In recent years, per- and poly-fluoroalkyl substances (PFAS) have emerged as a significant concern for water treatment professionals, environmental engineers, and regulatory bodies alike. These persistent organic pollutants, often dubbed "forever chemicals," are found in various consumer products and industrial processes, leading to widespread contamination of water sources. As the regulatory landscape evolves, it has become progressively critical for municipalities and industries to monitor and remediate PFAS. Liquid chromatography has established itself as one of the foremost analytical techniques for detecting and quantifying PFAS in environmental samples. This article aims to provide a comprehensive analysis of liquid chromatography for PFAS, covering its principles, methodologies, advantages, challenges, and emerging trends in widespread use in 2025.
Chromatography is one half of the technique covered in our guide to PFAS monitoring and analysis. For field and screening alternatives, see our article on rapid PFAS test kits; for source attribution work, see PFAS forensics; and for program design, see PFAS environmental monitoring.
According to recent EPA regulations, by mid-2025, maximum contaminant levels (MCLs) for specific PFAS compounds, including PFOA and PFOS, are being set at extremely low detection levels. With these regulations in place, accurate and efficient detection methods are essential. A study published in 2024 highlighted that nearly 50% of U.S. water supplies tested positive for at least one type of PFAS, emphasizing the urgency surrounding the issue.
The limits were finalized in 2024 rather than set in mid-2025, and their current status is summarized below. On the prevalence figure, the well-documented estimate is from a 2023 US Geological Survey study, which found that at least 45 percent of the nation’s tap water is likely to contain one or more PFAS.
Regulatory status, current as of this revision: EPA finalized the PFAS National Primary Drinking Water Regulation on April 10, 2024, setting enforceable maximum contaminant levels of 4.0 parts per trillion each for PFOA and PFOS, 10 parts per trillion each for PFHxS, PFNA and HFPO-DA (GenX), and a Hazard Index for mixtures of PFHxS, PFNA, HFPO-DA and PFBS. Public water systems must complete initial monitoring by 2027. In May 2026 EPA published two proposed rules: one would retain the PFOA and PFOS limits while allowing systems to request an extension of the compliance date from 2029 to 2031, and the other would rescind the limits for PFHxS, PFNA, HFPO-DA and the Hazard Index. Both remain proposals and related litigation is ongoing, so the status of those four is unsettled. Many states maintain their own enforceable PFAS standards, unaffected by the federal proposals. Because this area is under active rulemaking, re-check EPA and state sources before relying on any figure here.
The implications of PFAS contamination are dire:
Liquid chromatography (LC) is a separation technique used to analyze components in a mixture. The process involves a mobile phase carrying the sample through a stationary phase, where different components are separated based on their interaction with the stationary phase. This technique can be highly effective for analyzing PFAS due to its ability to resolve complex mixtures into individual components.
High-Performance Liquid Chromatography (HPLC):
Ultra-High-Performance Liquid Chromatography (UHPLC):
That list mixes up two different things: HPLC and UHPLC describe instrument capability, while reversed-phase describes the separation chemistry. In practice, essentially all regulatory PFAS analysis uses reversed-phase separation on a C18 column with a water and methanol gradient containing ammonium acetate, run on either an HPLC or a UHPLC system, coupled to a tandem mass spectrometer operating in negative electrospray ionization. PFAS are anionic surfactants rather than non-polar compounds, which is why they retain well on C18 and ionize readily in negative mode.
What matters more for a utility than the instrument is which method the laboratory is running, because the methods are not interchangeable:
Specifying the wrong method is a common and expensive error: drinking water methods are not validated for wastewater or biosolids matrices, and results from them may not be accepted by a regulator.
By 2025, new methodologies such as two-dimensional LC (2D-LC) have gained traction. 2D-LC offers enhanced separation power, allowing for the resolution of PFAS mixtures that traditional methods may struggle to analyze. Moreover, coupling LC with mass spectrometry (LC-MS) has emerged as a gold standard for PFAS analysis, enabling both quantification and identification with exceptionally high sensitivity.
The methodology’s inherent sensitivity allows for the detection of PFAS at sub-parts per trillion levels, making it suitable for complying with increasingly stringent regulatory limits. Recent validation studies indicate that LC-MS can achieve detection limits as low as 0.1 ng/L for certain PFAS types.
Liquid chromatography can analyze various PFAS compounds simultaneously, providing a comprehensive profile of contaminants in water samples. As PFAS encompasses thousands of different molecules, LC’s versatility supports the identification and quantification of targeted compounds within complex mixtures.
Liquid chromatography can be paired effectively with other analytical techniques to enhance overall data quality. For example, post-separation detection through mass spectrometry provides not only quantitative data but also structural information about the detected PFAS, which is pivotal for understanding their behavior and risks in environmental contexts.
One of the most significant challenges in using liquid chromatography for PFAS analysis is matrix interference. Environmental samples often contain a variety of co-contaminants, organic matter, and inorganic substances that can interfere with PFAS quantification. Therefore, sample preparation techniques, like solid-phase extraction (SPE), have become critical in ensuring reliable results.
Two further issues deserve equal weight, because both routinely invalidate results before the sample reaches the instrument.
Background contamination. PFAS are in the laboratory and in ordinary field equipment, so the analysis is uniquely vulnerable to false positives. Sampling protocols prohibit anything containing PTFE, including Teflon-lined caps, tubing, and tape; require HDPE or polypropylene bottles; and rule out common items such as waterproof or water-resistant clothing, adhesive notes, certain field markers, and some decontamination detergents. Field blanks and equipment blanks are not optional; without them, a low-level detection cannot be distinguished from contamination introduced during sampling.
Ion suppression. Co-eluting matrix components suppress ionization in the mass spectrometer, which biases results low, sometimes severely, in landfill leachate, wastewater, and biosolids. The defense is isotope dilution, in which isotopically labelled versions of the target compounds are added before extraction so that recovery and suppression are corrected compound by compound. This is built into Methods 533 and 1633 and is one reason they are preferred for difficult matrices.
A third, subtler issue is isomers. PFOS in particular occurs as a mixture of linear and branched forms, and the two behave differently on the column. Methods specify how branched isomers are to be integrated, and a laboratory that quantifies only the linear peak will under-report PFOS.
Investment in high-quality LC equipment and the ongoing costs associated with consumables, maintenance, and personnel training can be significant barriers for smaller water treatment facilities. As a solution, partnerships with specialized laboratories for PFAS analysis can help mitigate costs.
Although there are established methods for PFAS analysis using LC, constant changes in regulatory standards pose ongoing challenges for compliance. Water treatment facilities must continually adapt their methodologies and practices based on the latest regulatory recommendations.
As of 2025, there is a notable shift towards automation in LC systems to enhance throughput and reduce human error. Automated sample loaders and integrated data management systems can significantly streamline the workflow in laboratories.
Emerging technologies, such as portable LC systems capable of real-time monitoring of PFAS levels in the field, are becoming more economically viable and reliable. These systems enable proactive management of PFAS contamination, allowing for immediate response and risk communication.
This prediction should be treated with considerable caution. Regulatory PFAS quantification at parts per trillion requires solid-phase extraction, chromatographic separation, and tandem mass spectrometry, and no field-portable system currently delivers that combination at defensible sensitivity. Field screening tools do exist, including sensor-based and total-fluorine approaches, and they can be genuinely useful for locating hot spots, prioritizing sampling, or tracking a plume. They are screening aids, not substitutes for laboratory analysis, and results from them are not accepted for compliance reporting.
With future regulations likely to specify the analysis of an even broader suite of PFAS compounds, ongoing research into more efficient and comprehensive analytical techniques will be essential. Collaboration between government agencies, academic institutions, and the private sector will be vital in establishing new standard methodologies by 2030.
As the urgency to combat PFAS contamination intensifies, liquid chromatography continues to be an essential analytical tool that empowers municipalities, industrial operators, and environmental engineers to detect and quantify these harmful substances effectively. Its versatility in handling complex mixtures, combined with ongoing advancements, positions LC at the forefront of environmental monitoring technologies. As we look into the future, embracing innovation while navigating regulatory landscapes will be crucial for safeguarding public health and the environment against the backdrop of PFAS challenges. For water treatment professionals, the integration of liquid chromatography and commitment to ongoing education will be pivotal for ensuring compliance and enhancing public trust in water systems.