Thermal reactivation, a well-established high temperature process, mineralises the PFAS molecules adsorbed on the activated carbon to remove these persistent contaminants from the water cycle. During this process, the spent activated carbon can be recovered and thus be reused. Spent carbons containing PFOS, PFOA, and other PFAS have been reactivated by Chemviron for over 15 years.
Chemviron processes the saturated carbon in dedicated thermal reactivation furnaces at high temperature to regain the activity levels of adsorption required for the application and to mineralise the adsorbed organic PFAS species. These thermal reactivation furnaces are specifically engineered units for the purpose, meeting the local environmental requirements.
However, there is a significant difference between the process of carbon reactivation and that of carbon regeneration as the terms are sometimes, used interchangeably.
Carbon reactivation is where spent carbon is reactivated in a multi-hearth furnace or rotary kiln by volatilising and destroying the adsorbed contaminants and restoring the activated carbon to a reusable quality. All spent activated carbons are subjected to quality control to establish the proper reactivation conditions for those types of used activated carbon.
The reactivation temperature and feed throughput requirements may vary depending upon the adsorbate loading characteristics of the spent carbon being processed. Industrial reactivation furnace temperatures are generally around 900-950°C, similar to incineration conditions but in a low oxygen environment.
The current operating procedure for carbon reactivation of PFAS loaded activated carbon is regularly reviewed and can be summarised as follows:
Our reactivation process differs greatly from a “regeneration” process. Carbon regeneration does not have the same temperature requirements as Chemviron’s reactivation process and may be performed with steam or hot nitrogen that rarely gets above 100°C. As a result, activated carbons that have gone through a regeneration process remain partially spent and contain some, and potentially all, of the original adsorbates.
There are a number of literature references and third-party data that support the destruction of PFAS at temperatures similar to our reactivation conditions. Here are some examples for reference:
Based on significant R&D work completed both internally, by third parties, and various literature references, Chemviron are confident that PFAS are desorbed and abated through Chemviron’s reactivation process.
If you have any questions or concerns, please do not hesitate to contact us.
i Watanabe, N., Takemine, S., Yamamoto, K., Haga, Y., Takata, M. Residual organic fluorinated compounds from thermal treatment of PFOA, PFHxA and PFOS adsorbed onto granular activated carbon (GAC). Journal of Material Cycles and Waste Management, 2016, 18:625–630.
ii Yamada, T., Taylor, P. H., Buck, R. C., Kaiser, M. A., Giraud, R. J. Thermal degradation of fluorotelomer treated articles and related materials. Chemosphere, 2005, 61(7), 974 – 984.
iii Lemieux, P. M., Strynar, M., Tabor, D. G., Wood, J., Cooke, M., Rayfield, B., Kariher, P. Emissions of fluorinated compounds from the combustion of carpeting. Proceedings of the 2007 International Conference on Incineration and Thermal Treatment Technologies, Phoenix, AZ.
iv Krusic, P. J., and Roe, D. C. Gas-phase NMR technique for studying the thermolysis of materials: Thermal decomposition of ammonium perfluorooctanoate. Analytical Chemistry, 2004, 76(13), 3800–3803.
v Krusic, P. J., Marchione, A., Roe, D. C. Gas-phase NMR studies of, the thermolysis of perfluorooctanoic acid. Journal of Fluorine Chemistry, 2005, 126(11-12), 1510–1516.
vi Office of Pollution Prevention & Toxics, Docket AR226-1366, ed. Laboratory-Scale Thermal Degradation of Perfluorooctanyl Sulfonate and Related Substances. Washington DC: US Environmental Protection Agency, 2003, 13.
vii Office of Pollution Prevention & Toxics, Docket AR226-1367, ed. Final Report: Laboratory-Scale Thermal Degradation of Perfluoro-Octanyl Sulfonate and Related Substances. Washington DC: US Environmental Protection Agency, 2003, 142.
viii Xiao, F., Sasi, P. C., Yao, B., Kubatova, A., Golovko, S. A., Golovko, M. Y., Soli, D. Thermal stability and decomposition of perfluoroalkyl substances on spent granular activated carbon. Environmental Science & Technology Letters, 2020, 7, 343-350.
ix Baghirzade B.S., Zhang y., Reuther J.F., Saleh N.B. Venkatesan A.K., Apul O. G. Thermal regeneration of spent granular activated carbon to break the forever PFAS Cycle. Environmental Science & Technology, 2021, 55, 9, 5608 – 5619.
The webinar covers: