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首页> 外文期刊>Civil Engineering and Architecture >Immobilization of Heavy Metals in Waste Phosphate Coating Sludge Using Kiln Dust as Portland Cement Substitute
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Immobilization of Heavy Metals in Waste Phosphate Coating Sludge Using Kiln Dust as Portland Cement Substitute

机译:用窑灰替代硅酸盐水泥固定废磷酸盐涂料污泥中的重金属

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In the present study, stabilization and solidification (S/S) of the waste phosphate sludge (WPS) using Portland cement (PC) and cement kiln dust (CKD) was investigated. In the first place, only PC was used to stabilize 5, 10 and 15% WPS. At a later stage, 10 and 15% CKD were used as PC substitute to stabilize 15%WPS. WPS contained initially 130.2 mg/L Zn and 22.6 mg/L Ni. U.S. Environmental Protection Agency (US-EPA) landfilling limits for Zn and Ni are 4.3 mg/L and 11 mg/L, respectively. Setting times and unconfined compressive strength (UCS) values were measured and permeability of selected samples was determined. TCLP (Toxicity Characteristics Leaching Procedure) and SPLP (Synthetic Precipitation Leaching Procedure) were applied to determine the concentrations of Zn and Ni leached from the mortar samples and leachate pH values were measured. Use of the CKD as a cement substitute delayed setting times, decreased UCS and increased leached heavy metal concentrations. Leached Zn and Ni concentrations of the WPS stabilized with PC and CKD following SPLP were lower than the EPA landfilling limits. However, leached Zn concentrations following TCLP were not compatible with the EPA limit. Leached Ni concentrations remained lower than the EPA limit. It was concluded that relatively low levels of alkalies, CaO and SiO_(2) content of CKD negatively affected the setting, compressive strength and leaching characteristics.
机译:在本研究中,研究了使用波特兰水泥(PC)和水泥窑粉尘(CKD)的废磷酸盐污泥(WPS)的稳定和固化(S / S)。首先,只有PC用于稳定5、10和15%WPS。在稍后阶段,将10%和15%的CKD用作PC替代品以稳定15%WPS。 WPS最初包含130.2 mg / L Zn和22.6 mg / L Ni。美国环境保护局(US-EPA)的Zn和Ni填埋极限分别为4.3 mg / L和11 mg / L。测量凝固时间和无侧限抗压强度(UCS)值,并确定所选样品的渗透率。使用TCLP(毒性特征浸出程序)和SPLP(合成沉淀浸出程序)来确定从砂浆样品中浸出的Zn和Ni的浓度,并测量渗滤液的pH值。使用CKD作为水泥替代品会延迟凝固时间,降低UCS并增加浸出的重金属浓度。 SPLP后用PC和CKD稳定的WPS的浸出锌和镍浓度低于EPA填埋极限。但是,TCLP后浸出的锌浓度与EPA限值不兼容。浸出的镍浓度仍低于EPA限值。结论是,相对较低的碱度,CKD的CaO和SiO_(2)含量对凝结,抗压强度和浸出特性产生负面影响。

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