A limestone-based lead plaster pre-desulfurization method
A pre-desulfurization and limestone technology, applied in calcium/strontium/barium sulfate, recycling technology, recycling by waste collectors, etc., can solve the problem of high cost of lead plaster pre-desulfurization process, few applications, and recycling of sodium sulfate products Problems such as low price, to achieve the effect of good application prospect and good economic value
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Embodiment 1
[0025] Waste lead-acid batteries are crushed and screened to obtain lead paste, and water is added to make a lead paste slurry with a mass percentage of 40%, which is pumped into a desulfurization mixing tank, and then NaHCO is added 3 As a desulfurizer (according to NaHCO 3 with PbSO 4 The molar ratio is 2.1:1 to add), the reaction temperature is controlled by steam heating to 50°C, and the desulfurization reaction is carried out. The gas generated by the desulfurization reaction is extracted and passed into the limestone slurry storage tank. After the desulfurization reaction for 60 minutes, the lead paste slurry is filtered, and the filtrate is mixed with the supernatant in the limestone slurry; the filter residue is sent to the melting furnace, and the gas generated in the melting furnace is continuously passed into the limestone slurry storage tank. After desulfurization, the sulfur content of the lead paste is 0.42%.
Embodiment 2
[0027] Waste lead-acid batteries are crushed and screened to obtain lead paste, and water is added to make a lead paste slurry with a mass percentage of 40%, which is pumped into a desulfurization mixing tank, and then NaHCO is added 3 As a desulfurizer (according to NaHCO 3 with PbSO 4 The molar ratio is 2.1:1 to add), the reaction temperature is controlled by steam heating to 60°C, and the desulfurization reaction is carried out. The gas generated by the desulfurization reaction is extracted and passed into the limestone slurry storage tank. After the desulfurization reaction for 60 minutes, the lead paste slurry is filtered, and the filtrate is mixed with the supernatant in the limestone slurry; the filter residue is sent to the melting furnace, and the gas generated in the melting furnace is continuously passed into the limestone slurry storage tank. After desulfurization, the sulfur content of the lead paste is 0.38%.
Embodiment 3
[0029] Waste lead-acid batteries are crushed and screened to obtain lead paste, and water is added to make a lead paste slurry with a mass percentage of 70%, which is pumped into a desulfurization mixing tank, and then NaHCO is added 3 As a desulfurizer (according to NaHCO 3 with PbSO 4 The molar ratio is 2.05:1 to add), the reaction temperature is controlled by steam heating to 50°C, and the desulfurization reaction is carried out. The gas generated by the desulfurization reaction is extracted and passed into the limestone slurry storage tank. After the desulfurization reaction for 60 minutes, the lead paste slurry is filtered, and the filtrate is mixed with the supernatant in the limestone slurry; the filter residue is sent to the melting furnace, and the gas generated in the melting furnace is continuously passed into the limestone slurry storage tank. After desulfurization, the sulfur content of the lead paste is 0.35%.
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