Effect of using portland cement and tras soil to stabilize and solidify mercury-contaminated tailings in small-scale gold mining

• Published in: IOP conference series. Earth and environmental science 2021-10, Vol.871 (1), p.12026
• Main Authors: Rachman, R M, Ngii, E, Sriyani, R
• Format: Article
• Language: English
• Subjects: Binding; Cement; Composition; Compressive strength; Environmental impact; Gold; Gold mines & mining; Government regulations; Mercury; Mine tailings; Pollution control; Portland cement; Portland cements; Quality standards; Sediment pollution; Soil compression tests; Soil contamination; Soil management; Soil pollution; Soil stabilization; Soils; Solidification; Tailings
• ISSN: 1755-1307; 1755-1315
• DOI: 10.1088/1755-1315/871/1/012026

Small scale gold mining in Kulon progo district using mercury for binding gold. The total concentration of mercury in tailings has 383.21 mg/kg. Stabilization/solidification is one of the remediation technologies to reduce waste pollution. This research aims to know the optimum composition in the S/S process. The first stage uses a composition between Portland cement: tras soil. the ratio are 100: 0, 90:10, 80:20, 70:30, 60:40, 50:50, 40:60., 30:70, 20:80, and 10:90. In the second stage, the tailings sample is added to the optimum from the first stage, with the composition of the binder: tailings. the ratio are 50:50, 40:60, 30:70, 20:80, and 10:90. The TCLP is applied according to the US EPA 1311 method. The first test results in the optimum composition of Portland cement: tras soil (10:90), the compressive strength test value of 96 kg/cm2. The compressive test result met the quality standards of The Head of Environmental Impact Control Agency (BAPEDAL) Decree KEP-03/BAPEDAL/09/1995 for the management of contaminated soil at 1 kg/cm2. The second test of binding: tailings (50:50) was 39.2 kg/cm2 with no detectable mercury concentration. TCLP test results meet the S/S product quality based on Government Regulation 101 of 2014 of 0.05 mg/L.