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Editorial · CASRAI · Sustainable research and laboratory operations

Scientists Find Two New Ways to Break Down PFAS ‘Forever Chemicals’ in Water

HZDR researchers in Dresden report two lab-scale methods — hydrodynamic cavitation and cold atmospheric plasma — that break down PFAS ‘forever chemicals’ by attacking the carbon-fluorine bond directly, rather than just filtering it out of water.

Published 7 Aug 2026· 5 minute read

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Two research teams working within the same German laboratory network say they have made real progress on one of water treatment’s hardest problems: breaking apart PFAS, the family of synthetic chemicals nicknamed ‘forever chemicals’ because they resist virtually every conventional method of destruction. Researchers at the Helmholtz-Zentrum Dresden-Rossendorf (HZDR), working with confirmatory analysis from the Helmholtz Centre for Environmental Research (UFZ), have published results on two distinct destruction methods — hydrodynamic cavitation and cold atmospheric plasma — that attack the carbon-fluorine bond directly rather than simply filtering PFAS out of water and moving the problem elsewhere.

Why PFAS are so hard to destroy

Per- and polyfluoroalkyl substances (PFAS) are a class of thousands of synthetic compounds used since the 1940s in non-stick coatings, firefighting foam, water-resistant textiles and countless industrial processes. What makes them useful — extraordinary chemical stability — is exactly what makes them an environmental problem. The carbon-fluorine bond is one of the strongest single bonds in organic chemistry, which is why PFAS do not break down through the hydrolysis, oxidation or biodegradation that eventually clears most organic pollutants from water and soil. Conventional treatment technologies, such as activated carbon or ion-exchange resins, capture PFAS rather than destroy them, which means the concentrated waste still has to be dealt with. HZDR’s Department of Water and Environmental Technologies, within the Institute of Fluid Dynamics, set out to test methods that break the bond itself.

Method one: hydrodynamic cavitation

The first method, led by postdoctoral researcher Dr. Ysabel Huaccallo-Aguilar, forces water through a narrow constriction at high velocity. The pressure drop causes tiny vapor bubbles to form and then collapse almost instantly. That collapse generates localized temperature spikes of several thousand degrees Celsius for a fraction of a second, together with highly reactive hydroxyl radicals. PFAS molecules, which tend to concentrate at the bubble surface, are exposed to both the heat spike and the radical attack that follows. In the reported results, the technique degraded roughly 37 percent of PFOS (perfluorooctanesulfonic acid, one of the most studied and most regulated PFAS compounds) under laboratory conditions, with the team targeting substantially higher degradation efficiency as the process is optimized.

Method two: cold atmospheric plasma with gas dispersion

The second method, developed under the department led by Dr. Sebastian Reinecke with environmental engineer Dr. Amit Kumar, generates plasma at the water’s surface under ambient conditions, without added catalysts or chemical reagents. Gas bubbles are dispersed through the water to carry PFAS molecules up to the surface, where the plasma field breaks them apart. According to the reported results, this method achieved near-complete degradation of the target PFAS and released roughly 35 percent of the compounds’ bound fluorine as free fluoride salts — a marker of true mineralization rather than partial breakdown into other fluorinated byproducts. It works faster than cavitation but is more energy-intensive, a trade-off the team is now working to characterize for larger-scale use.

Who did the work, and how it was funded

The research was carried out at HZDR’s Clean Water Technology Lab (CLEWATEC), a Helmholtz Innovation Lab, with additional collaborators including Anett Georgi, Markus Meier, Holger Kryk and Uwe Hampel, and confirmatory chemical analysis from the Helmholtz Centre for Environmental Research (UFZ). Funding came from the Helmholtz Association’s Impulse and Networking Fund, together with European Union co-financing and Saxon state budget funds approved by the Saxon Parliament, channeled through two named projects: HyKaPro SAB-EFRE (cavitation) and Plasma4PFAS SAB-EFRE (plasma). This is Helmholtz Association and EU/Saxon state-funded research based in Dresden, Germany — not, as some aggregator coverage of the story has implied, a US federal grant program.

The two methods are described in separate peer-reviewed papers: the cavitation results appear in Scientific Reports (2026), DOI 10.1038/s41598-026-57490-6, and the plasma results appear in Chemical Engineering Journal Advances (2026), DOI 10.1016/j.ceja.2026.101046. HZDR published its own account of the work on July 17, 2026, and the story was subsequently picked up by ScienceDaily and other science-news aggregators.

What this does and doesn’t mean yet

Both results are laboratory-scale, and both teams describe the work as a step toward, not a finished replacement for, PFAS remediation at treatment-plant scale. A 37 percent degradation rate for PFOS via cavitation is meaningful progress but well short of the complete destruction municipal or industrial operators would need; the plasma method’s near-complete degradation is more striking but comes with a higher energy cost that has not yet been resolved for continuous, large-volume operation. What both methods share is the more important point for the field: they destroy the PFAS molecule at its most stable bond, rather than concentrating it into a filter medium that then needs its own disposal pathway. That distinction is why environmental engineers researching PFAS remediation are watching destructive methods — including cavitation, plasma, supercritical water oxidation and electrochemical oxidation — as the technologies most likely to eventually complement, rather than just supplement, adsorption-based treatment.

Why it matters for research and water-quality regulation

PFAS contamination has become one of the most consequential environmental-compliance issues facing research institutions, municipal utilities and manufacturers alike, driving new drinking-water standards and effluent limits in jurisdictions across North America and Europe over the past several years. Destructive treatment technologies that are still emerging from Helmholtz-network labs like CLEWATEC will need to clear the same bar every environmental remediation technology does before adoption: independent replication, cost modeling at scale and a regulatory pathway for by-product handling. For now, the two HZDR results give the field two additional, mechanistically distinct destruction pathways to build on.

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