4.7 Article

Study on the elemental mercury removal performance of co-pyrolyzed Cl-loading activated carbon and the formation mechanism of C-Cl functional groups

Journal

FUEL
Volume 322, Issue -, Pages -

Publisher

ELSEVIER SCI LTD
DOI: 10.1016/j.fuel.2022.124229

Keywords

Mercury; Activated carbon; C-Cl functional groups; Polyvinyl chloride; Co-pyrolysis

Funding

  1. National Natural Science Foundation of China [52076093]
  2. Key Research and Development Program of Hubei Province [2020BAB074]
  3. Science, Technology and Innovation Commission of Shenzhen Municipality [JCYJ20190809095003718]
  4. Postdoctoral Creative Research Funding of Hubei Province

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Co-pyrolysis of coconut shell activated carbon (AC) and polyvinyl chloride (PVC) was used to prepare a chloride-loading adsorbent with high mercury removal efficiency. The formation mechanism of C-Cl functional groups during the co-pyrolysis process was investigated, and two paths were identified. The first path involved the reformation of organic chlorine in PVC at low temperature, while the second path involved the combination of gaseous HCl with newly exposed carbon atom sites at high temperature. The study also revealed the promoting and inhibiting effects of NO, O2, and SO2 on the mercury removal ability of the chloride-loading adsorbent.
Co-pyrolysis is a convenient method to load chloride on an adsorbent to improve its mercury removal ability. However, as a main reactive species, the formation mechanism of C-Cl functional groups remained unclear. In this study, the coconut shell activated carbon (AC) was co-pyrolyzed with polyvinyl chloride (PVC) to prepare a Cl-loading activated carbon, and it presented the best mercury removal efficiency (greater than 85%) at 140 degrees C. NO, O-2 and HCl promoted the mercury removal ability of Cl-loading activated carbon, while SO2 inhibited. By comparing the performance of Cl-loading adsorbents using different Cl sources and supporters, we found that there were two formation paths for C-Cl functional groups. The first path was that some organic chlorine in PVC was reformed at low temperature (similar to 300 degrees C), and adhered to the surface of the adsorbent in the form of C-Cl functional groups. As the co-pyrolysis temperature increased, unstable C-Cl functional groups were decomposed and the mercury removal ability became weak. The second path was that the Cl first released out from PVC as gaseous HCl, and then combined with newly exposed carbon atom sites, which were generated owing to the devolatilization process of AC at high temperature (similar to 800 degrees C), to form C-Cl functional groups for mercury removal.

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