Abstract

This study presents the implementation of a desulphurization process for lead recycling under different chemical and physical conditions using pyro-metallurgical processes. Desulphurization was done using a hydrometallurgical process using sodium carbonate as a desulphurization agent and different lead-bearing loads compositions. Waste characterization included: SO2 concentrations in the stack emissions, total lead content in the furnace ash, the total lead content in the slag, and the toxicity characteristic leaching procedure (TCLP). A significant reduction in SO2 emissions was achieved (~55% reduction) where mean SO2 concentrations changed from 2193 ± 135 ppm to 1006 ± 62 ppm after the implementation of the modified processes. The desulfurized lead paste (i.e. the metallic fraction lead of the battery) of the modified process exhibited an improvement in the concentration of the lead in the TCLP test, with an average value of 1.5 ppm which is below US EPA limit of 5 ppm. The traditional process TCLP mean value for the TCLP was 54.2 ppm. The total lead content in the bag house ashes shows not significant variations, when comparing the desulphurization (67.6% m/m) and non-desulphurization process (64.9% m/m). The total lead mean content in the slag was higher in the desulphurization process (2.49% m/m) than the traditional process (1.91% m/m). Overall, the implementation of a new desulphurization method would potentially increase the operation costs in 10.3%. At the light of these results, a combination of hydrometallurgical and pyro-metallurgical processes in the recycling of lead-acid batteries can be used to reduce the environmental impact of these industries but would increase the operational costs of small lead recyclers.

Highlights

  • Lead-acid batteries belong to a group of commercial products that can become a potential hazardous waste after their use

  • According to Costa Rica’s environmental regulations, the SO2 concentration in the stack emissions from furnace charge composition [7.4]-[7.4]-[5.3] and [8]-[8]-[5] are according to the permissible limits; in the second and third furnace charge composition using the non-desulfurized lead paste the values are close to the limit (2500 mg/Nm3)

  • Desulfurized lead paste non-desulfurized paste lead content was very high compared with the United States Environmental Protection Agency (US-EPA) limit (5 ppm) showing a mean of 54.2 ppm

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Summary

Introduction

Lead-acid batteries belong to a group of commercial products that can become a potential hazardous waste after their use. Lead recovery from lead-acid batteries is the type of business that combines environmental protection and economic profits. The largest component of the lead-acid battery is the so-called metallic fraction lead or lead paste (60% - 75%) that is obtained during the processing of battery scrap. The other components are comprised of electrolytes and various types of plastics. Lead paste is primarily a mixture of PbSO4, PbO2, Pb2O, Pb2O3 and metallic lead. PbSO4 is the main lead carrier in the battery paste (40%). It is formed during the battery operation as a result of the reaction of metallic Pb and PbO2 with the electrolyte (i.e. aqueous solution of sulphuric acid IV) [1] [2] [3]

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