Journal
JOURNAL OF HAZARDOUS MATERIALS
Volume 410, Issue -, Pages -Publisher
ELSEVIER
DOI: 10.1016/j.jhazmat.2020.124583
Keywords
Sorbent; Mercury; Biomass; Bromine; Hydrothermal; WEEE
Categories
Funding
- National Key R&D Program of China [2018YFC1900104]
- National Natural Science Foundation of China (NSFC) [51806078]
- Foundation of State Key Laboratory of Coal Combustion [FSKLCCB1904]
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This study demonstrates a cost-effective strategy for capturing elemental mercury using bamboo saw dust and bromine flame retardant sorbents, prepared by a novel hydrothermal-pyrolysis method. The optimal conditions of bamboo/BFR ratio, hydrothermal temperature, and pyrolysis temperature result in highly efficient removal of elemental mercury with a 99% removal efficiency. Additionally, the C-Br groups in the sorbents play a key role in oxidizing Hg0 into HgBr2.
This work showcases cost-effective elemental mercury capture strategy enabled by bamboo saw dust and bromine flame retardant (BFR) derived sorbent prepared by a novel hydrothermal-pyrolysis method. The hydrothermal treatment of bamboo and BFR blend was conducted in subcritical water resulting in a hydrothermal char. Subsequently, the hydrothermal char was pyrolyzed in nitrogen atmosphere leading to an improved pore architecture. The resulting biomaterials were proven highly effective for Hg removal. A thorough analysis of the physicochemical properties of the samples was conducted by means of BET, SEM, XRD, XPS and FT-IR. Key parameters such as bamboo/BFR ratio, hydrothermal temperatures and pyrolysis temperatures influence Hg0 removal capacity of our bio-sorbents. Overall, the optimal bamboo/BFR ratio, hydrothermal temperature and pyrolysis temperature are 2:1, 320 ?C and 800 ?C, respectively. Under these optimized conditions, a very promising elemental mercury removal efficiency of 99% is attained. The kinetics and mechanism of Hg0 removal are also proposed. The experimental data fit well with a pseudo-second-order model, indicating that Hg0 adsorption over sorbents was dominated by chemisorption. Our results indicate that the C?Br groups in sorbents provide active sites for oxidizing Hg0 into HgBr2.
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