapted bacteria sample as reductively leached. In the solid-residue, the insoluble elemental Au, Ag and Te content was increased in the order of control, non-adapted bacteria, adapted bacteria without manganese crust, and adapted bacteria sample. Accordingly, it is expected that more Au, Ag and Te can be upgraded in the gold concentrate and more Mn, Ni, Co, Cr can be reductively leached from the manganese crust if the bacteria is adapted to heavy metal ions and an optimization of conditions is found in future bioleaching processes.

The Characteristic dissolution of valuable metals from mine-waste rock by heap bioleaching, and the recovery of metallic copper powder with Fe removal and electrowinning

In order to recover the metallic copper powder from the mine-waste rock, heap bioleaching, Fe removal and electrowinning experiments were carried out. The results of heap leaching with the mine-waste rock sample containing 0.034% Cu showed that, the leaching rate of Cu were 61% and 62% in the bacteria leaching and sulfuric acid leaching solution, respectively. Sodium hydroxide (NaOH), hydrogen peroxide (H2O2) and calcium hydroxide (Ca(OH)2) were applied to effectively remov Fe from the heap leaching solution, and then H2O2 was selected for the most effective removing Fe agent. In order to prepare the electrolytic solution, H2O2 were again treated in the heap leaching, and Fe removal rates were 99% and 60%, whereas Cu removal rates were 5% and 7% in the bacteria and sulfuric acid leaching solutions, respectively. After electrowinning was examined in these leaching solution, the recovery rates of Cu were obtained 98% in bacteria and obtained 76% in the sulfuric leaching solution. The dendritic form of metallic copper powder was recovered in both leaching solutions.

Enhancement of Au·Ag leaching by mechanochemical activation and thiourea-thiocyanate mixing solution

In order to enhance the Au·Ag leach rate, a mechanochemical activation process and a mixed thioureathiocyanate solution has been applied to Au concentrate. To achieve mechanochemical activation, the Au concentrate was mechanically ground using a dry and a wet process. The results of a particle size distribution analysis and an XRD analysis, average particle size and crystallite size were much smaller in the dry-sample than in the concentrate sample. As well the size was smaller in the wet-sample than in the dry-sample. In SEM and XRD analysis, the amorphization effect was observed in the wet-sample due to mechanochemical activation. Au·Ag leaching experiments were carried out with a thiourea solution, a thiocyanate solution and a mixed thiourea-thiocyanate solution. The Au · Ag leach rate was much greater in the dry-ground-sample than in the concentrate sample, and the leach rate was greater in the wet-ground-sample than in the dry-sample. The Au·Ag leach rate was much greater in the thiocyanate solution than in the thiourea solution, and the leaching rate was much greater in the mixed thiourea-thiocyanate solution than in the thiocyanate solution. Up to a 99% leach rate for Au · Ag were only achieved in the wet-sample using the mixed thiourea-thiocyanate leaching solution.

Selective phase transformation of arsenopyrite by microwave heating and their enhancement Au recovery by thiocyanate solution

In order to investigate selective phase transformations and to determine the maximum Au leaching factors from microwave treated Au-bearing complex sulfides, a microscope, SEM-EDS analysis, and thiocyanate leaching tests were performed. When the Au-bearing complex sulfides were exposed to microwave heating, increasing the microwave exposure time increased temperature and decreased weight. Arsenopyrite was first selectively transformed to hematite, which formed a concentric rim structure. In this hematite, oxygen and carbon was detected and always showed high iron content and low arsenic content due to arcing and oxidation from microwave heating. The results of the leaching test using microwave treated sample showed that the maximum Au leaching parameters was reached with 0.5 g concentration thiocyanate, 2.0 M hydrochloric acid, 0.3 M copper sulfate and leaching temperature at 60℃. Under the maximum Au leaching conditions, 59% to 96.69% of Au was leached from the microwave treated samples, whereas only 24.53% to 92% of the Au was leached from the untreated samples.

The characteristic of Te recovery in gold concentrate using electrolysis

In order to obtain pure metallic Te from gold concentrate, roasting treatment, hypochlorite leaching, Fe removal and electrolysis experiments were carried out. The contents of Au, Ag and Te from the concentrate sample and roasted sample were much more soluble in the hypochlorite solution than in aqua regia digestion, whereas the metals Pb, Zn, Fe and Cu were easier to leach with the aqua regia than the hypochlorite. With the addition of NaOH in the hypochlorite leaching solution prior to electrolysis, the Fe removal rate achieved was only 96% in the concentrate sample, while it reached 98% in the roasted sample. The results of electrolysis for 240 min, 98% of the metallic copper was recovered from the concentrate sample, while 99% was obtained from the roasted sample due to the removal of S by roasting. The amount of anode slime was also greater in the electrolytic solution with the roasted sample than with the concentrate sample. The results on the anode slime after the magnetic separation process showed the amount of metallic pure native tellurium recovered was greater in the roasted sample than in the concentrate sample.

Recycling of arsenic-rich mine tailings in controlled low-strength materials

This study investigated the engineering properties and leaching behavior of controlled low-strength materials (CLSM) containing arsenic-rich mine tailings and evaluates the feasibility of the tailings as source material for CLSM. The compressive strength of the CLSM mixtures was shown to satisfy that specified in American Concrete Institute (ACI) Committee 229R in which the content of cement was controlled to be 10-30% by the weight of the tailings. The leaching fraction of As from CLSM mixtures was found to be below 6% regardless of the mix proportion and grinding of samples. The leaching fraction from the mortar-type CLSM was lower than those of the slurry-type CLSM. Furthermore, the leaching fraction of the CLSM mixtures in the ground state by weathering and erosion was increased, whereas the absolute value remained below 2%, thus showing no significant influence.
Alternative Title
Leaching characteristics for recovery of valuable metals and improvement of Au-Ag ore minerals
Alternative Author(s)
Kim Bong Ju
Affiliation
조선대학교
Department
일반대학원 에너지자원공학
Advisor
박천영
Awarded Date
2016-08
Table Of Contents
Abstract
1. 개 요 1
가. 서 론 1
나. 연구 배경 3
1) 생물학적 용출 3
2) BIOXTM 4
3) 유가금속(Au, Ag, Te) 회수를 위한 물리적 전처리 6
가) 기계적 활성화 6
나) Microwave treatment 7
4) 전기분해를 통한 유용금속 회수 12
가) Te의 회수 12
나) 동 제련에서의 Te 회수 13
5) 폐광미의 순환자원화 17
가) 광산폐기물의 오염 저감화 기술개발 17
나) 광산폐기물을 이용한 건설재료 적용성 평가 18
다. 연구 목적 20

제 1 부 Cu 이온에 적응된 토착호산성박테리아를 이용한 정광 및 폐광석으로부터 미생물용출 효율 향상

2. 함-텔루륨 광석광물의 산출 특성과 미생물용출을 활용한 Au-Ag-Te 함량의 품위향상 22
가. 서론 22
나. 본 론 25
1) 실험 재료 및 방법 25
가) 토착호산성 박테리아 25
나) 토착박테리아 배양 25
다) 토착박테리아의 16S rRNA 동정 25
라) 토착박테리아 적응 27
마) 정광 및 광석광물 시료 27
바) 용출 실험 27
사) 분석 방법 28
2) 광석 광물 31
3) 중합효소연쇄반응과 16S rRNA 염기서열에 의한 토착박테리아 동정 40
5) 생물학적 산화작용에 의한 Ag, Te, Fe 및 Cu 용출 45
6) 적응 이온에 따른 용출율 향상 47
7) 고체-잔류물에 대한 XRD 51
다. 결 론 53

3. 박테리아의 생물학적 산화작용을 이용한 심해저 망간 각으로부터 Mn 환원용출과 비-가시성 금 정광의 Au-Ag-Te 품위 향상 54
가. 서 론 54
나. 본 론 56
1) 실험 재료 및 방법 56
가) 토착호산성 박테리아 56
나) 토착호산성 박테리아 56
다) 토착박테리아의 16S rRNA 동정 56
라) 토착박테리아 적응 58
마) 금 정광 시료 59
바) 심해저-망간 각 시료 59
사) 미생물용출 실험 61
아) 분석방법 64
2) 금정광 및 망간각 시료 65
3) 생물학적 산화작용에 의한 pH 및 Eh 변화 68
4) 유용금속 용출 효과 73
5) 고체-잔류물 78
6) 고체-잔류물의 XRD 80
다. 결 론 82

4. 더미 미생물용출에 의한 폐-광석으로부터 유용금속 용해 특성 83
가. 서 론 83
나. 본 론 86
1) 실험 재료 및 방법 86
가) 폐-광석 시료 86
나) 토착호산성 박테리아 86
다) 토착박테리아 배양 86
라) 더미 용출-용액 제조 88
마) 더미 미생물 용출 실험 92
바) 분석방법 92
2) 폐-광석 시료에 대한 현미경관찰 결과 93
3) 부유성 박테리아 95
4) pH 및 Eh 변화 97
5) 유용금속 용출 및 맥석광물의 용해 특성 99
6) Cu 용출 특성 101
7) 2차 광물 특성 105
8) Fe 제거제 선정 107
9) Fe 제거 효과 112
다. 결 론 114

제 2 부 물리/화학적 활성화에 따른 금-은-정광의 광물학적 상변화와 비-시안 용매에 의한 금-은 용출 향상
5. 기계적-화학적 활성화에 따른 금-은-정광의 광물학적 상변화와 비-시안 용매에 의한 금-은 용출 향상 116
가. 서론 116
나. 본 론 118
1) 실험 재료 및 방법 118
가) 실험 재료 118
나) 기계적-화학적 활성화 실험 118
다) 티오요소 용출실험 119
라) 분석 방법 119
2) 정광시료의 특성 119
3) 입도분석 결과 123
4) SEM 분석 결과 126
5) XRD 분석 결과 128
6) 등전위 측정 결과 129
7) 티오요소 농도 효과 130
8) 황산 제2철 농도 효과 132
9) 황산 농도 효과 134
10) 온도 효과 136
다. 결 론 138

6. 마이크로웨이브 가열에 의한 황비철석의 선택적 상변환과 티오시안산염 용액에 의한 Au 회수율 향상 139
가. 서 론 139
나. 본 론 141
1) 실험 재료 및 방법 141
가) 실험 재료 141
나) 마이크로웨이브 노출실험 142
다) 티오시안산염 용출실험 142
라) 분석 방법 142
2) 광석시료의 특성 144
3) 마이크로웨이브 가열에 따른 온도 및 무게변화 146
4) 마이크로웨이브 가열에 따른 XRD 147
5) 마이크로웨이브 가열에 의한 황비철석의 상변환 149
6) 티오시안산염 농도 효과 154
7) 염산 농도 효과 156
8) 황산구리 농도 효과 158
9) 온도 효과 160
다. 결 론 162

제 3 부 전기분해에 의한 금 정광으로부터 양극 슬라임 생성과 양극 슬라임으로부터 자연 텔루륨 회수에 관한 연구

7. 전기분해에 의한 금 정광으로부터 양극 슬라임 생성과 양극 슬라임으로부터 자연 텔루륨 회수에 관한 연구 164
가. 서론 164
나. 본 론 166
1) 실험 재료 및 방법 166
가) 금 정광 시료 166
나) 차아염소산 용액에 의한 용출실험 167
다) NaOH 의한 Fe 제거 167
라) 전기분해 실험 169
마) 분석 방법 170
2) 정광 및 소성시료의 특성 171
3) XRD 분석 173
4) 정광과 소성시료의 함량변화 174
5) 차아염소산 용출 및 NaOH 의한 Fe 제거 효과 174
6) 전기분해에 의한 Cu 및 Fe 함량변화 176
7) 전극의 무게 변화 177
8) 음극회수물질에 대한 XRD분석 결과 179
9) 전기분해에 의한 제거율과 회수율 상수 182
10) 양극 슬라임의 특성 184
11) 양극 슬라임에 대한 XRD분석 187
12) 양극 슬라임에 대한 자력선별 효과 189
13) 양극 슬라임에 대한 SEM 191
다. 결 론 194

제 4 부 비소가 함유된 폐광미를 활용한 CLSM의
공학적특성 및 침출 거동
8. 비소가 함유된 폐광미를 활용한 CLSM의 공학적특성 및 침출 거동 196
가. 서 론 196
나. 본 론 197
1) 실험 재료 및 방법 197
가) 폐 광미(mine tailings) 197
나) 시멘트, 골재, 물 200
다) 배합비 200
라) CLSM의 공학적 특성 측정 204
마) 용출 실험(leaching test) 205
바) 안정성 평가(Toxicity Characteristic Leaching Procedure) 207
2) 폐 광미 광물학적 특성 209
3) 워커빌리티 및 침하량 (settlement) 213
4) 압축 강도 216
5) CLSM에서 비소의 용출 거동 218
6) CLSM에서 비소의 고정상 223
7) 안정성 평가(TCLP) 224
다. 결 론 225
9. 최종 결론 226
참고문헌
감사의 글
Degree
Doctor
Publisher
조선대학교
Citation
김봉주. (2016). 금은광산 광석광물의 품위향상 및 유가금속 회수를 위한 용출특성.
Type
Dissertation
URI
https://oak.chosun.ac.kr/handle/2020.oak/12881
http://chosun.dcollection.net/common/orgView/200000265647
Appears in Collections:
General Graduate School > 4. Theses(Ph.D)
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