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PFAS Lead and Copper Rule



GUEST COLUMN | MAY 5, 2022




TAKING THE "FOREVER" OUT OF PFAS: THE FUTURE OF PFAS REMEDIATION

By Tamzen Macbeth and Charles Schaefer

As PFAS treatment technologies continue to emerge, CDM Smith reviews some
considerations for the existing options — and introduces a new one.

Per- and polyfluoroalkyl substances (PFAS) are some of the most difficult
chemicals to break down, or destroy, due to the strength of the carbon-fluorine
bond, the strongest bond in chemistry. Most PFAS destructive technologies
require extreme temperature or pressure, caustic conditions, or harsh chemical
additives and consume tremendous amounts of energy.

Currently, no destructive technology has been demonstrated at full scale for
large volumes of contaminated water. In addition, drinking water providers have
relied on conventional technologies using sorption, ion exchange, or
sequestration to separate and concentrate PFAS into other media or waste
streams. However, this poses the risk of re-releasing these “forever” chemicals
back into the environment. As such, destruction is a critical step in solving
the global PFAS crisis.

Today, destruction technologies such as electrochemical oxidation (ECO), plasma,
and supercritical water oxidation have demonstrated abilities to break down
PFAS. To integrate these promising technologies for future water treatment,
treatment trains that first separate and concentrate PFAS to reduce the volume
are necessary to make these (and other) destructive treatments viable.

Separate And Concentrate

To address urgent needs to remove PFAS from drinking water supplies, we have
developed methods to evaluate, design, and implement at full scale reliable
technologies such as granular activated carbon (GAC), ion exchange (IX), and
reverse osmosis (RO) for PFAS treatment. However, these technologies still
generate PFAS-laden waste streams with volumes that are often impractical to
treat with destructive technologies. Our researchers have been rigorously
testing new ways to separate and concentrate PFAS that can be used along with or
in place of these conventional treatments.

One particularly promising technology relies on using air bubbles to “strip”
PFAS out of water and into foams, which are condensed to highly concentrated
PFAS solutions. This technology has achieved concentration factors of 90,000
times at full scale and ongoing optimizations are working to achieve
concentration factors of one million times. In other words, one million gallons
of PFAS could be treated generating approximately one to 10 gallons of PFAS
concentrate for destructive treatment. Together with EPOC Enviro, CDM Smith has
been rigorously testing surface-active foam fractionation (SAFF®) in our
treatment train concept. We recently completed the first U.S. pilot application,
successfully treating 265,000 gallons of PFAS-contaminated groundwater and
generating three gallons of PFAS concentrate. The concentrate has been sent to
our laboratory in Denver, where it is being treated with our pilot destructive
ECO system.

Destroy

Numerous PFAS destruction technologies are under development (see
https://pfas-1.itrcweb.org/12-treatment-technologies/). Promising destruction
technologies that have progressed from bench- to pilot-scale include ECO,
plasma, UV-reductive, hydrothermal, and supercritical water oxidation. These
technologies have successfully treated an array of water samples highly
concentrated with PFAS and are considered ideal for destructive treatment,
including one or more of the following:

 * Aqueous film-forming foam (AFFF) concentrates
 * Groundwater within PFAS source areas
 * Remediation waste streams (such as wastewater generated from regeneration of
   GAC or regenerable IX resin; foam-fractionation, soil-washing, rejected-RO
   concentrates; chemical-or electro-coagulation.
 *  Landfill or biosolid leachate



Electrochemical Oxidation (ECO)

Our researchers have proven ECO to reduce high-concentration PFAS effectively,
typically achieving reductions of 90% to 99.999% in laboratory and pilot
studies.

ECO uses an electrochemical cell to generate an electric current between a
reactive anode and cathode (the electrodes). The process degrades PFAS through
two mechanisms:

 * Anodic oxidation (direct electrolysis) – PFAS adsorb onto an anode surface
   and are destroyed directly at the electrode by a direct electron transfer
   reaction.
 * Indirect oxidation – Strong oxidizing and nonselective radicals (such as
   hydroxyl, oxygen, sulfate, and carbonate) are generated in situ that react
   with, and break down, PFAS in the bulk liquid reactions.

Choosing A Destruction Approach

Because of the high demand for destructive PFAS technologies, they are often
promoted hastily without demonstrating complete destruction (e.g.,
defluorination) and without confidence the technology can meet stringent
effluent discharge requirements. The feasibility of these technologies must be
carefully considered for each new application. To effectively develop a
treatment train approach, technology compatibility, engineering constraints, and
O&M requirements must be considered.

Currently, technology evaluation for a particular site/application must include
bench- and pilot-scale tests to demonstrate technology and incorporate economic
feasibility in the selection process. A thoughtful approach will ensure the
system can meet required treatment volumes, rates, and discharge criteria.

The development and commercialization of PFAS destruction technologies is in its
infancy. Technology benefits and limitations should be discussed with technology
providers, including:

 * Energy demand and efficiency to achieve desired treatment goals at the scale
   required for the system.
 * Health and safety concerns.
 * O&M requirements and longevity of the system.
 * Scale of available systems and feasibility of operating largescale systems,
   if required.
 * Potential for incomplete PFAS destruction resulting in accumulation of
   fluorinated intermediates that are generated but not measurable.
 * Feasibility of achieving stringent (i.e., very low) treatment requirements.
   Often a treatment train approach may be needed before effluent discharge.
 * Effectiveness in destroying all PFAS chemicals, including short-chain PFAS
   (which are generally harder to treat) and precursors as sources of
   perfluoroalkyl acids (PFAAs).
 * Generation of non-PFAS toxic byproducts, such as perchlorate or hydrofluoric
   acid. For instance, perchlorate is known to be formed during electrochemical
   oxidation treatment due to the aggressive oxidation of chloride in the
   feedwater. Although perchlorate can be addressed easily, treatment systems
   must account for, and treat, perchlorate in the process

CDM Smith has been investigating PFAS destruction for nearly a decade. Our
approach to assessing PFAS destructive technologies at a site includes
treatability testing at the bench-, pilot-, and full-scale levels, using three
lines of evidence to confirm complete PFAS destruction.

About The Authors

Tamzen Macbeth, PhD, PE, BCEE, is an internationally recognized remediation
expert who develops innovative, cost-effective technologies for contaminated
soil, sediment, and groundwater. Tamzen has helped advance countless
technologies within her field, publishing more than 100 technical papers,
training manuals, and guidance documents on remediation topics.



Charles Schaefer Jr., PhD, is an environmental scientist and the director of CDM
Smith’s Bellevue, Washington, Research and Testing Laboratory. Charles has
received multiple awards for his research into PFAS, most recently earning a top
prize from the American Society of Civil Engineers (ASCE) for investigating AFFF
with the U.S. Department of Defense.


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