Recent concerns about exposure to non-polymer PFAS has led to concerns about exposure to other types of PFAS. For example, there have been recent efforts to evaluate the regulation of all types of PFAS [e.g., HR 535 PFAS Action Act of 2019 and a May 2020 REACH restriction proposal]. Additionally, citizen action groups have sought to bar the DoD from open burning of waste explosives containing PFAS. Research is required to address these concerns and determine the potential risk of emissions from polymeric PFAS thermal degradation products.
PFAS is used in a small percentage of energetics as binders and oxidizers, and in some military munitions for liners, o-rings, or other components. Although many of these components are routinely removed before thermal treatment, the types of PFAS that can be found in munitions can include fluoropolymers such as Teflon® (polytetrafluoroethylene or PTFE) Viton® (vinylidene fluoride and fluoropropylene copolymers), and Kel-F® chlorotrifluoroethylene/vinylidine). In most munitions, the mass of polymeric PFAS is small, less than 0.5 pound per munition item, which complicates the detection and quantification of fluorinated thermal degradation products.
Temperatures achieved during munitions use and thermal destruction depend on many factors including the characteristics of the munitions and their energetics (e.g., density, oxygen balance, etc.), level of confinement, and the method of treatment or expenditure. Temperatures and thermal residences time required for complete or partial combustion of PFAS may depend on the type of PFAS and other factors.
While munitions can contain small amounts of polymeric PFAS, the amount and identification of thermal decomposition products from these materials used in munitions are not known. Detection and identification of fluorinated products is an extremely complex subject as there are thousands of potential compounds and a very small percentage are currently targets for analysis.