Arsenic removal from high-arsenic dust by NaOH-Na 2 S alkaline leaching

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25 3 2015 3 Volume 25 Number 3 The Chinese Journal of Nonferrous Metals March 2015 1004-0609(2015)-03-0806-09 ( 410083) 0.5 0.2 5:1 90 2.0 h 400 r/min 89.64% 10.11% 1.16% 0.89% TF09 A Arsenic removal from high-arsenic dust by NaOH-Na 2 S alkaline leaching YI Yu, SHI Jing, TIAN Qing-hua, GUO Xue-yi (School of Metallurgy and Environment, Central South University, Changsha 410083, China) Abstract: The high-arsenic dust is produced from the jamesonite in pyrometallurgical process, and contains large amount of valuable metals, such as lead, antimony and indium. Because of the complex composition and high content of arsenic in high-arsenic dust, the current main processing is stockpiling. Arsenic was leached from high-arsenic dust by sodium hydroxide and sodium sulfide mixed solution. The optimum conditions were determined as follows: alkali material ratio 0.5, ratio of sodium sulfide to high-arsenic dust 0.2, leaching temperature 90, leaching time 2 h, liquid-to-solid ratio 5 and stirring speed 400r/min. Under these conditions, the leaching efficiencies of arsenic, antimony and lead are 89.64%, 10.11% and 1.16%, respectively, and the content of arsenic in leaching residue is 0.89%. The leaching residue can be returned to lead smelter for recycling lead and antimony. The leaching solution was treated by hydrogen peroxide oxidation and cooled to recover sodium arsenate. The filtrate was recycled with additional sodium hydroxide and sodium sulfide to alkaline leaching step. NaOH-Na 2 S alkaline leaching process provides a simple and highly effective way for the removal of arsenic from high-arsenic dust. Key words: high arsenic dust; alkaline leaching; arsenic removal; wet metallurgy ( ) [1 2] ( 12300001-2) 2014-05-28 2014-12-29 0731-88877863 E-mail: xyguo@csu.edu.cn

25 3 807 [3] [4] [5] [6 7] [8] [9] [10] [11] [12] [13] [14] [15] [16] [17] / / 1 1.1 105 24 h 0.6 mm XRD 1 1 1 1% 1 4 PbS Pb 5 (AsO 4 ) 3 OH Sb 2 O 3 Pb 5 O 8 1 Table 1 Chemical composition of high arsenic dust (mass fraction, %) As Sb Pb Sn Zn Cu 6.86 9.55 49.13 2.8 2.4 1.1 Fe S Na Ca In 1.8 5.5 0.24 0.29 0.26 1 XRD Fig. 1 XRD pattern of high arsenic dust [18] EDTA 2 2

808 2015 3 2 Table 2 Chemical phase analysis of arsenic in high arsenic dust (mass fraction, %) 2 Oxide phase Zn 3 (AsO 4 ) 2 Pb 3 (AsO 4 ) 2 Sulfide phase Others 26.75 3.34 59.34 8.20 2.37 1.2, Pb 5 (AsO 4 ) 3 OH+5Na 2 S=5PbS+3Na 3 AsO 4 +NaOH (1) As 2 O 3 +2NaOH=2NaAsO 2 +H 2 O (2) As 2 O 5 +6NaOH=2Na 3 AsO 4 +3H 2 O (3) Pb 5 O 8 +8Na 2 S+8H 2 O=5PbS+16NaOH+3S (4) Δ fg Θ m ΔrG Θ m (1)~(4) ΔrG Θ m 333.99 46.3 282.3 769.08 kj/mol Θ Δ rgm( T) = RTln p (1)~(4) K Θ K Θ 3.51 10 58 1.31 10 8 1.04 10 54 6.38 10 134 Δ p rg Θ m K Θ (1)~(4) p 2 Fig. 2 Process chart for alkaline leaching of high arsenic dust AFS 2202E WFX 130B 2 2.1 60 g 10 g 80 2 h 5:1 400 r/min 3 1.3 500 ml 3 Fig. 3 Effect of alkali material ratio on leaching efficiency

25 3 809 3 0.6 46.21% 89.26% 1.0 76.62% 2.99% 0.02% 20.49% 6.52% 88.67% 77% 82.17% 0.6 1.0 [19 20] As 2 O 5 NaOH NaOH 0.6 NaOH As( ) As( ) 0.5 4 14 g 76.48% 92.61% 14 g 14 g 5.95% 0.02% 10 g 6.63% 24.01% 14 g 2.3 60 g 0.5 14 g 5:1 2 h 400 r/min 5 2.2 60 g 0.5 80 2 h 5:1 400 r/min 4 5 Fig. 5 Effect of temperature on leaching efficiency 4 Fig. 4 Effect of Na 2 S addition on leaching efficiency 5 90 58.48% 92.11% [20]

810 2015 3 90 XRD 60 8% 60 90 8.08% 12.26% 90 2 h 16.17% 2.5 60 g 0.5 14 g 2.0 h 90 90 400 r/min 3% 7 0.09% 90 2.4 60 g 0.5 14 g 5:1 90 400 r/min 6 7 Fig. 7 Effect of liquid-to-solid ratio on leaching efficiency 6 Fig. 6 Effect of time on leaching efficiency 6 2 h 74.61% 92.88% 2 h 2 h 1.56% 0.22% 2 h 0.01% 1 h 16.45% 15% 7 5.0 85.43% 91.25% 5.0 4.0 18.24% 11.62% 4.0 7.0 (1.23%) As( ) S 2 Pb 2+

25 3 811 5.0 2.6 60 g 0.5 14 g 5:1 90 2.0 h 8 8 350 r/min 91.74% 93.22% 350 r/min 93% 18.56% 12.52% 400 r/min 2.7 0.5 0.2 5:1 90 2.0 h 400 r/min 3 3 4 XRD 9 3 4 3 Table 3 Experiment results of optimal experiment Experiment No. Volume of leaching solution/ml Concentration in leaching solution/(g L 1 ) Sb Pb Sn Zn Cu Fe 8 Fig. 8 Effect of stirring speed on leaching efficiency 89.64% 0.89% 1.83 1.08 1.39 1.69 0.002 0.005 g/l 10.11% 1.16% 26.18% 35.82% 0.11% 0.14% 9 3 PbS Sb 2 O 3 NaSb(OH) 6 XRD XRD Pb 5 (AsO 4 ) 3 OH Pb 5 O 8 4 Mass of leaching residue/g Mass fraction of As in leaching residue/% 1 330 1.827 1.136 1.313 1.575 0.002 0.005 47.45 0.924 2 305 1.846 1.122 1.452 1.675 0.003 0.005 48.59 0.891 3 315 1.816 0.976 1.407 1.641 0.002 0.004 48.18 0.847 4 Table 4 Leaching efficiencies of elements based on composition of leaching liquor Experiment No. Leaching efficiency/% As Sb Pb Sn Zn Cu Fe 1 89.35 10.52 1.27 25.79 36.09 0.1 0.15 2 89.48 9.83 1.16 26.36 35.48 0.14 0.14 3 90.08 9.98 1.04 26.38 35.90 0.1 0.12 Average 89.64 10.11 1.16 26.18 35.82 0.11 0.14 Leaching efficiency of As is based on composition of leaching residue.

812 9 XRD Fig. 9 XRD pattern of alkali leaching residue 2015 3 3 ml 20 min 2 h 40 XRD 5 10 3, 6 5 Table 5 Compositions of white crystalline (mass fraction, %) As Sb Sn Pb Zn 17.8 2.27 0.14 0.027 0.0085 NaSb(OH) 6 Sb 2 O 3 90% 90% 99% 74% 64% PbS 2.8 80 g/l As( ) As( ) As( ) 60 g 10 XRD Fig. 10 XRD pattern of white crystalline 5 10 Na 3 AsO 4 10H 2 O 17.8% Na 3 AsO 4 10H 2 O (19.31%) 6 3 90% 6 Table 6 Experiment results of circulation leaching of high-arsenic dust Experiment No. Volume of leaching solution/ml Leach solution/(g L 1 ) Mass of Mass fraction of Leaching Crystallizing rate/% leaching As in leaching rate of As Sb Sn Pb Zn residue/g residue/% As 1) /% As 2) Sb 2) 1 330 10.98 1.803 1.395 0.909 1.506 47.12 0.748 91.44 88.99 98.36 2 320 12.69 1.758 2.242 0.952 2.531 51.13 0.793 90.15 88.86 96.95 3 305 12.64 1.894 2.735 0.966 3.252 53.75 0.781 89.80 91.35 96.57 4 310 12.81 1.841 3.259 0.962 3.761 51.59 0.813 89.81 90.15 96.76 1) Based on residue; 2) Based on liquor.

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