PFAS

Related Applications

This application claims the priority benefit of U.S. Provisional Patent Application Ser. No. 63/327,788 filed 5 April 2023.

Introduction

Per- and polyfluoroalkyl substances (PFAS), including perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA), and hundreds of other similar compounds, have been widely used in the United States in a multitude of applications. There are significant concerns associated with these compounds due to widespread contamination coupled with uncertainties about risks to human health and the environment. PFAS are molecules having chains of carbon atoms surrounded by fluorine atoms. The C-F bond is very stable enabling the compounds to persist in the natural environment. Some PFAS include hydrogen, oxygen, sulfur, phosphorus, and/or nitrogen atoms. One example is PFOS:

Although some PFAS compounds with known human health risks have been voluntarily phased out (PFOA and PFOS), legacy contamination remains. Replacement PFAS compounds have been introduced with limited understanding of their health risks. Currently, only PFOA and PFOS are addressed in Lifetime Health Advisories at the Federal level, with no established maximum contaminant level (MCL) to regulate the acceptable level of these and other PFAS compounds in drinking water. PFAS contamination in drinking water sources in 1,582 locations in 49 states as of May 2020. Currently used techniques for treating PFAS-contaminated water are expensive, and management of spent media is costly and may result in long-term liability.

SCWO of organic compounds has long been known and is described in numerous papers and patents. For example, Welch et al. in US Patent No. 4,861,497 described the use of a liquid phase oxidant such as hydrogen peroxide or ozone in supercritical water for the destruction of organic compounds; testing with destruction of propylene glycol at 750 to 860 °F at 5000 psia (pounds per square inch atmospheric) resulted in about 98% destruction. Swallow et al. in US Patent No. 5,232,604 described SCWO of organic compounds with an oxidant such as hydrogen peroxide and a reaction rate enhancer such as nitric oxide; in one example, sodium hydroxide and sodium nitrate were used to neutralize hydrochloric acid formed in the oxidation of methylene chloride. Aquarden Technologies in US Published Patent Application No.

2019/0185361 notes that in the SCWO process precipitation occurs in a zone where the fluid goes from sub-critical to super-critical and designed a reactor with a residue outlet connection near this zone. Miller et al. in “Supercritical water oxidation of a model fecal sludge with the use of a co-fuel” Chemosphere 141 (2015) 189-196 reported on the SCWO reaction of a feces simulant in the presence of 48% excess oxygen. The use of auxiliary fuels can be used to generate hydrothermal flames in SCWO reactors that are characterized by high temperatures, typically above 1000 °C. See “Supercritical Water Oxidation,” in Advanced Oxidation Processes for Wastewater Treatment,” (2018), 333-353.

Despite extensive prior efforts to develop systems for destroying PFAS, there remains a need for efficient systems for treating PFAS compositions and the complete destruction of PFAS.

Summary of the Invention

We have discovered that, during treatment of PFAS containing influent in a super critical water oxidation system, lean oxygen conditions can occur leading to the evolution of surplus nascent hydrogen. This nascent hydrogen leads to failures in the process piping due to embrittlement of the base material. By ensuring an ample supply of oxygen and mixing in the influent stream, the surplus nascent hydrogen can be eliminated through reactions to produce water or diatomic hydrogen.

The invention provides a method of destroying PFAS under SCWO conditions, comprising: providing an initial aqueous solution comprising water and PFAS; passing the initial aqueous solution comprising water and PFAS and an oxidant into a reaction vessel; wherein the reaction vessel comprises metal walls; wherein the PFAS is an oxidizable species and the aqueous solution may, optionally, comprise other species that oxidize by contact with the oxidant under supercritical conditions and, wherein the sum of these species constitute a combined oxidizable species; controlling conditions within the reaction vessel such that the aqueous solution is in a supercritical state and that the amount of oxidant is at least 5% greater (or at least 10%, or at least 20%, or at least 30%, or at least 50%, or at least 90% greater or 5 to 200% greater) than that needed to oxidize all of the combined oxidizable species; producing, via exposure to the supercritical conditions, a clean hot water solution having a concentration of PFAS that is at least 90 mass% (or at least 95%, or at least 99%, or at least 99.9 mass%) less than the aqueous solution; and, optionally, transferring heat from the clean hot water solution to the aqueous solution in a heat exchanger in a preheating step.

Preferably, the method of destroying PFAS is a continuous method and the aqueous solution is passed in a stream through the reaction vessel. In the case of a continuous process, the method preferably maintains at least 5% oxidant surplus for at least 95% of a complete run (passage of the aqueous solution through the reaction vessel) and the complete length of the reaction vessel that is exposed to supercritical aqueous solution. Preferably, relative to a method having identical conditions but having 95% or less of the amount of oxidant needed to oxidize all of the combined oxidizable species; the method shows a reduction in hydrogen embrittlement of at least 10%, or at least 20%, or at least 50%. The extent of hydrogen embrittlement can be measured according to the methods as shown in the examples by calculating the ratio of relative surface areas of transgranular fracture mode compared to other fracture modes such as intergranular and ductile modes. This measurement is useful as for postmortem analysis but not as preventative method.

The method may further comprise one or any combination of the following features: wherein the reaction vessel comprises an inlet and an outlet and wherein the oxidant is added to the aqueous solution prior to the solution passing through the inlet; wherein the internal walls of the reaction vessel are cylindrical; wherein the supercritical aqueous solution directly contacts the metallic walls of the reaction vessel; wherein the metallic walls of the reaction vessel comprise a coating that is permeable to hydrogen; wherein the oxidant is 02; wherein the oxidant comprises hydrogen peroxide.

Reactor vessel materials are typically comprised of, but not limited to, nickel-based alloys such as UNS N06625 (Inconel 625) or UNS N10276 (Hastelloy C276). Nickel-based alloys may have, for example, 50 to 80 wt% of Ni, Fe and/or Co (preferably Ni), 3-20wt% Cr, 6wt% or less of Al, 5 wt% or less of Ti, 5wt% or less of Nb, up to 10 wt% of Re, W, Ta, Hf, and/or Mo; and trace amounts of C, B, and/or Zr (less than 0.2wt%). Generally, the present invention is applicable to SCWO in any material that can be weakened by hydrogen embrittlement.

Various aspects of the invention are described using the term “comprising;” however, in narrower embodiments, the invention may alternatively be described using the terms “consisting essentially of’ or, more narrowly, “consisting of.”

Brief Description of the Drawings

Fig. l is a schematic illustration of a water pretreatment system for treating PFAS-contaminated water prior to passage through a SCWO reactor.

Fig. 2 illustrates a salt separator with inlet and outlet pipes connected to a collector tube. Figs. 3-6 show photographs of fractures on the SCWO reactor showing evidence of hydrogen embrittlement.

Detailed Description of the Invention

According to the present invention, PFAS-contaminated water has the conventional meaning. Since the inventive methods are capable of reducing the concentration of PF AS to less than 5 ppt, the method can be applied to solutions containing greater than 5 ppt, more typically, at least 1 ppm. The source of the PFAS-contaminated water can be from soil or surface or underground water in areas subjected to PFAS contamination. These areas can be industrial areas such as the electronics industry (e.g., wire/cable coatings and semi-conductor board fabrication), leachates from waste facilities, and especially where water-proofing or non-stick coatings have been applied. Another common source of PFAS-contaminated water is in areas around airfields or firefighting training areas that have been exposed to AFFF (aqueous film forming foam). Another source can be storage vessels, typically these sources are accumulated for future destruction or disposal. Typically, there will be non-fluorinated organic compounds present in PFAS-contaminated water and, especially in AFFF residue, there can be chlorinated or brominated compounds.

Initially, water or soil samples may be treated to concentrate PFAS in a substantially reduced volume. In some instances, the PF AS-containing media has been stored in a concentrated form and does not require additional treatment to concentrate it. The concentrated PFAS mixtures can be put in containers and shipped to a centralized site for PFAS destruction. Alternatively, in some preferred embodiments, the concentrated PFAS mixtures are treated on- site where they originate. The concentrated PFAS solution is destroyed by Supercritical Water Oxidation (SCWO), which we have found can rapidly result in over 100,000 times reduction in PFAS concentration, for example, a reduction in PFOA from 1700 parts per million (ppm) to 5 parts per trillion (ppt) by weight or less. To enable efficient destruction with little or no external heat supply during steady state operation, fuels may be added (or, in some occurrences, PFAS may be present with sufficient organic materials that serve as the fuel) to supply some or all of the heat needed to power the oxidation. The resulting effluent can then be confirmed to contain little or no PFAS, typically 5 ppt or less, and then be released back into the environment as safe, clean water.

The invention provides an energy efficient method of destroying PFAS that is optionally characterized by the steps of reverse osmosis and salt separation followed by oxidation in a SCWO reactor; and optionally characterizable wherein the aqueous solution comprising water and PFAS has a first volume; wherein 10% or less (or 5% or less, or 1% or less, or 0.1% or less) of the first volume is subjected to supercritical conditions; and wherein, in said method, at least 95% (or at least 98% or at least 99%) of the PFAS in the first volume is destroyed in supercritical conditions.

In another aspect, the invention comprises a system for destroying PFAS, comprising: a reverse osmosis system; a conduit from the reverse osmosis system to a salt separator; and a conduit from the salt separator to a supercritical reactor.

The system can be further characterized by one or any combination of the following characteristics: wherein the collector vessel comprises a supercritical fluid; wherein the first tube projects at least 5 cm into the collector vessel and the second tube does not project into the interior of the collector tube; further comprising a first heat exchanger disposed in the conduit between the reverse osmosis system and the salt separator; wherein, during operation, the first heat exchanger exchanges heat between a subcritical PFAS-containing aqueous stream and a return stream of PFAS-free water from the supercritical reactor; wherein the first tube projects at least 5 cm further into the collector vessel than the second tube; wherein the heat exchanger is a tube-in-tube heat exchanger; wherein the salt separator comprises a plurality of collector vessels each collector vessel comprising a set of an inlet tube and an outlet tube; wherein each set is at a higher temperature that the previous set in the direction of flow. Any of the inventive aspects may be further defined by one or any combination of the following: wherein the method is carried out in a mobile trailer; the PFAS-containing aqueous mixture comprises at least 100 ppm PFAS and the method decreases the PFAS concentration by at least 10 ⁶ or 10 ⁷ or 10 ^s ; wherein the PFAS is reacted with oxidant in an oxidation reactor and after leaving the reactor the effluent is treated with a solution comprising NaOH, LiOH, or KOH to produce a neutralized solution that can be discharged or recycled to neutralize additional effluent; wherein the neutralized effluent is at least partially evaporated into the air; wherein by taking a PFAS-concentration wherein the PFAS-containing aqueous mixture comprises at least 100 ppm PFAS by weight (in some embodiments at least 500 ppm or at least 1000 ppm PFAS) that the method converts to an effluent comprising 1 ppm or less, or 0.1 ppm or less, or 0.01 ppm or less, or 1.0 ppb or less, or 0.1 ppb or less, or 0.01 ppb or less PFAS; in some embodiments in the range of 1 ppm to 5 ppt (part per trillion) PFAS or less; wherein the PFAS-containing solution is mixed with a solution comprising 30 to 50 wt% H2O2 at a weight ratio of preferably 30: 1 to 70: 1 wt% ratio PFAS solutiomFFCb: wherein the PFAS-containing solution is passed through a SCWO reactor with a residence time of 20 sec or less, preferably 10 sec, or 5 sec or less, or 0.5 to 5 seconds; wherein the PFAS-containing solution is added at a rate controlled between 50 and 150 mL/min (at STP); wherein no external heating is required after start-up; wherein the PFAS-containing aqueous mixture comprises at least 100 ppm PFOA and the method decreases the PFOA concentration by at least 10 ⁶ or 10 ⁷ or 10 ⁸ , and in some embodiments up to about 10 ⁹ ; wherein the method is conducted in a mobile trailer; wherein the method is conducted in a mobile trailer at a PFAS -contaminated site.

Any of the inventive methods may be further defined by, in the overall process, or the SCWO portion of the process, can be characterized by converting a PFAS-concentration of at least 100 ppb PFAS by weight (in some embodiments at least 500 ppb or at least 1000 ppb PFAS) to 1 ppb or less, or 0.1 ppb or less, or 0.01 ppm or less or 7 ppt or less. Alternatively, by converting a PFOA-concentration of at least 100 ppb PFOA by weight (in some embodiments at least 500 ppb or at least 1000 ppb PFOA) to 1 ppb or less, or 0.1 ppb or less, or 0.01 ppb or less, or 5.0 ppt or less PFOA; in some embodiments in the range of 1 ppm to 5 ppt (part per trillion) PFOA. Alternatively, by converting a PFOS-concentration of at least 100 ppb PFOS by weight (in some embodiments at least 500 ppb or at least 1000 ppb PFOS) to 1 ppb or less, or 0.1 ppb or less, or 0.01 ppb or less, or 5.0 ppt or less PFOS; in some embodiments in the range of 1 ppm to 5 ppt (part per trillion) PFOS The process can also be characterized by the same levels of destruction beginning with a PFAS concentration of 1 ppm or more. In some embodiments, PF AS-contaminated water comprising at least 1000 ppt of at least one (or at least 3 or at least 4 or at least 5 or at least 6) compound selected from the group consisting of PFHxA (perfluorohexanoic acid), PFHpA (perfluoroheptanoic acid), PFOA, PFBS (perfluorobutane sulfonate), PFHxS (perfluorohexane sulfonate), PFHpS (perfluoroheptane sulfonate), and PFOS and combinations thereof, treated by the process is (are) reduced by at least 2 (or at least 3 or at least 4 or at least 5) orders of magnitude. In some embodiments, PFAS-contaminated water comprising at least 100 ppt of at least one (or at least 3 or at least 4 or at least 5 or at least 6) compound selected from the group consisting of PFBA (perfluorobutanoic acid), PFPeA (perfluoropentanoic acid), PFHxA, PFHpA, PFOA, 6:2 FTS (6:2 fluorotelomer sulfonate), and 8:2 FTS (8:2 fluorotelomer sulfonate) and combinations thereof, treated by the process is (are) reduced by at least 2 (or at least 3 or at least 4 or at least 5) orders of magnitude and/or reduced to 5 ppt (or 1 ppt) or less.

The invention also includes apparatus for destroying PFAS comprising a SCWO reactor and any of the components described herein. The invention also includes a system for destroying PFAS comprising a SCWO reactor comprising a PF AS-containing aqueous mixture. The system may comprise any of the conditions and/or fluids described herein.

Leaving the SCWO reactor, the resulting clean water (non-briny) fraction can optionally be passed through adsorbent media such as activated carbon or ion exchange resin and returned to the environment. As with any of the aspects described herein, this pretreatment method may be used by itself or in combination with any of the other aspects or other techniques described herein.

Pretreatment

Debris and other solids can be removed from the PFAS-contaminated water prior destruction of the PFAS. Typically, this can be accomplished by one or a plurality of fdtration steps. In some embodiments, a plurality of filtration steps can be conducted in which increasingly smaller particles are removed. The filters can be valved so that only one or a series of filters can be utilized; for example one filter or a set of filters can be cleaned or exchanged while another filter or set of filters continue to operate. Filters can be any type of filter known for filtering water such as bag filters, cartridge filters, metal screen or sand (preferably silica sand). Alternatively, or in addition, centrifugal separation can be used to remove solids.

The PFAS-contaminated water can be subjected to a softening treatment to remove undesired counterions (typically Ca and Mg) because these foul the RO membrane. These softening treatments may include one or any combination of the following: ion exchange resin, lime softening (aqueous calcium hydroxide to precipitate solids); chelating agents (for example, treatment with EDTA or the like); and reverse osmosis. In any pretreatment, capture of PFAS in pretreatment media should be considered. Alternatively, or in addition, compounds such as organics can be removed by passage through hydrophobic clay to remove separated and/or emulsified hydrocarbons.

Reverse osmosis (RO) systems can remove or concentrate PFAS from water streams. PFAS-free (or PFAS-reduced) water travels through the membrane while the PFAS and salts are directed to a brine stream. Efficiency of PFAS removal and throughput is increased by implementing a cascade of RO membranes. In some embodiments, RO is utilized to increase the concentration of PFAS by at least 5 times or at least 10 times, and in some embodiments in the range of 5 to 30 times or 5 to 20 times, or 10 to 40 times. In some preferred embodiments, the influent to RO preferably has a total dissolved solids to 1200 ppm or less; however, other systems comprising larger pumps and tighter wound membranes can handle much higher TDS and achieve effective concentration in accordance with the present invention, chlorine levels of 0.5 ppm or less more preferably 0.1 ppm or less, pH between 1 and 12, more preferably between 2 and 11, the substantial absence of oil or grease, very low levels of Ba and Si (if present initially, these can be removed in a water softening step); a flowrate depending on the scale required, in some embodiments, the RO will be conducted in a range of about 3 to 5 gallons (11 L to 19 L) per minute.

A preferred embodiment of the invention is schematically illustrated in Figure 1. PFAS contaminated water entering the system can be subjected to numerous optional pretreatments including one of more of: filtration (not shown) storage in tank 102, a water softening pretreatment 104, a feed tank 106 connected to a reverse osmosis system 108. Water softening to replace other cations with sodium cations can be conducted by conventional means such as passage through an ion exchange resin. The reverse osmosis treatment (described above) produces a permeate 100 having PFAS concentrations that are reduced 10X, 100X, 1000X, 10,000X or more as compared to the PF AS contaminated water entering the system. Tn some cases, especially with relatively concentrated PFAS solution entering the system, the permeate can be subjected to additional RO treatment to bring the PFAS levels in the permeate down to a low level, such as below 70 ppt, where the water can be released to the environment; the retentate from the additional treatments can be combined with the concentrated solution or combined with incoming PFAS contaminated water such as in tank 102.

The retentate 112 typically comprises an aqueous solution having a PFAS concentration that is 10X, 100X, 1000X, 10,000X or more as compared to the PFAS contaminated water entering the system. Thus, the invention provides an energy efficient system in which greater than 90% or 99% or 99.9% or more of the PFAS in PFAS contaminated water is completely destroyed. Thus, in a preferred PFAS destruction process only 10%, or only 1%, or only 0.1%, or only 0.01% or less of the water in the PFAS contaminated water is heated to SCWO conditions.

The concentrated PFAS water can be passed through optional heat exchanger 114 which can be a tube-in-tube heat exchanger.

The concentrated PFAS water 112 passes into salt separator 116. The salt separator can have a plurality of zones that operate at different conditions of temperature or pressure. The tubes can be heated by a tube furnace that surrounds the tubes. In the case of a plurality of vertical tubes (six shown in Fig. 1, three upward and three downward) can have a relatively large inner diameter - for example, at least 1.5 cm or at least 2.0 cm or at least 1 inch (2.4 cm) - to prevent plugging. At the bottom (with respect to gravity) of each salt separator tube is a larger diameter container (collector vessel 220), preferably having an inner diameter of at least 5 cm, or at least 10 cm, or in the range of 5 to 20 cm. Preferably the collection vessel includes a diameter that is at least two times or at least four times larger than the inlet tube. The collection vessel can be heated; for example by electrical tape. The collector vessel(s) connect the inlet and outlet, preferably have a depth of at least 20 cm, or at least 30 cm, or at least 40 cm, and in some embodiments in the range of 25 to 75 cm. Salt forming in the inlet tube falls into the collection vessel where is can be continuously, or more typically, periodically removed and, if necessary, treated to remove PFAS or other contaminants. Toward the bottom of the collector vessels there is preferably a valve leading to a drain to remove brine or a briny slurry that collects at the bottom of the collector vessel. Optionally, a pump assembly can be used to evacuate the contents of the collector vessel at high pressure during operation. In some preferred embodiments, a salt separator tube inlet 222 (carrying fluid into the collector tube) extends into the collector vessel by at least 5 cm or at least 10 cm (relative to the outlet into an upward flowing tube); this enhances downward flow of the saltier fraction into the bottom of the collector tube forcing the lighter fraction out of the outlet 224. The collector vessel(s) may contain baffles to minimize turbulence and mixing near the bottom of the collector vessel(s). Typically, conditions in the bottom of the collection vessel are subcritical.

The concentrated PFAS water 112 typically enters the salt separator at subcritical but preferably near supercritical conditions so that the salt is completely dissolved in the water allowing greater residence time for salt to fall out of solution and fall into the collection vessel.. Alternatively, the water 112 can enter the salt separator at supercritical conditions. In the salt separator temperature is increased so that the solution becomes supercritical and sodium chloride and other salts precipitate from solution. Conditions (typically temperature) in successive zones of the salt separator can be controlled so that the salt becomes increasingly insoluble as it travels through the salt separator. In some embodiments, the solution entering the salt separator can be below 370 °C and increased in the range of 375 to 450 °C in the salt separator. Optionally, a fuel, such as an alcohol, could be added prior to or during the salt separation stage in order to increase temperature; this may be especially desirable since heat transfer from the tube furnaces into the aqueous composition was surprisingly found to be less than predicted by calculation.

Contact of the briny subcritical phase with the supercritical phase may allow PFAS to preferentially partition into the supercritical phase; preferably the concentration of PFAS in the briny phase is at least 20 mass% less or at least 50 mass% less than in the supercritical phase. Greater than 90 mass% or greater than 95 mass% of the NaCl (or other salts that are insoluble in supercritical water) can be removed in the salt separation stage while only 5 mass% or less, or 2 mass% or less, or 1 mass% or less or 0.5 mass% of the PFAS (or organic decomposition products) is removed in the briny phase. Different salts precipitate at different temperatures and can be removed at different stages of the salt separation.

Following the salt separator, the de-salted water can pass through a heat exchanger 118 and then is typically combined with an oxidant 120, such as hydrogen peroxide, prior to introduction into SCWO reactor 144 where any remaining PFAS is destroyed. Although in the figure provided, peroxide (or other oxidant) can be added is introduced immediately before the reactor, we more than likely will have the option to add the peroxide at various locations, including upstream of the salt separator. The advantages of adding oxidant in a plurality of locations include 1) minimizing the potential for a hot spot at the location where the peroxide is added, and 2) facilitating destruction of PFAS in the salt separator. However, a disadvantage of adding peroxide upstream of the salt separators is that corrosion can be exacerbated. The PFAS- free effluent can be passed through heat exchanger(s) such as 118, 114 to recover heat and then stored or passed out of the system as PFAS-free effluent 124.

The clean effluent preferably passes back through the second and first heat exchangers. At any point after the SCWO reactor, the cleaned water is preferably neutralized, such as by addition of sodium hydroxide. Also, if necessary, the cleaned water can be treated (for example to remove Cr or other metals) prior to disposal or return to the environment.

Supercritical Water Oxidation (SCWO)

PFAS-containing water is preferably heated prior (typically immediately prior) to entering the reactor. Heat from the reactor is used to heat water entering the reactor. The use of a heat exchanger makes the process more energy efficient, compact and extends service life of the reactor. A tube-in-tube heat exchanger is especially desirable. PFAS are destroyed and converted to carbonates, fluoride salts and sulfates. The device can be designed for 1) stationery applications or 2) transportation to a site. The stationery configuration can be employed at a permanent processing plant such as in a permanently installed water facility such as city water treatment systems. The portable units can be used in areas of low loading requirement where temporary structures are adequate. A portable unit is sized to be transported by a semi-truck or smaller enclosed space such as a trailer or shipping container. The design is adaptable to processing other organic contaminants by modifying operational parameters but without modification of the device.

A preferred SCWO reactor design is a continuous or semi -continuous system in which the (typically pre-treated) PFAS-containing aqueous solution is passed into a SCWO reactor. Because solids may form in the SCWO reactor, it is desirable for the reactor to slope downward so that solids are pulled by gravity downward and out of the reactor. In some embodiments, the flow path is straight and vertical (0°) with respect to gravity; in some embodiments, the reactor is sloped with respect to gravity, for example in the range of 5 to 70° (from vertical) or 10 to 50° or 10 to 30° or 10 to 20° and can have a bend so that flow moves in a reverse direction to provide a compact device in which flow is consistently downward with respect to gravity. Preferably, the reactor vessel is a cylindrical pipe formed of a corrosion resistant material. Desirably, the pipe has an internal diameter of at least 1 cm, preferably at least 2 cm and in some embodiments up to about 5 cm.

Flow through the components of the SCWO apparatus at supercritical conditions should be conducted under turbulent flow (Re of at least 2000, preferably in the range of 2500 to 6000). Effluent from the SCWO reactor can flow into a salt separator under supercritical conditions.

The SCWO system operates by raising the feed temperature and raising the feed pressure. The increased pressure can be due solely due to the heating (which is preferable) or can be further increased via a compressor or a high pressure (reciprocating) pump. The temperature is increased by: application of heat through the conduit (in the case of a continuous reactor) or through the reaction chamber in the case of a batch reactor, and/or by the addition of fuels such as alcohols or hydrocarbons that will be oxidized to generate heat in solution. Supercritical conditions are maintained for the oxidation; conditions within the reaction conduit or reaction chamber are preferably in the range of 374°C - 700 °C and at least 220 bar, more preferably 221 - 300 bar. In some embodiments, temperature in the SCWO reactor is maintained at 500 °C or more, or 600 °C or more and in the range of 500 to 650 °C, or 600 to 675 °C. The SCWO reactor is typically made of a high temperature resistive alloy. These alloys are useful for corrosion resistance at high temperature. In some preferred embodiments, the alloy comprises at least 50 wt% Ni and at least 5 wt% Cr. Suitable high temperature alloys are known in the SCWO art; one typical nickel -based alloy is Hastealloy® C-276.

Oxidants

The two tested feedstocks of reactant oxygen used in supercritical water oxidation for destruction of PFAS are oxygen gas (O2) and hydrogen peroxide (H2O2). In addition to, or alternative to, these two chemical species, other reactant oxygen sources or oxidizing agents could be added to destroy PFAS in the oxidation reactor. Other oxidants may comprise oxyanion species, ozone, and peroxy acids.

The preferred oxidant is hydrogen peroxide which can be added in excess (for example an excess of at least 50% or at least 100% or in the range of 50% to 300% excess) and the excess hydrogen peroxide reacting to form dioxygen and water. Fuels

At start up, the SCWO apparatus requires heating such as by external flame or resistive heating. Unless the reactive solution comprises high concentrations of PFAS or other organics, external heating is also needed during operation. As an alternative, or in addition to external heating of the SCWO apparatus, heat can be provided by the oxidation of fuels such as alcohols. Preferred fuels include methanol, ethanol, propanol (typically isopropanol), or combinations of these.

Handling The Fluorine By-Products From Destruction Of PFAS

The corrosive effluent from the SCWO reactor containing aqueous HF at high temperature (for example, around 600 °C) can flow into a mixing pipe. Cooling water, typically containing hydroxy salts, can be fed into a mixing pipe where it mixes with the corrosive effluent. The cooled effluent contains dissolved fluoride salts such as NaF.

Post Treatment

Since the SCWO process destroys essentially all of the PFAS, the treated effluent can be safely released back into the environment. In some embodiments, at least a portion of the effluent is evaporated into the air. The vapor generated will typically be at 100% humidity because it has been cooled and in equilibrium with the aqueous phase. However, the reason that there is a vapor stream is due to the carbon dioxide formed as a reaction byproduct as well as excess oxygen to ensure complete oxidation. Feeds (such as PFAS-spiked distilled water samples) that contain relatively little organic vapor generate very little (sometimes not measurable) vapor. This is safe since the PFAS has been destroyed and any remaining contaminants (such as metals, NaF, etc.) tend to have very high vapor pressure so that they do not evaporate with the water. Precipitates such as fluoride salts can be filtered or centrifuged from the effluent. PFAS-free effluent can be passed through the heat exchanger where the effluent is cooled by the PFAS-contaminated water flowing into the reactor. If necessary, the effluent may be subjected to treatments such as reverse osmosis and/or other treatments (ion exchange resins and other adsorptive media (Metsorb™), etc.) to remove metals or other contaminants prior to release or disposal of the effluent. Mobile Units

One example of a mobile unit is one that can be transported on (and preferably operated within) a trailer. For example, the system can be transported (and optionally operated) on a trailer having dimensions of 29 feet (8.8 m) in length or less, 8 ft 6 in (2.6 m) or less width, and 13 ft 6in (4.1 m) height or less. These dimensions define preferred size of a mobile system, although workers in this area will understand that other dimensions could be utilized in a mobile unit. Examples

A PFAS-containing aqueous solution was passed through a pipe that was used in a supercritical water oxidation process. The pipe was made from a high temperature alloy (C-276). Cracking of the pipe was observed after 20, 34, and 50 hours. Data from the testing is shown in Figs. 3-6 and the Table below: Table: Chemical Composition - EDS

Fracture surface Base Metal

We have subsequently found that maintaining an excess of oxidant has prevented hydrogen embrittlement.