• Title/Summary/Keyword: 암모니아 침출

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Development of Ammoniacal Leaching Processes; A Review (암모니아 침출공정(浸出工程) 기술개발(技術開發) 동향(動向))

  • Yoo, Kyoungkeun;Kim, Hyunjung
    • Resources Recycling
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    • v.21 no.5
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    • pp.3-17
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    • 2012
  • Selective leaching processes for copper, gold, nickel, and cobalt have been investigated because there is an advantage of ammoniacal hydrometallurgy that metal such as copper could be selectively extracted restricting the dissolution of iron or calcium. In the present article, the studies for selective ammoniacal leaching of copper from motor scraps and waste printed circuit boards (PCBs), for ammoniacal leaching of gold to decrease the amount of cyanide used or to substitute cyanide by thiosulfate, and for ammoniacal leaching to recover nickel and cobalt from nickel oxide ore and intermidiate obtained from manganese nodule treatment process were summarized and further studies were proposed for domestic technology development for ammoniacal hydrometallurgy processes.

Removal of Ammonia-Nitrogen Contained in Landfill Leachate by Ammonia Stripping(I) (암모니아 탈기공정을 이용한 침출수의 암모니아성 질소제거(I))

  • Lee, Byung-Jin;Cho, Soon-Haing
    • Journal of Korean Society of Environmental Engineers
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    • v.22 no.10
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    • pp.1893-1904
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    • 2000
  • Nitrogen compounds are one of the major pollutants which cause eutrophication problems of the river or lake and red tides problems of the ocean. Currently available technologies for the removal of nitrogen compounds are mostly biological treatment. However, biological treatment is only effective for the wastewater which contains low concentration of nitrogen compounds. Leachate from solid waste landfill or industrial wastewater which contains high concentration of nitrogen can not be effectively treated by most of the currently available biological treatment technologies. With this connection. the objective of this study is to examine the applicability of ammonia stripping technology for the removal of high concentration of ammonia nitrogen compounds of the leachate from solid waste landfill. It can be concluded that ammonia stripping technology which was placed before the biological treatment process was very effective for the removal of high concentration of ammonium compounds. The chemical cost for the ammonia stripping was 16 percent higher than MLE process, so other methods like sludge recycling are needed for the reduction of operation cost. Further details are discussed in this paper.

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Ammoniacal Leaching for Recovery of Valuable Metals from Spent Lithium-ion Battery Materials (폐리튬이온전지로부터 유가금속을 회수하기 위한 암모니아 침출법)

  • Ku, Heesuk;Jung, Yeojin;Kang, Ga-hee;Kim, Songlee;Kim, Sookyung;Yang, Donghyo;Rhee, Kangin;Sohn, Jeongsoo;Kwon, Kyungjung
    • Resources Recycling
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    • v.24 no.3
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    • pp.44-50
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    • 2015
  • Recycling technologies would be required in consideration of increasing demand in lithium ion batteries (LIBs). In this study, the leaching behavior of Ni, Co and Mn is investigated with ammoniacal medium for spent cathode active materials, which are separated from a commercial LIB pack in hybrid electric vehicles. The leaching behavior of each metal is analyzed in the presence of reducing agent and pH buffering agent. The existence of reducing agent is necessary to increase the leaching efficiency of Ni and Co. The leaching of Mn is insignificant even with the existence of reducing agent in contrast to Ni and Co. The most conspicuous difference between acid and ammoniacal leaching would be the selective leaching behavior between Ni/Co and Mn. The ammoniacal leaching can reduce the cost of basic reagent that makes the pH of leachate higher for the precipitation of leached metals in the acid leaching.

Selective Leaching of Vanadium and Nickel in Metal Oxides Obtained from Orimulsion Ash (오리멀젼회(灰)로부터 제조(製造)된 중간(中間) 생성물(生成物)로부터 바나듐과 니켈의 선택적(選擇的) 침출(浸出))

  • Kim, Eun-Young;Lee, Sung-Ki;Park, Kyung-Ho
    • Resources Recycling
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    • v.15 no.6 s.74
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    • pp.10-15
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    • 2006
  • As a basic study on recovery of valuable metals such as vanadium and nickel from metal oxide obtained from waste orimulsion ash, we conducted selectively leaching of vanadium and nickel using $Na_2CO_3$ leaching and ammoniacal leaching, respectively. The 97% of vanadium was selectively leached at an optimum experimental condition, 50g/L $Na_2CO_3$, pulp density 50g/L, and 35% $H_2O_2$ 50ml/L, $25^{\circ}C$... for 1 hr, whereas no nickel was leached. In ammoniacal leaching study, 95% of nickel was selectively leached at the optimal experimental condition, $NH_4OH\;2M,\;(NH_4){_2}SO_4$ 1.5M, pulp density 50g/L, 25, for 4 hr along with 3% of vanadium.

Chemical Treatment of Leachate from Swine Manure Composting System (양돈분뇨 퇴비화공정에서 발생하는 침출액의 화학적처리)

  • 정태영;오인환;김동수
    • Journal of Animal Environmental Science
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    • v.8 no.3
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    • pp.145-152
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    • 2002
  • This experiment was conducted to investigate the efficiency and compatibility of the coagulation and settling processes of leachates from the compost of two swine farms. And results obtained are as follows : 1 In the farm A where $COD_{Cr}$, $COD_{Mn}$ and $BOD_5$ of original leachate were 4,400, 2,950 and 87mg/l, respectively, the rate of coagulation and settling process was more efficient in the leachate treated with the conjugate of Alum and cation polymer than that of Alum and anion polymer. The concentrations of BOD$_{5}$, T-N and T-P of the effluent after treatment with the conjugate of Alum and cation polymer under the optimum condition were 19, 257.5 and 0.4mg/l, respectively which are under the governmental regulation level. 2. In the farm B where $COD_{Cr}$, $COD_{Mn}$ and $BOD_5$ of original leachate were 4,720, 3,040 and 95mg/l, respectively, the conjugate of $FeCl_3$, 1,500mg/l and cation polymer 10mg/l ($FeCl_3$+FO4240) was most effective coagulation and settling agent compared with the others. The concentrations of BOD$_{5}$, T-N and T-P of the effluent after treatment with $FeCl_3$+FO4240 were 15.3, 829.4 and 2.8mg/l, respectively. And the concentration of T-N was higher than the governmental regulation level, presumably because of too high concentration of NH$_4$$^{+}$-N in the leachate.

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Integrated membrane distillation process for separation of ammonia from domestic waste water (생활폐수로부터 암모니아 분리를 위한 통합형 막증류 시스템)

  • Choi, Youngkwon;Park, Yoonkyung
    • Proceedings of the Korea Water Resources Association Conference
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    • 2022.05a
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    • pp.338-338
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    • 2022
  • 2050년까지 탄소중립 사회구현을 위한 방안을 모색하기 위한 논의가 활발히 이루어지고 있으며, 이에 수소도시 실현을 통한 화석연료와 탄소배출을 줄이는 방법들이 주목받고 있다. 그린수소가스의 생산 및 운송, 저장과 가스형태의 수소를 액화 수소로 압축시키는데 드는 막대한 에너지가 소비되는 문제점에 대한 대안책으로 암모니아를 캐리어로 이용하여 운송 및 저장하고 수소를 생산하는 방식이 널리 이용되고 있으며, 효율 향상을 위한 추가 연구들이 진행되고 있다. 또한, 중국에 대한 우리나라의 요소수 수입 의존도가 높음에 따라 요소수 주요성분인 암모니아와 탄산가스를 합성한 요소수 생산 방식에 대한 연구가 이루어지고 있다. 하지만, 현재 산업계에서 석탄과 같은 석유자원에서부터 암모니아를 추출하는 방식이 가장 널리 적용되고 있다. 이와 같은 암모니아 생산에 대한 석유자원 의존도를 낮추기 위한 방안에 대한 도출 및 연구가 필요한 실정이다. 이와 같은 상황에 맞춰 본 연구에서는 생활하수로부터 암모니아를 추출하는 방법으로서 통합형 막증류 시스템에 연구하고자 한다. 분뇨, 음식물 폐기물 침출수 등 유기성 폐기물의 수집, 운송 및 처리에서 발생되는 생활하수에는 암모니아성 질소 및 탄소가 다량 포함되어 있어 이를 추출하여 순수한 암모니아 생산에 대해 석유자원을 대체할 수 있는 대안으로서의 효용성을 갖고 있다. 하지만, 이와같은 생활하수는 암모니아성 질소 이외 성분들이 고농도로 포함되어 있어 암모니아 생산에 대한 원료만을 선택적으로 분리하는데 많은 어려움이 있다. 본 연구에서는 생활하수에서 암모니아를 선택적으로 분리하는 방법으로서 막증류(Membrane Distillation, MD) 기반의 통합 암모니아 분리기술을 개발하고 이에 대한 적용 가능성과 효율 향상에 대해 평가 하였다. 또한, 암모니아와 탄산가스 합성을 통한 요소수 생산 방법에 대한 연구를 진행하였다.

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Pretreatment of Helianthus tuberosus Residue by Two-Stage Flow Through Process (2단 흐름형 침출공정에 의한 돼지감자 줄기의 전처리)

  • Park, Yong Cheol;Kim, Jun Seok
    • Korean Chemical Engineering Research
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    • v.53 no.4
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    • pp.417-424
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    • 2015
  • In this study, the pretreatment of Helianthus tuberosus residue had been performed. The two-stage pretreatment on flow-through process were applied in the interests of increase of sugar production yield on enzymatic saccharification. The delignification by aqueous ammonia and the fractionation of hemicellulose by sulfuric acid solution as pretreatment solution were confirmed for effects of enzymatic saccharification. Two-stage pretreatment process was performed using aqueous ammonia and sulfuric acid. The first step was performed with aqueous ammonia for 40 min at $163.2^{\circ}C$ and the second step was performed with sulfuric acid solution for 20 min at $169.7^{\circ}C$. And then, the first step was performed with sulfuric acid solution and the second step was pretreated with aqueous ammonia. At this time, the glucose production was 30.7 g and the glucose yield was 72.4% in the first step process with aqueous ammonia. And, the glucose production was 20.9 g and the glucose yield was 49.3% in the first step process with sulfuric acid solution.

Effect of the Physical Parameters and Alkalinity in the Ammonia Stripping (반응조의 물리적 인자와 알칼리도가 암모니아 탈기에 미치는 영향에 관한 연구)

  • An, Ju-Suk;Lim, Ji-Hye;Back, Ye-Ji;Chung, Tae-Young;Chung, Hyung-Keun
    • Journal of Korean Society of Environmental Engineers
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    • v.33 no.8
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    • pp.583-590
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    • 2011
  • The effect of the physical parameters in the reactor (aeration depth, bubble size, and surface area) and the alkalinity of the solution on the ammonia stripping by bubbling were evaluated. When an airflow of 30 L/min was bubbled below the solution surface in the range 6-53 cm, the ammonia removal rate were observed to be the same regardless of the bubbling depths. At pH 10.0 and a temperature of $30^{\circ}C$, the average rate constant and the standard deviation were $0.178h^{-1}$ and 0.004. No appreciable changes in the ammonia removal rate were also observed with varying the bubble size and the air-contacting surface area. Alkalinity of the solution was found to affect the ammonia removal rate indirectly. This is expected because the pH of the solution would vary with dissolution of gaseous $CO_2$ by air bubbling. The real wastewaters from landfill site and domestic wastewater treatment plant were tested. In the case of domestic wastewater (pH = 7.1, alkalinity = 75 mg/L), the ammonia removal rate was poor even with the control of pH to 9.3. The raw landfill leachate (pH = 8.0, alkalinity = 6,525 mg/L), however, showed the appreciable removal rate with increasing pH during aeration. When the initial pH of the leachate was adjusted 9.4, the removal rate was significantly increased without changing the pH during aeration.

오염지하수정화를 위한 반응벽체의 설계 및 시공

  • 이동호;지원현;이재원;박준범
    • Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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    • 2004.04a
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    • pp.434-437
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    • 2004
  • 본 반층벽체 적용지역의 경우, 침출수의 영향으로 암모니아성 질소의 농도가 최대 29.12mg/L까지 검출되고 있으며 반응물질은 암모니아성 질소제거에 적합한 제올라이트를 선정하였다. 투수성 및 다짐강도를 고려하여 왕사와 50:50의 비율로 혼합, 적용하였으며 지하수 평균유속은 0.0864m/d이고 평균지하수위는 원지반 기준 - 4.0m의 분포를 나타내었다. 지질조사 결과, 적용구간의 지질구조는 매립층, 풍화토, 풍차암, 연암의 순서로 분포하고 있으며, 반응벽체의 설계깊이는 현장 시추조사 결과를 바탕으로 지하수의 Under-pass를 방지하기 위하여 연암층 50cm까지 관입시키도록 설계하였다. 최종적으로 선정된 반응벽체의 규모는 35m(길이) $\times$ 1.2m(두께) $\times$ 8.5 ~ 9.42m(구간별 깊이)로 설계에 반영되었다. 현재, 지하수감시정을 이용한 모니터링 결과, 상부지하수 감시정에서의 오염원은 우기의 영향으로 간헐적으로 발생하고 있으나 하부 지하수 감시정에서의 암모니아성 질소농도는 불검출 되거나 0.5 mg/L 이하로 유지되고 있다.

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Recovery of Valuable Metals from the Desulfurizing Spent Catalyst Used in Domestic Petrochemical Industry (국내 석유공장의 탈황 폐촉매로부터 유가금속의 회수에 관한 연구)

  • 김종화;양종규
    • Resources Recycling
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    • v.4 no.3
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    • pp.2-9
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    • 1995
  • The rccoverg and separation pracess of nikcl, vanadium and molybdenum from spent dcsulfilrizing catalyst ofpetrochemical rndustries was studied. Tnis process was canied out wet process which is consist of roasting, ammonialeaching and solve111 exDaction techniqcs. The metal ions of NI, V and Mo as vduable compollents were treated byroasting them a1 low lernperatuc, 400$^{\circ}$C in first dep, and then dlssah'ed nu1 at 80$^{\circ}$C wlth ammonium cabonate mlulion.Aftcr cooling them a1 room tempertaure, vanadium wa rccavered from mathcr iiquur in thc f n m of precipitate, sodiumvanadales The Secand slep, roasting the catalyst which is added sodium carbonate ul IOOO"C, was employed. Leachingwith distilled ~ a l e rga ve a iwo phase resultant, solutio~c~a ntaning Ni, V and Mo and solid residue containing sibca,alurmniu~n and iron. A solvcnt exlclction technique uslng vvriuus extractanls, MSP-8, TOIUC, LIX64Pi was eflecnve farthc extraclion and scparation ol thrcc mcfals from thc ammonical 11qou1 thc ammonical 11qou1.

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