Inorganic Chemicals Industry ›› 2024, Vol. 56 ›› Issue (11): 151-157.doi: 10.19964/j.issn.1006-4990.2024-0153

• Environment·Health·Safety • Previous Articles     Next Articles

Study on sulfate activation performance of electrolytic manganese residue in hydrated lime-slag system

NI Dong1(), TANG Liang2, HE Zhaoyi2, WANG Jian1, PEI Shanshan3, XIA Lei4   

  1. 1.Research Institute of Highway Science,Ministry of Transport,Key Laboratory of Highway Traffic Environmental Protection Technology,Ministry of Transpor,Beijing 100088,China
    2.School of Civil Engineering,Chongqing Jiaotong University,Chongqing 400074,China
    3.Xiongzhong Bilingual Primary School,Budapest 1158,China
    4.School of;materials science and engineering,Chang′an university,Xi′an 710064,China
  • Received:2024-03-17 Online:2024-11-10 Published:2024-11-27

Abstract:

Electrolytic manganese residue(EMR),as an industrial solid waste,contains a large amount of heavy metals,ammonia nitrogen,and sulfates,posing great harm to the environment and human health.To address this issue,this study utilized the sulfate rich nature of EMR as a sulfate activator to investigate the sulfate activation effect,hydration mechanism,microstructure,and pollutant solidification mechanism of EMR in the hydrated lime-slag system.The results from compressive strength,XRD,and SEM-EDS testing showed that EMR had a positive effect on the sulfate activation of the limestone-slag system,with the optimal ratio of 50% EMR,46% slag,and 4% quicklime.The compressive strengths at 3 d,7 d,and 28 d were 15.55,27.44 and 44.52 MPa,respectively,which were 1.65,1.80 and 1.97 times higher compared to the limestone-slag system without EMR at the corresponding ages.Under EMR activation,the hydration products of the hydrated lime-slag system were AFt(ettringite) and C-(A)-S-H (calcium silicate hydrate),interwoven to form a dense network structure.Whereas the main hydration products of the hydrated lime-slag system were C-(A)-S-H with larger pores in the transition interface zone.The released OH- and the formation of hydrated products including AFt,AFM and C-(A)-S-H and

in the EMR-hydrated lime-slag system facilitated ion exchange,adsorption,encapsulation,and precipitation of heavy metals and ammonia nitrogen in EMR,ultimately meeting the leaching toxicity requirements of GB 8978—1996 emission standards.

Key words: electrolytic manganese residue, industrial solid waste, sulfate, hydration mechanism, heavy metals

CLC Number: