• 제목/요약/키워드: Stabilization/solidification

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산업폐기물 중의 유해중금속의 환경친화적 안정화 처리(I) (Environmentally Adaptive Stabilization of the Hazardous Heavy Metal Waste by Cementious Materials(I))

  • 원종한;안태호;최광휘;최상흘;손진군;심광보
    • 한국세라믹학회지
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    • 제39권7호
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    • pp.680-686
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    • 2002
  • 각 시멘트 구성 광물별로 중금속의 고정/안정화 메커니즘과 수화거동을 검토하였다. $C_3$S수화 시 Pb는 불용성화합물인 Ca[Pb(OH)$_3$.$H_2O$]$_2$를, Cr은 CaCr $O_4$$H_2O$를 생성하였으며, 초기 7일까지는 전체적으로 중금속이 첨가되어진 경우 수화가 늦어지는 경향을 보이고 있었다. $C_3$A와 $C_4$ $A_3$ $S^{S}$수화 시 Pb, Cr 이온이 ettringite 또는 monosulfate에 의한 수화물에 치환에 의한 고정/안정화되고 있다. 수화물에서 Pb, Cr, Zn등 유해중금속의 용출은 극미하였으며 이는 수화물에 중금속이 고정/안정화되었음을 알 수 있다. 슬래그 혼합 시멘트를 이용한 산업 폐기물 STS, BF, COREX 슬러지 함유 중금속의 고정화/안정화를 검토하였다 시멘트와 폐슬러지를 3 : 7의 비율로 혼합 고화 처리한 결과 유해 중금속의 용출은 극미하였으며, 효과적으로 고정/안정화됨을 확인할 수 있었다.다.

FIXATION OF LEAD CONTAMINANTS IN Pb-DOPED SOLIDIFIED WASTE FORMS

  • Lee, Dong-Jin;Chung, David;Hwang, Jong-Yeon;Choi, Hyun-Jin
    • Environmental Engineering Research
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    • 제12권3호
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    • pp.101-108
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    • 2007
  • Fixation of lead contaminants in the solidification/stabilization using Portland cement has been investigated by X-ray diffraction, scanning electron microscopy and compressive strength. The presence of lead was observed to produce lead carbonate sulfate hydroxide ($Pb_4SO_4(CO_3)_2(OH)_2$), lead carbonate hydroxide hydrate ($3PbCO_3{\cdot}2Pb(OH)_2{\cdot}H_2O$) and two other unidentified lead salts in cavity areas and was observed to significantly retard the hydration of cement. By 28 days, howevere, the XRD peaks of most of the lead precipitates have essentially disappeared with only residual traces of lead carbonate sulfate hydroxide and lead carbonate hydroxide hydrate evident. After 28 days of curing, hydration appears well advanced with a strong portlandite peak present though C-S-H gel peaks are not particularly evident. Lead species produced with the dissolution of lead precipitates are fixed into the cement matrix to be calcium lead silicate hydrate (C-Pb-S-H) during cement-based solidification.

특수시멘트 고화재를 이용한 지정폐기물의 고형화/안정화(I) (solidification/Stabilization of Hazardous Wasted Using Cementitious Material(I))

  • 임채용;백상현;엄태선;최롱;오병;이경훈
    • 한국콘크리트학회:학술대회논문집
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    • 한국콘크리트학회 2000년도 봄 학술발표회 논문집
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    • pp.205-210
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    • 2000
  • This study concerns the cement-solidification. stabilization of the electric furnace dust. Compressive strength and leaching test of heavy metals were evaluated for varing types and ratios of cements and the effect of some additives of hauyne clinker and slag were also discussed. In this cases of using cement binders more than 30%, the compressive strength showed the values over 150kgf/cm2. so it can be used as filler for concrete precastings. Type III cement and Hauyne clinker improved the compressive strength, especially early strength. Leaching amount of heavy metals was decreased when using type III cement and adding hauyne clinker and slag. The values were especially low in the case of slag addition.

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폐기물을 활용한 저투수성 오염토양의 정화 및 안정화 기술 개발 (Development of Remediation and Stabilization Technique for Low-Permeable Contaminated Soil Using Waste Materials)

  • 박상규;이기호;박준범
    • 한국지반공학회:학술대회논문집
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    • 한국지반공학회 2002년도 가을 학술발표회 논문집
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    • pp.681-688
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    • 2002
  • Study was peformed to develop the‘environmental double pile’for the remediation of low-permeable contaminated soil. This technique is similar in function to‘sand drain pile’But this applies recyclable oyster shell treated as waste materials to a drain material and the pile is consisted of two layers. Inner metal pile is located in center and oyster shells are filled around it. By this technology, contaminated ground water is pumped out through the oyster shell and purified by drainage, adsorption, and reaction processes. Afterwards, the grout material is injected through the inner pile for the effect of the solidification / stabilization. As a result, the concept of this technique is a development of one-step process technology. Through the test, a consolidation characteristic by radial drain is going to be evaluated and the optimum standard of this technology will be calculated.

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DSP 시멘트를 이용한 중금속 이온의 고화 (The Solidification of the Heavy Metal Ion by Using DSP Cement)

  • 소정섭;최상홀
    • 한국세라믹학회지
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    • 제33권8호
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    • pp.889-894
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    • 1996
  • This study was subjected to the stabilization of heavy metals using DSp cement. Heavy metal Cr and Pb ions were mixed with cement paste and hydration behavior and leaching property by heavy metal were exami-ned. It was found that, Cr ion accelerated the early hydration of the cement and has no accelerating effect in later hydration period. However Pb ion retarded the hydration of the cement for a early hydration periods. As a result of leaching test the quantity of leachant has a very low value and the influence of leached heavy metal effected on the environments is very weak.

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Solidification/stabilization of simulated cadmium-contaminated wastes with magnesium potassium phosphate cement

  • Su, Ying;Yang, Jianming;Liu, Debin;Zhen, Shucong;Lin, Naixi;Zhou, Yongxin
    • Environmental Engineering Research
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    • 제21권1호
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    • pp.15-21
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    • 2016
  • Magnesium potassium phosphate cement (MKPC) is an effective agent for solidification/stabilization (S/S) technology. To further explore the mechanism of the S/S by MKPC, two kinds of Cd including $Cd(NO_3)_2$ solution (L-Cd) and municipal solid waste incineration fly ash (MSWI FA) adsorbed Cd (S-Cd), were used to compare the effects of the form of heavy metal on S/S. The results showed that all the MKPC pastes had a high unconfined compressive strength (UCS) above 11 MPa. For L-Cd pastes, Cd leaching concentration increased with the increase of Cd content, and decreased with the increase of curing time. With the percentage of MSWI FA below 20%, S-Cd pastes exhibited similar Cd leaching concentrations as those of L-Cd pastes, while when the content of MSWI FA come up to 30%, the Cd leaching concentration increased significantly. To meet the standard GB5085.3-2007, the highest addition of S-Cd was 30% MSWI FA (6% Cd contained), with the Cd leaching concentration of 0.817 mg/L. The S/S of L-Cd is mainly due to chemical fixation, and the hydration compound of Cd was $NaCdPO_4$, while the S/S of S-Cd is due to physical encapsulation, which is dependent on the pore/crack size and porosity of the MKPC pastes.