Fixed-bed columns
Adsorbent regenerationOn-line treatment process a b s t r a c t Remediation of metallurgical industry wastewater has presented a great environmental challenge for decades. In this study, a complete remediation technology was proposed for simultaneous As(III) and Cd adsorptive removal, adsorbent regeneration, and recovery of As and Cd. Using three granular TiO 2 columns in series, As(III) and Cd in the raw water at 2590 ± 295 and 12 ± 2 mg/L, respectively, could be reduced to 0.16 ± 0.11 and 0.0133 ± 0.0134 mg/L, well below the wastewater discharge limit. Spent TiO 2 media could be regenerated using H 2 SO 4 and NaOH, and the regenerated adsorbent could be re-used for at least 10 treatment cycles and 770 bed volumes with no decrease in its adsorption capacity.Remediation of 1 L wastewater generated 0.89e1.5 g solid residue which could be used as an intermediate for the As and Cd chemical refinement. The waste solution can be further treated after mixing with raw water to adjust the raw pH from 1.4 to 7. This adsorption, regeneration, and reuse process provides an innovative technology for metallurgical industry wastewater remediation that is promising for practical application.© 2014 Elsevier Ltd. All rights reserved.
IntroductionMining and smelting are major industrial processes that are associated with multiple toxic metal contaminants (Bian et al., 2012). In these industrial wastewaters, coexistence of As(III) and Cd is a great public concern because of their carcinogenicity (Barrett, 2012;Lubin et al., 2008). Thus, developing effective and robust wastewater treatment technology for simultaneous As(III) and Cd removal has motivated extensive research (Allende et al., 2012;Deschamps et al., 2005;Dey et al., 2009;Jiang et al., 2014;Johnson and Hallberg, 2005). Many efforts have been made to solve this problem over past decades, with the result that neutralization-precipitation has been adopted as a commonly used method for removal of heavy metals, including As(III) and Cd, from mining and smelting wastewaters (Dong et al., 2011;McDonald et al., 2006;Wang et al., 2003). For example, an approach using iron precipitation and high density sludge (HDS) recycling has become a benchmark procedure in acid mine drainage treatment (Dey et al., 2009). This HDS process requires increasing the pH with hydrated lime and subsequently adding iron salts to form precipitates with As. However, HDS generates large volumes of sludge with low chemical stability (Dey et al., 2009;McDonald et al., 2006), which may release As under the attack of carbon dioxide (Nishimura and Robins, 1998;Pantuzzo and Ciminelli, 2010 Available online at www.sciencedirect.com ScienceDirect journal homepage: ww w.else vier.com/locate /wa tres w a t e r r e s e a r c h 6 8 ( 2 0 1 5 ) 5 7 2 e5 7 9http://dx